Basic Information
Threat: Urban development
Threat Code: URBDEV
Threat Map
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Legend

Threat Background

MSP Threat/Stressor Background

Goals and Objectives

Goal: The goal for managing the effects of urban development in the preserves is to better understand and reduce the impacts on Conserved Lands where urban development is reducing the population levels and/or viability of MSP species populations.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021
MGT-RSUP-TRASH URBDEV-1

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

From 2017-2021, support land managers in preventing or cleaning up dump sites & trash collection.

Action Statement Action status Projects
RSUP-1 Provide support to land managers for enforcement, signage or fencing, public outreach, or cleanup projects. Available for implementation
Criteria Deadline year
Project reports submitted within 1 Year of Management Efforts 2021
Threat Name Threat Code
Urban developmentURBDEV

Species objectives associated with this threat

regional and/or local PRE 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-FMGT ACAILI-1

Management units: 3, 4, 5, 6

Starting in 2017, reduce the potential impact of fire for at risk large populations of San Diego thornmint (see occurrence table) by reducing fuel loads of invasive annuals

Action Statement Action status Projects
IMP-1 Manage thatch and invasive annuals every 3-5 years to reduce fire threat for populations of San Diego thornmint most at risk of fire (populations with ignition probability or fire frequency > 3 or that have burned since 2003) available for implementation
IMP-2 Submit project metadata, monitoring datasets and report with management actions to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Fuel Loads and Invasive Grasses Reduced for at Risk Populations 2021
Code Obj. code Statement
ACAILI-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG ACAILI-2

Management units: 3, 4, 5, 6

Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, occurrence status, habitat and threats data, and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ACAILI-3 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego thornmint occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ACAILI-4 MGT-DEV-BMP In 2017, continue refining BMPs developed for San Diego thornmint (CBI 2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal studies at Mission Trails and South Crest) and based on research studies (e.g., seed bulking guidelines, seed transfer zones).
ACAILI-5 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for San Diego thornmint occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG ACAILI-3

Management units: 3, 4, 5, 6

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego thornmint occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. available for implementation San Diego Thornmint Restoration
IMP-2 Submit project metadata and management data to MSP web portal. available for implementation San Diego Thornmint Restoration
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ACAILI-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
ACAILI-4 MGT-DEV-BMP In 2017, continue refining BMPs developed for San Diego thornmint (CBI 2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal studies at Mission Trails and South Crest) and based on research studies (e.g., seed bulking guidelines, seed transfer zones).
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
ACAILI-9 MGT-PRP-SBPL In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional NFO 2017 SO
MGT-DEV-BMP ACAILI-4

Management units: 3, 4, 5, 6

In 2017, continue refining BMPs developed for San Diego thornmint (CBI 2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal studies at Mission Trails and South Crest) and based on research studies (e.g., seed bulking guidelines, seed transfer zones).

Action Statement Action status Projects
DEV-1 Refine BMPs prepared by CBI in the San Diego Thornmint Adaptive Management Framework (2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal and South County Grasslands projects) and based on research studies (e.g., seed bulking guidelines, seed transfer) In progress
DEV-2 Submit project metadata, management datasets and BMP report to MSP web portal. In progress
Criteria Deadline year
BMPs for San Diego Thornmint Prepared by 2018 2021
Code Obj. code Statement
ACAILI-3 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego thornmint occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
regional NFO 2018 SO
MGT-PRP-MGTPL ACAILI-6

Management units: 3, 4, 5, 6

In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Diego thornmint section in the MSP Rare Plant Management Plan. waiting for precedent action
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to San Diego thornmint occurrences. waiting for precedent action
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. waiting for precedent action
PRP-4 Develop an implementation plan for San Diego thornmint that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. waiting for precedent action
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2019 Completed Section for San Diego Thornmint in the MSP Rare Plant Management Plan. 2021
Code Obj. code Statement
ACAILI-1 MGT-IMP-FMGT Starting in 2017, reduce the potential impact of fire for at risk large populations of San Diego thornmint (see occurrence table) by reducing fuel loads of invasive annuals
ACAILI-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
ACAILI-3 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego thornmint occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ACAILI-4 MGT-DEV-BMP In 2017, continue refining BMPs developed for San Diego thornmint (CBI 2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal studies at Mission Trails and South Crest) and based on research studies (e.g., seed bulking guidelines, seed transfer zones).
ACAILI-5 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for San Diego thornmint occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
ACAILI-7 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for San Diego thornmint in the MSP Rare Plant Management Plan.
ACAILI-8 MON-IMP-MGTPL In 2019, begin monitoring the effectiveness of implementation of the highest priority management actions identified in the San Diego thornmint section of the MSP Rare Plant Management Plan.
ACAILI-9 MGT-PRP-SBPL In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional and/or Local NFO 2019, 2020, 2021 SO
MGT-IMP-MGTPL ACAILI-7

Management units: 3, 4, 5, 6

In 2019, begin implementing highest priority management actions identified for San Diego thornmint in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2023, =2 High Priority Management Actions Implemented for San Diego Thornmint from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
ACAILI-8 MON-IMP-MGTPL In 2019, begin monitoring the effectiveness of implementation of the highest priority management actions identified in the San Diego thornmint section of the MSP Rare Plant Management Plan.
ACAILI-9 MGT-PRP-SBPL In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional and/or Local NFO 2019, 2020, 2021 SO
MON-IMP-MGTPL ACAILI-8

Management units: 3, 4, 5, 6

In 2019, begin monitoring the effectiveness of implementation of the highest priority management actions identified in the San Diego thornmint section of the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
ACAILI-7 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for San Diego thornmint in the MSP Rare Plant Management Plan.
Regional NFO 2018 SO
MGT-PRP-SBPL ACAILI-9

Management units: 3, 4, 5, 6

In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Diego thornmint section of the MSP Seed Collection, Banking and Bulking Plan. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2019, Completed Section for San Diego thornmint in the MSP Seed Collection Banking and Bulking Plan 2021
Code Obj. code Statement
ACAILI-5 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for San Diego thornmint occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional and/or Local NFO 2019, 2020, 2021 SO
MGT-IMP-SBPL ACAILI-10

Management units: 3, 4, 5, 6

In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for San Diego thornmint to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2023, =2 Highest Priority Actions Implemented for San Diego thornmint from the MSP Seed Banking and Bulking Plan 2021
Code Obj. code Statement
ACAILI-5 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for San Diego thornmint occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
ACAILI-9 MGT-PRP-SBPL In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional NFO 2017 SO
MON-RES-SPEC ACAILI-11

Management units: 3, 4, 5, 6

In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for San Diego thornmint and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.

Action Statement Action status Projects
RES-1 Test soils at potential expansion sites and compare to occupied reference sites to determine site suitability based on soils. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-2 Prepare habitat suitability models under current environmental conditions and for different scenarios of climate change to delineate potential future habitat. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-3 Collect covariate data on vegetation composition and cover (alliance and association-level mapping), soils, invasive plants and other threats for selected populations. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-4 Prioritize locations for conservation, management, and future surveys based on predicted distributions and environmental correlates. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-5 Submit project metadata, monitoring data and report to MSP web portal. In progress Enhancing the Resilience of Edaphic Endemic Plants
Criteria Deadline year
Refined Models and Prioritized Future Survey Locations for San Diego Thornmint by 2018 2021
Code Obj. code Statement
ACAILI-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
ACAILI-5 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for San Diego thornmint occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
ACAILI-6 MGT-PRP-MGTPL In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG ACMPRO-1

Management units: 1, 7

From 2017-2012, inspect extant Nuttall's acmispon occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ACMPRO-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Nuttall's acmispon occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ACMPRO-4 MGT-PRP-SBPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
ACMPRO-6 MGT-PRP-MGTPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG ACMPRO-2

Management units: 1, 7

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Nuttall's acmispon occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. some occurrences are in progress
IMP-2 Submit project metadata and management data to the MSP Web Portal. some occurrences are in progress Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ACMPRO-1 MON-IMP-IMG From 2017-2012, inspect extant Nuttall's acmispon occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
Regional NFO 2017 SO
MGT-PRP-SBPL ACMPRO-4

Management units: 1, 7

In 2017, begin preparing a section for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan. Available for implementation
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. Available for implementation
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. Available for implementation
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). Available for implementation
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. Available for implementation
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. Available for implementation
Criteria Deadline year
By 2018, Completed Nuttall's Acmispon Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
ACMPRO-1 MON-IMP-IMG From 2017-2012, inspect extant Nuttall's acmispon occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
ACMPRO-3 MGT-IMP-IEX From 2017 through 2019, enhance and expand the 4 Nuttall's acmispon occurrences at Mariner's Point, South Shores, South Carlsbad State Beach and Cardiff State Beaches (see occurrence table) and establish a new occurrence at Stony Point in Mission Bay. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence
ACMPRO-5 MGT-IMP-SBPL In 2018, begin implementing the Nuttall's acmispon section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
ACMPRO-6 MGT-PRP-MGTPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
Regional and/or Local NFO 2018, 2019, 2020, 2021 SO
MGT-IMP-SBPL ACMPRO-5

Management units: 1, 7

In 2018, begin implementing the Nuttall's acmispon section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. Available for implementation
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. Available for implementation
Criteria Deadline year
By 2021, =1 Highest Priority Action Implemented for Nuttall's Acmispon from the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
ACMPRO-4 MGT-PRP-SBPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
regional NFO 2017 SO
MGT-PRP-MGTPL ACMPRO-6

Management units: 1, 7

In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Nuttall's acmispon in the MSP Rare Plant Management Plan. available for implementation
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Nuttall's acmispon occurrences. available for implementation
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. available for implementation
PRP-4 Develop an implementation plan for Nuttall's acmispon that prioritizes management actions for the nex 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. available for implementation
PRP-5 Submit project metadata, project datasets, and the MSP Rare Plant Management Plan to the MSP Web Portal. available for implementation
Criteria Deadline year
By 2018, Completed Nuttall's Acmispon Section in the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
ACMPRO-1 MON-IMP-IMG From 2017-2012, inspect extant Nuttall's acmispon occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
ACMPRO-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Nuttall's acmispon occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ACMPRO-3 MGT-IMP-IEX From 2017 through 2019, enhance and expand the 4 Nuttall's acmispon occurrences at Mariner's Point, South Shores, South Carlsbad State Beach and Cardiff State Beaches (see occurrence table) and establish a new occurrence at Stony Point in Mission Bay. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence
ACMPRO-4 MGT-PRP-SBPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
ACMPRO-5 MGT-IMP-SBPL In 2018, begin implementing the Nuttall's acmispon section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
ACMPRO-7 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.
ACMPRO-8 MON-IMP-MGTPL In 2018, monitor effectiveness of implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2018, 2019, 2020, 2021 SO
MGT-IMP-MGTPL ACMPRO-7

Management units: 1, 7

In 2018, begin implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2021, =1 High Priority Management Action Implemented for Nuttall's Acmispon from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
ACMPRO-6 MGT-PRP-MGTPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
ACMPRO-8 MON-IMP-MGTPL In 2018, monitor effectiveness of implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2018, 2019, 2020, 2021 SO
MON-IMP-MGTPL ACMPRO-8

Management units: 1, 7

In 2018, monitor effectiveness of implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
ACMPRO-6 MGT-PRP-MGTPL In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
ACMPRO-7 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Nuttall's acmispon in the MSP Rare Plant Management Plan.

regional NFO 2017, 2018 SL
MGT-IMP-IEX AGETRI-1

Management units: 3, 4, 5, 6, 9, 10, 11

From 2017-2018, support the existing efforts to restore the El Monte ponds and any other on-going habitat restoration projects for the benefit of nesting tricolored blackbird. This objective to be incorporated into the Tricolored Blackbird Management Plan after 2018.

Action Statement Action status Projects
IMP-1 Submit project metadata, data, and annual reports documenting project methods and results to the MSP Web Portal. Available for implementation
Criteria Deadline year
Restoration of El Monte ponds implemented for Tricolored Blackbird 2021
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MON-RSUP-SPEC AGETRI-2

Management units: 3, 4, 5, 6, 9, 10, 11

From 2017 to 2021, support statewide survey efforts for Tricolored blackbird held every 3 years.

Action Statement Action status Projects
RSUP-1 Submit monitoring data and management recommendations to MSP web portal available for implementation
Criteria Deadline year
Participate in Surveys every 3 Years 2021
local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG AGETRI-3

Management units: 3, 4, 5, 6, 9, 10, 11

Beginning in 2017, annually inspect suitable nesting habitat at current and historically occupied sites (see occurrence table) to determine management needs (including need for additional water) taking care not to disturb nesting tricolored blackbirds, and use a regional IMG monitoring protocol to collect covariate data on human activities and other threats to determine management needs.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol surveys to determine management needs (including need for additonal water) taking care not to disturb nesting tricolored blackbirds, available for implementation Tricolored Blackbird (Agelaius tricolor) Surveys
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. available for implementation
IMP-3 Submit monitoring data and management recommendations to MSP web portal available for implementation Tricolored Blackbird (Agelaius tricolor) Surveys
Criteria Deadline year
Annual IMG monitoring of Tricolored Blackbird completed 2021
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG AGETRI-4

Management units: 3, 4, 5, 6, 9, 10, 11

Beginning in 2017, conduct routine management actions identified through the IMG regional protocol monitoring.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement and adding additonal water to ponded sites. available for implementation
IMP-2 Submit project metadata and management data to the MSP web portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
regional NFO 2018 SL
MGT-PRP-MGTPL AGETRI-5

Management units: 3, 4, 5, 6, 9, 10, 11

In 2018, prepare a management plan for tricolored blackbird that prioritizes management actions to protect nesting sites from disturbance and enhances habitat using data from annual IMG monitoring.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. Available for implementation
PRP-2 Develop an implementation plan for tricolored blackbird that prioritizes management actions for the next five years. Available for implementation
PRP-3 Submit management plan to MSP web portal Available for implementation
Criteria Deadline year
Management Plan for Tricolored Blackbird prepared by 2019 2021
regional and/or local NFO 2019, 2020, 2021 SL
MGT-IMP-MGTPL AGETRI-6

Management units: 3, 4, 5, 6, 9, 10, 11

Beginning in 2019, implement the highest priority management actions for tricolored blackbird on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the management plan. waiting for precedent action
IMP-2 Submit project data and management actions to MSP web portal waiting for precedent action
Criteria Deadline year
Management actions implemented for Tricolored Blackbird 2021
regional and/or local NFO 2019, 2020, 2021 SL
MON-IMP-MGTPL AGETRI-7

Management units: 3, 4, 5, 6, 9, 10, 11

Beginning in 2019, monitor the effectiveness of management actions implemented for tricolored blackbird on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring Completed within one year of management actions and Report Submitted 2021

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG AMBPUM-1

Management units: 3, 4, 6, 8

Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
AMBPUM-6 MGT-PRP-SBPL In 2020, begin preparing a section for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG AMBPUM-2

Management units: 3, 4, 6, 8

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. available for implementation
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal.
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-1 MON-IMP-IMG Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
regional NFO 2020 SO
MGT-PRP-MGTPL AMBPUM-3

Management units: 3, 4, 6, 8

In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for San Diego ambrosia in the MSP Rare Plant Management Plan. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to San Diego ambrosia occurrences. on hold
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-4 Develop an implementation plan for San Diego ambrosia that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata, management datasets and the MSP Rare Plant Management Plan to MSP web portal on hold
Criteria Deadline year
By 2021, Completed San Diego Ambrosia Section in the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-1 MON-IMP-IMG Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-4 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for San Diego ambrosia in the MSP Rare Plant Management Plan.
AMBPUM-6 MGT-PRP-SBPL In 2020, begin preparing a section for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional and/or Local NFO 2021 SO
MGT-IMP-MGTPL AMBPUM-4

Management units: 3, 4, 6, 8

In 2021, begin implementing highest priority management actions identified for San Diego ambrosia in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Using BMPs, conduct invasive plant control annually until success criteria are met and then as needed thereafter. waiting for precedent action
IMP-2 Submit project metadata, management data and monitoring data to MSP web portal. waiting for precedent action
Criteria Deadline year
By 2025, >1 High priority Management Actions for San Diego Ambrosia initiated from the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
AMBPUM-5 MON-IMP-MGTPL In 2021, monitor the effectiveness of highest priority management actions for San Diego Ambrosia in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SO
MON-IMP-MGTPL AMBPUM-5

Management units: 3, 4, 6, 8

In 2021, monitor the effectiveness of highest priority management actions for San Diego Ambrosia in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
AMBPUM-4 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for San Diego ambrosia in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2020 SO
MGT-PRP-SBPL AMBPUM-6

Management units: 3, 4, 6, 8

In 2020, begin preparing a section for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan. On hold
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. On hold
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. On hold
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). On hold
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. On hold
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. On hold
Criteria Deadline year
By 2021, Completed San Diego Ambrosia section in the MSP Seed Collection Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-1 MON-IMP-IMG Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
AMBPUM-7 MGT-IMP-SBPL In 2021, begin implementing the San Diego Ambrosia section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seed at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
Regional and/or Local NFO 2021 SO
MGT-IMP-SBPL AMBPUM-7

Management units: 3, 4, 6, 8

In 2021, begin implementing the San Diego Ambrosia section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seed at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2025, >1 San Diego Ambrosia Seed Collection, Banking and Bulking initiated 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AMBPUM-3 MGT-PRP-MGTPL In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
AMBPUM-6 MGT-PRP-SBPL In 2020, begin preparing a section for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG ANACAL-1

Management units: 3, 4, 5, 6, 8, 9, 10, 11

Annually inspect known areas occupied by arroyo toad to identify and reduce threats that can be managed at the local scale including road crossings, illegal encroachment, off-road vehicle use, non-native plants, trash dumping, grazing by livestock, and incompatible human recreation. Where possible, restrict access to arroyo toad upland and breeding habitats to help prevent disturbance to all arroyo toad life history stages (eggs, larvae, metamorphs and adults). Activities should be restricted in upland habitat year-round and in breeding habitat during the core of the breeding season (March to July).

Action Statement Action status Projects
IMP-1 Using a regional "IMG" monitoring protocol, annually inspect significant Arroyo toad occurrences to assess status and quantify potential threats to determine management needs. AID_20161229_1831_100 Available for implementation
IMP-2 Roads should be examined for high risk areas for arroyo toad crossing and use. Only slow moving vehicles (<5mph) with an occupant experienced in arroyo toad identification should be allowed on high risk roads after sunset (Zimmitti and Mahrdt 1999). Available for implementation
IMP-3 An education program should be implemented that promotes the value of the arroyo toad and informs the public of restrictions and the importance of not disturbing the wildlife. Available for implementation
IMP-4 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. Available for implementation
IMP-5 Submit monitoring and management recommendations to the MSP web portal Available for implementation
Criteria Deadline year
Annual IMG monitoring of Arroyo toad completed 2021
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG ANACAL-2

Management units: 3, 4, 5, 6, 8, 9, 10, 11

Beginning in 2018, conduct routine management actions for arroyo toad identified through the IMG regional protocol monitoring, including protecting populations from detrimental human use (e.g. ORV, trampling, altered hydrology), removing invasive plants, and removing aquatic predators and exotic species (which compete and/or prey on arroyo toads, primarily young) within the known arroyo toad habitat.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from human disturbance, controlling invasive plants, and removing invasive aquatic animals. available for implementation
IMP-2 Submit project metadata and management data to MSP web portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Code Obj. code Statement
ANACAL-1 MON-IMP-IMG Annually inspect known areas occupied by arroyo toad to identify and reduce threats that can be managed at the local scale including road crossings, illegal encroachment, off-road vehicle use, non-native plants, trash dumping, grazing by livestock, and incompatible human recreation. Where possible, restrict access to arroyo toad upland and breeding habitats to help prevent disturbance to all arroyo toad life history stages (eggs, larvae, metamorphs and adults). Activities should be restricted in upland habitat year-round and in breeding habitat during the core of the breeding season (March to July).
regional NFO 2020, 2021 SO
MON-SURV-SPEC ANACAL-4

Management units: 3, 4, 5, 6, 8, 9, 10, 11

In 2020 and 2021 (assuming adequate rainfall levels), conduct comprehensive arroyo toad surveys using USGS survey protocols throughout the MSPA on Conserved Lands in known occupied and potential habitat to determine current distribution and status of arroyo toad, collect data on threats and habitat covariates, and identify management needs.

Action Statement Action status Projects
SURV-1 Survey known occupied and potantial habitat on Conserved Lands across the MSPA to determine the distribution and abundance of arroyo toad on Conserved Lands. Available for implementation
SURV-2 Collect data on threats and identify management needs to support self-sustaining occurrences. Available for implementation
SURV-3 Continue to collect genetic samples from all arroyo toads captured. Available for implementation
SURV-4 Submit survey data and management recommendations to MSP web portal Available for implementation
Criteria Deadline year
Comprehensive surveys completed for Arroyo toad by 2021 2021
Code Obj. code Statement
ANACAL-1 MON-IMP-IMG Annually inspect known areas occupied by arroyo toad to identify and reduce threats that can be managed at the local scale including road crossings, illegal encroachment, off-road vehicle use, non-native plants, trash dumping, grazing by livestock, and incompatible human recreation. Where possible, restrict access to arroyo toad upland and breeding habitats to help prevent disturbance to all arroyo toad life history stages (eggs, larvae, metamorphs and adults). Activities should be restricted in upland habitat year-round and in breeding habitat during the core of the breeding season (March to July).
regional NFO 2017, 2018, 2019 SO
MGT-PRP-MGTPL ANACAL-5

Management units: 3, 4, 5, 6, 8, 9, 10, 11

In 2017, continue to convene with the working group of land managers, scientists, wildlife agencies, and local biologists knowledgeable in arroyo toad to review existing conditions of known occurrences on Conserved Lands, to prepare a plan for management of arroyo toad which considers each site, and to develop a regional monitoring strategy.

Action Statement Action status Projects
PRP-1 Convene working group meetings to review existing conditions of known occurrences. in progress
PRP-2 Use habitat models developed by USGS and results from survey and genetic analyses to identify suitable areas for long-term management. in progress
PRP-3 Conduct site visits as necessary to identify appropriate management actions. in progress
PRP-4 Develop an arroyo toad management plan. The plan should prioritize management actions for the next five years and detail tasks, lead entities, responsibilities, timelines, and budgets. in progress
PRP-5 Submit management plan to MSP web portal in progress
Criteria Deadline year
Arroyo toad management plan completed by 2018 2021
Code Obj. code Statement
ANACAL-1 MON-IMP-IMG Annually inspect known areas occupied by arroyo toad to identify and reduce threats that can be managed at the local scale including road crossings, illegal encroachment, off-road vehicle use, non-native plants, trash dumping, grazing by livestock, and incompatible human recreation. Where possible, restrict access to arroyo toad upland and breeding habitats to help prevent disturbance to all arroyo toad life history stages (eggs, larvae, metamorphs and adults). Activities should be restricted in upland habitat year-round and in breeding habitat during the core of the breeding season (March to July).
ANACAL-2 MGT-IMP-IMG Beginning in 2018, conduct routine management actions for arroyo toad identified through the IMG regional protocol monitoring, including protecting populations from detrimental human use (e.g. ORV, trampling, altered hydrology), removing invasive plants, and removing aquatic predators and exotic species (which compete and/or prey on arroyo toads, primarily young) within the known arroyo toad habitat.
ANACAL-3 MON-RES-GEN From 2017 to 2021, continue genetic studies of the arroyo toad in San Diego Co. (using genetic material collected during past and present regional surveys) to evaluate the degree of genetic variation within and between populations and to possibly identify genetic bottlenecks or barriers; this information will also be used to determine source populations to use in re-establishing arroyo toads in previously occupied areas.
ANACAL-4 MON-SURV-SPEC In 2020 and 2021 (assuming adequate rainfall levels), conduct comprehensive arroyo toad surveys using USGS survey protocols throughout the MSPA on Conserved Lands in known occupied and potential habitat to determine current distribution and status of arroyo toad, collect data on threats and habitat covariates, and identify management needs.
regional NFO 2018, 2019, 2020, 2021 SO
MGT-IMP-MGTPL ANACAL-6

Management units: 3, 4, 5, 6, 8, 9, 10, 11

Beginning in 2018, implement high priority actions identified in the Arroyo Toad Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management actions and report to MSP web portal waiting for precedent action
Criteria Deadline year
High priority management actions implemented for Arroyo toad 2021
Code Obj. code Statement
ANACAL-1 MON-IMP-IMG Annually inspect known areas occupied by arroyo toad to identify and reduce threats that can be managed at the local scale including road crossings, illegal encroachment, off-road vehicle use, non-native plants, trash dumping, grazing by livestock, and incompatible human recreation. Where possible, restrict access to arroyo toad upland and breeding habitats to help prevent disturbance to all arroyo toad life history stages (eggs, larvae, metamorphs and adults). Activities should be restricted in upland habitat year-round and in breeding habitat during the core of the breeding season (March to July).
ANACAL-2 MGT-IMP-IMG Beginning in 2018, conduct routine management actions for arroyo toad identified through the IMG regional protocol monitoring, including protecting populations from detrimental human use (e.g. ORV, trampling, altered hydrology), removing invasive plants, and removing aquatic predators and exotic species (which compete and/or prey on arroyo toads, primarily young) within the known arroyo toad habitat.
ANACAL-3 MON-RES-GEN From 2017 to 2021, continue genetic studies of the arroyo toad in San Diego Co. (using genetic material collected during past and present regional surveys) to evaluate the degree of genetic variation within and between populations and to possibly identify genetic bottlenecks or barriers; this information will also be used to determine source populations to use in re-establishing arroyo toads in previously occupied areas.
ANACAL-4 MON-SURV-SPEC In 2020 and 2021 (assuming adequate rainfall levels), conduct comprehensive arroyo toad surveys using USGS survey protocols throughout the MSPA on Conserved Lands in known occupied and potential habitat to determine current distribution and status of arroyo toad, collect data on threats and habitat covariates, and identify management needs.
ANACAL-5 MGT-PRP-MGTPL In 2017, continue to convene with the working group of land managers, scientists, wildlife agencies, and local biologists knowledgeable in arroyo toad to review existing conditions of known occurrences on Conserved Lands, to prepare a plan for management of arroyo toad which considers each site, and to develop a regional monitoring strategy.
regional NFO 2018, 2019, 2020, 2021 SO
MON-IMP-MGTPL ANACAL-7

Management units: 3, 4, 5, 6, 8, 9, 10, 11

Beginning in 2018, monitor the effectiveness of management actions implemented for the arroyo toad.

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Effectiveness of implementing high priority arroyo toad management actions determined 2021

regional NFO 2017 SL
MON-RES-SPEC ANTPAL-1

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2017-2018, finalize the results of research begun in 2015 on pallid bats to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas, and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat, assess threats to bats at all preserves where they occur, and develop management recommendations.

Action Statement Action status Projects
RES-1 Submit project metadata, survey data, and report with management recommendations to the MSP web portal. in progress
Criteria Deadline year
Pallid Bat Surveys and Reports Completed in 2017. 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-4 MGT-PRP-MGTPL In 2018-2019, prepare a management plan for pallid bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the pallid bat research study.
local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG ANTPAL-2

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2017, inspect the vicinity of pallid bat roosts on an annual basis (see occurrence table), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol surveys to quantify signs of human activity near occupied or potential roosts and to identify other potential threats. Care should be taken to avoid disturbing roosting bats. available for implementation Pallid Bat Surveys - Sweetwater Marsh
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. available for implementation Pallid Bat Surveys - Sweetwater Marsh
IMP-3 Submit monitoring data and management recommendations to MSP web portal available for implementation Pallid Bat Surveys - Sweetwater Marsh
Criteria Deadline year
Annual IMG monitoring of Pallid bat completed 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-1 MON-RES-SPEC In 2017-2018, finalize the results of research begun in 2015 on pallid bats to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas, and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat, assess threats to bats at all preserves where they occur, and develop management recommendations.
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG ANTPAL-3

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2017, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting occurrences from disturbance through fencing, signage, and enforcement.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. available for implementation
IMP-2 Submit project metadata and management data to the MSP web portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-2 MON-IMP-IMG Beginning in 2017, inspect the vicinity of pallid bat roosts on an annual basis (see occurrence table), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
regional NFO 2018, 2019 SL
MGT-PRP-MGTPL ANTPAL-4

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2018-2019, prepare a management plan for pallid bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the pallid bat research study.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. available for implementation Pallid Bat Surveys - Sweetwater Marsh
PRP-2 Develop a management plan for pallid bat that prioritizes management actions for the next five years. waiting for precedent action Pallid Bat Surveys - Sweetwater Marsh
PRP-3 Identify areas where pallid bat and Townsend?s big-eared bat management can be complimentary. waiting for precedent action Pallid Bat Surveys - Sweetwater Marsh
PRP-4 Submit management plan to MSP web portal waiting for precedent action Pallid Bat Surveys - Sweetwater Marsh
Criteria Deadline year
Management Plan for Pallid bat prepared by 2018 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-1 MON-RES-SPEC In 2017-2018, finalize the results of research begun in 2015 on pallid bats to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas, and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat, assess threats to bats at all preserves where they occur, and develop management recommendations.
ANTPAL-2 MON-IMP-IMG Beginning in 2017, inspect the vicinity of pallid bat roosts on an annual basis (see occurrence table), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
ANTPAL-3 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting occurrences from disturbance through fencing, signage, and enforcement.
regional and/or local NFO 2020, 2021 SL
MGT-IMP-MGTPL ANTPAL-5

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2020, implement highest priority management actions for pallid bats on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the implementation plan. waiting for precedent action
IMP-2 Submit project data and management actions to MSP web portal waiting for precedent action
Criteria Deadline year
Management actions implemented for Pallid bat 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-4 MGT-PRP-MGTPL In 2018-2019, prepare a management plan for pallid bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the pallid bat research study.
regional and/or local NFO 2020, 2021 SL
MON-IMP-MGTPL ANTPAL-6

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2020, monitor the effectiveness of management actions implemented for pallid bats on Conserved Lands.

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Effectiveness of Implementing Pallid Bat High Priority Actions Determined 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
ANTPAL-5 MGT-IMP-MGTPL Beginning in 2020, implement highest priority management actions for pallid bats on Conserved Lands.

Regional NFO 2019 SL
MON-SURV-SPEC APHBLI-3

Management units: 1, 7

In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. On hold
SURV-2 Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. On hold
Criteria Deadline year
Surveys and Report Completed by 2020 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
APHBLI-1 MON-IMP-IMG Beginning in 2017, inspect extant aphanisma occurrence(s) on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.
APHBLI-4 MGT-PRP-SBPL In 2021, begin preparing a section for aphanisma in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
APHBLI-5 MGT-PRP-MGTPL In 2021, begin preparing a section for aphanisma in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences and/or establishment of new occurrences in suitable habitat as needed to achieve at least 3 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2021 SL
MGT-PRP-SBPL APHBLI-4

Management units: 1, 7

In 2021, begin preparing a section for aphanisma in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the aphanisma section of the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Write a seed collection plan section that includes collecting seeds over multiple years and several times within a season, accumulating seeds across populations, and sampling among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from occurrences with <1,000 plants and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan section should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2022, Completed Aphanisma Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
APHBLI-1 MON-IMP-IMG Beginning in 2017, inspect extant aphanisma occurrence(s) on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.
APHBLI-3 MON-SURV-SPEC In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
APHBLI-3 MON-SURV-SPEC In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
APHBLI-5 MGT-PRP-MGTPL In 2021, begin preparing a section for aphanisma in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences and/or establishment of new occurrences in suitable habitat as needed to achieve at least 3 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
regional and/or local NFO 2021 SL
MGT-PRP-MGTPL APHBLI-5

Management units: 1, 7

In 2021, begin preparing a section for aphanisma in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences and/or establishment of new occurrences in suitable habitat as needed to achieve at least 3 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the aphanisma section of the MSP Rare Plant Management Plan. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to aphanisma populations. some occurrences are in progress
PRP-3 Prioritize occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. available for implementation
PRP-3 Prioritize occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-4 Develop an implementation plan for aphanisma that prioritizes management actions for the next 5 year and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata, project datasets, and MSP Rare Plant Management Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2022, Completed Aphanisma Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
APHBLI-1 MON-IMP-IMG Beginning in 2017, inspect extant aphanisma occurrence(s) on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.
APHBLI-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at aphamisma occurrence(s) on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
APHBLI-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the "IMG" monitoring at aphamisma occurrence(s) on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
APHBLI-3 MON-SURV-SPEC In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
APHBLI-3 MON-SURV-SPEC In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
APHBLI-4 MGT-PRP-SBPL In 2021, begin preparing a section for aphanisma in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

regional NFO 2017, 2018, 2019 SO
MON-RES-SPEC AQUCHR-1

Management units: 3, 4, 5, 6, 8, 9, 10, 11

From 2017 to 2019, continue the Golden Eagle Nesting, Foraging, and Habitat Use Study, begun in 2014, to monitor golden eagle territory occupancy and reproduction in the MSPA (see occurrence table) and to track eagle movements to identify important foraging, nesting and roosting areas. Continue to study the influence of human activity and land use on patterns of eagle movement and habitat use, measure the response of eagles to human activity while foraging, and determine whether locally produced floaters recruit into the breeding population.

Action Statement Action status Projects
RES-1 Monitor territory occupancy and reproduction in suitable golden eagle habitat within the MSPA. Identify any threats or disturbance to eagles and provide this information to land managers so that management actions can be taken to reduce impacts from human disturbance and other threats. in progress
RES-2 Capture adult eagles at selected territories and attach GPS-transmitters that track eagle movements to identify important foraging areas and to study movement patterns relative to human activity within a landscape matrix of urban, rural, and undeveloped lands. Determine whether eagles switch territories and mates, document individual mortality, and track emigration or short term movements outside of the MSPA. Determine if there are multiple nesting sites within a territory and identify nest sites that are unstable or vulnerable to loss. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
RES-3 Analyze golden eagle foraging habitat data and develop objectives with criteria for managing open areas (grasslands and suitable areas in coastal sage scrub and chaparral) to conditions preferred by foraging eagles and that support abundant prey (e.g., black-tailed jack rabbits, ground squirrels). unknown
RES-4 Measure eagle behavioral responses to human activity at foraging areas. Identify the intensity and type of human activity that affects foraging behavior. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
RES-5 Use the GPS and behavioral response data to model potential impacts to foraging eagles under different scenarios of human disturbance at important foraging areas. Prepare management recommendations to reduce human impacts on foraging eagles, including alignment of trails, restriction of activities, and educational outreach. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
RES-6 Submit project metadata, datasets, and report with management recommendations to the MSP Web Portal. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
Criteria Deadline year
Golden Eagle Nesting, Foraging, and Habitat Use Study Report with Management Recommendations Completed by 2020 2021
Code Obj. code Statement
AQUCHR-2 MON-RES-GEN From 2017 to 2019, continue the Golden Eagle Genetics Study begun in 2014 and collect genetic samples in conjunction with eagle captures for the Golden Eagle Nesting, Foraging, and Habitat Use Study. Analyze these samples to determine the population genetic structure of golden eagles within the MSPA (see occurrence table) and their relationship to eagle populations in other parts of the western United States.
AQUCHR-3 MGT-PRP-MGTPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Management Plan for managing golden eagle territories with nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include recommendations for managing important foraging habitat to minimize human disturbance to foraging eagles and to improve habitat quality to enhance prey availability, especially during drought periods. The plan should also include specifications to control human disturbance that could discourage nesting, cause nest abandonment, or adversely affect the survival of nestlings, and for managing unstable nest ledges or tree nest sites that are critical to maintaining a breeding pair in territories with limited nesting sites.
AQUCHR-4 MON-PRP-MONPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Monitoring Plan for monitoring golden eagle status and assessing nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include standardized monitoring protocols to track the status of eagles at nesting territories, to monitor use of important foraging areas, and to collect habitat and threats covariate data to inform needed management actions.
regional NFO 2017, 2018, 2019 SO
MON-RES-GEN AQUCHR-2

Management units: 3, 4, 5, 6, 8, 9, 10, 11

From 2017 to 2019, continue the Golden Eagle Genetics Study begun in 2014 and collect genetic samples in conjunction with eagle captures for the Golden Eagle Nesting, Foraging, and Habitat Use Study. Analyze these samples to determine the population genetic structure of golden eagles within the MSPA (see occurrence table) and their relationship to eagle populations in other parts of the western United States.

Action Statement Action status Projects
RES-1 Collect blood samples from captured birds to include in a larger study of golden eagle population genetics in the western United States to determine the population genetic structure within the MSPA. Genetic parameters that can be measured include gene flow between territories, relatedness of individuals, effective breeding population size, and overall genetic diversity. Determine whether eagles produced outside the MSPA immigrate into the MSPA to establish breeding territories and evaluate genetic relationships to other eagle populations in the western United States. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
RES-2 Submit project metadata, datasets, and Golden Eagle Genetics Study report to the MSP Web Portal. in progress Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California
Criteria Deadline year
Golden Eagle Genetic Study with Report Completed by 2020 2021
Threat Name Threat Code
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
AQUCHR-1 MON-RES-SPEC From 2017 to 2019, continue the Golden Eagle Nesting, Foraging, and Habitat Use Study, begun in 2014, to monitor golden eagle territory occupancy and reproduction in the MSPA (see occurrence table) and to track eagle movements to identify important foraging, nesting and roosting areas. Continue to study the influence of human activity and land use on patterns of eagle movement and habitat use, measure the response of eagles to human activity while foraging, and determine whether locally produced floaters recruit into the breeding population.
AQUCHR-3 MGT-PRP-MGTPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Management Plan for managing golden eagle territories with nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include recommendations for managing important foraging habitat to minimize human disturbance to foraging eagles and to improve habitat quality to enhance prey availability, especially during drought periods. The plan should also include specifications to control human disturbance that could discourage nesting, cause nest abandonment, or adversely affect the survival of nestlings, and for managing unstable nest ledges or tree nest sites that are critical to maintaining a breeding pair in territories with limited nesting sites.
AQUCHR-4 MON-PRP-MONPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Monitoring Plan for monitoring golden eagle status and assessing nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include standardized monitoring protocols to track the status of eagles at nesting territories, to monitor use of important foraging areas, and to collect habitat and threats covariate data to inform needed management actions.
regional NFO 2021 SO
MGT-PRP-MGTPL AQUCHR-3

Management units: 3, 4, 5, 6, 8, 9, 10, 11

In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Management Plan for managing golden eagle territories with nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include recommendations for managing important foraging habitat to minimize human disturbance to foraging eagles and to improve habitat quality to enhance prey availability, especially during drought periods. The plan should also include specifications to control human disturbance that could discourage nesting, cause nest abandonment, or adversely affect the survival of nestlings, and for managing unstable nest ledges or tree nest sites that are critical to maintaining a breeding pair in territories with limited nesting sites.

Action Statement Action status Projects
PRP-1 Prepare a five year plan for maintaining and enhancing golden eagle foraging habitat in grasslands and suitable areas in open coastal sage scrub and chaparral, and for reducing human impacts to foraging eagles. Use the Golden Eagle Nesting, Foraging, and Habitat Use Study and modeling results to identify important foraging areas for golden eagles on Conserved Lands in the MSPA. Specify management to reduce human disturbance in important foraging habitat and to manage invasive annual grasses to promote abundant prey, such as California ground squirrels and black-tailed jackrabbit. Include a mechanism for updating the management plan with monitoring results and specific management recommendations from the Comprehensive Golden Eagle Monitoring Plan. waiting for precedent action
PRP-2 Prioritize for management, those nest ledges and trees that are in territories where alternative nest sites are limited. Prepare a nest restoration plan for each prioritized unstable nest ledge or vulnerable nest tree in consultation with a qualified golden eagle biologist. waiting for precedent action
PRP-3 Establish procedures for managing human activities within the nest site protective zone, including rerouting trails, closing trails during the breeding season, educational outreach, and enforcement. waiting for precedent action
PRP-4 Submit project metadata and Comprehensive Golden Eagle Management Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Comprehensive Golden Eagle Management Plan Completed by 2022 2021
Code Obj. code Statement
AQUCHR-1 MON-RES-SPEC From 2017 to 2019, continue the Golden Eagle Nesting, Foraging, and Habitat Use Study, begun in 2014, to monitor golden eagle territory occupancy and reproduction in the MSPA (see occurrence table) and to track eagle movements to identify important foraging, nesting and roosting areas. Continue to study the influence of human activity and land use on patterns of eagle movement and habitat use, measure the response of eagles to human activity while foraging, and determine whether locally produced floaters recruit into the breeding population.
AQUCHR-2 MON-RES-GEN From 2017 to 2019, continue the Golden Eagle Genetics Study begun in 2014 and collect genetic samples in conjunction with eagle captures for the Golden Eagle Nesting, Foraging, and Habitat Use Study. Analyze these samples to determine the population genetic structure of golden eagles within the MSPA (see occurrence table) and their relationship to eagle populations in other parts of the western United States.
AQUCHR-4 MON-PRP-MONPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Monitoring Plan for monitoring golden eagle status and assessing nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include standardized monitoring protocols to track the status of eagles at nesting territories, to monitor use of important foraging areas, and to collect habitat and threats covariate data to inform needed management actions.
regional NFO 2021 SO
MON-PRP-MONPL AQUCHR-4

Management units: 3, 4, 5, 6, 8, 9, 10, 11

In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Monitoring Plan for monitoring golden eagle status and assessing nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include standardized monitoring protocols to track the status of eagles at nesting territories, to monitor use of important foraging areas, and to collect habitat and threats covariate data to inform needed management actions.

Action Statement Action status Projects
PRP-1 Complete a plan to monitor the status and habitat use of eagles over the long term within the MSPA that is based upon the occupancy monitoring study in the Golden Eagle Nesting, Foraging and Habitat Use Study. The plan should include detailed monitoring objectives, statistically valid sampling design, sampling locations, monitoring timeline, and standardized monitoring protocols to record eagles and important habitat and threat attributes. waiting for precedent action
PRP-2 Develop a plan to rapidly assess the condition of important golden eagle foraging habitat on Conserved Lands across the MSPA using a standardized protocol, statistically valid sampling design, and designated sampling locations. The protocol should describe monitoring methods to collect specific habitat and threat covariates associated with habitat quality, as identified by the Golden Eagle Nesting, Foraging, and Habitat Use Study. The results of this monitoring will be used to periodically prioritize sites and develop specific recommendations for managing foraging habitat to minimize human disturbance and enhance habitat quality to support abundant eagle prey. waiting for precedent action
PRP-3 A golden eagle expert should prepare a protocol, standardized data sheets, and provide periodic training to land managers in how to safely conduct annual nest inspections and determine management needs with minimal disturbance to eagles. The protocol should assess nest sites during the non-breeding season to identify nest ledges that are unstable and nest trees that are vulnerable to loss from threats such as wildfire, pests, and fungal pathogens. waiting for precedent action
PRP-4 Submit project metadata, sampling design, sampling locations, protocols and Comprehensive Golden Eagle Monitoring Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Comprehensive Golden Eagle Monitoring Plan Completed by 2022 2021
Code Obj. code Statement
AQUCHR-1 MON-RES-SPEC From 2017 to 2019, continue the Golden Eagle Nesting, Foraging, and Habitat Use Study, begun in 2014, to monitor golden eagle territory occupancy and reproduction in the MSPA (see occurrence table) and to track eagle movements to identify important foraging, nesting and roosting areas. Continue to study the influence of human activity and land use on patterns of eagle movement and habitat use, measure the response of eagles to human activity while foraging, and determine whether locally produced floaters recruit into the breeding population.
AQUCHR-2 MON-RES-GEN From 2017 to 2019, continue the Golden Eagle Genetics Study begun in 2014 and collect genetic samples in conjunction with eagle captures for the Golden Eagle Nesting, Foraging, and Habitat Use Study. Analyze these samples to determine the population genetic structure of golden eagles within the MSPA (see occurrence table) and their relationship to eagle populations in other parts of the western United States.
AQUCHR-3 MGT-PRP-MGTPL In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Management Plan for managing golden eagle territories with nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include recommendations for managing important foraging habitat to minimize human disturbance to foraging eagles and to improve habitat quality to enhance prey availability, especially during drought periods. The plan should also include specifications to control human disturbance that could discourage nesting, cause nest abandonment, or adversely affect the survival of nestlings, and for managing unstable nest ledges or tree nest sites that are critical to maintaining a breeding pair in territories with limited nesting sites.

regional NFO 2017, 2018, 2019, 2020, 2021 SL
MON-RES-SPEC ATHCUN-1

Management units: 3, 4, 5, 6, 9

Continue the research study of breeding burrowing owls, foraging, threats, artifiical and natural burrows, movements, and habitat assessments to inform management at existing occupied and future potential nodes. Include translocated owls in the study to determine effectiveness of translocation and to gather information to inform continued management at new nodes.

Action Statement Action status Projects
RES-1 Submit project metadata, survey data, and report with management recommendations to the MSP web portal. In progress
Criteria Deadline year
Burrowing Owl Surveys and Reports Completed by 2021. 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG ATHCUN-3

Management units: 3, 4, 5, 6, 9

Annually inspect artificial and natural burrows and occupied habitat to determine management needs using a regional IMG protocol. The monitoring should include considerations for retrofitting existing artificial burrows with the most current design to maximize fledgling success, removal/closing of burrows at poorly performing sites, and addition of burrows to maximize success.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. available for implementation
IMP-2 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. available for implementation
IMP-3 Submit monitoring and management data to the regional MSP web portal. available for implementation
Criteria Deadline year
Surveys Completed Annually with management recommendations 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG ATHCUN-4

Management units: 3, 4, 5, 6, 9

Conduct management actions identified through the IMG regional protocol monitoring, including protecting populations from disturbance, removing invasive plants, cleaning, repairing, and fortifying burrows within the known occupied and suitable habitat, retrofitting existing artificial burrows with the most current design to maximize fledgling success, removal/closing of burrows at poorly performing sites, and addition of burrows to maximize success.

Action Statement Action status Projects
IMP-1 Perform management activities such as protecting populations from disturbance, removing invasive plants, cleaning, repairing, and fortifying burrows, retrofitting existing artificial burrows with the most current design to maximize fledgling success, removal/closing of burrows at poorly performing sites, and addition of burrows to maximize success.. some occurrences are in progress
IMP-2 Submit project metadata and management data to MSP web portal. some occurrences are in progress
Criteria Deadline year
Management Completed as Needed Based Upon Monitoring Recommendations 2021
regional NFO 2017 SL
MGT-PRP-MGTPL ATHCUN-5

Management units: 3, 4, 5, 6, 9

In 2017, finalize the Burrowing Owl Conservation and Management Plan that includes results from the research study and habitat assessments and recommendations for the establishment of at least two nodes and enhancement of existing occurrences to ensure persistence on Conserved Lands and establishment of a captive breeding population as a source for burrowing owls.

Action Statement Action status Projects
PRP-1 Consult with the Burrowing Owl Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to gather input into prioritized management actions. completed
PRP-2 Submit project metadata and Burrowing Owl Conservation and Management Plant to the MSP Web Portal.
Criteria Deadline year
Burrowing Owl Management Plan Completed in 2017 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-MGTPL ATHCUN-6

Management units: 3, 4, 5, 6, 9

Beginning in 2017, implement highest priority management actions from the Burrowing Owl Conservation and Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. available for implementation
Criteria Deadline year
By 2021, =1 High Priority Management Action Implemented from the Burrowing Owl Conservation and Management Plan 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-MGTPL ATHCUN-7

Management units: 3, 4, 5, 6, 9

Beginning in 2017, monitor the effectiveness of management actions implemented for western burrowing owl on Conserved Lands.

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring Completed and Data and Report Submitted within one year of management actions 2021

regional and/or local NFO 2018 VF
MON-IMP-IMG ATRCOU-1

Management units: 3, 5

In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2018 with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV

regional and/or local NFO 2018 VF
MON-IMP-IMG ATRPAR-1

Management units: 5

In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2018 with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV

regional and/or local NFO 2017, 2019, 2021 SO
MON-IMP-IMG BACVAN-1

Management units: 3, 4, 6

Beginning in 2017, inspect Encinitas baccharis occurrences on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs. After 2017, repeat monitoring every 2 years.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. in progress
Criteria Deadline year
Surveys Completed Every 2 Years with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Encinitas baccharis occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BACVAN-4 MGT-PRP-SBPL In 2018, begin preparing a section for Encinitas baccharis in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG BACVAN-2

Management units: 3, 4, 6

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Encinitas baccharis occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-1 MON-IMP-IMG Beginning in 2017, inspect Encinitas baccharis occurrences on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional NFO 2017 SO
MON-RES-GEN BACVAN-3

Management units: 3, 4, 6

In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Encinitas baccharis occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.

Action Statement Action status Projects
RES-1 Use BMPs to collect plant material for genetic samples at Encinitas baccharis occurrences in the MSPA. In progress Wed Demo
RES-2 Evaluate the overall long-term genetic trajectory for Encinitas baccharis. In progress
RES-3 Hold a workshop of scientists, rare plant experts, and land managers to develop management recommendations based upon the results of genetic analyses. In progress
RES-4 Submit project metadata, genetic datasets and analyses, and report with management recommendations to the MSP Web Portal. In progress
Criteria Deadline year
By 2017, Completed Genetic Study with Management Recommendations 2021
Threat Name Threat Code
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-4 MGT-PRP-SBPL In 2018, begin preparing a section for Encinitas baccharis in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional NFO 2018 SO
MGT-PRP-SBPL BACVAN-4

Management units: 3, 4, 6

In 2018, begin preparing a section for Encinitas baccharis in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Encinitas baccharis section in the MSP Species Seed Collection, Banking and Bulking Plan. some occurrences are in progress Wed Demo
PRP-2 Design the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2019, Completed Encinitas Baccharis Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-3 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Encinitas baccharis occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional and/or Local NFO 2019, 2020, 2021 SO
MGT-IMP-SBPL BACVAN-5

Management units: 1, 7

In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Encinitas baccharis to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2021, =1 Highest Priority Action Implemented for Encinitas Baccharis from the MSP Seed Collection, Banking, and Bulking Plan 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-4 MGT-PRP-SBPL In 2018, begin preparing a section for Encinitas baccharis in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BACVAN-7 MGT-IMP-MGTPL Beginning in 2019, implement highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.
regional NFO 2018 SO
MGT-PRP-MGTPL BACVAN-6

Management units: 4, 5, 8

Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Encinitas baccharis section of the MSP Rare Plant Management Plan. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Encinitas baccharis occurrences. some occurrences are in progress
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-4 Develop an implementation plan for Encinitas Baccharis that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2019, Completed Encinitas Baccharis Section of the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-1 MON-IMP-IMG Beginning in 2017, inspect Encinitas baccharis occurrences on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
BACVAN-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Encinitas baccharis occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BACVAN-3 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Encinitas baccharis occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
BACVAN-4 MGT-PRP-SBPL In 2018, begin preparing a section for Encinitas baccharis in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BACVAN-5 MGT-IMP-SBPL In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Encinitas baccharis to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BACVAN-7 MGT-IMP-MGTPL Beginning in 2019, implement highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.
BACVAN-8 MON-IMP-MGTPL Beginning in 2019, monitor effectiveness of implementation of highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.
BACVAN-9 MON-RES-SPEC Determine the population dynamics of Encinitas baccharis in response to natural and altered fire frequencies that may affect successional processes and population dynamics. The study should begin when the next fire burns an Encinitas baccharis occurrence and include subsequently burned occurrences to research post-fire recovery mechanisms (e.g., resprouter vs. obligate seeder) and circumstances in which post-fire management is necessary to facilitate robust post-fire recovery. Use results to identify postfire management actions for Encinitas baccharis to assist in recovery of burned populations.
Regional and/or Local NFO 2019, 2020, 2021 SO
MGT-IMP-MGTPL BACVAN-7

Management units: 1, 7

Beginning in 2019, implement highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2021, =1 High Priority Management Action Implemented for Encinitas Baccharis from the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-5 MGT-IMP-SBPL In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Encinitas baccharis to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BACVAN-8 MON-IMP-MGTPL Beginning in 2019, monitor effectiveness of implementation of highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2019, 2020, 2021 SO
MON-IMP-MGTPL BACVAN-8

Management units: 1, 7

Beginning in 2019, monitor effectiveness of implementation of highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BACVAN-6 MGT-PRP-MGTPL Begin preparing a section for Encinitas baccharis in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BACVAN-7 MGT-IMP-MGTPL Beginning in 2019, implement highest priority management actions identified in the Encinitas baccharis section of the MSP Rare Plant Management Plan.

regional and/or local NFO 2018, 2020 SS
MON-IMP-IMG BLOCLE-1

Management units: 3, 4, 6

Beginning in 2018, inspect extant San Diego goldenstar occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed Every 2 Years with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BLOCLE-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016, 2018, and 2020 at San Diego goldenstar occurrence(s) on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
local NFO 2017, 2018, 2019, 2020, 2021 SS
MGT-IMP-IMG BLOCLE-2

Management units: 3, 4, 6

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016, 2018, and 2020 at San Diego goldenstar occurrence(s) on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BLOCLE-1 MON-IMP-IMG Beginning in 2018, inspect extant San Diego goldenstar occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.

regional and/or local NFO 2017, 2019, 2021 SS
MON-IMP-IMG BROFIL-1

Management units: 6, 7, 8

Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs. After 2017, repeat monitoring every 2 years.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Every 2 Years with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BROFIL-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at thread-leaved brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SS
MGT-IMP-IMG BROFIL-2

Management units: 6, 7, 8

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at thread-leaved brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BROFIL-1 MON-IMP-IMG Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs. After 2017, repeat monitoring every 2 years.
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
NFO 2017 SS
MON-RES-SPEC BROFIL-3

Management units: 6, 7, 8

In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for thread-leaved brodiaea and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.

Action Statement Action status Projects
RES-1 Test soils at potential expansion sites and compare to occupied reference sites to determine site suitability based on soils. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-2 Prepare habitat suitability models under current environmental conditions and for different scenarios of climate change to delineate potential future habitat. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-3 Collect covariate data on vegetation composition and cover (alliance and association-level mapping), soils, invasive plants and other threats for selected populations. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-4 Prioritize locations for conservation, management, and future surveys based on predicted distributions and environmental correlates. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-5 Submit project metadata, monitoring data and report to MSP web portal. In progress Enhancing the Resilience of Edaphic Endemic Plants
Criteria Deadline year
Refined Models and Prioritized Future Survey Locations for thread-leaved brodiaea by 2018 2021
Threat Name Threat Code
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional NFO 2019 SS
MON-SURV-SPEC BROFIL-4

Management units: 6, 7, 8

In 2019, survey historic thread-leaved brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. On hold
SURV-2 Submit project metadata, occurrence status, habitat mapping and assessment, and report to the MSP Web Portal. On hold
Criteria Deadline year
Surveys and Report Completed by 2020 2021
Code Obj. code Statement
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
regional NFO 2020 SS
MGT-PRP-MGTPL BROFIL-5

Management units: 6, 7, 8

In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Prioritize extant occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to thread-leaved brodiaea occurrences. some occurrences are in progress
PRP-3 Identify and prioritize sites for re-establishment of historic occurrences or that appear suitable for establishment of new occurrences. Specify the highest priority sites for establishing occurrences on Conserved Lands. some occurrences are in progress
PRP-4 Develop an implementation plan for thread-leaved brodiaea that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2021, Completed Section for Thread-leaved brodiaea in the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
BROFIL-1 MON-IMP-IMG Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs. After 2017, repeat monitoring every 2 years.
BROFIL-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at thread-leaved brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BROFIL-3 MON-RES-SPEC In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for thread-leaved brodiaea and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.
BROFIL-4 MON-SURV-SPEC In 2019, survey historic thread-leaved brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
BROFIL-6 MGT-IMP-MGTPL Beginning in 2021, begin implementing highest priority management actions identified in the thread-leaved brodiaea section of the MSP Rare Plant Management Plan.
BROFIL-7 MON-IMP-MGTPL Monitor effectiveness of implementation of highest priority management actions identified in the thread-leaved brodiaea section in the MSP Rare Plant Management Plan.
BROFIL-8 MGT-PRP-SBPL In 2020, begin preparing a section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
regional and/or local NFO 2021 SS
MGT-IMP-MGTPL BROFIL-6

Management units: 6, 7, 8

Beginning in 2021, begin implementing highest priority management actions identified in the thread-leaved brodiaea section of the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2025, =1 High priority Management Action Implemented for Thread-leaved Brodiaea from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BROFIL-7 MON-IMP-MGTPL Monitor effectiveness of implementation of highest priority management actions identified in the thread-leaved brodiaea section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SS
MON-IMP-MGTPL BROFIL-7

Management units: 6, 7, 8

Monitor effectiveness of implementation of highest priority management actions identified in the thread-leaved brodiaea section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BROFIL-6 MGT-IMP-MGTPL Beginning in 2021, begin implementing highest priority management actions identified in the thread-leaved brodiaea section of the MSP Rare Plant Management Plan.
Regional NFO 2020 SS
MGT-PRP-SBPL BROFIL-8

Management units: 6, 7, 8

In 2020, begin preparing a section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Thread-leaved brodiaea MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Design a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. waiting for precedent action
Criteria Deadline year
By 2021, completed section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
BROFIL-1 MON-IMP-IMG Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs. After 2017, repeat monitoring every 2 years.
BROFIL-3 MON-RES-SPEC In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for thread-leaved brodiaea and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.
BROFIL-4 MON-SURV-SPEC In 2019, survey historic thread-leaved brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
BROFIL-5 MGT-PRP-MGTPL In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BROFIL-9 MGT-IMP-SBPL In 2021, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Thread-leaved brodiaea to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences
NFO 2021 SS
MGT-IMP-SBPL BROFIL-9

Management units: 6, 7, 8

In 2021, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Thread-leaved brodiaea to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences

Action Statement Action status Projects
IMP-1 Seed should be stored for conservation banking and as source of propagules for enhancement and restoration projects at a permanent, established seed bank. waiting for precedent action
IMP-2 Submit project metadata and Thread-leaved brodiaea MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2025, =1 Highest Priority Action Implemented for Thread-leaved brodiaea from the MSP Seed Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
BROFIL-8 MGT-PRP-SBPL In 2020, begin preparing a section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG BROORC-1

Management units: 2, 3, 4, 6, 8

From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BROORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BROORC-3 MON-SURV-SPEC In 2019, survey historic Orcutt's brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
BROORC-5 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG BROORC-2

Management units: 2, 3, 4, 6, 8

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation Otay Mesa Rare Plants
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation Otay Mesa Rare Plants
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BROORC-1 MON-IMP-IMG From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional NFO 2019 SO
MON-SURV-SPEC BROORC-3

Management units: 2, 3, 4, 6, 7, 8

In 2019, survey historic Orcutt's brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. On hold
SURV-2 Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. On hold
Criteria Deadline year
Surveys and Report Completed by 2020 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
BROORC-1 MON-IMP-IMG From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
BROORC-5 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
regional and/or local NFO 2017, 2018, 2019 SO
MGT-IMP-IEX BROORC-4

Management units: 3

Beginning in 2017, establish 2 new Orcutt's brodiaea occurrences at Proctor Valley and Cal Terraces/Dennery Canyon. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
IMP-1 Conduct invasive plant control and distribute seed to establish new Orcutt's brodiaea occurrences. in progress
IMP-2 Implement seed augmentation using seed collected and bulked by San Diego Zoo's Institute for Conservation Research. in progress
IMP-3 Submit project metadata, management datasets and report to the MSP Web Portal. in progress
Criteria Deadline year
By 2020, 2 New Occurrences of Orcutt's Brodiaea Established and Report Submitted 2021
Code Obj. code Statement
BROORC-6 MGT-IMP-SBPL From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BROORC-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.
BROORC-9 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's brodiaea section in the MSP Rare Plant Management Plan.
Regional NFO 2020 SO
MGT-PRP-SBPL BROORC-5

Management units: 2, 3, 4, 6, 8

In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Design the seed collection plan to include recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2021, Completed Orcutt's Brodiaea Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
BROORC-1 MON-IMP-IMG From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
BROORC-3 MON-SURV-SPEC In 2019, survey historic Orcutt's brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
BROORC-4 MGT-IMP-IEX Beginning in 2017, establish 2 new Orcutt's brodiaea occurrences at Proctor Valley and Cal Terraces/Dennery Canyon. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence
BROORC-6 MGT-IMP-SBPL From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional and/or Local NFO 2021 SO
MGT-IMP-SBPL BROORC-6

Management units: 2, 3, 4, 6, 8

From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. some occurrences are in progress
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2025, =1 Highest Priority Action Implemented for Orcutt's brodiaea from the MSP Seed Banking and Bulking Plan 2021
Code Obj. code Statement
BROORC-4 MGT-IMP-IEX Beginning in 2017, establish 2 new Orcutt's brodiaea occurrences at Proctor Valley and Cal Terraces/Dennery Canyon. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence
BROORC-5 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BROORC-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.
regional NFO 2020, 2021 SO
MGT-PRP-MGTPL BROORC-7

Management units: 2, 3, 4, 6, 8

In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Rare Plant Management Plan. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's brodiaea occurrences. some occurrences are in progress
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-4 Develop an implementation plan for Orcutt's brodiaea that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2021, Completed Orcutt's Brodiaea Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
BROORC-1 MON-IMP-IMG From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
BROORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
BROORC-3 MON-SURV-SPEC In 2019, survey historic Orcutt's brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
BROORC-4 MGT-IMP-IEX Beginning in 2017, establish 2 new Orcutt's brodiaea occurrences at Proctor Valley and Cal Terraces/Dennery Canyon. Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than 20% absolute cover within the occurrence
BROORC-5 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
BROORC-6 MGT-IMP-SBPL From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BROORC-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.
BROORC-9 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's brodiaea section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SO
MGT-IMP-MGTPL BROORC-8

Management units: 2, 3, 4, 6, 8

In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2025, =1 High Priority Management Action Implemented for Orcutt's Brodiaea from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
BROORC-6 MGT-IMP-SBPL From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BROORC-9 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's brodiaea section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SO
MON-IMP-MGTPL BROORC-9

Management units: 2, 3, 4, 6, 8

In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's brodiaea section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
BROORC-7 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
BROORC-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.

regional and/or local POST 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-MGTPL CAMBRU-1

Management units: 2, 3, 4

From 2017 through 2021, continue implementing high priority management actions to: expand coastal cactus wren populations; rehabilitate habitat destroyed in the 2003 Cedar and 2007 Harris wildfires; improve connectivity within and between the Otay and San Diego/El Cajon genetic clusters (see occurrence table); and manage high risk of anthropogenic predation of adults and nestlings. These priority management actions are identified in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan prepared in 2015.

Action Statement Action status Projects
IMP-1 Following best practices in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan, design cactus scrub enhancement and restoration projects to provide high quality nesting and foraging habitat with large patches of cacti >1 m tall in a mosaic of open scrub that provides sufficient food resources for reproduction and survival, especially during drought. As they become available, incoporate the results from the Cactus Wren Demography, Foraging and Arthropod Study to create restoration palettes that favor plant species associated with important arthropod food resources. Design planting layouts to maximize water availability by allocating a portion of the plantings to more mesic sites, such as ravines, at the bottom of slopes, and on northerly and easterly aspects. Control invasive nonnative plants to =20% absolute cover to reduce competition with native plants for water and light. some occurrences are in progress Otay River Valley Cactus Wren Habitat Restoration and Enhancement , Salt Creek Coastal Cactus Wren Habitat Restoration Project
IMP-2 Implement management actions, as needed, to reduce anthropogenic predation on wrens and their nests in fragmented habitats bordered by development where wrens are vulnerable to predation by cats, Cooper's hawks, corvids and other human-subsidized predators. Actions could include removing selected trees within or bordering cactus scrub that provide hunting, roosting, and nesting perches for hawks and corvids and avoiding cactus scrub restoration in areas where the terrain and location make wrens especially vulnerable to predation. Other measures could involve humanely removing feral cats from Conserved Lands and providing educational material and signage encouraging neighboring homeowners to keep their cats indoors so that wrens are protected and cats are safe from predation by wild animals, such as coyotes. some occurrences are in progress Otay River Valley Cactus Wren Habitat Restoration and Enhancement , Salt Creek Coastal Cactus Wren Habitat Restoration Project
Criteria Deadline year
By 2021, =3 High Priority Management Actions Implemented from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan 2021
Code Obj. code Statement
CAMBRU-2 MON-IMP-MGTPL From 2017-2021, collect data on the effectiveness of implementing high priority management actions from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan. In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for the combined Otay and San Diego/El Cajon genetic clusters (see occurrence table) in south San Diego County. These results will be used in 2022 to update management recommendations and success criteria for the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan.
CAMBRU-3 MON-SURV-SPEC From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-6 MGT-IMP-NUR From 2017-2021, continue operation of the North San Diego County Cactus Nursery and support a South San Diego County Cactus Nursery to supply cactus to land managers to enhance, restore and create coastal cactus wren habitat. Grow cactus pads, segments and entire plants sufficient for restoration projects to expand and enhance cactus scrub habitat and as a source of plants for immediate habitat rehabilitation following severe wildfire.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-MGTPL CAMBRU-2

Management units: 2, 3, 4

From 2017-2021, collect data on the effectiveness of implementing high priority management actions from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan. In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for the combined Otay and San Diego/El Cajon genetic clusters (see occurrence table) in south San Diego County. These results will be used in 2022 to update management recommendations and success criteria for the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan.

Action Statement Action status Projects
IMP-1 Collect vegetation data to document success of cactus scrub restoration projects. This can include monitoring the height, diameter and survival of planted cactus and the composition and percent cover of native and nonnative shrubs, forbs and grasses. Document wren use of restored cactus scrub. some occurrences are in progress
IMP-2 Submit restoration and enhancement project metadata, management datasets, and reports to the MSP Web Portal. in progress
IMP-3 Conduct a meta-analysis of habitat restoration data and cactus wren population survey data to determine whether short-term success criteria have been achieved for habitat restoration actions and for wren populations in south San Diego County. Based upon these results, prepare recommendations for the 2022-2031 management strategy for coastal cactus wren. These broad recommendations can be used in 2022 to update the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan with the next set of success criteria and specific, prioritized management actions. waiting for precedent action
IMP-4 Submit cactus wren habitat restoration and population meta-analysis datasets, results, and management strategy recommendations for south San Diego County to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Success Criteria 2013-2021: Restore =70 Acres of High Quality Cactus Scrub and Increase the Combined Otay and San Diego/El Cajon Genetic Clusters to =75 Territories on C 2021
Code Obj. code Statement
CAMBRU-1 MGT-IMP-MGTPL From 2017 through 2021, continue implementing high priority management actions to: expand coastal cactus wren populations; rehabilitate habitat destroyed in the 2003 Cedar and 2007 Harris wildfires; improve connectivity within and between the Otay and San Diego/El Cajon genetic clusters (see occurrence table); and manage high risk of anthropogenic predation of adults and nestlings. These priority management actions are identified in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan prepared in 2015.
CAMBRU-3 MON-SURV-SPEC From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-6 MGT-IMP-NUR From 2017-2021, continue operation of the North San Diego County Cactus Nursery and support a South San Diego County Cactus Nursery to supply cactus to land managers to enhance, restore and create coastal cactus wren habitat. Grow cactus pads, segments and entire plants sufficient for restoration projects to expand and enhance cactus scrub habitat and as a source of plants for immediate habitat rehabilitation following severe wildfire.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-SURV-SPEC CAMBRU-3

Management units: 2, 3, 4, 6

From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.

Action Statement Action status Projects
SURV-1 Conduct 2 rounds of protocol surveys each year for coastal cactus wrens in mapped cactus at long term monitoring sites and expand monitoring sites, as needed, to include restoration sites and newly conserved cactus scrub. Use standardized protocols to document the number of wrens observed, age, sex, pairing and nesting status, and color band combinations, and to assess habitat for shrub overgrowth and crowding, invasive plants, unhealthy or dead cactus, and dominant shrub and cactus species. Update cactus mapping at restored and newly conserved sites. in progress
SURV-2 In conjunction with the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, focus on collecting banding status data to better understand cactus wren population dynamics, adult and juvenile survival, and dispersal capabilities in south San Diego County. unknown
SURV-3 Submit project metadata, cactus wren survey and habitat assessment datasets, analyses and survey reports to the MSP Web Portal. in progress
Criteria Deadline year
Cactus Wren Surveys and Habitat Assessments Completed 2017-2021 2021
Code Obj. code Statement
CAMBRU-1 MGT-IMP-MGTPL From 2017 through 2021, continue implementing high priority management actions to: expand coastal cactus wren populations; rehabilitate habitat destroyed in the 2003 Cedar and 2007 Harris wildfires; improve connectivity within and between the Otay and San Diego/El Cajon genetic clusters (see occurrence table); and manage high risk of anthropogenic predation of adults and nestlings. These priority management actions are identified in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan prepared in 2015.
CAMBRU-2 MON-IMP-MGTPL From 2017-2021, collect data on the effectiveness of implementing high priority management actions from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan. In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for the combined Otay and San Diego/El Cajon genetic clusters (see occurrence table) in south San Diego County. These results will be used in 2022 to update management recommendations and success criteria for the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-7 MGT-IMP-IEX In 2017-2021, continue supporting restoration of cactus scrub based upon ICR's Restoration Analyses for the San Pasqual Valley/Lake Hodges coastal cactus wren genetic cluster (see occurrence table) to: rehabilitate cactus scrub destroyed or degraded by the 2007 Witch Fire; to expand occurrences, particularly adjacent to Lake Hodges; to improve connectivity within the genetic cluster; and as needed, to manage high risk of anthropogenic predation of adults and nestlings.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
CAMBRU-10 MON-IMP-FMGT For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of coastal cactus wren occurrences affected by the wildfire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing postfire cactus scrub habitat recovery. Collect habitat recovery data at unoccupied cactus scrub sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover wren populations and important cactus scrub habitat patches.
CAMBRU-11 MGT-IMP-FMGT For at least the first 3 years following a wildfire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality cactus scrub to allow for recovery of coastal cactus wren occurrences affected by the wildfire.
regional and/or local NFO 2017, 2018, 2019 SO
MON-RES-SPEC CAMBRU-4

Management units: 2, 3, 4

From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.

Action Statement Action status Projects
RES-1 Capture, uniquely color band, and monitor cactus wrens regularly during the breeding season to collect data on territory and breeding status, nesting phenology, nest fate, number of eggs/nestlings/fledglings per nest, and annual productivity, dispersal and survival. Measure habitat quality at each territory by characterizing the vegetation and by sampling arthropod communities associated with bare ground and 8 plant species common to cactus scrub. Determine nestling diets by collecting fecal samples during banding and using DNA barcoding methods to identify the arthropod taxa fed to nestlings. in progress
RES-2 Identify arthropods important in the diet of nestling cactus wrens based on a DNA barcoding identification of arthropods in fecal samples obtained from the south San Diego County study, from the results of a similar study in Orange County, and from a literature search of adult and nestling cactus wren diets across their range. Evaluate the occurrence of arthropod taxa important to wren diets in association with 8 specific plant species and bare ground to determine those habitat attributes in cactus scrub that provide significant food resources for cactus wrens. Analyze wren reproductive parameters in relation to expected arthropod food availability based on the habitat attributes of each territory. Use the results to develop specific management recommendations for plant restoration palettes and for restoring the composition and cover of plants and bare ground that enhance food availablity for wrens. Determine how plants might be situated in the landscape to enhance arthropod food availability during droughts, such as planting a portion of plants in more mesic sites in ravines, at the bottom of slopes and on northerly and easterly aspects. in progress
RES-3 Project metadata, datasets, analyses, and report with specific management recommendations will be submitted to the MSP Web Portal. in progress
Criteria Deadline year
Coastal Cactus Wren Demography, Vegetation and Arthropod Study and Report with Management Recommendations Completed by 2020 2021
Code Obj. code Statement
CAMBRU-1 MGT-IMP-MGTPL From 2017 through 2021, continue implementing high priority management actions to: expand coastal cactus wren populations; rehabilitate habitat destroyed in the 2003 Cedar and 2007 Harris wildfires; improve connectivity within and between the Otay and San Diego/El Cajon genetic clusters (see occurrence table); and manage high risk of anthropogenic predation of adults and nestlings. These priority management actions are identified in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan prepared in 2015.
CAMBRU-2 MON-IMP-MGTPL From 2017-2021, collect data on the effectiveness of implementing high priority management actions from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan. In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for the combined Otay and San Diego/El Cajon genetic clusters (see occurrence table) in south San Diego County. These results will be used in 2022 to update management recommendations and success criteria for the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan.
CAMBRU-3 MON-SURV-SPEC From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-7 MGT-IMP-IEX In 2017-2021, continue supporting restoration of cactus scrub based upon ICR's Restoration Analyses for the San Pasqual Valley/Lake Hodges coastal cactus wren genetic cluster (see occurrence table) to: rehabilitate cactus scrub destroyed or degraded by the 2007 Witch Fire; to expand occurrences, particularly adjacent to Lake Hodges; to improve connectivity within the genetic cluster; and as needed, to manage high risk of anthropogenic predation of adults and nestlings.
CAMBRU-8 MON-IMP-MGTPL From 2017-2021, collect data on the effectiveness of implementing high priority management actions to restore cactus scrub to expand coastal cactus wren populations and enhance connectivity within the San Pasqual Valley/Lake Hodges genetic cluster (see occurrence table). In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for north San Diego County. Use these results to develop a management strategy that will provide the basis for preparing a North County Coastal Cactus Wren Habitat Conservation and Management Plan in 2022.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
CAMBRU-10 MON-IMP-FMGT For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of coastal cactus wren occurrences affected by the wildfire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing postfire cactus scrub habitat recovery. Collect habitat recovery data at unoccupied cactus scrub sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover wren populations and important cactus scrub habitat patches.
CAMBRU-11 MGT-IMP-FMGT For at least the first 3 years following a wildfire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality cactus scrub to allow for recovery of coastal cactus wren occurrences affected by the wildfire.
regional and/or local PRE 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-NUR CAMBRU-6

Management units: 2, 3, 4, 6

From 2017-2021, continue operation of the North San Diego County Cactus Nursery and support a South San Diego County Cactus Nursery to supply cactus to land managers to enhance, restore and create coastal cactus wren habitat. Grow cactus pads, segments and entire plants sufficient for restoration projects to expand and enhance cactus scrub habitat and as a source of plants for immediate habitat rehabilitation following severe wildfire.

Action Statement Action status Projects
IMP-1 Implement BMPs when harvesting and growing cactus at a nursery in preparation for transplant into natural lands for cactus restoration projects and to provide an emergency source of cactus following wildfire. some occurrences are in progress North County Cactus Nursery and Coastal Cactus Wren Habitat Restoration (2015-2018)
IMP-2 Grow and supply cactus pads, segments, and entire plants from locally harvested native cactus with a composition of species reflecting what naturally occurs in each geographic area. The North County Cactus Nursery should cactus to projects in MUs 6 and 8 and those areas in MU 4 dominated by prickly pear cactus. The South County Cactus Nursery should supply cactus to MUs 2 and 3 and to those areas in MU 4 dominated by coast cholla. The amount of cactus produced will be determined periodically based upon: management recommendations from the 2015 South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan; from ICR's Restoration Analyses for the San Pasqual Valley and Lake Hodges; an evaluation of planned and ongoing cactus restoration projects; and an assessment of cactus needed to be kept in reserve for future post-fire rehabilitation efforts. some occurrences are in progress North County Cactus Nursery and Coastal Cactus Wren Habitat Restoration (2015-2018)
IMP-3 Submit project metadata, nursery plans, and reports with information on harvesting, growing and distributing cactus for restoration projects to the MSP Web Portal. some occurrences are in progress North County Cactus Nursery and Coastal Cactus Wren Habitat Restoration (2015-2018)
Criteria Deadline year
Cactus Nurseries Established in North and South San Diego County to Provide Sufficient Cactus for Restoration and PostFire Rehabilitation 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CAMBRU-1 MGT-IMP-MGTPL From 2017 through 2021, continue implementing high priority management actions to: expand coastal cactus wren populations; rehabilitate habitat destroyed in the 2003 Cedar and 2007 Harris wildfires; improve connectivity within and between the Otay and San Diego/El Cajon genetic clusters (see occurrence table); and manage high risk of anthropogenic predation of adults and nestlings. These priority management actions are identified in the South San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan prepared in 2015.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-7 MGT-IMP-IEX In 2017-2021, continue supporting restoration of cactus scrub based upon ICR's Restoration Analyses for the San Pasqual Valley/Lake Hodges coastal cactus wren genetic cluster (see occurrence table) to: rehabilitate cactus scrub destroyed or degraded by the 2007 Witch Fire; to expand occurrences, particularly adjacent to Lake Hodges; to improve connectivity within the genetic cluster; and as needed, to manage high risk of anthropogenic predation of adults and nestlings.
CAMBRU-11 MGT-IMP-FMGT For at least the first 3 years following a wildfire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality cactus scrub to allow for recovery of coastal cactus wren occurrences affected by the wildfire.
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IEX CAMBRU-7

Management units: 5, 6

In 2017-2021, continue supporting restoration of cactus scrub based upon ICR's Restoration Analyses for the San Pasqual Valley/Lake Hodges coastal cactus wren genetic cluster (see occurrence table) to: rehabilitate cactus scrub destroyed or degraded by the 2007 Witch Fire; to expand occurrences, particularly adjacent to Lake Hodges; to improve connectivity within the genetic cluster; and as needed, to manage high risk of anthropogenic predation of adults and nestlings.

Action Statement Action status Projects
IMP-1 Following best practices, design cactus scrub enhancement and restoration projects to provide high quality nesting and foraging habitat with large patches of cacti >1 m tall in a mosaic of open scrub that provides sufficient food resources for reproduction and survival, especially during drought years when arthropod food resources are limiting. As they become available, incoporate the results from the Cactus Wren Demography, Foraging and Arthropod Study to create restoration palettes that favor plant species associated wtih important wren food resources. Design planting layouts to maximize water availability by allocating a portion of the plantings to more mesic sites, such as ravines, at the bottom of slopes, and on northerly and easterly aspects. Control invasive nonnative plants to =20% absolute cover to reduce competition with native plants for water and light. in progress Hodges Reservoir-Bernardo Bay Cactus Wren Habitat Restoration Grant Project
IMP-2 Implement management actions, as needed, to reduce anthropogenic predation on wrens and their nests in fragmented habitats bordered by development where wrens are vulnerable to predation by cats, Cooper's hawks, corvids and other human-subsidized predators. Actions could include removing selected trees within or bordering cactus scrub that provide hunting, roosting, and nesting perches for hawks and corvids and avoiding cactus scrub restoration in areas where the terrain and location make wrens especially vulnerable to predation. Other measures could involve humanely removing feral cats from Conserved Lands and providing educational material and signage encouraging neighboring homeowners to keep their cats indoors so that wrens are protected and cats are safe from predation by wild animals, such as coyotes. in progress Hodges Reservoir-Bernardo Bay Cactus Wren Habitat Restoration Grant Project
Criteria Deadline year
By 2021, =2 High Priority Management Actions Implemented from ICR's Restoration Analyses for the San Pasqual Valley and Lake Hodges 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CAMBRU-3 MON-SURV-SPEC From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-6 MGT-IMP-NUR From 2017-2021, continue operation of the North San Diego County Cactus Nursery and support a South San Diego County Cactus Nursery to supply cactus to land managers to enhance, restore and create coastal cactus wren habitat. Grow cactus pads, segments and entire plants sufficient for restoration projects to expand and enhance cactus scrub habitat and as a source of plants for immediate habitat rehabilitation following severe wildfire.
CAMBRU-8 MON-IMP-MGTPL From 2017-2021, collect data on the effectiveness of implementing high priority management actions to restore cactus scrub to expand coastal cactus wren populations and enhance connectivity within the San Pasqual Valley/Lake Hodges genetic cluster (see occurrence table). In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for north San Diego County. Use these results to develop a management strategy that will provide the basis for preparing a North County Coastal Cactus Wren Habitat Conservation and Management Plan in 2022.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-MGTPL CAMBRU-8

Management units: 5, 6

From 2017-2021, collect data on the effectiveness of implementing high priority management actions to restore cactus scrub to expand coastal cactus wren populations and enhance connectivity within the San Pasqual Valley/Lake Hodges genetic cluster (see occurrence table). In 2021, compile data from all restoration projects and determine the effectiveness of cumulative management actions for north San Diego County. Use these results to develop a management strategy that will provide the basis for preparing a North County Coastal Cactus Wren Habitat Conservation and Management Plan in 2022.

Action Statement Action status Projects
IMP-1 Collect vegetation data to document success of cactus scrub restoration projects. This can include monitoring the height, diameter and survival of planted cactus and the composition and percent cover of native and nonnative shrubs, forbs and grasses. Document wren use of restored cactus scrub. some occurrences are in progress
IMP-2 Submit restoration and enhancement project metadata, management datasets, and reports to the MSP Web Portal. some occurrences are in progress
IMP-3 Conduct a meta-analysis of habitat restoration data and cactus wren population survey data to determine whether short-term success criteria have been achieved for habitat restoration actions and for wren populations in north San Diego County. Based upon these results, prepare recommendations for a 2022-2031 management strategy for coastal cactus wren. These broad recommendations can be used in 2022 to prepare a North San Diego County Coastal Cactus Wren Habitat Conservation and Management Plan with specific, prioritized management actions. waiting for precedent action
IMP-4 Submit cactus wren habitat restoration and population meta-analysis datasets, results, and management strategy recommendations for north San Diego County to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Success Criteria 2013-2021: Restore =75 Acres of High Quality Cactus Scrub and Increase the San Pasqual Valley/Lake Hodges Genetic Cluster to =90 Territories on Conserve 2021
Code Obj. code Statement
CAMBRU-3 MON-SURV-SPEC From 2017 to 2021, use a standardized protocol to survey for cactus wrens to determine territory, pairing and banding status and collect habitat covariate data in cactus scrub habitats on Conserved Lands in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
CAMBRU-4 MON-RES-SPEC From 2017 to 2019, continue the Coastal Cactus Wren Demography, Vegetation and Arthropod Study begun in 2015 to investigate relationships between habitat quality and wren reproduction, dispersal and survival in the Otay and San Diego/El Cajon genetic clusters (see occurrence table). Habitat quality is measured at the territory scale and characterized by vegetation attributes, arthropod community composition, nestling diet, and potential availability of arthropod prey based on plant associations. Use the results to develop specific restoration recommendations to enhance habitat suitability and food resources important to cactus wren reproduction and survival.
CAMBRU-5 MON-RES-GEN From 2017-2019, in conjunction with standardized surveys and with banding activities for the Coastal Cactus Wren Demography, Vegetation and Arthropod Study, collect feather or blood samples from nestling and adult cactus wren at sites where wrens were sampled in 2011-2012 for the Southern California Cactus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay, San Diego/El Cajon, and San Pasqual genetic clusters (see occurrence table) and evaluate whether there are potential threats to long-term population sustainability from inbreeding. Based on these results, prepare specific recommendations for managing gene flow and/or population expansion to enhance genetic diversity and effective population size.
CAMBRU-7 MGT-IMP-IEX In 2017-2021, continue supporting restoration of cactus scrub based upon ICR's Restoration Analyses for the San Pasqual Valley/Lake Hodges coastal cactus wren genetic cluster (see occurrence table) to: rehabilitate cactus scrub destroyed or degraded by the 2007 Witch Fire; to expand occurrences, particularly adjacent to Lake Hodges; to improve connectivity within the genetic cluster; and as needed, to manage high risk of anthropogenic predation of adults and nestlings.
CAMBRU-9 MGT-IMP-FMGT Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.

regional and/or local NFO 2018 VF
MON-IMP-IMG CENPAR-1

Management units: 5, 6

In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2018 with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV

regional NFO 2018, 2019 SL
MGT-RSUP-MGT CHANIV-1

Management units: 1, 7

In 2018 and 2019, coordinate with land managers and the wildlife agencies to determine if there are gaps in monitoring and/or management that could use regional support and to develop joint management recommendations.

Action Statement Action status Projects
RSUP-1 Hold meetings with land managers and the wildlife agencies to identify any management and/or monitoring gaps that could use regional support and to develop joint management recommendations.
Criteria Deadline year
Gaps Identified and Recommendations Created in Coordination with Land Managers and Wildlife Agencies 2021
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-MONPL CHANIV-2

Management units: 1, 7

From 2017 to 2021, continue the existing survey efforts for western snowy plover implemented by the wildlife agencies and military.

Action Statement Action status Projects
IMP-1 Submit monitoring data and management recommendations to the MSP web portal.
Criteria Deadline year
Western Snowy Plover Surveys and Reports Completed Annually 2021
local NFO 2020, 2021 SL
MGT-IMP-MGT CHANIV-3

Management units: 1, 7

Beginning in 2020, implement management actions on Conserved Lands as identified through monitoring and the coordination efforts with the land managers and wildlife agencies.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP web portal.
Criteria Deadline year
By 2021, at least 1 Management Actions Implemented for Western Snowy Plover 2021
local NFO 2020, 2021 SL
MON-IMP-MONPL CHANIV-4

Management units: 1, 7

Beginning in 2020, monitor the effectiveness of management actions implemented for western snowy plover on Conserved Lands.

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal.
Criteria Deadline year
Monitoring data submitted to MSP web portal within one year of management actions being completed. 2021

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG CHLMAR-1

Management units: 1

Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CHLMAR-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHLMAR-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHLMAR-4 MON-DEV-MODL in 2018, develop models predicting habitat suitability under future climate scenarios and combine the habitat models with projected increases in sea level and urban development to evaluate and prioritize sites for establishing new occurrences of salt marsh bird's-beak. Formulate management recommendations to reduce risk and increase persistence of salt marsh bird's-beak populations under changing conditions of climate and land use.
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-6 MGT-IMP-SBPL From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
CHLMAR-8 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for salt marsh bird's-beak in the MSP Rare Plant Management Plan.
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG CHLMAR-2

Management units: 1

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CHLMAR-1 MON-IMP-IMG Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional NFO 2018 SL
MON-DEV-MODL CHLMAR-4

Management units: 1

in 2018, develop models predicting habitat suitability under future climate scenarios and combine the habitat models with projected increases in sea level and urban development to evaluate and prioritize sites for establishing new occurrences of salt marsh bird's-beak. Formulate management recommendations to reduce risk and increase persistence of salt marsh bird's-beak populations under changing conditions of climate and land use.

Action Statement Action status Projects
DEV-1 Work with land managers, species experts, scientists and other stakeholders to identify opportunities to manage for long-term persistence of salt marsh bird's-beak under changing climate and land use conditions. On hold
DEV-2 Submit project metadata, models, data layers and report with management recommendation to the MSP Web Portal. On hold
Criteria Deadline year
Modeling and Management Recommendations Completed by 2019 2021
Threat Name Threat Code
Climate changeCLICHN
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHLMAR-1 MON-IMP-IMG Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
CHLMAR-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for salt marsh bird's-beak occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing to enhance existing occurrences and establish new occurrences.
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
Regional NFO 2018 SL
MGT-PRP-SBPL CHLMAR-5

Management units: 1

Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-2 Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2019, Completed Salt Marsh Bird's-beak Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
CHLMAR-1 MON-IMP-IMG Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
CHLMAR-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for salt marsh bird's-beak occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing to enhance existing occurrences and establish new occurrences.
CHLMAR-4 MON-DEV-MODL in 2018, develop models predicting habitat suitability under future climate scenarios and combine the habitat models with projected increases in sea level and urban development to evaluate and prioritize sites for establishing new occurrences of salt marsh bird's-beak. Formulate management recommendations to reduce risk and increase persistence of salt marsh bird's-beak populations under changing conditions of climate and land use.
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-6 MGT-IMP-SBPL From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
Regional and/or Local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-SBPL CHLMAR-6

Management units: 1

From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2022, =2 Highest Priority Actions Implemented for Salt Marsh Bird's-beak from the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
CHLMAR-8 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for salt marsh bird's-beak in the MSP Rare Plant Management Plan.
regional NFO 2018, 2019 SL
MGT-PRP-MGTPL CHLMAR-7

Management units: 1

In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the salt marsh bird's-beak section in the MSP Rare Plant Management Plan. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to salt marsh bird's-beak occurrences. some occurrences are in progress
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-4 Develop an implementation plan for salt marsh bird's-beak that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2019, Completed Salt Marsh Bird's-beak Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
CHLMAR-1 MON-IMP-IMG Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
CHLMAR-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHLMAR-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHLMAR-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for salt marsh bird's-beak occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing to enhance existing occurrences and establish new occurrences.
CHLMAR-4 MON-DEV-MODL in 2018, develop models predicting habitat suitability under future climate scenarios and combine the habitat models with projected increases in sea level and urban development to evaluate and prioritize sites for establishing new occurrences of salt marsh bird's-beak. Formulate management recommendations to reduce risk and increase persistence of salt marsh bird's-beak populations under changing conditions of climate and land use.
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-6 MGT-IMP-SBPL From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CHLMAR-8 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for salt marsh bird's-beak in the MSP Rare Plant Management Plan.
CHLMAR-9 MON-IMP-MGTPL In 2019, begin monitoring effectiveness of implementation of highest priority management actions identified in the salt marsh bird's-beak section in the MSPRare Plant Management Plan.
Regional and/or Local NFO 2019, 2020, 2021 SL
MGT-IMP-MGTPL CHLMAR-8

Management units: 1

In 2019, begin implementing highest priority management actions identified for salt marsh bird's-beak in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =2 High Priority Management Actions Implemented for Salt Marsh Bird's-beak from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
CHLMAR-5 MGT-PRP-SBPL Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHLMAR-6 MGT-IMP-SBPL From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
CHLMAR-9 MON-IMP-MGTPL In 2019, begin monitoring effectiveness of implementation of highest priority management actions identified in the salt marsh bird's-beak section in the MSPRare Plant Management Plan.
Regional and/or Local NFO 2019, 2020, 2021 SL
MON-IMP-MGTPL CHLMAR-9

Management units: 1

In 2019, begin monitoring effectiveness of implementation of highest priority management actions identified in the salt marsh bird's-beak section in the MSPRare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
CHLMAR-7 MGT-PRP-MGTPL In 2018, begin preparing a salt marsh bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and enhance large occurrences, enhance and expand at least 3 small occurrences, and establish at least 1 new occurrence on Conserved Lands (see occurrence table). Management actions should be based upon an assessment of data on occurrence status, habitat and threats and include recommendations for creating salt marsh habitat and establishing new occurrences in response to a projected rise in sea level and for re-establishing historic occurrences as necessary for gene flow and long term persistence. Include recommendations from the 2017 genetics study, MSP Seed Collection, Banking and Bulking Plan, relevant best management practices (BMPs), and for monitoring the effectiveness of management actions.
CHLMAR-8 MGT-IMP-MGTPL In 2019, begin implementing highest priority management actions identified for salt marsh bird's-beak in the MSP Rare Plant Management Plan.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG CHOORC-1

Management units: 6, 7

Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at Orcutt's spineflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHOORC-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.
CHOORC-5 MGT-PRP-SBPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHOORC-6 MGT-IMP-SBPL In 2020, begin implementing high priority actions for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG CHOORC-2

Management units: 6, 7

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at Orcutt's spineflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. in progress Otay Mesa Rare Plants
IMP-2 Submit project metadata and management data to the MSP Web Portal. in progress Otay Mesa Rare Plants
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2017 SL
MON-SURV-SPEC CHOORC-3

Management units: 6, 7

In 2017, continue efforts begun in 2015 to survey historic Orcutt's spineflower locations to: determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. In progress
SURV-2 Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. In progress
Criteria Deadline year
Baseline Surveys and Report Completed by 2018 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
regional NFO 2017 SL
MGT-IMP-IEX CHOORC-4

Management units: 6, 7

In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.

Action Statement Action status Projects
IMP-1 Establish 4 new occurrences of Orcutt in progress
IMP-2 Use BMPs for site preparation (Bauder 2010a,b). Sites with ice plant or Acacia shrubs should be cleared of these invasive plants and duff and then watched for at least 2 years with suitable growing conditions to determine if there are viable spineflower in progress
IMP-3 Maintain newly established occurrences so that there is <20% invasive non-native absolute cover, minimal encroachment of native plants (based upon standards used at the Point Loma Naval Base), and no ground disturbance from erosion or trampling. in progress
IMP-4 Use the seed collection and bulking plan to determine seed sources and timing and amount of seeding. in progress
IMP-5 Submit project metadata, monitoring and management data to MSP web portal. in progress
Criteria Deadline year
4 New Occurrences of Orcutt's Spineflower Established by 2018 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-3 MON-SURV-SPEC In 2017, continue efforts begun in 2015 to survey historic Orcutt's spineflower locations to: determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2019 SL
MGT-PRP-SBPL CHOORC-5

Management units: 6, 7

In 2019, begin preparing a section for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's spineflower section in the MSP Seed Collection, Banking and Bulking Plan. On hold
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. On hold
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. On hold
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). On hold
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. On hold
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. On hold
Criteria Deadline year
By 2020, Completed Section for Orcutt's Spineflower in MSP Seed Collection Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
CHOORC-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2020, 2021 SL
MGT-IMP-SBPL CHOORC-6

Management units: 6, 7

In 2020, begin implementing high priority actions for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =1 Highest Priority Actions Implemented for Orcutt's Spineflower from the MSP Seed Collection, Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-5 MGT-PRP-SBPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
regional NFO 2019 SL
MGT-PRP-MGTPL CHOORC-7

Management units: 6, 7

In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Orcutt's spineflower in the MSP Rare Plant Management Plan. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's spineflower occurrences. on hold
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-4 Develop an implementation plan for Orcutt's spineflower that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. on hold
Criteria Deadline year
By 2020, Completed Section for Orcutt's Spineflower in MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
CHOORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at Orcutt's spineflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CHOORC-3 MON-SURV-SPEC In 2017, continue efforts begun in 2015 to survey historic Orcutt's spineflower locations to: determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
CHOORC-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.
CHOORC-5 MGT-PRP-SBPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
CHOORC-8 MGT-IMP-MGTPL Beginning in 2020, begin implementation of the highest priority management actions for Orcutt's spineflower identified in the MSP Rare Plant Management Plan.
CHOORC-9 MON-IMP-MGTPL Monitor the effectiveness of highest priority management actions implemented for Orcutt's spineflower.
Regional NFO 2020, 2021 SL
MGT-IMP-MGTPL CHOORC-8

Management units: 6, 7

Beginning in 2020, begin implementation of the highest priority management actions for Orcutt's spineflower identified in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =1 High Priority Management Action Initiated for Orcutt's spineflower from the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2021 SL
MON-IMP-MGTPL CHOORC-9

Management units: 6, 7

Monitor the effectiveness of highest priority management actions implemented for Orcutt's spineflower.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
CHOORC-7 MGT-PRP-MGTPL In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
CHOORC-8 MGT-IMP-MGTPL Beginning in 2020, begin implementation of the highest priority management actions for Orcutt's spineflower identified in the MSP Rare Plant Management Plan.

regional NFO 2019 SO
MON-SURV-SPEC CIRCYA-1

Management units: 1, 3, 4, 5, 6, 7, 8

In 2019, conduct a survey for northern harrier and other associated raptors to document the harrier's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.

Action Statement Action status Projects
SURV-1 Submit monitoring data and management recommendations to MSP web portal Available for implementation
Criteria Deadline year
Northern Harrier Surveys and Reports Completed by 2020 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV
local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG CIRCYA-2

Management units: 1, 3, 4, 5, 6, 7, 8

From 2017 to 2021, annually inspect the existing nesting occurrences of northern harrier, taking precautions to avoid disturbance, to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. Available for implementation
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. Available for implementation
IMP-3 Submit monitoring data and management recommendations to MSP web portal Available for implementation
Criteria Deadline year
Surveys Completed Annually with management recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG CIRCYA-3

Management units: 1, 3, 4, 5, 6, 7, 8

From 2017-2021, perform routine management activities such as protecting nesting occurrences from disturbance through fencing, signage, and enforcement.

Action Statement Action status Projects
IMP-1 Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. Available for implementation
IMP-2 Submit project metadata and management data to MSP web portal. Available for implementation
Criteria Deadline year
Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV
regional NFO 2020 SO
MGT-PRP-MGTPL CIRCYA-4

Management units: 1, 3, 4, 5, 6, 7, 8

In 2020, prepare a management plan for northern harrier that prioritizes management actions to protect nesting sites from disturbance and enhances habitat using data from annual IMG monitoring.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. Available for implementation
PRP-2 Develop a management plan for northern harrier that prioritizes management actions for the next five years. Available for implementation
PRP-3 Submit management plan to MSP web portal Available for implementation
Criteria Deadline year
Management Plan for Northern Harrier prepared by 2021 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV
regional and/or local NFO 2021 SO
MGT-IMP-MGTPL CIRCYA-5

Management units: 1, 3, 4, 5, 6, 7, 8

Beginning in 2021, implement the highest priority management actions for northern harrier on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the management plan. waiting for precedent action
IMP-2 Submit project data and management actions to MSP web portal waiting for precedent action
Criteria Deadline year
Management actions implemented for Northern Harrier 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV
regional and/or local NFO 2021 SO
MON-IMP-MGTPL CIRCYA-6

Management units: 1, 3, 4, 5, 6, 7, 8

Beginning in 2021, monitor the effectiveness of management actions implemented for northern harrier on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring completed and data and report submited within 1 year of management actions being completed. 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Pesticides
Urban developmentURBDEV

regional and/or local NFO 2018, 2020 SL
MON-IMP-IMG CLICHA-1

Management units: 3, 4

Beginning in 2018, inspect San Miguel savory occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.

Action Statement Action status Projects
IMP-1 Conduct regional monitoring protocol surveys to assess abundance status and quantify potential threats. on hold
IMP-2 Based upon occurrence status and threats, determine if routine management or more intensive management is warranted. on hold
Criteria Deadline year
Surveys Completed Every 2 Years with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CLICHA-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CLICHA-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CLICHA-3 MGT-PRP-SBPL In 2019, begin preparing a San Miguel savory section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CLICHA-5 MGT-PRP-MGTPL In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG CLICHA-2

Management units: 3, 4

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. available for implementation
IMP-2 Submit monitoring and management data to the SC-MTX website portal. available for implementation
IMP-2 Submit monitoring and management data to the SC-MTX website portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CLICHA-1 MON-IMP-IMG Beginning in 2018, inspect San Miguel savory occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
CLICHA-5 MGT-PRP-MGTPL In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional NFO 2019 SL
MGT-PRP-SBPL CLICHA-3

Management units: 3, 4

In 2019, begin preparing a San Miguel savory section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Miguel savory section in the MSP Seed Collection, Banking and Bulking Plan. On hold
PRP-2 Prepare the seed collection plan to include recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. On hold
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. On hold
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). On hold
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. On hold
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. On hold
Criteria Deadline year
By 2020, Completed San Miguel Savory Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
CLICHA-1 MON-IMP-IMG Beginning in 2018, inspect San Miguel savory occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
CLICHA-4 MGT-IMP-SBPL In 2020, begin implementing high priority actions for San Miguel savory in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CLICHA-5 MGT-PRP-MGTPL In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
Regional and/or Local NFO 2020, 2021 SL
MGT-IMP-SBPL CLICHA-4

Management units: 3, 4

In 2020, begin implementing high priority actions for San Miguel savory in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2024, =1 Highest Priority Action Implemented for San Miguel Savory from the MSP Seed Banking and Bulking Plan 2021
Code Obj. code Statement
CLICHA-3 MGT-PRP-SBPL In 2019, begin preparing a San Miguel savory section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CLICHA-6 MGT-IMP-MGTPL In 2020, begin implementing highest priority management actions identified for San Miguel savory in the MSP Rare Plant Management Plan.
regional NFO 2019, 2020 SL
MGT-PRP-MGTPL CLICHA-5

Management units: 3, 4

In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Miguel savory section in the MSP Rare Plant Management Plan. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to San Miguel savory occurrences. on hold
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-4 Develop an implementation plan for San Miguel savory that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. on hold
Criteria Deadline year
By 2020, Completed San Miguel Savory Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
CLICHA-1 MON-IMP-IMG Beginning in 2018, inspect San Miguel savory occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
CLICHA-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CLICHA-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
CLICHA-3 MGT-PRP-SBPL In 2019, begin preparing a San Miguel savory section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
CLICHA-4 MGT-IMP-SBPL In 2020, begin implementing high priority actions for San Miguel savory in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CLICHA-6 MGT-IMP-MGTPL In 2020, begin implementing highest priority management actions identified for San Miguel savory in the MSP Rare Plant Management Plan.
CLICHA-7 MON-IMP-MGTPL In 2020, begin monitoring effectiveness of implementation of highest priority management actions identified in the San Miguel savory section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2020, 2021 SL
MGT-IMP-MGTPL CLICHA-6

Management units: 3, 4

In 2020, begin implementing highest priority management actions identified for San Miguel savory in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2024, =1 High Priority Management Action Implemented for San Miguel Savory Section from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
CLICHA-4 MGT-IMP-SBPL In 2020, begin implementing high priority actions for San Miguel savory in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
CLICHA-5 MGT-PRP-MGTPL In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
CLICHA-7 MON-IMP-MGTPL In 2020, begin monitoring effectiveness of implementation of highest priority management actions identified in the San Miguel savory section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2020, 2021 SL
MON-IMP-MGTPL CLICHA-7

Management units: 3, 4

In 2020, begin monitoring effectiveness of implementation of highest priority management actions identified in the San Miguel savory section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
CLICHA-5 MGT-PRP-MGTPL In 2019, begin preparing a San Miguel savory section in the MSP Rare Plant Management Plan that prioritizes management actions to enhance at least 3 occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, if determined to be necessary for gene flow and population persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
CLICHA-6 MGT-IMP-MGTPL In 2020, begin implementing highest priority management actions identified for San Miguel savory in the MSP Rare Plant Management Plan.

regional and/or local NFO 2021 VF
MON-IMP-IMG CYLCAL-1

Management units: 1, 2, 3

In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus, and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2021 with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ERIPAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
FERVIR-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SS
MON-IMP-IMG DEICON-1

Management units: 3

In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record spatial extent, estimate abundance, and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine if routine management or more intensive management is warranted. some occurrences are in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP web portal. some occurrences are in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DEICON-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at Otay tarplant occurrences on Conserved Lands (see occurrence table) . Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DEICON-4 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Otay tarplant occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
local NFO 2017, 2018, 2019, 2020, 2021 SS
MGT-IMP-IMG DEICON-2

Management units: 3

Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at Otay tarplant occurrences on Conserved Lands (see occurrence table) . Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. available for implementation
IMP-2 Submit project metadata, monitoring and management recommendations to the MSP web portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DEICON-1 MON-IMP-IMG In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record spatial extent, estimate abundance, and collect habitat and threat covariate data to determine management needs.
DEICON-3 MGT-DEV-BMP In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
DEICON-4 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Otay tarplant occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
regional NFO 2017 SS
MGT-DEV-BMP DEICON-3

Management units: 3

In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.

Action Statement Action status Projects
DEV-1 Conduct experiments using mowing, prescribed burns herbicide and potentially grazing to control invasive non-native grasses and forbs at a landscape-scale and to compare drill seeding versus hand broadcast seeding in order to determine economical and effect. in progress
DEV-2 Based upon experiment results, develop explicit BMPs for the restoration of Otay tarplant. Submit project metadata, monitoring datasets and BMP report to MSP web portal. in progress
Criteria Deadline year
BMPs Developed for Restoration of Otay tarplant by 2017 2021
Code Obj. code Statement
DEICON-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at Otay tarplant occurrences on Conserved Lands (see occurrence table) . Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
regional NFO 2018, 2019, 2020, 2021 SS
MGT-IMP-IEX DEICON-5

Management units: 3

Beginning in 2018, and continuing for 3 years at the 3 Otay tarplant restoration sites initiated under the South County Grasslands project, use BMPs to maintain the maximum occupied extent and a surrounding buffer area equal to 25% of this extent by preventing ground disturbance and reducing nonnative plants and thatch to less than 20% total cover and thatch to <5 cm tall.

Action Statement Action status Projects
IMP-1 Conduct invasive plant control annually using BMPs until success criteria are met and then as needed thereafter. waiting for precedent action
IMP-2 Submit project metadata and management data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2021, 3 Otay Tarplant Occurrences Enhanced/Established and Reports Submitted 2021
Code Obj. code Statement
DEICON-3 MGT-DEV-BMP In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
regional NFO 2018 SS
MGT-PRP-MGTPL DEICON-6

Management units: 3

In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Otay tarplant in the MSP Rare Plant Management Plan. some occurrences are in progress
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Otay tarplant occurrences. some occurrences are in progress
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. some occurrences are in progress
PRP-4 Develop an implementation plan for Otay tarplant that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. some occurrences are in progress
PRP-5 Submit project metadata, project datasets, and the MSP Rare Plant Management Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2019, Completed Otay Tarplant Section in the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
DEICON-1 MON-IMP-IMG In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record spatial extent, estimate abundance, and collect habitat and threat covariate data to determine management needs.
DEICON-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at Otay tarplant occurrences on Conserved Lands (see occurrence table) . Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DEICON-3 MGT-DEV-BMP In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
DEICON-4 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Otay tarplant occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DEICON-5 MGT-IMP-IEX Beginning in 2018, and continuing for 3 years at the 3 Otay tarplant restoration sites initiated under the South County Grasslands project, use BMPs to maintain the maximum occupied extent and a surrounding buffer area equal to 25% of this extent by preventing ground disturbance and reducing nonnative plants and thatch to less than 20% total cover and thatch to <5 cm tall.
DEICON-7 MGT-IMP-MGTPL In 2019, begin implementation of highest priority management actions for Otay tarplant identified in the MSP Rare Plant Management Plan.
DEICON-8 MON-IMP-MGTPL In 2019, begin monitoring the effectiveness of implementation of highest priority management actions identified in the Otay tarplant section in the MSP Rare Plant Management Plan.
DEICON-9 MGT-PRP-SBPL In 2018, begin preparing a section for Otay tarplant in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for:collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional and/or Local NFO 2019, 2020, 2021 SS
MGT-IMP-MGTPL DEICON-7

Management units: 3

In 2019, begin implementation of highest priority management actions for Otay tarplant identified in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata and management datasets, report to MSP web portal waiting for precedent action
Criteria Deadline year
By 2023, =1 High Priority Management Action Implemented for Otay tarplant from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
DEICON-8 MON-IMP-MGTPL In 2019, begin monitoring the effectiveness of implementation of highest priority management actions identified in the Otay tarplant section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2019, 2020, 2021 SS
MON-IMP-MGTPL DEICON-8

Management units: 3

In 2019, begin monitoring the effectiveness of implementation of highest priority management actions identified in the Otay tarplant section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
DEICON-7 MGT-IMP-MGTPL In 2019, begin implementation of highest priority management actions for Otay tarplant identified in the MSP Rare Plant Management Plan.
Regional NFO 2018 SS
MGT-PRP-SBPL DEICON-9

Management units: 3

In 2018, begin preparing a section for Otay tarplant in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for:collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Otay tarplant section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2019, Completed Otay Tarplant Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
DEICON-1 MON-IMP-IMG In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record spatial extent, estimate abundance, and collect habitat and threat covariate data to determine management needs.
DEICON-3 MGT-DEV-BMP In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
DEICON-4 MON-RES-GEN In 2017, continue a study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Otay tarplant occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DEICON-6 MGT-PRP-MGTPL In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
DEICON-10 MGT-IMP-SBPL In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Otay tarplant to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
Regional and/or Local NFO 2014, 2015, 2016, 2017, 2018, 2019, 2020, 2021 SS
MGT-IMP-SBPL DEICON-10

Management units: 3

In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Otay tarplant to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. some occurrences are in progress
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2023, > 1 Highest Priority Action Implemented for Otay Tarplant from the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
DEICON-9 MGT-PRP-SBPL In 2018, begin preparing a section for Otay tarplant in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for:collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
Regional NFO 2017 SS
MON-RES-SPEC DEICON-11

Management units: 3

In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for Otay tarplant and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.

Action Statement Action status Projects
RES-1 Test soils at potential expansion sites and compare to occupied reference sites to determine site suitability based on soils. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-2 Prepare habitat suitability models under current environmental conditions and for different scenarios of climate change to delineate potential future habitat. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-3 Collect covariate data on vegetation composition and cover (alliance and association-level mapping), soils, invasive plants and other threats for selected populations. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-4 Prioritize locations for conservation, management, and future surveys based on predicted distributions and environmental correlates. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-5 Submit project metadata, monitoring data, habitat models, analyses, and report to MSP web portal. In progress Enhancing the Resilience of Edaphic Endemic Plants
Criteria Deadline year
Refined Models and Prioritized Future Survey Locations for Otay Tarplant by 2018 2021
Threat Name Threat Code
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DEICON-10 MGT-IMP-SBPL In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Otay tarplant to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG DICORC-1

Management units: 1, 3

From 2017 to 2021, inspect Orcutt's bird's-beak occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. in progress
Criteria Deadline year
Surveys Completed Annually with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DICORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DICORC-4 MON-SURV-SPEC In 2019, survey historic Orcutt's bird's-beak locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG DICORC-2

Management units: 1, 3

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DICORC-1 MON-IMP-IMG From 2017 to 2021, inspect Orcutt's bird's-beak occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2019 SL
MON-SURV-SPEC DICORC-4

Management units: 1, 3

In 2019, survey historic Orcutt's bird's-beak locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. On hold
SURV-2 Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. On hold
Criteria Deadline year
Surveys and Report Completed by 2020 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2020 SL
MGT-PRP-SBPL DICORC-6

Management units: 1, 3

In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-2 Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2021, Completed Orcutt's Bird's-beak Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
DICORC-1 MON-IMP-IMG From 2017 to 2021, inspect Orcutt's bird's-beak occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DICORC-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Orcutt's bird's-beak occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DICORC-5 MGT-IMP-IEX From 2017 to 2019, enhance Orcutt's bird's-beak at the Cal Terraces/Dennery Canyon occurrence (see occurrence table). Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than or equal to 20% absolute cover within the occurrence’s occupied extent and adjacent suitable habitat.
DICORC-7 MGT-IMP-SBPL From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional and/or Local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-SBPL DICORC-7

Management units: 1, 3

From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2025, =1 Highest Priority Action Implemented for Orcutt'sBird's-beak from the MSP Seed Banking and Bulking Plan 2021
Code Obj. code Statement
DICORC-5 MGT-IMP-IEX From 2017 to 2019, enhance Orcutt's bird's-beak at the Cal Terraces/Dennery Canyon occurrence (see occurrence table). Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than or equal to 20% absolute cover within the occurrence’s occupied extent and adjacent suitable habitat.
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
DICORC-9 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's bird's-beak in the MSP Rare Plant Management Plan.
regional NFO 2020 SL
MGT-PRP-MGTPL DICORC-8

Management units: 1, 3

In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's bird's-beak occurrences. on hold
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-4 Develop an implementation plan for Orcutt's bird's-beak that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. on hold
Criteria Deadline year
By 2021, Completed Orcutt's Bird's-beak Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
DICORC-1 MON-IMP-IMG From 2017 to 2021, inspect Orcutt's bird's-beak occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DICORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DICORC-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for Orcutt's bird's-beak occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting, bulking and distributing seed to enhance existing occurrences or establish new occurrences.
DICORC-4 MON-SURV-SPEC In 2019, survey historic Orcutt's bird's-beak locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
DICORC-5 MGT-IMP-IEX From 2017 to 2019, enhance Orcutt's bird's-beak at the Cal Terraces/Dennery Canyon occurrence (see occurrence table). Invasive plant control should be conducted using BMPs so that invasive plants are reduced to less than or equal to 20% absolute cover within the occurrence’s occupied extent and adjacent suitable habitat.
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-7 MGT-IMP-SBPL From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
DICORC-9 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's bird's-beak in the MSP Rare Plant Management Plan.
DICORC-10 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SL
MGT-IMP-MGTPL DICORC-9

Management units: 1, 7

In 2021, begin implementing highest priority management actions identified for Orcutt's bird's-beak in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2025, =1 High Priority Management Action Implemented for Orcutt's Bird's-beak from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-7 MGT-IMP-SBPL From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
DICORC-10 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan.
regional and/or local NFO 2021 SL
MON-IMP-MGTPL DICORC-10

Management units: 1, 7

In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
DICORC-6 MGT-PRP-SBPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DICORC-7 MGT-IMP-SBPL From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
DICORC-8 MGT-PRP-MGTPL In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
DICORC-9 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for Orcutt's bird's-beak in the MSP Rare Plant Management Plan.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG DUDBLO-1

Management units: 1, 6

From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. in progress
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. in progress
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DUDBLO-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Blochman's dudleya occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DUDBLO-4 MGT-PRP-SBPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DUDBLO-6 MGT-PRP-MGTPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG DUDBLO-2

Management units: 1, 6

Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Blochman's dudleya occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-4 MGT-PRP-SBPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DUDBLO-6 MGT-PRP-MGTPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence
Regional NFO 2019 SL
MON-SURV-SPEC DUDBLO-3

Management units: 1, 2, 6, 7

In 2019, survey historic Blochman's dudleya locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. On hold
SURV-2 Submit project metadata, habitat mapping, and a report with site prioritizations and recommendations for management based upon occurrence status, habitat and threats assessments to the MSP Web Portal. On hold
Criteria Deadline year
Surveys and Report Completed by 2020 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DUDBLO-4 MGT-PRP-SBPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DUDBLO-6 MGT-PRP-MGTPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence
Regional NFO 2021 SL
MGT-PRP-SBPL DUDBLO-4

Management units: 1, 2, 6, 7

In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Blochman's dudleya section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2022, Completed Blochman's Dudleya Section in MSP Seed Collection, Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-6 MGT-PRP-MGTPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence
regional NFO 2021 SL
MGT-PRP-MGTPL DUDBLO-6

Management units: 1, 2, 6, 7

In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Blochman's dudleya in the MSP Rare Plant Management Plan. waiting for precedent action
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Blochman's dudleya populations. waiting for precedent action
PRP-3 Use occurrence status and threats data to develop management recommendations to reduce threats and promote resilience of occurrences. waiting for precedent action
PRP-4 Develop an implementation plan for Blochman's dudleya that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. waiting for precedent action
PRP-5 Submit project metadata, project datasets, and MSP Rare Plant Management Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, Completed Blochman's Dudleya Section in MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-1 MON-IMP-IMG From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DUDBLO-3 MON-SURV-SPEC In 2019, survey historic Blochman's dudleya locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
DUDBLO-4 MGT-PRP-SBPL In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG DUDBRE-1

Management units: 6, 7

In 2017, continue annual inspections of short-leaved dudleya on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. available for implementation
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. available for implementation
Criteria Deadline year
Surveys Completed Every Year with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DUDBRE-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at short leaved dudleya occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DUDBRE-3 MGT-PRP-SBPL In 2021, begin preparing a section for short-leaved dudleya in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and to provide seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
DUDBRE-4 MGT-PRP-MGTPL In 2021, begin preparing a section for short-leaved dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Include recommendations for short-leaved dudleay from MSP Seed Collection, Banking and Bulking Plan, relevant BMPs, and recommendations for monitoring effectiveness of management actions.
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG DUDBRE-2

Management units: 6, 7

Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at short leaved dudleya occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to at most 20% absolute cover. available for implementation Otay Mesa Rare Plants
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation Otay Mesa Rare Plants
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DUDBRE-1 MON-IMP-IMG In 2017, continue annual inspections of short-leaved dudleya on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
local NFO 2021 SL
MGT-PRP-SBPL DUDBRE-3

Management units: 6, 7

In 2021, begin preparing a section for short-leaved dudleya in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and to provide seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the short-leaved dudleya section of the MSP Seed Collection, Banking and Bulking Plan. on hold
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. on hold
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. on hold
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). on hold
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. on hold
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. on hold
Criteria Deadline year
By 2022, Completed Short-leaved dudleya Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DUDBRE-1 MON-IMP-IMG In 2017, continue annual inspections of short-leaved dudleya on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
DUDBRE-4 MGT-PRP-MGTPL In 2021, begin preparing a section for short-leaved dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Include recommendations for short-leaved dudleay from MSP Seed Collection, Banking and Bulking Plan, relevant BMPs, and recommendations for monitoring effectiveness of management actions.
regional NFO 2021 SL
MGT-PRP-MGTPL DUDBRE-4

Management units: 6, 7

In 2021, begin preparing a section for short-leaved dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Include recommendations for short-leaved dudleay from MSP Seed Collection, Banking and Bulking Plan, relevant BMPs, and recommendations for monitoring effectiveness of management actions.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for short-leaved dudleya in the MSP Rare Plant Management Plan. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to short-leaved dudleya occurrences. on hold
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-4 Develop an implementation plan for short-leaved dudleya that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal.
Criteria Deadline year
By 2022, Completed Short-leaved dudleya section in the MSP Rare Plant Management Plan 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
DUDBRE-1 MON-IMP-IMG In 2017, continue annual inspections of short-leaved dudleya on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
DUDBRE-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at short leaved dudleya occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
DUDBRE-3 MGT-PRP-SBPL In 2021, begin preparing a section for short-leaved dudleya in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and to provide seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

regional NFO 2017, 2018, 2019 SL
MON-RES-SPEC EMPTRA-1

Management units: 1, 4, 6, 8, 9, 10, 11

In 2017-2019, continue the 5-year breeding bird study begun by USGS in 2015 of southwestern willow flycatcher in the San Luis Rey River and other drainages to determine the status in the MSPA and impacts to riparian habitat from SHB/Fusarium complex and other threats. Prepare site-specific management recommendations based on survey results.

Action Statement Action status Projects
RES-1 Submit monitoring data and management recommendations to MSP web portal In progress
Criteria Deadline year
Southwestern Willow Flycatcher Surveys and Reports Completed by 2020 2021
regional NFO 2020, 2021 SL
MGT-PRP-MGTPL EMPTRA-2

Management units: 1, 4, 6, 8, 9, 10, 11

In 2020-2021, prepare a management plan for southwestern willow flycatcher based on survey recommendations and that includes provisions for reducing potential impacts of SHB/Fusarium infestation in occupied or potential habitat. Incorporate SHB/Fusarium monitoring results into the management plan, particularly along the San Luis Rey River.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. Available for implementation
PRP-2 Develop an implementation plan for southwestern willow flyycatcher that prioritizes management actions for the next five years. Available for implementation
PRP-3 Submit management plan to MSP web portal Available for implementation
Criteria Deadline year
Management Plan for Southwestern Willow Flycatcher prepared by end 2021 2021
regional NFO 2021 SL
MGT-IMP-MGTPL EMPTRA-3

Management units: 1, 4, 6, 8, 9, 10, 11

Beginning in 2021, implement the highest priority management actions for southwestern willow flycatcher on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the management plan. waiting for precedent action
IMP-2 Submit project data and management actions to MSP web portal waiting for precedent action
Criteria Deadline year
Management actions initiated for Southwestern Willow Flycatcher 2021
regional NFO 2021 SL
MON-IMP-MGTPL EMPTRA-4

Management units: 1, 4, 6, 8, 9, 10, 11

Beginning in 2021, monitor the effectiveness of management actions implemented for southwestern willow flycatcher on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring completed and data and report submitting within 1 year of management actions being completed. 2021

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-TRAN EMYMAR-1

Management units: 3, 4, 5, 6, 8

From 2017 to 2021, continue efforts to expand and translocate occurrences of pond turtles to increase to self-sustaining levels in MU3 in the Sweetwater and Otay River Watersheds (at SPER, RJER, and other suitable sites) and identify, expand, and translocate pond turtles in at least 2 other watersheds in the MSPA, including but not limited to the San Diego and San Dieguito Rivers. Translocation efforts may include management of invasive aquatic and plant species, providing access protection, and headstart efforts.

Action Statement Action status Projects
IMP-1 Conduct routine management as needed at the Sycuan Peak ER occurrence of southwestern pond turtle. In progress
IMP-2 Conduct routine management as needed at the Rancho Jamul ER translocated occurrence of southwestern pond turtle. In progress
IMP-3 Continue to identify, begin management of invasive species, and translocate pond turtle to at least 2 suitable locations in the San Dieguito and San Diego River (e.g. El Monte Ponds, Boulder Creek Preserve) watersheds. In progress
IMP-4 Submit monitoring and management data to the regional MSP web portal. In progress
Criteria Deadline year
By 2021, 2 new occurrences translocated in the San Diego and San Dieguito River Watersheds; SPER and RJER occurrences increased by 20% through recruitment from 2017 leve 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-TRAN EMYMAR-2

Management units: 3, 4, 5, 6, 8

From 2017 to 2021, continue monitoring the effectiveness of southwestern pond turtle translocation experiments at SPER and RJER (see Table of Occurrences) and any additional translocated occurrences.

Action Statement Action status Projects
IMP-1 Continue to monitor the expanded and head-started occurrence and/or habitat at SPER and RJER to document success. In progress
IMP-2 Monitor other translocated occurrences to document success. waiting for precedent action
Criteria Deadline year
Southwestern Pond Turtle Translocation Monitoring and Reports Completed Annually 2021
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-IMG EMYMAR-4

Management units: 3, 4, 5, 6, 8

From 2017 to 2021, biennially inspect the existing occurrences of southwestern pond turtle to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.

Action Statement Action status Projects
IMP-1 Use regional IMG monitoring protocol to assess status, habitat, and quantify potential threats. Available for implementation
IMP-2 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. Available for implementation
IMP-3 Submit monitoring and management data to the regional MSP web portal. Available for implementation
Criteria Deadline year
Surveys Completed every two years with management recommendations 2021
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG EMYMAR-5

Management units: 3, 4, 5, 6, 8

From 2017 to 2021, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting populations from disturbance, removing invasive plants, and removing aquatic predators and exotic species (which compete and or prey on western pond turtle, primarily young) within the known occupied and suitable habitat.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance, controlling invasive plants, and removing invasive aquatic animals. some occurrences are in progress
IMP-2 Submit project metadata and management data to MSP web portal. some occurrences are in progress
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Code Obj. code Statement
EMYMAR-3 MGT-IMP-IEX From 2017 to 2021, implement invasive aquatic animal and invasive plant control at natural and translocated pond turtle occurrences as needed to increase recruitment and basking habitat.
regional NFO 2018 SL
MGT-PRP-MGTPL EMYMAR-6

Management units: 3, 4, 5, 6, 8

Beginning in 2018, prepare a management plan for southwestern pond turtles that includes identification of high priority management actions at sites with self sustaining populations, as well as actions to establish of at least 2 additional pond turtle populations to increase resilience to fire and other threats. Include guidance & prioritizations for next steps for translocations. The plan should include actions to manage threats from hydrology, debris, invasive animals and plants, and fire, and the creation of basking sites.

Action Statement Action status Projects
PRP-1 Develop a southwestern pond turtle management plan using the survey data with information on occurrence status and threats, habitat models, and management needs to determine if an appropriate location waiting for precedent action
PRP-2 The plan should prioritize management actions for the next five years and detail tasks, lead entities, responsibilities, timelines, and budgets waiting for precedent action
PRP-3 Submit management plan to MSP web portal waiting for precedent action
Criteria Deadline year
Management Plan for Southwestern pond turtle completed by 2018. 2018
Code Obj. code Statement
EMYMAR-1 MGT-IMP-TRAN From 2017 to 2021, continue efforts to expand and translocate occurrences of pond turtles to increase to self-sustaining levels in MU3 in the Sweetwater and Otay River Watersheds (at SPER, RJER, and other suitable sites) and identify, expand, and translocate pond turtles in at least 2 other watersheds in the MSPA, including but not limited to the San Diego and San Dieguito Rivers. Translocation efforts may include management of invasive aquatic and plant species, providing access protection, and headstart efforts.
EMYMAR-2 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of southwestern pond turtle translocation experiments at SPER and RJER (see Table of Occurrences) and any additional translocated occurrences.
EMYMAR-3 MGT-IMP-IEX From 2017 to 2021, implement invasive aquatic animal and invasive plant control at natural and translocated pond turtle occurrences as needed to increase recruitment and basking habitat.
EMYMAR-4 MON-IMP-IMG From 2017 to 2021, biennially inspect the existing occurrences of southwestern pond turtle to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.
EMYMAR-9 MGT-PRP-RESCPL Beginning in 2018, establish program and permits to allow emergency management actions for the Southwestern pond turtle during or immediately following wildfire events, such as implementation of emergency rescue and temporary translocation, to protect from potential loss or extirpation.
regional NFO 2019, 2020, 2021 SL
MGT-IMP-MGTPL EMYMAR-7

Management units: 3, 4, 5, 6, 8

Beginning in 2019, implement highest priority management actions as identified in the Southwestern pond turtle management plan.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the management plan. waiting for precedent action
IMP-4 Submit project metadata and management data to MSP web portal. unknown
Criteria Deadline year
By 2021, =1 High Priority Management Action Implemented from the Southwestern pond turtle Management Plan 2021
Code Obj. code Statement
EMYMAR-5 MGT-IMP-IMG From 2017 to 2021, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting populations from disturbance, removing invasive plants, and removing aquatic predators and exotic species (which compete and or prey on western pond turtle, primarily young) within the known occupied and suitable habitat.
regional NFO 2019, 2020, 2021 SL
MON-IMP-MGTPL EMYMAR-8

Management units: 3, 4, 5, 6, 8

Beginning in 2019, monitor the effectiveness of management actions implemented for the Southwestern pond turtle.

Action Statement Action status Projects
IMP-1 Submit monitoring data and report to MSP web portal waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
EMYMAR-5 MGT-IMP-IMG From 2017 to 2021, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting populations from disturbance, removing invasive plants, and removing aquatic predators and exotic species (which compete and or prey on western pond turtle, primarily young) within the known occupied and suitable habitat.
EMYMAR-6 MGT-PRP-MGTPL Beginning in 2018, prepare a management plan for southwestern pond turtles that includes identification of high priority management actions at sites with self sustaining populations, as well as actions to establish of at least 2 additional pond turtle populations to increase resilience to fire and other threats. Include guidance & prioritizations for next steps for translocations. The plan should include actions to manage threats from hydrology, debris, invasive animals and plants, and fire, and the creation of basking sites.

regional and/or local NFO 2021 VF
MON-IMP-IMG ERIPAL-1

Management units: 3, 4, 5, 6, 7

In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2021 with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CYLCAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus, and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
FERVIR-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

regional and/or local NFO 2017, 2019, 2021 SL
MON-IMP-IMG ERYAMM-1

Management units: 6, 7

Beginning in 2017, inspect occurrences of coast wallflower on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record status and to collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. some occurrences are in progress Rare Plant Inspect and Manage Monitoring 2014-2026, Demo Tues April 2 - 2019
IMP-2 Submit project metadata, status, habitat and threats data, and management recommendations to the MSP Web Portal. some occurrences are in progress Rare Plant Inspect and Manage Monitoring 2014-2026
Criteria Deadline year
Surveys Completed in 2017, 2019, and 2021 with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ERYAMM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at coastal wallflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ERYAMM-4 MGT-PRP-SBPL In 2021, begin preparing a section for coast wallflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences.
ERYAMM-5 MGT-PRP-MGTPL In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG ERYAMM-2

Management units: 6, 7

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at coastal wallflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species =20% absolute cover. some occurrences are in progress
IMP-2 Submit project metadata and management datasets to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ERYAMM-1 MON-IMP-IMG Beginning in 2017, inspect occurrences of coast wallflower on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record status and to collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
ERYAMM-5 MGT-PRP-MGTPL In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2019 SL
MON-SURV-SPEC ERYAMM-3

Management units: 1, 6, 7

In 2019, conduct baseline surveys of historic coast wallflower locations to determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats covariates and determine management needs.

Action Statement Action status Projects
SURV-1 Map suitable habitat based on soils, topography, openings in vegetation communities, and general location for existing occurrence expansion and new occurrence establishment. On hold
SURV-2 Submit project metadata, occurrence status, habitat mapping and assessment, and report to the MSP Web Portal. On hold Demo Tues April 2 - 2019
Criteria Deadline year
By 2020, Surveys and Report Completed 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ERYAMM-4 MGT-PRP-SBPL In 2021, begin preparing a section for coast wallflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences.
ERYAMM-5 MGT-PRP-MGTPL In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
Regional NFO 2021 SL
MGT-PRP-SBPL ERYAMM-4

Management units: 1, 6, 7

In 2021, begin preparing a section for coast wallflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the coast wallflower section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress
PRP-2 Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. some occurrences are in progress
Criteria Deadline year
By 2022, Completed Coast Wallflower Section in MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
ERYAMM-1 MON-IMP-IMG Beginning in 2017, inspect occurrences of coast wallflower on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record status and to collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
ERYAMM-3 MON-SURV-SPEC In 2019, conduct baseline surveys of historic coast wallflower locations to determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats covariates and determine management needs.
ERYAMM-5 MGT-PRP-MGTPL In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
regional NFO 2021 SL
MGT-PRP-MGTPL ERYAMM-5

Management units: 1, 6, 7

In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Prioritize extant occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. on hold
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to coast wallflower occurrences. on hold
PRP-3 Identify and prioritize sites for re-establishment of historic occurrences or that appear suitable for establishment of new occurrences. Specify the highest priority sites for establishing occurrences to reach the goal of at least 4 extant occurrences on Conserved Lands. on hold
PRP-4 Develop an implementation plan for coast wallflower that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. on hold
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to MSP Web Portal. on hold
Criteria Deadline year
By 2022, Completed Coast Wallflower Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
ERYAMM-1 MON-IMP-IMG Beginning in 2017, inspect occurrences of coast wallflower on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record status and to collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
ERYAMM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at coastal wallflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
ERYAMM-3 MON-SURV-SPEC In 2019, conduct baseline surveys of historic coast wallflower locations to determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats covariates and determine management needs.
ERYAMM-4 MGT-PRP-SBPL In 2021, begin preparing a section for coast wallflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences.

Regional and/or Local NFO 2018, 2019, 2020, 2021 VF
MON-IMP-MONPL ERYARI-1

Management units: 3, 6

Beginning in 2018, conduct annual surveys for San Diego button-celery in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
NAVFOS-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
ORCCAL-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGABR-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGNUD-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

regional NFO 2017, 2018 SL
MON-DEV-MODL EUPEDI-1

Management units: 3, 4, 6, 9

In 2017-2018, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.

Action Statement Action status Projects
DEV-1 Submit project metadata, modeling datasets, results and report to the MSP Web Portal. In progress
Criteria Deadline year
Quino Checkerspot Current and Future Climate Habitat Models and Report Completed in 2017 2021
Code Obj. code Statement
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
regional NFO 2017, 2018, 2019 SL
MON-PRP-MONPL EUPEDI-2

Management units: 3, 4, 6, 9

Beginning in 2017, prepare a long-term Quino checkerspot metapopulation monitoring plan to track population distribution, abundance, and phenology, and to assess habitats and threats at checkerspot occurrences (see occurrence table), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to include specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, sampling locations, timeline, and standardized protocols for determining the status and abundance of larval and adult butterflies and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations. The monitoring plan will be piloted with field surveys in 2018 to determine if adjustments need to be made and will be finalized in 2019 and then added to the final management plan in 2021 to create a comprehensive Quino Checkerspot Management and Monitoring Plan.

Action Statement Action status Projects
PRP-1 Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop the monitoring plan. in progress
PRP-2 Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. in progress
PRP-3 Submit project metadata, datasets and Quino Checkerspot Monitoring Plan to the MSP Web Portal. in progress
Criteria Deadline year
Quino Checkerspot Metapopulation Monitoring Plan Completed in 2019 2019
Code Obj. code Statement
EUPEDI-1 MON-DEV-MODL In 2017-2018, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.
EUPEDI-1 MON-DEV-MODL In 2017-2019, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.
EUPEDI-3 MON-IMP-MONPL In 2018 conduct pilot monitoring to evaluate monitoring methodology and sampling design and locations, and prepare recommendations for any adjustments to the monitoring plan. From 2019 to 2021, implement monitoring annually and submit data with management recommendations.
regional NFO 2018, 2019, 2020, 2021 SL
MON-IMP-MONPL EUPEDI-3

Management units: 3, 4, 6, 9

In 2018 conduct pilot monitoring to evaluate monitoring methodology and sampling design and locations, and prepare recommendations for any adjustments to the monitoring plan. From 2019 to 2021, implement monitoring annually and submit data with management recommendations.

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Monitoring Implemented and Data with Recommendations Submitted Annually 2021
regional NFO 2017, 2018 SL
MGT-PRP-SBPL EUPEDI-4

Management units: 3, 4, 6, 9

In 2017-2018, develop a section for Quino checkerpot nectaring forbs and host plants in the MSP Seed Collection, Banking and Bulking Plan to enhance and restore habitat for the butterfly. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences of Quino checkerspot.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Quino checkerspot section in the MSP Seed Collection, Banking and Bulking Plan. on hold
PRP-2 Design a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. waiting for precedent action
PRP-3 The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. waiting for precedent action
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). waiting for precedent action
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. waiting for precedent action
PRP-6 Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By end 2017, Completed Quino Checkerspot Section in MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
EUPEDI-5 MGT-IMP-SBPL In 2018, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot to collect and store seeds to provide propagules as needed for management oriented research, existing population enhancement and establishment of new butterfly occurrences.
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
regional NFO 2018, 2019, 2020, 2021 SL
MGT-IMP-SBPL EUPEDI-5

Management units: 3, 4, 6, 9

In 2018, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot to collect and store seeds to provide propagules as needed for management oriented research, existing population enhancement and establishment of new butterfly occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for butterfly habitat enhancement, expansion, and restoration projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2021, =1 Highest Priority Action Implemented for Quino checkerspot from the MSP Seed Collection, Banking, and Bulking Plan 2021
Code Obj. code Statement
EUPEDI-4 MGT-PRP-SBPL In 2017-2018, develop a section for Quino checkerpot nectaring forbs and host plants in the MSP Seed Collection, Banking and Bulking Plan to enhance and restore habitat for the butterfly. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences of Quino checkerspot.
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-PRP-MGTPL EUPEDI-6

Management units: 3, 4, 6, 9

In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.

Action Statement Action status Projects
PRP-1 Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop prioritized management actions. waiting for precedent action
PRP-2 Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. waiting for precedent action
PRP-3 Submit project metadata and management and monitoring plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Quino Checkerspot Management and Monitoring Plan Completed in 2021 2021
Code Obj. code Statement
EUPEDI-1 MON-DEV-MODL In 2017-2019, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.
EUPEDI-1 MON-DEV-MODL In 2017-2018, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.
EUPEDI-4 MGT-PRP-SBPL In 2017-2018, develop a section for Quino checkerpot nectaring forbs and host plants in the MSP Seed Collection, Banking and Bulking Plan to enhance and restore habitat for the butterfly. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences of Quino checkerspot.
EUPEDI-9 MGT-IMP-CAPR From 2017 to 2021, support existing efforts by the wildlife agencies to collect eggs and captive rear larvae to use in reestablishing and augmenting wild Quino checkerspot populations. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
regional and/or local NFO 2018, 2019, 2020, 2021 SL
MGT-IMP-MGTPL EUPEDI-7

Management units: 3, 4, 6, 9

Beginning in 2018, implement highest priority management actions for Quino checkerspot on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the Quino Checkerspot Management Plan. waiting for precedent action Quino Habitat Restoration
IMP-2 Submit project metadata and management data to MSP web portal waiting for precedent action Quino Habitat Restoration
Criteria Deadline year
=1 Management actions implemented for Quino checkerspot by 2021 2021
Code Obj. code Statement
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
regional and/or local NFO 2018, 2019, 2020, 2021 SL
MON-IMP-MGTPL EUPEDI-8

Management units: 3, 4, 6, 9

From 2018 to 2021, monitor the effectiveness of management actions implemented for Quino checkerspot on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit metadata, monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Effectiveness Monitoring Completed within 1 Year of Management Actions 2021
Code Obj. code Statement
EUPEDI-7 MGT-IMP-MGTPL Beginning in 2018, implement highest priority management actions for Quino checkerspot on Conserved Lands.
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-CAPR EUPEDI-9

Management units: 3, 4, 6, 9

From 2017 to 2021, support existing efforts by the wildlife agencies to collect eggs and captive rear larvae to use in reestablishing and augmenting wild Quino checkerspot populations. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.

Action Statement Action status Projects
IMP-1 Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the captive rearing. in progress
IMP-2 Submit project metadata and management data to MSP web portal. in progress
Criteria Deadline year
Captive Rearing Implemented and Report Submitted by 2021 2021
Code Obj. code Statement
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
EUPEDI-10 MGT-IMP-TRAN From 2017 to 2021, support existing efforts by the wildlife agenices to translocate captive bred Quino checkerspot larvae to historically occupied habitat.
EUPEDI-11 MON-IMP-TRAN From 2017 to 2021, support efforts by the wildlife agencies to monitor the effectivenss of translocated captive bred Quinoo checkerspot larvae. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-TRAN EUPEDI-10

Management units: 3, 4, 6, 9

From 2017 to 2021, support existing efforts by the wildlife agenices to translocate captive bred Quino checkerspot larvae to historically occupied habitat.

Action Statement Action status Projects
IMP-1 Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the translocation project. in progress
IMP-1 Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the translocation project. in progress
IMP-2 Submit project metadata and management data to MSP web portal. in progress
Criteria Deadline year
Translocation Implemented by 2020 2021
Code Obj. code Statement
EUPEDI-6 MGT-PRP-MGTPL In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
EUPEDI-9 MGT-IMP-CAPR From 2017 to 2021, support existing efforts by the wildlife agencies to collect eggs and captive rear larvae to use in reestablishing and augmenting wild Quino checkerspot populations. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
EUPEDI-11 MON-IMP-TRAN From 2017 to 2021, support efforts by the wildlife agencies to monitor the effectivenss of translocated captive bred Quinoo checkerspot larvae. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
regional NFO 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-TRAN EUPEDI-11

Management units: 3, 4, 6, 9

From 2017 to 2021, support efforts by the wildlife agencies to monitor the effectivenss of translocated captive bred Quinoo checkerspot larvae. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring data and reportto MSP web portal in progress
Criteria Deadline year
Translocation Monitoring Completed and Report Submitted by 2021 2021
Code Obj. code Statement
EUPEDI-9 MGT-IMP-CAPR From 2017 to 2021, support existing efforts by the wildlife agencies to collect eggs and captive rear larvae to use in reestablishing and augmenting wild Quino checkerspot populations. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
EUPEDI-10 MGT-IMP-TRAN From 2017 to 2021, support existing efforts by the wildlife agenices to translocate captive bred Quino checkerspot larvae to historically occupied habitat.

regional and/or local NFO 2021 VF
MON-IMP-IMG EUPMIS-1

Management units: 1, 3, 6, 7

In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed 2021 with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CYLCAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus, and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
ERIPAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
FERVIR-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

regional NFO 2017, 2020 SL
MON-SURV-SPEC EYPHAR-1

Management units: 3, 4, 5, 6, 8, 11

In 2017 and 2020, conduct host plant (San Diego sedge), adult, larval and hibernaculum surveys, and habitat assessments for Harbison's dun skipper that were initiated in 2013 in the MSPA (see Table of Occurrences) to further document the butterfly's current distribution and population size, define habitat requirements, and to assess habitat and threats at survey sites.

Action Statement Action status Projects
SURV-1 Search for Harvison's dun skipper adults, butterfly hiberniculum, larvae and host plants (San Diego sedge) at known occupied habitat, historically occupied habitat and in suitable potential habitat, to determine the extent of the butterfly's range, population sizes, and to better understand habitat relationships. Use a standardized protocol to collect habitat and threats covariate data at each site for developing and prioritizing management actions. In progress
SURV-2 Submit project metadata, datasets, analyses and report with management recommendations to the MSP Web Portal. In progress
Criteria Deadline year
Harbison's Dun Skipper Surveys and Reports Completed in 2018 and 2021 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Altered hydrologyALTHYD
Climate changeCLICHN
Invasive animalsINVANI
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
EYPHAR-2 MON-RES-GEN In 2017, in conjunction with adult surveys and the marking study for Harbison's dun skipper (see Table of Occurrences), capture adult butterflies and collect non-lethal genetic samples (i.e., legs) to analyze population genetic structure, dispersal and connectivity between populations, and genetic diversity. Use the analytical results to develop management recommendations to improve connectivity and to maintain or enhance genetic diversity at Harbison's dun skipper occurrences.
EYPHAR-3 MON-RES-SPEC In 2017, conduct a marking study of adult Harbison's dun skippers during the flight season to determine connectivity within habitat patches in a watershed. Design the study to obtain information on local movement patterns, flight season phenology, demography, detection probabilities, longevity, individual behavior, nectaring sources, and relationship between maximum counts and local population size. The results of this study should be used to develop specific management recommendations to be incorporated in the Harbison's Dun Skipper Management Plan.
EYPHAR-4 MON-DEV-MODL In 2017, develop habitat suitability models for Harbison's dun skipper, the host plant (San Diego sedge), and oak woodlands under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential fire and climate refugia. The results of this modeling will be considered in the development of monitoring and management plans.
EYPHAR-5 MGT-PRP-MGTPL In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.
regional PRE 2017 SL
MON-DEV-MODL EYPHAR-4

Management units: 3, 4, 5, 6, 8, 11

In 2017, develop habitat suitability models for Harbison's dun skipper, the host plant (San Diego sedge), and oak woodlands under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential fire and climate refugia. The results of this modeling will be considered in the development of monitoring and management plans.

Action Statement Action status Projects
DEV-1 Submit project metadata, modeling datasets, results and report to the MSP Web Portal. In progress
Criteria Deadline year
Harbison's Dun Skipper Current and Future Climate Habitat Models and Report Completed in 2017 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive animalsINVANI
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
EYPHAR-5 MGT-PRP-MGTPL In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.
EYPHAR-8 MGT-IMP-IGNPL Beginning in 2019, implement high priority MSP 2018 Wildfire Ignition Reduction Plan measures developed for Harbison's Dun Skipper to reduce the probability of ignition at most at-risk occurrences.
regional PRE 2017 SL
MGT-PRP-MGTPL EYPHAR-5

Management units: 3, 4, 5, 6, 8, 11

In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.

Action Statement Action status Projects
PRP-1 Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop prioritized management actions. In progress
PRP-2 Submit project metadata and Harbison's Dun Skipper Management Plant to the MSP Web Portal. In progress
Criteria Deadline year
Harbison's Dun Skipper Management Plan Completed in 2017 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Altered hydrologyALTHYD
Climate changeCLICHN
Invasive animalsINVANI
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
EYPHAR-1 MON-SURV-SPEC In 2017 and 2020, conduct host plant (San Diego sedge), adult, larval and hibernaculum surveys, and habitat assessments for Harbison's dun skipper that were initiated in 2013 in the MSPA (see Table of Occurrences) to further document the butterfly's current distribution and population size, define habitat requirements, and to assess habitat and threats at survey sites.
EYPHAR-2 MON-RES-GEN In 2017, in conjunction with adult surveys and the marking study for Harbison's dun skipper (see Table of Occurrences), capture adult butterflies and collect non-lethal genetic samples (i.e., legs) to analyze population genetic structure, dispersal and connectivity between populations, and genetic diversity. Use the analytical results to develop management recommendations to improve connectivity and to maintain or enhance genetic diversity at Harbison's dun skipper occurrences.
EYPHAR-3 MON-RES-SPEC In 2017, conduct a marking study of adult Harbison's dun skippers during the flight season to determine connectivity within habitat patches in a watershed. Design the study to obtain information on local movement patterns, flight season phenology, demography, detection probabilities, longevity, individual behavior, nectaring sources, and relationship between maximum counts and local population size. The results of this study should be used to develop specific management recommendations to be incorporated in the Harbison's Dun Skipper Management Plan.
EYPHAR-4 MON-DEV-MODL In 2017, develop habitat suitability models for Harbison's dun skipper, the host plant (San Diego sedge), and oak woodlands under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential fire and climate refugia. The results of this modeling will be considered in the development of monitoring and management plans.
EYPHAR-5 MGT-PRP-MGTPL In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.
EYPHAR-6 MGT-IMP-MGTPL Beginning in 2018, implement highest priority management actions identified in the Harbison's Dun Skipper Management Plan.
EYPHAR-7 MON-IMP-MGTPL Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Harbison's Dun Skipper Management Plan.
EYPHAR-8 MGT-IMP-IGNPL Beginning in 2019, implement high priority MSP 2018 Wildfire Ignition Reduction Plan measures developed for Harbison's Dun Skipper to reduce the probability of ignition at most at-risk occurrences.
EYPHAR-9 MON-IMP-FMGT For at least the first 3 years following a wildfire, monitor recovery of Harbison's dun skipper occurrences and habitat affected by fire. Use a standardized postfire protocol to document the butterfly's distribution and abundance over time and to characterize habitat recovery and threats following a wildfire. Postfire monitoring should encompass occupied dun skipper sites and unoccupied sites that are important for enhancing connectivity or for future population expansion. The postfire monitoring should identify and prioritize management actions to assist in recovery of Harbison's dun skipper populations and important habitat patches.
EYPHAR-10 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and recover Harbison's dun skipper occurrences and habitat impacted by wildfire.
regional PRE 2018, 2019, 2020, 2021 SL
MGT-IMP-MGTPL EYPHAR-6

Management units: 3, 4, 5, 6, 8, 11

Beginning in 2018, implement highest priority management actions identified in the Harbison's Dun Skipper Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =1 High Priority Management Action Implemented from the Harbison's Dun Skipper Management Plan 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Altered hydrologyALTHYD
Climate changeCLICHN
Invasive animalsINVANI
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
EYPHAR-5 MGT-PRP-MGTPL In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.
EYPHAR-7 MON-IMP-MGTPL Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Harbison's Dun Skipper Management Plan.
regional PRE 2018, 2019, 2020, 2021 SL
MON-IMP-MGTPL EYPHAR-7

Management units: 3, 4, 5, 6, 8, 11

Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Harbison's Dun Skipper Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Altered hydrologyALTHYD
Climate changeCLICHN
Invasive animalsINVANI
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
EYPHAR-5 MGT-PRP-MGTPL In 2017, prepare a 5 year Harbison's Dun Skipper Management Plan that includes the results from butterfly surveys and habitat assessments, genetic and marking studies, and climate and fire modeling to characterize habitat quality at occupied occurrences and unoccupied suitable habitat important for enhancing connectivity, expanding populations or that could serve as fire and climate refugia. The plan should include an overall management strategy, identification and prioritization of sites where management is needed, and specific management recommendations for each site. It should also include actions to reduce fire risk at prioritized occurrences and specifications for monitoring the effectiveness of implementing high priority management actions.
EYPHAR-6 MGT-IMP-MGTPL Beginning in 2018, implement highest priority management actions identified in the Harbison's Dun Skipper Management Plan.

regional and/or local NFO 2021 VF
MON-IMP-IMG FERVIR-1

Management units: 1, 2, 3, 4, 5, 6, 7

In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. On hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Surveys Completed 2021 with Management Recommendations 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
CYLCAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus, and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
ERIPAL-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
EUPMIS-1 MON-IMP-IMG In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.

regional and/or local NFO 2018, 2020 SL
MON-IMP-IMG HAZORC-1

Management units: 6, 7

In 2018, inspect Orcutt's hazardia occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed Every 2 Years with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
HAZORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through 2016, 2018 and 2020 IMG monitoring of Orcutt's hazardia occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
HAZORC-3 MGT-PRP-SBPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
HAZORC-5 MGT-PRP-MGTPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL
MGT-IMP-IMG HAZORC-2

Management units: 6, 7

Beginning in 2017, conduct routine management actions identified through 2016, 2018 and 2020 IMG monitoring of Orcutt's hazardia occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. available for implementation
IMP-2 Submit project metadata and management data to the MSP Web Portal. available for implementation
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
HAZORC-1 MON-IMP-IMG In 2018, inspect Orcutt's hazardia occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
Regional NFO 2017 SL
MGT-PRP-SBPL HAZORC-3

Management units: 6, 7

In 2017, begin preparing an Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan. Available for implementation
PRP-2 Design the seed collection plan to include recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. Available for implementation
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. Available for implementation
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). Available for implementation
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. Available for implementation
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. Available for implementation
Criteria Deadline year
By 2018, Completed Orcutt's Hazardia Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
HAZORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through 2016, 2018 and 2020 IMG monitoring of Orcutt's hazardia occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
HAZORC-4 MGT-IMP-SBPL In 2018, begin implementing high priority actions for Orcutt's hazardia in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
HAZORC-5 MGT-PRP-MGTPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
HAZORC-6 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.
HAZORC-7 MON-IMP-MGTPL In 2018, begin monitoring effectiveness of implementation of highest priority management actions identified in the Orcutt's hazardia section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2018, 2019, 2020, 2021 SL
MGT-IMP-SBPL HAZORC-4

Management units: 6, 7

In 2018, begin implementing high priority actions for Orcutt's hazardia in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =1 Highest Priority Action Implemented for Orcutt's hazardia from the MSP Seed Banking and Bulking Plan 2021
Code Obj. code Statement
HAZORC-3 MGT-PRP-SBPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
HAZORC-6 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.
regional NFO 2017 SL
MGT-PRP-MGTPL HAZORC-5

Management units: 6, 7

In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Rare Plant Management Plan. available for implementation
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's hazardia occurrences. available for implementation
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. available for implementation
PRP-4 Develop an implementation plan for Orcutt's hazardia that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. available for implementation
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. available for implementation
Criteria Deadline year
By 2018, Completed Orcutt's Hazardia Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
HAZORC-1 MON-IMP-IMG In 2018, inspect Orcutt's hazardia occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
HAZORC-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through 2016, 2018 and 2020 IMG monitoring of Orcutt's hazardia occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
HAZORC-3 MGT-PRP-SBPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
HAZORC-4 MGT-IMP-SBPL In 2018, begin implementing high priority actions for Orcutt's hazardia in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
HAZORC-6 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.
HAZORC-7 MON-IMP-MGTPL In 2018, begin monitoring effectiveness of implementation of highest priority management actions identified in the Orcutt's hazardia section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2018, 2019, 2020, 2021 SL
MGT-IMP-MGTPL HAZORC-6

Management units: 6, 7

In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2022, =1 High Priority Management Action Implemented for Orcutt's Brodiaea from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
HAZORC-5 MGT-PRP-MGTPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
HAZORC-7 MON-IMP-MGTPL In 2018, begin monitoring effectiveness of implementation of highest priority management actions identified in the Orcutt's hazardia section in the MSP Rare Plant Management Plan.
regional and/or local NFO 2018, 2019, 2020, 2021 SL
MON-IMP-MGTPL HAZORC-7

Management units: 6, 7

In 2018, begin monitoring effectiveness of implementation of highest priority management actions identified in the Orcutt's hazardia section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
HAZORC-5 MGT-PRP-MGTPL In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
HAZORC-6 MGT-IMP-MGTPL In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.

Regional NFO 2018 VF
MON-PRP-MONPL LEPCAL-1

Management units: 1, 2, 3, 4, 5, 6, 7

In 2018, develop a long-term San Diego Black-tailed Jackrabbit Monitoring Plan to track their distribution and status, habitat associations and level of threats in coastal sage scrub and grassland vegetation communities across the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the jackrabbit and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.

Action Statement Action status Projects
PRP-1 Submit project metadata and San Diego Black-tailed Jackrabbit Monitoring Plan to the MSP Web Portal. On hold
Criteria Deadline year
San Diego Black-tailed Jackrabbit Monitoring Plan completed in 2018 2021
Code Obj. code Statement
LEPCAL-2 MON-IMP-MONPL In 2019, begin implementing long-term San Diego black-tailed jackrabbit monitoring as specified in the San Diego Black-tailed Jackrabbit Monitoring Plan. Prepare a report detailing jackrabbit and habitat and threat assessment results and with site specific vegetation management recommendations.
Regional NFO 2019 VF
MON-IMP-MONPL LEPCAL-2

Management units: 1, 2, 3, 4, 5, 6, 7

In 2019, begin implementing long-term San Diego black-tailed jackrabbit monitoring as specified in the San Diego Black-tailed Jackrabbit Monitoring Plan. Prepare a report detailing jackrabbit and habitat and threat assessment results and with site specific vegetation management recommendations.

Action Statement Action status Projects
IMP-1 Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
San Diego Black-tailed Jackrabbit Monitoring and Report completed by 2020 2021
Code Obj. code Statement
LEPCAL-1 MON-PRP-MONPL In 2018, develop a long-term San Diego Black-tailed Jackrabbit Monitoring Plan to track their distribution and status, habitat associations and level of threats in coastal sage scrub and grassland vegetation communities across the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the jackrabbit and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.

regional POST 2017, 2018, 2019 SL
MON-SURV-SPEC LYCHER-1

Management units: 2, 3, 4, 6, 10, 11

In 2017-2019, continue surveys for adult Hermes copper (see occurrence table) and habitat assessments begun in 2016 to document the butterfly's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.

Action Statement Action status Projects
SURV-1 Search for adult Hermes copper butterflies and host plants (spiny redbery) at known occupied habitat, historically occupied habitat, habitat recovering from wildfire, and suitable habitat with potential to support the butterfly to determine the extent of the range, population sizes, and to better understand habitat relationships. Use a standardized protocol to collect habitat and threats covariate data at each site for developing and prioritizing management actions. in progress
SURV-2 Submit project metadata, datasets, analyses and report with management recommendations to the MSP Web Portal. in progress
Criteria Deadline year
Hermes Copper Surveys and Reports Completed in 2017 and 2018 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-3 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-9 MON-PRP-MONPL In 2018, develop a monitoring plan to track long term distribution, abundance, and phenology, and to assess habitats and threats at Hermes copper occurrences (see Table of Occurrences), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations.
regional POST 2017, 2018, 2019 SL
MGT-IMP-TRAN LYCHER-2

Management units: 2, 3, 4, 6, 10, 11

From 2017 to 2019, continue Hermes Copper translocation experiments begun in 2014 to test the effectiveness of releasing eggs and larvae to repopulate the Hollenbeck Canyon Wildlife Area (see Table of Occurrences) where the original population was extirpated by fire.

Action Statement Action status Projects
IMP-1 Continue releasing Hermes copper eggs at Hollenbeck Canyon Wildlife Area where the butterfly was extirpated in 2017, to see if translocation success can be improved under normal rainfall conditions. Nine of 14 larvae emerged in 2015 from translocated eggs and 1 adult was observed in 2016, despite the prolonged and intense drought. In progress
Criteria Deadline year
Hermes Copper Translocation Experiments Completed in 2019 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-1 MON-SURV-SPEC In 2017-2019, continue surveys for adult Hermes copper (see occurrence table) and habitat assessments begun in 2016 to document the butterfly's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.
LYCHER-3 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
LYCHER-4 MGT-DEV-BMP In 2017, continue development of BMPs begun in 2013 for captive rearing Hermes Copper at the San Diego Zoo. Attempt to determine optimal conditions for rearing Hermes copper in captivity to provide a source of butterflies for translocations to re-establish populations at sites where the butterfly has been extirpated or to establish new populations in suitable habitat.
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-13 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
regional POST 2017, 2018, 2019, 2020, 2021 SL
MON-IMP-TRAN LYCHER-3

Management units: 2, 3, 4, 6, 10, 11

From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets, analyses and report with management recommendations to the MSP Web Portal. In progress
Criteria Deadline year
Hermes Copper Translocation Monitoring and Reports Completed Annually 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-2 MGT-IMP-TRAN From 2017 to 2019, continue Hermes Copper translocation experiments begun in 2014 to test the effectiveness of releasing eggs and larvae to repopulate the Hollenbeck Canyon Wildlife Area (see Table of Occurrences) where the original population was extirpated by fire.
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-13 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
regional NFO 2017 SL
MGT-DEV-BMP LYCHER-4

Management units: 2, 3, 4, 6, 10, 11

In 2017, continue development of BMPs begun in 2013 for captive rearing Hermes Copper at the San Diego Zoo. Attempt to determine optimal conditions for rearing Hermes copper in captivity to provide a source of butterflies for translocations to re-establish populations at sites where the butterfly has been extirpated or to establish new populations in suitable habitat.

Action Statement Action status Projects
DEV-1 Submit project metadata, datasets, and report with management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Hermes Copper Captive Rearing Experiments and Report Completed by 2018 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-2 MGT-IMP-TRAN From 2017 to 2019, continue Hermes Copper translocation experiments begun in 2014 to test the effectiveness of releasing eggs and larvae to repopulate the Hollenbeck Canyon Wildlife Area (see Table of Occurrences) where the original population was extirpated by fire.
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-13 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
regional PRE 2017 SL
MON-DEV-MODL LYCHER-5

Management units: 2, 3, 4, 6, 10, 11

In 2017, develop habitat suitability models for Hermes copper and the host plant (spiny redberry), and the primary nectaring plant (California buckwheat) under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans for this butterfly.

Action Statement Action status Projects
DEV-1 Submit project metadata, modeling datasets, results and report to the MSP Web Portal. In progress
Criteria Deadline year
Hermes Copper Current and Future Climate Habitat Models and Report Completed in 2017 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-9 MON-PRP-MONPL In 2018, develop a monitoring plan to track long term distribution, abundance, and phenology, and to assess habitats and threats at Hermes copper occurrences (see Table of Occurrences), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations.
regional PRE 2017 SL
MGT-PRP-MGTPL LYCHER-6

Management units: 2, 3, 4, 6, 10, 11

In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.

Action Statement Action status Projects
PRP-1 Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop prioritized management actions. completed
PRP-2 Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. completed
PRP-3 Submit project metadata and Herme's Copper Management Plant to the MSP Web Portal. completed
Criteria Deadline year
Hermes Copper Management Plan Completed in 2017 2021
Code Obj. code Statement
LYCHER-1 MON-SURV-SPEC In 2017-2019, continue surveys for adult Hermes copper (see occurrence table) and habitat assessments begun in 2016 to document the butterfly's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.
LYCHER-3 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
LYCHER-4 MGT-DEV-BMP In 2017, continue development of BMPs begun in 2013 for captive rearing Hermes Copper at the San Diego Zoo. Attempt to determine optimal conditions for rearing Hermes copper in captivity to provide a source of butterflies for translocations to re-establish populations at sites where the butterfly has been extirpated or to establish new populations in suitable habitat.
LYCHER-5 MON-DEV-MODL In 2017, develop habitat suitability models for Hermes copper and the host plant (spiny redberry), and the primary nectaring plant (California buckwheat) under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans for this butterfly.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-13 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
regional PRE 2018, 2019, 2020, 2021 SL
MGT-IMP-MGTPL LYCHER-7

Management units: 2, 3, 4, 6, 10, 11

In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, management datasets, and report to the MSP Web Portal. available for implementation
Criteria Deadline year
By 2021, =1 High Priority Management Action Implemented from the Hermes Copper Management Plan 2021
Code Obj. code Statement
LYCHER-2 MGT-IMP-TRAN From 2017 to 2019, continue Hermes Copper translocation experiments begun in 2014 to test the effectiveness of releasing eggs and larvae to repopulate the Hollenbeck Canyon Wildlife Area (see Table of Occurrences) where the original population was extirpated by fire.
LYCHER-3 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-8 MON-IMP-MGTPL Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Hermes Copper Management Plan.
LYCHER-13 MGT-IMP-FMGT For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
regional PRE 2018, 2019, 2020, 2021 SL
MON-IMP-MGTPL LYCHER-8

Management units: 2, 3, 4, 6, 10, 11

Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Hermes Copper Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined and Report Completed 2021
Code Obj. code Statement
LYCHER-6 MGT-PRP-MGTPL In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-7 MGT-IMP-MGTPL In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
LYCHER-9 MON-PRP-MONPL In 2018, develop a monitoring plan to track long term distribution, abundance, and phenology, and to assess habitats and threats at Hermes copper occurrences (see Table of Occurrences), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations.
LYCHER-10 MON-IMP-MONPL In 2020, begin implementing long term Hermes copper monitoring as specified in the Hermes Copper Monitoring Plan. Prepare a report detailing butterfly and habitat assessment results and with site specific management recommendations.
LYCHER-12 MON-IMP-FMGT For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of Hermes copper occurrences impacted by fire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing Hermes copper habitat recovery following a fire. Postfire monitoring should include collecting habitat recovery data at unoccupied sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover Hermes copper populations and important habitat patches.
regional NFO 2018 SL
MON-PRP-MONPL LYCHER-9

Management units: 2, 3, 4, 6, 10, 11

In 2018, develop a monitoring plan to track long term distribution, abundance, and phenology, and to assess habitats and threats at Hermes copper occurrences (see Table of Occurrences), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations.

Action Statement Action status Projects
PRP-1 Incorporate previously tested survey methods into development of a Hermes copper monitoring protocol and habitat assessment.The sampling frame should include the current and historic range of the butterfly on Conserved Lands and any unoccupied suitable habitat modeled as climate or fire refugia. Include a subset of sites in north and south San Diego County classified as sentinel sites and monitored every survey year to characterize the conditions and phenology for the butterfly in that year. The remainder of sites should be included in a rotating panel to be surveyed in alternative years. waiting for precedent action
PRP-2 Submit project metadata and Hermes Copper Monitoring Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Hermes Copper Monitoring Plan Completed in 2018 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-1 MON-SURV-SPEC In 2017-2019, continue surveys for adult Hermes copper (see occurrence table) and habitat assessments begun in 2016 to document the butterfly's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.
LYCHER-3 MON-IMP-TRAN From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
LYCHER-5 MON-DEV-MODL In 2017, develop habitat suitability models for Hermes copper and the host plant (spiny redberry), and the primary nectaring plant (California buckwheat) under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans for this butterfly.
LYCHER-8 MON-IMP-MGTPL Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Hermes Copper Management Plan.
LYCHER-10 MON-IMP-MONPL In 2020, begin implementing long term Hermes copper monitoring as specified in the Hermes Copper Monitoring Plan. Prepare a report detailing butterfly and habitat assessment results and with site specific management recommendations.
LYCHER-12 MON-IMP-FMGT For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of Hermes copper occurrences impacted by fire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing Hermes copper habitat recovery following a fire. Postfire monitoring should include collecting habitat recovery data at unoccupied sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover Hermes copper populations and important habitat patches.
regional NFO 2020, 2021 SL
MON-IMP-MONPL LYCHER-10

Management units: 2, 3, 4, 6, 10, 11

In 2020, begin implementing long term Hermes copper monitoring as specified in the Hermes Copper Monitoring Plan. Prepare a report detailing butterfly and habitat assessment results and with site specific management recommendations.

Action Statement Action status Projects
IMP-1 Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Hermes Copper Monitoring and Report Completed Each Survey Year 2021
Threat Name Threat Code
Altered fire regimeALTFIR
Climate changeCLICHN
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
LYCHER-9 MON-PRP-MONPL In 2018, develop a monitoring plan to track long term distribution, abundance, and phenology, and to assess habitats and threats at Hermes copper occurrences (see Table of Occurrences), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations.
LYCHER-12 MON-IMP-FMGT For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of Hermes copper occurrences impacted by fire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing Hermes copper habitat recovery following a fire. Postfire monitoring should include collecting habitat recovery data at unoccupied sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover Hermes copper populations and important habitat patches.

regional NFO 2019 SL
MON-SURV-SPEC MONVIM-4

Management units: 4, 6

In 2019, survey historic willowy monardella locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs. Conduct a hydrological evaluation at each site to determine the current hydrology and risk to existing or potential occurrences from erosion and flooding. Prioritize all evaluated sites based on feasibility of maintaining a sustainable population over the long term and recommend management needed to reduce threats to existing and potential new occurrences.

Action Statement Action status Projects
SURV-1 At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. on hold
SURV-2 Submit project metadata, habitat mapping, and a report with site prioritizations and recommendations for management based upon occurrence status, habitat and threats assessments and hydrological evaluations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys and Report Completed by 2019 2021
Code Obj. code Statement
MONVIM-1 MON-IMP-IMG From 2017-2021, inspect willowy monardella occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
MONVIM-7 MGT-PRP-MGTPL In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
MONVIM-10 MGT-MON-FMGT Beginning in 2018, conduct a post fire evaluation of hydrological processes at willowy monardella occurrences following a fire to determine risks from erosion and flooding and prepare a report with prioritized management recommendations to reduce risk to population persistence and sustainability.
Regional NFO 2020 SL
MGT-PRP-SBPL MONVIM-5

Management units: 4, 6

In 2020, begin preparing a section for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should also include recommendations from the 2016-2017 genetic study and the 2019 baseline surveys and hydrological evaluation to guide collection and storage of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, MCAS Miramar, and other stakeholders to provide input and recommendations for the willowy monardella section in the MSP Seed Collection, Banking and Bulking Plan. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-2 Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-3 The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-4 Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-5 Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
PRP-6 Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. some occurrences are in progress California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2020, Completed Willowy Monardella Section in the MSP Seed Collection, Banking and Bulking Plan 2021
Code Obj. code Statement
MONVIM-1 MON-IMP-IMG From 2017-2021, inspect willowy monardella occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
MONVIM-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for willowy monardella occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting and redistributing or bulking seed to enhance existing occurrences or establish new occurrences.
MONVIM-4 MON-SURV-SPEC In 2019, survey historic willowy monardella locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs. Conduct a hydrological evaluation at each site to determine the current hydrology and risk to existing or potential occurrences from erosion and flooding. Prioritize all evaluated sites based on feasibility of maintaining a sustainable population over the long term and recommend management needed to reduce threats to existing and potential new occurrences.
MONVIM-6 MGT-IMP-SBPL In 2021, begin implementing high priority actions for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
MONVIM-7 MGT-PRP-MGTPL In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
regional and/or local NFO 2021 SL
MGT-IMP-SBPL MONVIM-6

Management units: 4, 6

In 2021, begin implementing high priority actions for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.

Action Statement Action status Projects
IMP-1 Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
IMP-2 Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. waiting for precedent action California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank
Criteria Deadline year
By 2024, =2 Seed Collection, Banking and Bulking Action Completed for Willowy Monardella 2021
Code Obj. code Statement
MONVIM-5 MGT-PRP-SBPL In 2020, begin preparing a section for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should also include recommendations from the 2016-2017 genetic study and the 2019 baseline surveys and hydrological evaluation to guide collection and storage of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
MONVIM-7 MGT-PRP-MGTPL In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
MONVIM-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for willowy monardella in the MSP Rare Plant Management Plan.
regional NFO 2020 SL
MGT-PRP-MGTPL MONVIM-7

Management units: 4, 6

In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.

Action Statement Action status Projects
PRP-1 Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, MCAS Miramar, and other stakeholders to provide input and recommendations for the willowy monardella section in the MSP Rare Plant Management Plan. waiting for precedent action
PRP-2 Develop a conceptual model that identifies management actions to effectively reduce threats to willowy monardella occurrences. waiting for precedent action
PRP-3 Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. waiting for precedent action
PRP-4 Develop an implementation plan for willowy monardella that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. waiting for precedent action
PRP-5 Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2020, Completed Willowy Monardella Section in MSP Rare Plant Management Plan 2021
Code Obj. code Statement
MONVIM-1 MON-IMP-IMG From 2017-2021, inspect willowy monardella occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
MONVIM-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at willowy monardella occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
MONVIM-3 MON-RES-GEN In 2017, complete the study begun in 2016 to characterize the population genetic structure, gene flow, and genetic diversity for willowy monardella occurrences (see occurrence table). The study will determine if there is evidence of mixed ploidy levels within or among occurrences; evaluate vulnerability of occurrences to genetic drift and loss of genetic diversity; assess the level of gene flow among occurrences; identify if there are signatures of genetic bottlenecks or low genetic diversity in occurrences that have undergone recent reductions; and look for evidence of local population adaptation. Based on the results of the genetic analyses, management recommendations will include whether common garden and reciprocal transplantations are necessary before proceeding with population enhancement or restoration and will provide specific recommendations for collecting and redistributing or bulking seed to enhance existing occurrences or establish new occurrences.
MONVIM-4 MON-SURV-SPEC In 2019, survey historic willowy monardella locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs. Conduct a hydrological evaluation at each site to determine the current hydrology and risk to existing or potential occurrences from erosion and flooding. Prioritize all evaluated sites based on feasibility of maintaining a sustainable population over the long term and recommend management needed to reduce threats to existing and potential new occurrences.
MONVIM-5 MGT-PRP-SBPL In 2020, begin preparing a section for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should also include recommendations from the 2016-2017 genetic study and the 2019 baseline surveys and hydrological evaluation to guide collection and storage of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
MONVIM-6 MGT-IMP-SBPL In 2021, begin implementing high priority actions for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
MONVIM-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for willowy monardella in the MSP Rare Plant Management Plan.
MONVIM-9 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the willowy monardella section in the MSP Rare Plant Management Plan.
MONVIM-10 MGT-MON-FMGT Beginning in 2018, conduct a post fire evaluation of hydrological processes at willowy monardella occurrences following a fire to determine risks from erosion and flooding and prepare a report with prioritized management recommendations to reduce risk to population persistence and sustainability.
regional and/or local NFO 2021 SL
MGT-IMP-MGTPL MONVIM-8

Management units: 4, 6

In 2021, begin implementing highest priority management actions identified for willowy monardella in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management datasets, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
By 2024, =2 High Priority Management Action Implemented for Willowy Monardella from the MSP Rare Plant Management Plan 2021
Code Obj. code Statement
MONVIM-6 MGT-IMP-SBPL In 2021, begin implementing high priority actions for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
MONVIM-7 MGT-PRP-MGTPL In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
MONVIM-9 MON-IMP-MGTPL In 2021, monitor effectiveness of implementation of highest priority management actions identified in the willowy monardella section in the MSP Rare Plant Management Plan.
Regional and/or Local NFO 2021 SL
MON-IMP-MGTPL MONVIM-9

Management units: 4, 6

In 2021, monitor effectiveness of implementation of highest priority management actions identified in the willowy monardella section in the MSP Rare Plant Management Plan.

Action Statement Action status Projects
IMP-1 Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Effectiveness of High Priority Management Actions Determined 2021
Code Obj. code Statement
MONVIM-7 MGT-PRP-MGTPL In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
MONVIM-8 MGT-IMP-MGTPL In 2021, begin implementing highest priority management actions identified for willowy monardella in the MSP Rare Plant Management Plan.

Regional and/or Local NFO 2018, 2019, 2020, 2021 VF
MON-IMP-MONPL NAVFOS-1

Management units: 2, 3, 6

Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
NAVFOS-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
ORCCAL-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGABR-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGNUD-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

Regional and/or Local NFO 2018, 2019, 2020, 2021 SL
MON-IMP-MONPL ORCCAL-1

Management units: 3

Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
NAVFOS-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
ORCCAL-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGABR-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGNUD-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

Regional NFO 2021 VF
MON-PRP-MONPL PANERR-1

Management units: 1, 7

In 2021, develop a long-term Wandering Skipper Monitoring Plan to track their distribution and status, habitat associations and level of threats in salt marsh vegetation on Conserved Lands in the MSPA. The plan should integrate with the Salt Marsh Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.

Action Statement Action status Projects
PRP-1 Submit project metadata and Wandering Skipper Monitoring Plan to the MSP Web Portal. On hold
Criteria Deadline year
Wandering Skipper Monitoring Plan completed by 2021 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
SALMAR-1 MON-PRP-MONPL In 2021, evaluate existing salt marsh monitoring programs for Conserved Lands in the MSPA to determine gaps in monitoring salt marsh vegetation to assess community composition, structure and ecological integrity, and to document threats and assess environmental conditions. If there are gaps in current monitoring, develop a long-term regional salt marsh vegetation monitoring plan. The plan should include a conceptual model, specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, permanent sampling locations, timeline, and standardized protocols. Use models predicting future sea level rise under changing climate to help determine the sampling frame. Evaluate ecological integrity at monitoring sites by integrating other types of monitoring into the long-term sampling plots, such as abiotic element monitoring (e.g., tidal flow monitoring, automated weather stations and soil sensors, GIS-data layers), ecological integrity monitoring (e.g., plant and animal communities, ecological processes), MSP VF species monitoring, and threats monitoring (e.g., climate change, invasive plants).

Regional NFO 2019 VF
MON-PRP-MONPL PASSAN-1

Management units: 1, 7

In 2019, develop a regional, long-term monitoring plan to integrate habitat assessment and threat evaluations into the Belding's savannah sparrow population monitoring conducted by the California Department of Fish and Wildlife on Conserved Lands in the MSPA. Develop a sampling design and standardized protocol to assess habitat and threats at occupied, historically occupied and suitable unoccupied habitats for the sparrow. Design the habitat and threats assessment to inform regional salt marsh vegetation monitoring. The purpose of the plan is to use habitat and threat monitoring data to develop site specific management recommendations to maintain, enhance or restore Belding's savannah sparrow habitat.

Action Statement Action status Projects
PRP-1 Coordinate with the California Department of Fish and Wildlife, U.S. Fish and Wildlife Service, scientists and land managers to develop a habitat and threats assessment monitoring protocol to integrate into ongoing regional Belding's savannah sparrow population monitoring. On hold
PRP-2 Submit project metadata and Belding's Savannah Sparrow Habitat and Threat Assessment Monitoring Plan to the MSP Web Portal. On hold
Criteria Deadline year
Belding's Savannah Sparrow Habitat and Threat Assessment Monitoring Plan completed by 2019 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
PASSAN-2 MON-IMP-MONPL In 2020 or 2021, depending on timing of Belding's savannah sparrow population monitoring implemented by the California Department of Fish and Wildlife, conduct habitat and threats assessment as specified in the Belding's Savannah Sparrow Habitat and Threat and Assessment Monitoring Plan and in conjunction with sparrow population monitoring on Conserved Lands in the MSPA.
SALMAR-1 MON-PRP-MONPL In 2021, evaluate existing salt marsh monitoring programs for Conserved Lands in the MSPA to determine gaps in monitoring salt marsh vegetation to assess community composition, structure and ecological integrity, and to document threats and assess environmental conditions. If there are gaps in current monitoring, develop a long-term regional salt marsh vegetation monitoring plan. The plan should include a conceptual model, specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, permanent sampling locations, timeline, and standardized protocols. Use models predicting future sea level rise under changing climate to help determine the sampling frame. Evaluate ecological integrity at monitoring sites by integrating other types of monitoring into the long-term sampling plots, such as abiotic element monitoring (e.g., tidal flow monitoring, automated weather stations and soil sensors, GIS-data layers), ecological integrity monitoring (e.g., plant and animal communities, ecological processes), MSP VF species monitoring, and threats monitoring (e.g., climate change, invasive plants).
Regional NFO 2020, 2021 VF
MON-IMP-MONPL PASSAN-2

Management units: 1, 7

In 2020 or 2021, depending on timing of Belding's savannah sparrow population monitoring implemented by the California Department of Fish and Wildlife, conduct habitat and threats assessment as specified in the Belding's Savannah Sparrow Habitat and Threat and Assessment Monitoring Plan and in conjunction with sparrow population monitoring on Conserved Lands in the MSPA.

Action Statement Action status Projects
IMP-1 Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Belding's Savannah Sparrow Habitat and Threat Monitoring and Report completed by 2021 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
PASSAN-1 MON-PRP-MONPL In 2019, develop a regional, long-term monitoring plan to integrate habitat assessment and threat evaluations into the Belding's savannah sparrow population monitoring conducted by the California Department of Fish and Wildlife on Conserved Lands in the MSPA. Develop a sampling design and standardized protocol to assess habitat and threats at occupied, historically occupied and suitable unoccupied habitats for the sparrow. Design the habitat and threats assessment to inform regional salt marsh vegetation monitoring. The purpose of the plan is to use habitat and threat monitoring data to develop site specific management recommendations to maintain, enhance or restore Belding's savannah sparrow habitat.
SALMAR-1 MON-PRP-MONPL In 2021, evaluate existing salt marsh monitoring programs for Conserved Lands in the MSPA to determine gaps in monitoring salt marsh vegetation to assess community composition, structure and ecological integrity, and to document threats and assess environmental conditions. If there are gaps in current monitoring, develop a long-term regional salt marsh vegetation monitoring plan. The plan should include a conceptual model, specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, permanent sampling locations, timeline, and standardized protocols. Use models predicting future sea level rise under changing climate to help determine the sampling frame. Evaluate ecological integrity at monitoring sites by integrating other types of monitoring into the long-term sampling plots, such as abiotic element monitoring (e.g., tidal flow monitoring, automated weather stations and soil sensors, GIS-data layers), ecological integrity monitoring (e.g., plant and animal communities, ecological processes), MSP VF species monitoring, and threats monitoring (e.g., climate change, invasive plants).

Regional NFO 2018 VF
MON-PRP-MONPL PHABLA-2

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2018, develop a long-term Blainville's Horned Lizard Monitoring Plan to track their distribution and status, habitat associations and level of threats in chaparral, coastal sage scrub and grassland vegetation communities across Conserved Lands in the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the lizard and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.

Action Statement Action status Projects
PRP-1 Submit project metadata and Blainville's Horned Lizard Monitoring Plan to the MSP Web Portal. On hold
Criteria Deadline year
Blainville's Horned Lizard Monitoring Plan completed in 2018 2021
Code Obj. code Statement
PHABLA-3 MON-IMP-MONPL In 2019, begin implementing long term Blainville's horned lizard monitoring as specified in the Blainville's Horned Lizard Monitoring Plan. Prepare a report detailing lizard and habitat and threat assessment results and with site specific vegetation management recommendations.
Regional NFO 2019 VF
MON-IMP-MONPL PHABLA-3

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2019, begin implementing long term Blainville's horned lizard monitoring as specified in the Blainville's Horned Lizard Monitoring Plan. Prepare a report detailing lizard and habitat and threat assessment results and with site specific vegetation management recommendations.

Action Statement Action status Projects
IMP-1 Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. waiting for precedent action
Criteria Deadline year
Blainville's Horned Lizard Monitoring and Report completed by 2020 2021
Code Obj. code Statement
PHABLA-2 MON-PRP-MONPL In 2018, develop a long-term Blainville's Horned Lizard Monitoring Plan to track their distribution and status, habitat associations and level of threats in chaparral, coastal sage scrub and grassland vegetation communities across Conserved Lands in the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the lizard and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.

local NFO 2017, 2018 SO
MON-RES-SPEC PLETOW-1

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2017-2018, finalize the results of research begun in 2015 on Townsend's big-eared bat to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat and assess threats to bats at all preserves where they occur and develop management recommendations.

Action Statement Action status Projects
RES-1 Submit project metadata, survey data, and report with management recommendations to the MSP web portal. In progress
Criteria Deadline year
Townsend's Big-Eared Bat Surveys and Reports Completed in 2018. 2018
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG PLETOW-2

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2017, annually inspect the vicinity of Townsend's big-eared bat roosts on an annual basis (see Table of Occurrences), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol surveys to quantify signs of human activity near occupied or potential roosts and to identify other potential threats. Care should be taken to avoid disturbing roosting bats. In progress
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. Unknown
IMP-3 Submit monitoring data and management recommendations to the MSP web portal. Unknown
Criteria Deadline year
Annual monitoring of Townsend's big-eared bat completed 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PLETOW-1 MON-RES-SPEC In 2017-2018, finalize the results of research begun in 2015 on Townsend's big-eared bat to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat and assess threats to bats at all preserves where they occur and develop management recommendations.
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG PLETOW-3

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2017, perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. Available for implementation
IMP-2 Submit project metadata and management data to MSP web portal Unknown
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PLETOW-2 MON-IMP-IMG Beginning in 2017, annually inspect the vicinity of Townsend's big-eared bat roosts on an annual basis (see Table of Occurrences), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
regional NFO 2018, 2019 SO
MGT-PRP-MGTPL PLETOW-4

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

In 2018-2019, prepare a management plan for Townsend's big-eared bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the Townsend's big-eared bat research study.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. available for implementation
PRP-2 Identify areas where Townsends big-eared bat and pallid bat management can be complimentary. available for implementation
PRP-3 Develop a plan for Townsends big-eared bat that prioritizes management actions for the next five years and details tasks, lead entities, responsibilities, and timelines, budgets. available for implementation
PRP-4 Submit management plan to MSP web portal available for implementation
Criteria Deadline year
Management Plan for Townsend's big-eared bat prepared by 2018 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PLETOW-1 MON-RES-SPEC In 2017-2018, finalize the results of research begun in 2015 on Townsend's big-eared bat to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat and assess threats to bats at all preserves where they occur and develop management recommendations.
PLETOW-2 MON-IMP-IMG Beginning in 2017, annually inspect the vicinity of Townsend's big-eared bat roosts on an annual basis (see Table of Occurrences), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
PLETOW-3 MGT-IMP-IMG Beginning in 2017, perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement.
regional NFO 2020, 2021 SO
MGT-IMP-MGTPL PLETOW-5

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2020, implement highest priority management actions for Townsend

Action Statement Action status Projects
IMP-1 Management actions to be determined by the implementation plan. waiting for precedent action
IMP-2 Submit project metadata and management data to MSP web portal. waiting for precedent action
Criteria Deadline year
Management actions implemented for Townsend's big-eared bat 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PLETOW-4 MGT-PRP-MGTPL In 2018-2019, prepare a management plan for Townsend's big-eared bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the Townsend's big-eared bat research study.
regional NFO 2020, 2021 SO
MON-IMP-MGTPL PLETOW-6

Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11

Beginning in 2020, monitor the effectiveness of management actions implemented for Townsend's big-eared bats on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit metadata, monitoring data and reports to MSP web portal. waiting for precedent action
Criteria Deadline year
Monitoring data submitted to MSP web portal within one year of management actions being completed. 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PLETOW-5 MGT-IMP-MGTPL Beginning in 2020, implement highest priority management actions for Townsend

Regional and/or Local NFO 2018, 2019, 2020, 2021 VF
MON-IMP-MONPL POGABR-1

Management units: 6

Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
NAVFOS-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
ORCCAL-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGABR-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGNUD-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

Regional and/or Local NFO 2018, 2019, 2020, 2021 SL
MON-IMP-MONPL POGNUD-1

Management units: 3

Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
ERYARI-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego button-celery in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
NAVFOS-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
ORCCAL-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
POGABR-1 MON-IMP-MONPL Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

regional NFO 2020 VF
MON-IMP-MONPL POLPOL-1

Management units: 1, 2, 3, 4, 5, 6, 7, 8

In 2020, implement regional and subregional California gnatcatcher monitoring initiated in 2016 to determine the percent area occupied (PAO) by California gnatcatcher in modeled high and very high suitability habitat on Conserved Lands and military lands in the MSPA as part of a larger monitoring program for southern California. Over the next 15 years, determine trends in California gnatcatcher PAO and in their colonization and extinction rates and be able to detect at least 30% change in PAO. Identify associations between habitat and threat correlates with gnatcatcher PAO and with extinction and colonization rates and develop biologically meaningful thresholds for management and to specify management criteria and recommendations.

Action Statement Action status Projects
IMP-1 When the results of the 2016 California gnatcatcher surveys become available, coordinate with the regional California gnatcatcher survey group made up of wildlife agencies, land managers and scientists, to determine when the next round of regional surveys should be implemented. It is anticipated that the surveys are likely to be held in 2020. Based on the monitoring results and group recommendations, adjust the habitat model and sampling frame as necessary to better predict suitable habitat in the northern extent of the range. on hold
IMP-2 Submit project metadata, monitoring datasets, analyses and reports to the MSP Web Portal. on hold
Criteria Deadline year
Regional and Subregional California Gnatcatcher Surveys completed and report submitted by 2021 2021
Code Obj. code Statement
POLPOL-2 MON-RES-SPEC In 2020, implement California gnatcatcher postfire monitoring conducted in 2015 and 2015 to: determine whether there has been further recovery of California gnatcatchers in areas burned in 2003, 2007 and 2014 (i.e., PAO>10%); evaluate if there is a difference in PAO between areas burned in 2003, 2007 and 2014; investigate the relationship between gnatcatcher PAO and vegetation composition, cover and structure; and evaluate the composition, cover and structure of coastal sage scrub in areas with different fire frequencies and patterns of vegetation recovery based upon time since fire, spatial distribution, previous land use, and environmental conditions. Use the regional gnatcatcher and vegetation monitoring protocols to monitor postfire recovery of gnatcatchers and vegetation at sampling points surveyed in 2016. Analyze gnatcatcher and vegetation data to develop overall and site specific vegetation management recommendations for postfire recovery of coastal sage scrub vegetation to support California gnatcatchers.
regional POST 2020 VF
MON-RES-SPEC POLPOL-2

Management units: 1, 2, 3, 4, 5, 6, 7, 8

In 2020, implement California gnatcatcher postfire monitoring conducted in 2015 and 2015 to: determine whether there has been further recovery of California gnatcatchers in areas burned in 2003, 2007 and 2014 (i.e., PAO>10%); evaluate if there is a difference in PAO between areas burned in 2003, 2007 and 2014; investigate the relationship between gnatcatcher PAO and vegetation composition, cover and structure; and evaluate the composition, cover and structure of coastal sage scrub in areas with different fire frequencies and patterns of vegetation recovery based upon time since fire, spatial distribution, previous land use, and environmental conditions. Use the regional gnatcatcher and vegetation monitoring protocols to monitor postfire recovery of gnatcatchers and vegetation at sampling points surveyed in 2016. Analyze gnatcatcher and vegetation data to develop overall and site specific vegetation management recommendations for postfire recovery of coastal sage scrub vegetation to support California gnatcatchers.

Action Statement Action status Projects
RES-1 Submit project metadata, monitoring datasets, analyses and reports to the MSP Web Portal. On hold
Criteria Deadline year
Postfire California Gnatcatcher Surveys completed and report submitted by 2021 2021
Code Obj. code Statement
POLPOL-1 MON-IMP-MONPL In 2020, implement regional and subregional California gnatcatcher monitoring initiated in 2016 to determine the percent area occupied (PAO) by California gnatcatcher in modeled high and very high suitability habitat on Conserved Lands and military lands in the MSPA as part of a larger monitoring program for southern California. Over the next 15 years, determine trends in California gnatcatcher PAO and in their colonization and extinction rates and be able to detect at least 30% change in PAO. Identify associations between habitat and threat correlates with gnatcatcher PAO and with extinction and colonization rates and develop biologically meaningful thresholds for management and to specify management criteria and recommendations.

regional NFO 2017 SL
MON-RES-SPEC PUMCON-1

Management units: 3, 4, 5, 8, 9, 10

In 2017, finalize efforts begun in 2016, using available regional mountain lion movement data, to develop quantitative models of mountain lion movement in the MSPA to validate likely movement patterns and to assist with linkage and land protection prioritization.

Action Statement Action status Projects
RES-1 Project metadata, data, and report submitted to MSP web portal completed Mountain Lion Connectivity and Genetics Study- North San Diego County, Mountain Lion Critical Linkage Evaluation in MSPA
Criteria Deadline year
Mountain lion connectivity model completed by 2017 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
regional NFO 2017, 2018 SL
MON-EVAL-LINK PUMCON-2

Management units: 5, 8, 9, 10

In 2017-2018, guided by information from telemetry studies and mountain lion movement modelling, prioritize potential mountain lion crossing locations for SR 78, SR 76, SR 79, I-15, and other priority roads. For each priority crossing location, conduct detailed linkage assessments to identify existing impediments to successful crossings and recommendations for wildlife crossing infrastructure improvement (culvert maintenance, undercrossing construction, fencing, etc.) and habitat/land protection needs.

Action Statement Action status Projects
EVAL-1 Use telemetry and modelling data to inform important wildlife crossing locations along SR 78, SR 76 and SR 79 where follow up surveys will be conducted to identify specific locations and recommendations for wildlife crossing infrastructure improvements. in progress Mountain Lion Connectivity and Genetics Study- North San Diego County
EVAL-2 At each location, detailed field assessments will be performed to identify existing impediments to successful crossings, specific recommendations for wildlife crossing infrastructure improvements, and land protection needs in the area defined in order to provide for long term successful connectivity between protected lands for mountain lions and other wildlife. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
EVAL-3 Project metadata, data, and reports submitted to MSP web portal. in progress Mountain Lion Connectivity and Genetics Study- North San Diego County
Criteria Deadline year
By 2019, linkage evaluations completed for mountain lion crossing locations for SR 76, SR 79, SR 78 and other priority roads 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-1 MON-RES-SPEC In 2017, finalize efforts begun in 2016, using available regional mountain lion movement data, to develop quantitative models of mountain lion movement in the MSPA to validate likely movement patterns and to assist with linkage and land protection prioritization.
regional NFO 2017, 2018, 2019 SL
MGT-PRP-LINKPL PUMCON-3

Management units: 5, 8, 9, 10

Beginning in 2017 and based on linkage assessment results, prepare Linkage Implementation Plan that outlines specific locations and recommendations for improving mountain lion and deer connectivity across SR 78, 76, 79 and other priority roads in MU s 5, 8, 9, and 10.

Action Statement Action status Projects
PRP-1 Linkage Implementation Plans will identify the locations and design criteria for needed wildlife crossing infrastructure for priority roads and highways in MUs 5, 8, 9, and 10, including locations for road under/overcrossings and barrier fences to funnel lions and other wildlife to crossing locations for priority highways and roads waiting for precedent action
PRP-2 Submit data and reports to MSP web portal. waiting for precedent action
Criteria Deadline year
Mountain lion and deer linkage implementation plan completed for MU 5, 8, 9 and 10 by 2019 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-2 MON-EVAL-LINK In 2017-2018, guided by information from telemetry studies and mountain lion movement modelling, prioritize potential mountain lion crossing locations for SR 78, SR 76, SR 79, I-15, and other priority roads. For each priority crossing location, conduct detailed linkage assessments to identify existing impediments to successful crossings and recommendations for wildlife crossing infrastructure improvement (culvert maintenance, undercrossing construction, fencing, etc.) and habitat/land protection needs.
regional NFO 2019, 2020, 2021 SL
MGT-IMP-LINKPL PUMCON-4

Management units: 5, 8, 9, 10

Beginning in 2019, implement linkage enhancement actions outlined in linkage evaluations and linkage implementation plans

Action Statement Action status Projects
IMP-1 As funding becomes available, implement priority wildlife crossing improvements for MU 5, 8, 9, 10 and other priority roads. waiting for precedent action
Criteria Deadline year
Management actions to improve connectivity for mountain lions and deer implemented 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-2 MON-EVAL-LINK In 2017-2018, guided by information from telemetry studies and mountain lion movement modelling, prioritize potential mountain lion crossing locations for SR 78, SR 76, SR 79, I-15, and other priority roads. For each priority crossing location, conduct detailed linkage assessments to identify existing impediments to successful crossings and recommendations for wildlife crossing infrastructure improvement (culvert maintenance, undercrossing construction, fencing, etc.) and habitat/land protection needs.
PUMCON-3 MGT-PRP-LINKPL Beginning in 2017 and based on linkage assessment results, prepare Linkage Implementation Plan that outlines specific locations and recommendations for improving mountain lion and deer connectivity across SR 78, 76, 79 and other priority roads in MU s 5, 8, 9, and 10.
regional NFO 2019, 2020, 2021 SL
MON-IMP-LINKPL PUMCON-5

Management units: 5, 8, 9, 10

Beginning in 2019, monitor implementation and effectiveness of linkage enhancements actions for mountain lions and other species, including mule deer.

Action Statement Action status Projects
IMP-1 Submit Metadata, data, and report to MSP web portal. waiting for precedent action
Criteria Deadline year
Monitoring data submitted to MSP web portal within one year of management actions being completed. 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
regional NFO 2017, 2018, 2019 SL
MGT-DEV-BMP PUMCON-6

Management units: 5, 8, 9, 10

Beginning in 2017, support efforts by UC Davis Wildlife Health Center and others to test the effectiveness of various methods to deter mountain lions and other native predators from preying on livestock/domestic animals in locations where depredation permits have been issued in recent past, with the goal of reducing depredation permits by 50%.

Action Statement Action status Projects
DEV-1 Research existing predator deterrent systems for their applicability to southern California wildlife communities. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
DEV-2 Implement quantitative pilot study to evaluate effectiveness of various methods in deterring native predators from taking livestock. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
DEV-3 From these studies, establish a set of "Best Practices" for protecting livestock from native predators. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
DEV-4 Support efforts in the development of outreach materials to livestock owners on proper husbandry and native predator deterrence techniques to protect livestock from native predators. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
DEV-5 Submit project metadata, data, and BMPs to MSP web portal. in progress Mountain Lion Road Crossing and Deterrent Methods Evaluations
Criteria Deadline year
Best Practices for Reducing native predator take of domestic livestock developed and disseminated to landowners. 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
regional NFO 2019, 2020, 2021 SL
MGT-IMP-BMP PUMCON-7

Management units: 5, 8, 9, 10

Beginning in 2019, implement Best Management Practices for deterring mountain lions and other predators from preying on livestock/domestic animals with the goal of reducing depredation permits by 50%.

Action Statement Action status Projects
IMP-1 Submit Metadata, data, and management actions to MSP web portal. waiting for precedent action
Criteria Deadline year
BMPs implemented to reduce mountain lion predation on domestic animals 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-6 MGT-DEV-BMP Beginning in 2017, support efforts by UC Davis Wildlife Health Center and others to test the effectiveness of various methods to deter mountain lions and other native predators from preying on livestock/domestic animals in locations where depredation permits have been issued in recent past, with the goal of reducing depredation permits by 50%.
regional NFO 2019, 2020, 2021 SL
MON-DEV-BMP PUMCON-8

Management units: 5, 8, 9, 10

Beginning in 2019, monitor the effectiveness of BMPs implemented to deter mountain lions and other predators from preying on livestock/domestic animals.

Action Statement Action status Projects
DEV-1 Implement field studies to assess effectiveness of BMPs in reducing livestock predation by mountain lions and other native predators Unknown
DEV-2 Monitor rate of depredation permits to evaluate if BMPs are having desired effect on reducing lion mortalities. Unknown
DEV-3 Submit project metadata, monitoring data and results to MSP web portal. Unknown
Criteria Deadline year
Monitoring effectiveness of BMPs implemented within one year of management actions 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-6 MGT-DEV-BMP Beginning in 2017, support efforts by UC Davis Wildlife Health Center and others to test the effectiveness of various methods to deter mountain lions and other native predators from preying on livestock/domestic animals in locations where depredation permits have been issued in recent past, with the goal of reducing depredation permits by 50%.
PUMCON-7 MGT-IMP-BMP Beginning in 2019, implement Best Management Practices for deterring mountain lions and other predators from preying on livestock/domestic animals with the goal of reducing depredation permits by 50%.
regional NFO 2020 SL
MON-PRP-MONPL PUMCON-9

Management units: 3, 4, 5, 8, 9, 10

In 2020, develop a long-term monitoring strategy that integrates BMPs to document mountain lion population, connectivity and distribution within the MSPA. Monitoring plan will incorporate, as feasible: 1) possible non invasive methods for monitoring genetic connectivity (scat, hair snares, tracks, etc.), 2) methods for integrating camera trap data from various sources to answer questions regarding lion movement and distribution, and 3) a regional database to track information on lion mortalities and cause (vehicle strikes, depredation permits, illegal take, etc.) to identify problem areas and to inform management actions.

Action Statement Action status Projects
PRP-1 Work with UCD to evaluate the feasibility of various mountain lion DNA testing methods (scat, hair snare, etc.) for use in future long term monitoring of genetic connectivity Unknown
PRP-2 Identify and collate data from various relevant camera trap studies (SDTT, UCD-WHC, USGS, Feral Pig Study, land managers) and evaluate how data could be integrated as part of a long term monitoring strategy for documenting mountain lion movement and distribution within the MSPA. Unknown
PRP-3 Identify existing sources for lion mortality data, conduct outreach, and work to develop a system for collating and integrating lion mortality data from various sources into the MSP Database. Unknown
Criteria Deadline year
Monitoring plan for documenting mountain lion connectivity are developed and integrated with available track and camera data from other sources to identify the level of 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-1 MON-RES-SPEC In 2017, finalize efforts begun in 2016, using available regional mountain lion movement data, to develop quantitative models of mountain lion movement in the MSPA to validate likely movement patterns and to assist with linkage and land protection prioritization.
PUMCON-2 MON-EVAL-LINK In 2017-2018, guided by information from telemetry studies and mountain lion movement modelling, prioritize potential mountain lion crossing locations for SR 78, SR 76, SR 79, I-15, and other priority roads. For each priority crossing location, conduct detailed linkage assessments to identify existing impediments to successful crossings and recommendations for wildlife crossing infrastructure improvement (culvert maintenance, undercrossing construction, fencing, etc.) and habitat/land protection needs.
PUMCON-3 MGT-PRP-LINKPL Beginning in 2017 and based on linkage assessment results, prepare Linkage Implementation Plan that outlines specific locations and recommendations for improving mountain lion and deer connectivity across SR 78, 76, 79 and other priority roads in MU s 5, 8, 9, and 10.
PUMCON-6 MGT-DEV-BMP Beginning in 2017, support efforts by UC Davis Wildlife Health Center and others to test the effectiveness of various methods to deter mountain lions and other native predators from preying on livestock/domestic animals in locations where depredation permits have been issued in recent past, with the goal of reducing depredation permits by 50%.
regional NFO 2021 SL
MON-IMP-MONPL PUMCON-10

Management units: 3, 4, 5, 8, 9, 10

In 2021, implement monitoring actions as identified in the Mountain lion monitoring plan.

Action Statement Action status Projects
IMP-1 Submit project metadata, data, and reports to MSP web portal Unknown
Criteria Deadline year
Monitoring program for mountain lions implemented by 2021 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
PUMCON-9 MON-PRP-MONPL In 2020, develop a long-term monitoring strategy that integrates BMPs to document mountain lion population, connectivity and distribution within the MSPA. Monitoring plan will incorporate, as feasible: 1) possible non invasive methods for monitoring genetic connectivity (scat, hair snares, tracks, etc.), 2) methods for integrating camera trap data from various sources to answer questions regarding lion movement and distribution, and 3) a regional database to track information on lion mortalities and cause (vehicle strikes, depredation permits, illegal take, etc.) to identify problem areas and to inform management actions.

Regional NFO 2021 VF
MON-IMP-MONPL QUEENG-1

Management units: 2, 3, 4, 5, 6, 8, 9, 10, 11

In 2021, conduct Engelmann oak woodland monitoring as part of implementation of the Oak Woodland Vegetation Monitoring Plan on Conserved Lands in the MSPA.

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and reports to the MSP web portal waiting for precedent action
Criteria Deadline year
Oak Woodland Vegetation Monitoring Plan implemented 2021 2021
Code Obj. code Statement
OAKWOO-1 MON-DEV-MAP Starting in 2017, map tree mortality in oak woodlands across the MSPA using high resolution aerial imagery, LIDAR and other remote sensing data and incorporate existing datasets, where available, to determine the current status of oak woodlands in the MSPA that are affected by drought, wildfire and invasive pests and fungal pathogens.
OAKWOO-2 MON-PRP-MONPL Beginning in 2019, prepare an oak woodland vegetation monitoring plan for Conserved Lands in the MSPA to assess tree mortality and recruitment, including that of coast live oak and Engelmann oak, track community composition, structure and ecological integrity, and to document threats and assess environmental conditions. Prepare the oak woodland monitoring to integrate where feasible or bulid upon the results of other monitoring projects such as riparian forest and scrub vegetation monitoring, shothole borer/Fusarium complex monitoring, and golden-spotted oak borer and fungal pathogen monitoring. The monitoring plan should include a conceptual model, specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, permanent sampling locations, timeline, and standardized protocols. Use the Oak Woodland Tree Mortality map and the distribution of coast live oak and Engelmann oaks to develop a sampling frame and stratified sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate ecological integrity at monitoring sites by integrating other types of monitoring into the long-term sampling plots, such as abiotic element monitoring (e.g., automated weather stations and soil sensors, GIS-data layers), ecological integrity monitoring (e.g., plant and animal communities, ecological processes), MSP VF species monitoring, and threats monitoring (e.g., fire, climate change, disease, invasive animals and invasive plants).
OAKWOO-3 MON-IMP-MONPL In 2021, conduct oak woodland monitoring to implement the Oak Woodland Vegetation Monitoring Plan on Conserved Lands in the MSPA.

regional NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-CAPR RALOBS-1

Management units: 1, 7

From 2017 to 2021, continue the existing captive rearing and release efforts for Rideway's rail implememted by the wildlife agencies.

Action Statement Action status Projects
IMP-1 Implement management actions specified by the wildlife agencies for recovery of light-footed Ridgway's rail. in progress
Criteria Deadline year
Wildlife Agency specified management actions completed 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG RALOBS-2

Management units: 1, 7

From 2017 to 2021, annually inspect the existing occurrences of Ridgway's rail to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. available for implementation
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. available for implementation
IMP-3 Submit monitoring data and management recommendations to MSP web portal available for implementation
Criteria Deadline year
Surveys Completed Annually with management recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Urban developmentURBDEV
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG RALOBS-3

Management units: 1, 7

From 2017-2021, perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement.

Action Statement Action status Projects
IMP-1 Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. available for implementation
IMP-2 Submit project metadata and management data to MSP web portal. available for implementation
Criteria Deadline year
Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Urban developmentURBDEV

Regional and/or Local NFO 2018, 2019, 2020, 2021 VF
MON-IMP-MONPL SPEHAM-1

Management units: 2, 3, 4, 5, 6

Beginning in 2018, conduct annual surveys for western spadefoot in vernal pools to determine distribution and status and to assess habitat conditions and threats. Management recommendations will be made and implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).

Action Statement Action status Projects
IMP-1 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. On hold
Criteria Deadline year
Annual Surveys Completed with Management Recommendations 2021
Threat Name Threat Code
Altered hydrologyALTHYD
Climate changeCLICHN
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
VERPOO-1 MON-SURV-VEG Beginning in 2018, conduct annual qualitative monitoring of all vernal pools on Conserved Lands in the MSPA to document threats such as trampling, dumping and invasive plants, and as defined in the City of San Diego's Vernal Pool Managment and Monitoring Plan (VPMMP; City of San Diego 2015). Qualitative surveys should be conducted during the wet season using standardized protocols and should assess threats, whether pools are inundated, and verify fairy shrimp viability and reproduction. Three visits should be made during the wet season to determine pool inundation. The monitoring results should be used to determine the overall disturbance category (i.e., Levels 1-3), formulate management recommendations and to determine whether more comprehensive threats monitoring is required.
VERPOO-2 MON-SURV-VEG Beginning in 2018, conduct baseline hydrological surveys of vernal pools on Conserved Lands in the MSPA to characterize the hydrology of each basin within a vernal pool complex and prepare a report with survey results for each pool complex. Use a standardized methodology and protocol to determine maximum pool depth, define pool inlet and outlets, and geomorphic setting of the complex, as described in the VPMMP (City of San Diego 2015).
VERPOO-3 MON-EVAL-DIST Starting in 2018, conduct a topographic disturbance assessment if annual qualitiative monitoring indicates there is topographical and/or hydrological disturbance at a vernal pool (see City of San Diego VPMMP). Measure maximum pool depth for each basin, determine inlet and outlet locations. These data can be compared against baseline hydrological survey data to inform management recommendations. If there is a need to reconstruct a basin because of disturbance, then monitoring should be repeated to determine if the restored pool has achieved hydrological function.
VERPOO-4 MGT-IMP-VPML1 Beginning in 2018, conduct annual routine stewardship management to maintain vernal pool habitat and existing MSP species populations as defined in the VPMMP (City of San Diego 2015). Level 1 pools are those where little maintenance is needed, other than routine access patrols and enforcement, removal of trash and debris, edge effects maintenance (e.g., offsite erosion control and irrigation management), maintaining fencing and signage, reparing trespass damage, repairing minor topographic disturbances, and controlling invasive plants for MSP species and general habitat maintenance (2 visits per spring).
VERPOO-5 MGT-IMP-VPML2 Beginning in 2018, conduct Level 2 management to enhance and stabilize vernal pool habitat and MSP species that monitoring has shown to be in decline based on VPMMP (City of San Diego 2015) management triggers. Level 2 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes mechanized and hand repair to baseline conditions those moderate topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in = 20-foot surrounding site-specific management buffers followed up with invasive plant control 2 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 3 per year. For Level 2 management, seed banking, bulking and redistribution may be needed to enhance declining populations of MSP plant species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.
VERPOO-6 MGT-IMP-VPML3 Beginning in 2018, conduct Level 3 management to restore vernal pool habitat and MSP species that monitoring has shown to be in decline or in very poor condition based on VPMMP (City of San Diego 2015) management triggers. Level 3 management includes implementing all Level 1 actions in addition to other more intensive management. This more intensive management includes restoring existing pools to increase populaitons of MSP species, mechanized and hand repair to baseline conditions those extensive topographic disturbances that affect pool integrity, ponding potential and overall size as defined in the VPMMP (City of San Diego 2015). Vernal pools with MSP species should be dethatched as needed to clear thatch from vernal pool basins and in a 35-foot watershed management buffer followed up with invasive plant control 4 times in the spring. General invasive plant control should be conducted in other vernal pool basins and/or associated upland watersheds, with the number of visits increased to 4 per year. For Level 3 management, some MSP species may be absent from the seed bank, requiring off-site collection from genetically appropriate populations, bulking and redistribution to restore the MSP species seed bank. Container plantings may also be needed to restore MSP species. For declining MSP fairy shrimp populations, additional monitoring is required to determine what is causing the decline followed by management to mitigate the threat. Shrimp cysts may need to be collected from other pools in the complex and redistributed into the impacted pool, although with no collection from pools containing Lindahl's fairy shrimp. Off-site cyst collection may be implemented if there is no on-site cyst bank or it is too depauperate.

local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-PRED STEANT-1

Management units: 1, 7

From 2017-2021, annually conduct predator control at breeding least tern colonies before and during the nesting season to improve fledgling success. Include tracking of predator-tern interactions to provide real-time data to improve control efforts during the breeding season.

Action Statement Action status Projects
IMP-1 Conduct predator control prior to breeding and during the breeding season to control the various taxa (e.g. mammals, reptiles, birds, inverebrates) that prey on adult, nestling, and fledgling least terns. in progress
IMP-2 Submit data and reports to MSP web portal. in progress
Criteria Deadline year
Predator Control Implemented and Reports Completed Annually 2021
local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-PRED STEANT-2

Management units: 1, 7

From 2017-2021, monitor the effectiveness of predator control at least tern colonies and monitor overall tern predator status and trend to identify larger issues potentially affecting other MSP species and to improve management effectiveness.

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal available for implementation
Criteria Deadline year
Monitoring completed and data and report submitted within 1 year of management actions being completed. 2021
regional NFO 2017, 2018, 2019, 2020, 2021 SO
MON-SURV-SPEC STEANT-3

Management units: 1, 7

From 2017 to 2021, continue the existing survey efforts for California least tern implemented by the wildlife agencies and military.

Action Statement Action status Projects
SURV-1 Submit monitoring data and management recommendations to MSP web portal In progress
Criteria Deadline year
Least Tern Surveys and Reports Completed Annually 2021
local NFO 2017, 2018, 2019, 2020, 2021 SO
MON-IMP-IMG STEANT-4

Management units: 1, 7

From 2017 to 2021, annually inspect the existing nest sites for California least tern, taking precautions to avoid disturbance during the nesting season, to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.

Action Statement Action status Projects
IMP-1 Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. Available for implementation
IMP-2 Based upon threat evaluation, determine if routine management or more intensive management is warranted. Available for implementation
IMP-3 Submit monitoring data and management recommendations to MSP web portal Available for implementation
Criteria Deadline year
Surveys Completed Annually with management recommendations 2021
local NFO 2017, 2018, 2019, 2020, 2021 SO
MGT-IMP-IMG STEANT-5

Management units: 1, 7

From 2017-2021, perform routine management activities such as invasives removal, sand replenishment, nest prep, and protecting occurrences from disturbance through fencing, signage, and enforcement.

Action Statement Action status Projects
IMP-1 Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. Available for implementation Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern
IMP-2 Submit project metadata and management data to MSP web portal. Available for implementation Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern
Criteria Deadline year
Management Completed as Needed Based Upon Monitoring Recommendations 2021

regional and/or local NFO 2019 SS
MON-IMP-IMG TETDIO-1

Management units: 3, 8

In 2019, inspect Parry's tetracoccus occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Action Statement Action status Projects
IMP-1 Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. on hold
IMP-2 Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. on hold
Criteria Deadline year
Surveys Completed in 2019 with Management Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
TETDIO-2 MGT-IMP-IMG Beginning in 2020, conduct routine management actions identified through the 2019 IMG monitoring at Parry's tetracoccus occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
local NFO 2020, 2021 SS
MGT-IMP-IMG TETDIO-2

Management units: 3, 8

Beginning in 2020, conduct routine management actions identified through the 2019 IMG monitoring at Parry's tetracoccus occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.

Action Statement Action status Projects
IMP-1 Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species to less than 20% absolute cover. On hold
IMP-2 Submit project metadata and management data to the MSP Web Portal. On hold
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Threat Name Threat Code
Human uses of the PreservesHUMUSE
Invasive plantsINVPLA
Urban developmentURBDEV
Code Obj. code Statement
TETDIO-1 MON-IMP-IMG In 2019, inspect Parry's tetracoccus occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
Regional NFO 2017 SS
MON-RES-SPEC TETDIO-3

Management units: 3, 8

In 2017, begin field research into soils and habitat relationships and conduct habitat suitability and climate change modeling for Parry's tetracoccus and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.

Action Statement Action status Projects
RES-1 Test soils at potential expansion sites and compare to occupied reference sites to determine site suitability based on soils. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-2 Prepare habitat suitability models under current environmental conditions and for different scenarios of climate change to delineate potential future habitat. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-3 Collect covariate data on vegetation composition and cover (alliance and association-level mapping), soils, invasive plants and other threats for selected populations. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-4 Prioritize locations for conservation, management, and future surveys based on predicted distributions and environmental correlates. In progress Enhancing the Resilience of Edaphic Endemic Plants
RES-5 Submit project metadata, monitoring data, habitat models, analyses, and report to MSP web portal. In progress Enhancing the Resilience of Edaphic Endemic Plants
Criteria Deadline year
Refined Models and Prioritized Future Survey Locations for Parry's Tetracoccus by 2018 2021
Threat Name Threat Code
Climate changeCLICHN
Invasive plantsINVPLA
Loss of connectivityLOSCON
Urban developmentURBDEV
Code Obj. code Statement
TETDIO-1 MON-IMP-IMG In 2019, inspect Parry's tetracoccus occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

regional NFO 2017, 2018 SO
MON-SURV-SPEC VIRBEL-1

Management units: 1, 6, 8

In 2017-2019, conduct surveys for least Bell's vireo and habitat assessment to compare population status and recovery in the MSPA before, during, and after SHB/Fusarium complex in infested habitat over time at the Tijuana River Valley and other sites, if funding available, such as Camp Pendelton and San Luis Rey River. Prepare site-specific management recommendations based on survey results and habitat assessments.

Action Statement Action status Projects
SURV-1 Submit monitoring data and management recommendations to MSP web portal In progress
Criteria Deadline year
Least Bell's Vireo Surveys and Reports Completed by 2020 2021
regional NFO 2020 SO
MGT-PRP-MGTPL VIRBEL-2

Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11

In 2020, if least Bell's vireo survey results indicate management is needed to reduce impacts from SHB/Fusarium infestation, then develop a management plan that incorporate SHB/Fusarium monitoring and management and prioriotize management recommendations.

Action Statement Action status Projects
PRP-1 Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. waiting for precedent action
PRP-2 Develop a management plan for least Bell's vireo that prioritizes management actions for the next five years. waiting for precedent action
PRP-3 Submit management plan to MSP web portal waiting for precedent action
Criteria Deadline year
Management Plan for Least Bell's Vireo Completed by 2021 2021
regional and/or local NFO 2021 SO
MGT-IMP-MGTPL VIRBEL-3

Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11

Beginning in 2021, implement the highest priority management actions for least Bell's vireo on Conserved Lands.

Action Statement Action status Projects
IMP-1 Management actions to be determined by the management plan. waiting for precedent action
IMP-2 Submit project data and management actions to MSP web portal waiting for precedent action
Criteria Deadline year
Management actions implemented for Least Bell's Vireo 2021
regional and/or local NFO 2021 SO
MON-IMP-MGTPL VIRBEL-4

Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11

Beginning in 2021, monitor the effectiveness of management actions implemented for least Bell's vireo on Conserved Lands

Action Statement Action status Projects
IMP-1 Submit monitoring data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring completed and data and report submitted within 1 year of management actions 2021
2017-2019 Developing a Map of Ecological Integrity Using Remote Sensing
This project's objective is to create a map of ecological integrity using remotely sensed data. Data sources include high resolution lidar and high resolution 4-band imagery from multiple sources. Final products from this work will include: 1) an updated high resolution Digital Elevation Model, 2) an updated high resolution Digital Surface Model, 3) a raster image depicting vegetation height (using lidar), 4) a raster image depicting herbaceous, shrub, and tree cover, 5) a map layer of ecological integrity (at a 50m grid) for coastal sage scrub, chaparral, oak woodlands, and riparian woodlands. Ecological integrity is defined for each vegetation community independently, based on analysis of previous field work. This project will build off the information and products previously created.
2021-2026 Rare Plant Regional Discovery Surveys
Starting in 2021, surveys were conducted on suitable habitat on Conserved Lands to document whether historic plant occurrences were extant and to discover new occurrences for rare plant species. The purpose of these surveys is to refine and update the distribution of these plants in the Management and Monitoring Strategic Plan Area. Voucher specimens and photographs are taken for each occurrence. Some species are already part of the Rare Plant Inspect and Manage Program and any new occurrences for these species will be included in future monitoring. In the next update of the Management and Monitoring Strategic Plan (2027), species not formerly monitored will be evaluated and potentially added to the Rare Plant Inspect and Manage Program. Botanists surveyed for four rare plant species in 2021: San Diego coastalcreeper (Aphanisma blitoides), Blochman’s dudleya (Dudleya blochmaniae), coast wallflower (Erysimum ammophilum), and Orcutt’s bird’s-beak (Dicranostegia orcuttiana). In 2022, botanists surveyed for: San Diego coastalcreeper (Aphanisma blitoides), Baja California oat grass (Sphenopholis interrupta ssp californica), San Diego ambrosia (Abrosia pumila), Wiggins’ cryptantha (Crytantha wigginsii). In 2023, botanists will survey for five rare plant species: Deane’s milkvetch (Astragalus deanei), Parish brittlescale (Atriplex parishii), Mexican flannelbush (Fremontodendron mexicanum), Jennifer’s monardella (Monardella stoneana ), and small-leaved rose (Rosa minutifolia).
An Adaptive Management Approach to Recovering Burrowing Owl Populations and Restoring a Grassland Ecosystem in San Diego County
San Diego Zoo Institute for Conservation Research (ICR), in partnership with multiple agencies, has developed an adaptive conservation management program to assist in the recovery of Western Burrowing Owls (BUOW; Athene cunicularia hypugaea) and their grassland ecosystem in San Diego County. Main objectives include (1) establishing more natural grassland ecosystems in San Diego County by re-establishing ground squirrels that provide critical resources for BUOW and valuable ecosystem engineering effects; (2) better understanding of the factors regulating BUOW population dynamics; (3) developing a comprehensive strategic management plan for BUOW in San Diego County; and (4) implementing the strategic management plan to begin establishing additional breeding nodes of burrowing owls. In 2017 ICR partnered with SDMMP to make publicly available a BUOW Conservation and Management Plan for San Diego County. This is a living document developed with input from local, state, and federal wildlife agencies, and will continue to be updated in the future.
Argentine Ant Study
The USGS conducted the experimental implementation of sampling MSP sites during wet year conditions. The project utilized a stratified sampling design and a protocol developed in 2014. A combination of GIS and field measured covariates were used to identify drivers that impact Argentine ant population dynamics. The project also included developing potential measures to make the site less or unsuitable for Argentine ants. The outcome of this study will inform management actions for experimental implementation.
Bat Community Management and Monitoring
Both the pallid bat (Antrozous pallidus) and Townsend’s big-eared bat (Corynorhinus townsendii), have been proposed as covered species in the North County MSCP plan and are included in the MSP. These two species are believed to be at high to moderate risk of loss in the MSP area because of their low numbers and sensitivity to human disturbance. However, their population status, locations of roosts (diurnal, nocturnal, and maternity), primary foraging areas, water sources used, threats, and connectivity between populations in the MSP area are largely unknown. For this reason, San Diego County-wide surveys for these species were needed to document where they were found and what their current population status was. Information gleaned from these surveys will allow land managers to implement appropriate management actions to conserve their habitats. The MSP identified this work as a priority for implementation starting in 2015. In 2015, the SDNHM under contract to USGS surveyed areas with known pallid and Townsend's big-eared bat occurrences as identified in the MSP and in other high potential sites based on previous survey work by USGS and the SDNHM. A variety of methods were used (roost surveys, mist-netting, acoustic surveys, etc.) to identify and map the primary roosts and foraging areas used by pallid bat and Townsend's big-eared bat.
Carlsbad Wildlife Movement Analysis
A study of wildlife movement within the Carlsbad’s NCCP plan, known as the Habitat Management Plan (HMP). The HMP is the only approved subarea plan of the sub regional Multiple Habitat Conservation Plan (MHCP). A key objective of the HMP is to “maintain functional wildlife corridors and habitat linkages within the city and to the region.” An inventory of possible wildlife movement corridors and constraints, and an initial monitoring of key locations, is necessary to provide a baseline assessment of animal movement within the city and to begin evaluating the MHCP and HMP objectives. This Wildlife Movement Analysis Final Report is a summary of the methods and results of an inventory of potential wildlife movement corridors and pinchpoints within the City of Carlsbad.
Coastal Cactus Wren Conservation Network
The Coastal Cactus Wren Conservation Network is an ad hoc group of more than 100 individuals representing research institutions, land management agencies, local government, non-profit conservation organizations and wildlife agencies. Members work together to exchange research and management information to develop best practices, policies, and programs that promote conservation and recovery of this bird throughout its range (Ventura, Los Angeles, San Bernardino, Orange, Riverside, and San Diego counties). This information will inform publication of a regional conservation strategy for the coastal cactus wren. Cactus wrens (Campylorhynchus brunneicapillus) are distributed across the arid regions of the southwestern United States and northern and central Mexico (Hamilton et al. 2011). While the desert populations are fairly abundant, populations of coastal cactus wrens have declined dramatically over the past 30 years, with extirpation and genetic isolation affecting many locations as a result of habitat loss, habitat fragmentation, edge effects of development, and catastrophic fires (Solek and Szijj 2004). The coastal population is unique in that it occurs exclusively within the coastal sage scrub plant community, ranging from Ventura County south into San Diego County, U.S.A. and northwestern Baja California, Mexico. The firestorms of 2007 impacted several strongholds for the coastal cactus wren in Orange and San Diego counties. The significant loss of habitat and birds was the impetus for formation of the Coastal Cactus Wren Network. For more information on the Coastal Cactus Wren Conservation Network, please see the document titled &amp;quot;Coastal Cactus Wren Working Group Regional Goals, Objectives, and Strategies&amp;quot;.
Covered and Invasive Species Management: Crestridge Ecological Reserve and South Crest Properties
This was a two year, TransNet-funded study (#5001586) on Crestridge Ecological Reserve and South Crest properties. Both properties support MSCP covered species and sensitive habitats, and function as critical landscape linkages between the northern and southern MSCP. Surrounded by residential development and heavily impacted by the 2003 Cedar Fire, these properties are subject to ongoing invasive plant issues. Specific task actions included invasive plant and covered plant species mapping and risk assessment s, invasive plant control and experimental studies, and development of an early detection invasive control plan.
El Monte Preserve Bat Hotel
The goal of this project is to aid the recovery of locally declining bat species, by: 1) Creating a thermally stable, long-term (i.e., 50-75 years) roost site, or bat hotel, on the El Monte Preserve; 2) Creating replicable building plans for the "bat hotel" so it can be used as a prototype on other conserved lands; and 3) Engaging and educating the public about the ecological importance and conservation value of bats, both online and through in-person educational events. Both the Townsend's big-eared bat (Corynorhinus townsendii) and pallid bat (Antrozous pallidus), California Species of Special Concern, were observed within 3.5 miles of the El Monte Preserve during 2017 bat surveys conducted at El Monte County Park. De Boer Engineering will build the roosting structure in close coordination with Drew Stokes, Wildlife Biologist and local bat expert for the San Diego Natural History Museum. Together, de Boer Engineering and Mr. Stokes designed the structure to be long lasting, low maintenance, and cost efficient. We envision the "bat hotel" as a prototype for additional structures to be constructed on suitable preserves throughout the MSCP Plan Area, thereby contributing to a long-term recovery strategy for this taxon on a landscape scale. This project is fully funded by SANDAG TransNet EMP Land Management Grant #S1125486
Golden Eagle (Aquila chrysaetos) Monitoring and Management Plan
Golden eagles (Aquila chrysaetos) face many threats in southern California. To reduce these threats and successfully conserve this species in western San Diego County, MSP Roadmap 2021-2026 objectives include the development and implementation of a “Management Strategic Plan for Golden Eagles in San Diego County” and a “Monitoring Strategic Plan for Golden Eagles in San Diego County”. These plans include general sections with background information and rationale for prioritizing and developing monitoring and management recommendations. Previously, the U.S. Geological Survey (USGS) in collaboration with local, State, and other Federal agencies has conducted a multi-year research study of golden eagles to address questions regarding habitat use, movement behavior, nest occupancy, genetic population structure, and human impacts on eagles. From 2016-17, occupancy analyses were conducted and it was concluded that estimates of occupancy were greatest at sample sites with more rugged terrain conditions, lower human development, and lower amounts of scrubland vegetation cover (Weins et al. 2022). Tracking data from the last 10 years in the Western Unites States have shown eagles exhibit long-distance, nonroutine movements that were responsive to the updraft potential of the spatial and temporal landscape they encountered (Poessel et al. 2022). For the development of both Plans, chapters will be shaped based on the latest scientific information regarding occupancy, natal nesting success, juvenile dispersal, movement and biotelemetry, home range estimation, habitat use, and prey availability. Site-based threats assessment will be used to determine the best management practices. These plans are developed with input and guidance provided by the San Diego Golden Eagle working group, which includes include landowners and managers, scientists, species experts, and representatives from non-profit organizations, government, and wildlife agencies. Occurrence-specific management recommendations will be based on working group input and multiple years of data on Golden Eagle population status, habitat associations, and threats. These are living documents as the plans will be updated when new information becomes available or management actions are completed, and new recommendations are needed.
Hermes Copper Adult Surveys
In 2016, researchers conducted butterfly surveys and habitat assessments at small northern populations and at southern sites. They did not detect Hermes copper adults at any of the eight northern sites, although this was consistent with other (larger) sites in the county due to continuing drought conditions. They did detect Hermes copper at some of the southern sites. Habitat assessments resulted in the mapping of 65 spiny redberry patches and 11 single redberry shrubs across the 8 sites. Up to 90 redberry shrubs were recorded in a single patch, but more patches were represented by a relatively low number of shrubs, and most of the redberry patches had at least 60% shrub cover. Additional insight may be gained from a more formal comparison to the habitat measured at Hermes copper sites in southern San Diego County. Monitoring for Hermes copper has continued at a subset of the sites in since 2016. The species has been greatly affected by the drought. This contract is funded by a combination of SANDAG (5004388 and 5005783) and USFWS (Contract: F17AC00963) contracts.
Mountain Lion Road Crossing and Deterrent Methods Evaluations
This proposed contract expands upon work conducted under contracts #5004037 and #5004593 between SANDAG and the UC Davis Wildlife Health Center to study mountain lions and their habitat use and movement patterns in San Diego County for conservation purposes. Work under this contract will help to address connectivity and survival threats for mountain lions, other wildlife, livestock, and humans by creating guidance for reducing wildlife-vehicle collisions, improving wildlife connectivity, and reducing mortality of livestock, mountain lions, and other wildlife. Task 1: Conduct highway crossing assessments; Task 2: Test Lion hazing and deterrent devices; Task 3: Write final report.
MSCP Wildlife Corridor Monitoring
A CBI study evaluating several MSCP habitat linkages and corridors critical to regional wildlife movement in the MSCP preserve. The study evaluated the functionality of the linkages, the large mammals and mesopredators using the linkages, constraints to animal movement, and underpass function.
Mule Deer Habitat Connectivity
Southern mule deer connectivity will focus on improving two major undercrossings in the eastern portion of the San Elijo Lagoon where Escondido Creek flows. These lands are heavily used by Southern mule deer as they move along this important wildlife corridor. The initial restoration site chosen is a 665 square meter (0.16 acre) parcel of land on the edge of the SELER and just south of the bridge undercrossing at Rancho Santa Fe Road. Planting here was strategized as a way to influence Southern Mule Deer to cross Escondido Creek within the creek corridor under the bridge rather than travel into the busy roadway. Nature Collective staff began removing dead black mustard (Brassica nigra) biomass within native vegetation, mostly California sagebrush (Artemisia californica) and mulefat (Baccharis salicifolia). The following day Nature Collective staff planted 90 native trees and shrubs in five-gallon containers along the busy street corner of La Bajada and S Rancho Santa Fe Road to enhance riparian scrub connectivity of the southern mule deer (Odocoileus hemionus fuliginatus). Coast Live Oak (Quercus agrifolia), elderberry (Sambucus nigra), and mulefat (Baccharis salicifolia) were planted on the upper to mid-levels of the slope, while cottonwood (Populus fremontii) and sycamore (Platanus racemosa) were planted at the toe of the slope.
Open Space Enforcement Program (CDFW and County Sheriff)
Illegal activities, such as off-road riding, trespassing, vandalism, and littering have complicated efforts to preserve and manage open space lands in the region of San Diego. Despite passive enforcement efforts, open space violations continued to persist on both publicly owned lands and privately owned properties and are believed to be adversely affecting the species and habitats that the open space lands were intended to preserve. To address this issue, the San Diego Association of Governments in association with its partners, developed an Open Space Enforcement Program to coordinate and implement an aggressive multi-agency enforcement effort for conservation and management of the open space in the region. Through a cooperative approach, the California Department of Fish and Wildlife and San Diego County Sheriff’s Department Off-Road Enforcement Team (ORET) participated in a Pilot Program to advance the following goals: 1. Prevent/reduce habitat damage 2. Reduce/prevent take of MHCP and MSCP “covered species” 3. Reduce preserve management and remediation costs 4. Support volunteer patrol activities on preserves CDFW Game Wardens primarily focused on increasing law enforcement patrols in open space areas for illegal activity to control damage of property and the environment. Game Wardens enforced state law and local ordinances against violators in the targeted areas to help reduce and deter criminal activities on open space lands in the region.The ORET developed an open space enforcement plan and conducted enforcement actions that have a nexus and contributed to the protection of open spaces throughout the region. A majority of the ORET’s efforts focused on areas previously identified, while the remainder of their effort focused on response to specific and often one-time requests for open space enforcement response. To the extent possible, the ORET and DFG collaborated on developing joint operational plans and information sharing to enhance the logistical and tactical effectiveness of the Program.
Otay Mesa Vernal Pool Restoration
The primary goal is to expand on previous grant projects to protect, and enhance vernal pool ecosystems, maritime succulent scrub (MSS) and Western burrowing owl habitats in the Goat Mesa and Wruck Canyon vernal pool complexes to create a buffer from invasive weed species and reduce sediment erosion. The main objectives to reach these goals are 1) perform brush/thatch removal and weed control within enhancement areas, 2) collect and broadcast vernal pool species seed within pools and install MSS habitat plants and seed in the upland enhancement areas and 3) install fence around Wruck Canyon vernal pools to protect them from illegal off-road activity. Contracted crews will be hired to perform brush/weed control, herbicide application and be used to collect, grow and bulk vernal pool species seed from nearby pools to seed the vernal pools and install MSS container plants/cuttings/seeds in the habitat enhancement areas. Contracted crews will also be used to install fence, erosion control materials and perform access road repairs as needed to safely access the areas. Container plants, seeds, plant protectors, fence materials and erosion control materials will be purchased directly by City staff or supplied by the contractors. City staff will perform project management.
Quino Habitat Restoration
The County of San Diego proposes to reduce a threat to the Quino checkerspot butterfly by increasing and improving habitat on a County-owned site that had previously supported a hundred or more butterflies. The Quino is threatened by development pressure, invasion by non-native grasslands (NNG) and forbs, and, likely, changes to climate and long-term drought. It is considered an MSP Category SL (species at risk of loss). The County intends to significantly enhance improve Quino habitat conditions and connectivity by: 1) identifying and closing roads/portions of road on the site to vehicular activity; 2) preventing off-road vehicle activity that may be bifurcating and destroying Quino habitat; 3) fencing and signing these areas to be restored; 4) controlling and removing invasive NNG that compete with plantago erecta, the primary Quino habitat and food source seeding areas with primarily native plant species required for Quino survival; 5) documenting site condition improvements as well as any beneficial effect for Quino,
Rare Plant Inspect and Manage Monitoring 2014-2026
From 2014-2026, a Management and Monitoring Strategic Plan (MSP Roadmap) monitoring objective for 30 rare plant species is to inspect occurrences to determine management needs. The inspect and manage (IMG) objective is implemented to document the status of rare plant occurrences and assess habitats and threats to develop specific management recommendations. IMG monitoring is implemented by a combination of land managers and contracted biologists in coordination with the SDMMP. Available rare plant data is posted below. New annual updates are typically posted in March. Based upon an evaluation of these data, a 2014-2026 monitoring schedule has been developed for the 30 rare plant species (attached below). Coordinating data collection across the region allows analyses of species and population trends over time and provides a better understanding of the association between habitat and threat covariates and population dynamics.
SAN DIEGO THORNMINT ENHANCEMENT PROJECT
Project will expand and enhance three populations of San Diego thornmint (ACIL) on San Diego Habitat Conservancy managed properties. Project main goals are to improve ACIL habitat, and increase the ACIL seed bank to reduce the likelihood of extirpation. This project is partially funded by SANDAG TransNet EMP Land Management Grant #S1125501.
San Dieguito Citizen Science Monitoring Program
The San Dieguito River Valley Conservancy (SDRVC) developed the San Dieguito Citizen Science Monitoring Program as a sustainable, cost-effective, and scientifically valid approach to gather critical data on lands within the San Dieguito River Park Focused Planning Area. This program seeks to fill knowledge gaps on the diversity, population, movements and spatial ecology of species within the watershed to better inform future land acquisitions, adaptive land management, habitat and species restoration, educational initiatives and future research. One of the main objectives of this program is to gather data that is consistent and shared with other regional planning efforts being coordinated by the San Diego Management & Monitoring Program. Data collected is submitted to regional databases and will help meet the management goals and objectives identified in the Management & Monitoring Strategic Plan. Annual expert-led surveys are carried out by volunteer citizen scientists following approved protocols and encourage community involvement and engagement.
Small Vertebrate Underpass Study
In 2012, the small animal connectivity study began as part of Connectivity Monitoring Strategic Plan (CMSP) developed by the San Diego Monitoring and Management Program (SDMMP). There were three main objectives in this study. First, to determine which groups of small vertebrates are currently using or avoiding these wildlife underpasses and understand how these behaviors may be predicted by life history characteristics. Secondly, to investigate the effectiveness of adding cover structures to underpasses as a way to enhance small vertebrate use of underpasses. Third, to evaluate the extent to which larger vertebrates often used as focus species in connectivity studies in the region act as indicators of use by small vertebrate species.
SR 94 Wildlife Infrastructure Plan
Proposed road improvements to SR 94 provide an opportunity to mitigate the potential barrier effects of the highway. This project identifies where improvements to existing infrastructure on SR-94 could improve connectivity across the South County preserves, using Best Management Practices from the scientific literature; recommends wildlife movement monitoring to identify where new crossings are needed; and identifies where additional conservation would enhance the integrity of South County linkages. The review prioritizes infrastructure improvements of 35 existing undercrossings inspected by wildlife experts in the field along 14.6 miles of SR-94 where the highway bisects conserved lands. The majority of the recommendations for infrastructure improvement focus on increasing the diameter, and thus the openness ratio (cross-sectional area divided by length), of the undercrossing itself, removing vegetation and debris blocking the undercrossing, restoring habitat in the approach to the undercrossing, and installing fencing to both (1) keep animals off the highway and (2) funnel wildlife to the undercrossings.
File name Lead Author Year Type
A Clarification on the Effects of Urbanization on Golden Eagle (Aquila chrysaetos) Habitat Selection Tracey, Jeff; Madden, Melanie; Bloom, Peter; Fisher, Robert N. 2020 report
Appendices C-F. Comprehensive Multi-species Connectivity Assessment and Planning for the Highway 67 Region of San Diego County, California Jennings, Megan; Zeller, Katherine 2017 report
Appendix A. MSCP Species_SR 94 Wildlife Infrastructure Plan 2016 report
Appendix B. Roadkill by Segment_SR 94 Wildlife Infrastructure Plan 2016 report
Appendix C. Example Infrastructure Designs, Costs, and Schedules_ SR 94 Wildlife Infrastructure Plan 2016 report
Appendix D_SIMBA SR-94 Wildlife Crossing and Highway Expansion_SR 94 Wildlife Infrastructure Plan 2016 report
Appendix E. State Route 94 Culvert and Bridge Evaluation_SR 94 Wildlife Infrastructure Plan 2016 report
Assessing Presence of Argentine Ants Using the Bait Method Matsuda, Tritia; Brehme, Cheryl; Fisher, Robert N. 2015 protocol
Bat Management in San Diego County Myers, Brian; Stokes, Drew; Preston, Kris; Fisher, Robert N.; Vandergast, Amy 2022 powerpoint presentation
CBI 2002 MSCP Wildlife Corridor Monitoring Study 2002 report
CBI 2003 MSCP Linkage Monitoring Review Conservation Biology Institute 2003 report
CBI 2003 MSCP Wildlife Corridor Monitoring Study 2003 report
CBI 2016 Wildlife Infrastructure Plan for SR-94 2016 report
Comprehensive Multi-species Connectivity Assessment and Planning for the Highway 67 Region of San Diego County, California Jennings, Megan; Zeller, Katherine 2017 report
Genetic Connectivity in the Coastal Cactus Wren Barr, Kelly; Kus, Barbara; Vandergast, Amy 2012 report
Genetic Isolation of Coastal Cactus Wren Follows Habitat Fragmentation Patterns in Southern California Barr, K. R.; Kus, Barbara; Preston, Kris; Howell, Scarlett L.; Perkins, Emily; Vandergast, Amy 2015 fact sheet
Hermes Copper Butterfly Surveys and Translocation Efforts: Task 4: 2020 Hermes Copper Adult Surveys Marschalek, Dan 2020 report
Mission Bay Park Conservation Program: Habitat Assessment, Invasive Control, and Community-Based Habitat Restoration Redfern, Chris 2013 powerpoint presentation
MSCP Linkage Evaluation_June 30, 2014 2013 report
Multi-scale effects of land cover and urbanization on the habitat suitability of an endangered toad Treglia, Michael ; Landon, Adam C.; Fisher, Robert N.; Gerard, Kyle; Fitzgerald, Lee 2018 journal article
Rare Butterfly Monitoring and Translocation Marschalek, Dan; Deutschman, Douglas 2018 report
Rarest Plants Project: Orcutt's Spineflower Hogan, Dave 2016 powerpoint presentation
Regional Occupancy and Post-Fire Recovery of California Gnatcatcher in Southern California Kus, Barbara; Preston, Kris; Houston, Alexandra 2017 powerpoint presentation
Spatial structuring and temporal shifts in the genetic composition of Blainville’s horned lizard (Phrynosoma blainvillii) populations in southern California Richmond, Jonathan; Fisher, Robert N. 2017 report
SR-94 WILDLIFE CROSSING AND HIGHWAY EXPANSION Al-Shamas, Frank; Balan, Matt; Carranza, Jecelyn; Nouri, Daniel; Tran, Brian 2013 report
Survival and Mortality of Pumas (Puma concolor) in a Fragmented, Urbanizing Landscape Vickers, Winston; Sanchez, Jessica; Johnson, Christine; Morrison, Scott; Botta, Randy; Smith, Trish; Cohen, Brian; Huber, Patrick; Ernest, Holly; Boyce, Walter 2015 journal article