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San Diego Management & Monitoring Program


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Tracker results - long format


San Diego thorn-mint Acanthomintha ilicifolia

Goal: Maintain large populations, enhance small populations, and establish new populations of San Diego thornmint or pollinator habitat to buffer against environmental stochasticity, maintain genetic diversity, and promote connectivity, thereby enhancing resilience within and among MUs over the long-term (>100 years) in native habitats.

regional and/or local PRE 2017, 2018, 2019, 2020, 2021 SO View map

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.
ACAILI-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint 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 View map

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
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-3 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the "IMG" monitoring at San Diego thornmint occurrences on Conserved Lands. 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-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
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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
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
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-2 MON-IMP-IMG Beginning in 2017, annually inspect conserved populations of San Diego thornmint 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-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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 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 and/or Local NFO 2019, 2020, 2021 SO View map

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-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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 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 View map

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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
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 and/or Local NFO 2019, 2020, 2021 SO View map

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
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 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-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.

Nuttall's acmispon Acmispon prostratus

Goal: Maintain or enhance existing Nuttall's acmispon occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in coastal bluff and coastal dune habitats.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
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-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
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-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 =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 = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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 Adaptive Management of Coastal San Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern
IMP-2 Submit project metadata and management data to the MSP Web Portal. some occurrences are in progress Adaptive Management of Coastal San 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
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-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 and/or local NFO 2017, 2018, 2019 SO View map

MGT-IMP-IEX ACMPRO-3

Management units: 1

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
Action Statement Action status Projects
IMP-1 Conduct invasive plant control within each occurrence in progress
IMP-2 Seed collection, bulking and redistribution should follow recommendations for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to minimize potential risks to populations from seed collection and distribution activities. in progress
IMP-3 Submit project metadata and management data to the MSP Web Portal. in progress
Criteria Deadline year
By 2019, 5 Nuttall's Acmispon Occurrences Enhanced/Established and Reports Submitted 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-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-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
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-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 =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 = 20% absolute cover within the occurrence
Regional and/or Local NFO 2018, 2019, 2020, 2021 SO View map

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 and/or Local NFO 2018, 2019, 2020, 2021 SO View map

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-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 =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 = 20% absolute cover within the occurrence
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 View map

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-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 =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 = 20% absolute cover within the occurrence
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.

Shaw's agave Agave shawii var shawii

Goal: Maintain existing Shaw's agave occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity and improve chances of persistence over the long term (>100 years) in coastal bluff, coastal sage scrub, and Torrey pine forest vegetation communities.

local NFO 2017, 2018, 2019, 2020, 2021 SL View map

MGT-IMP-IMG AGASHA-2

Management units: 1, 6, 7

Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016 and 2021 at Shaw's agave 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
Code Obj. code Statement
AGASHA-1 MON-IMP-IMG In 2021, inspect extant Shaw's agave 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.
AGASHA-1 MON-IMP-IMG In 2021, inspect extant Shaw's agave 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.

Tricolored blackbird Agelaius tricolor

Goal: Protect, enhance, and restore Tricolored blackbird occupied and historically occupied habitat to create resilient, self-sustaining populations that provide for persistence over the long-term (>100 years).

regional NFO 2017, 2018, 2019, 2020, 2021 SL View map

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 View map

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
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
Annual IMG monitoring of Tricolored Blackbird completed 2021
local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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 and/or local NFO 2019, 2020, 2021 SL View map

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 View map

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

Altered fire regime

Goal: The fire management goal for the MSPA is to maintain the long-term ecological integrity and viability of ecosystems, MSP species, and vegetation communities on Conserved Lands in a cost effective manner by managing the current human altered fire regime to promote a fire regime, with lower fire frequency and reduced impacts (direct and indirect) to natural resources.

regional PRE 2019, 2020, 2021 View map

MGT-PRP-IGNPL ALTFIR-1

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

Starting in 2019, prepare a Wildfire Ignition Reduction Plan detailing measures to reduce wildfire threat to Conserved Lands and at-risk resources in the MSPA. The plan should include: a review of wildfire ignitions and methods for reducing risk; analyses and spatially explicit recommendations for decreasing ignitions along roadways; recommended Project Activity Levels (PAL) for land managers to minimize ignitions from power equipment; analyses of ignition "hotspots" and ignition probabilities relative to at-risk resources with specific management actions to reduce risks; and specifications for establishing a "Fire Watch Program" to reduce ignitions and improve early fire suppression.
Action Statement Action status Projects
PRP-1 Use USGS fire risk analyses, expert and stakeholder input, and information on ignition risk reduction methods to develop a prioritized action plan for wildfire ignition reduction to protect MSP species and vegetation communities most vulnerable to catastrophic wildfire. available for implementation
PRP-2 Submit project data and Wildfire Ignition Reduction Plan to MSP Web Portal. available for implementation
Criteria Deadline year
Completed Fire Ignition Reduction Plan for the MSPA by 2021 2021
Code Obj. code Statement
ALTFIR-2 MGT-IMP-IGNPL Implement priority actions identified in the Fire Ignition Reduction Plan to reduce catastrophic wildfire ignitions on Conserved Lands in the MSPA.
ALTFIR-2 MGT-IMP-IGNPL Implement priority actions identified in the Fire Ignition Reduction Plan to reduce catastrophic wildfire ignitions on Conserved Lands in the MSPA.
ALTFIR-2 MGT-IMP-IGNPL Implement priority actions identified in the Fire Ignition Reduction Plan to reduce catastrophic wildfire ignitions on Conserved Lands in the MSPA.
regional and/or local PRE 2017, 2018, 2019, 2020, 2021 View map

MGT-RSUP-RAAM ALTFIR-3

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

Beginning in 2017, with the help of a wildfire coordinator, prepare a regional Resource Avoidance Area map (RAA Map) that identifies MSP species/vegetation communities and other at-risk resources to be avoided on Conserved Lands by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The coordinator should work with Preserve owner managers and their responding (local, state and federal) fire agencies to develop the regional RAA Map in a compatible format with fire agencies' Wildland Fire Decision Support Systems.
Action Statement Action status Projects
RSUP-1 The wildfire coordinator should work with land managers to prepare brief handouts for each preserve that accompany the Resource Avoidance Areas map and provide guidance to fire crews about what type of fire suppression actions are to be avoided in specific areas and the preferred sites for staging areas. Available for implementation
RSUP-2 Submit project metadata, datasets and RAA Map to MSP Web Portal. Available for implementation
Criteria Deadline year
Completed RAA Map for Region by 2021 2021
Code Obj. code Statement
ALTFIR-4 MGT-IMP-RAAM Starting in 2019, coordinate and integrate MSP Resource Avoidance Areas (RAA) Map into local state and federal management agencies GIS Wildland Fire Decision Support Systems.
regional and/or local PRE 2019, 2020, 2021 View map

MGT-IMP-RAAM ALTFIR-4

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

Starting in 2019, coordinate and integrate MSP Resource Avoidance Areas (RAA) Map into local state and federal management agencies GIS Wildland Fire Decision Support Systems.
Action Statement Action status Projects
IMP-1 The wildfire coordinator should work with local, state and federal fire management agencies to incorporate the MSP RAA Map into their Wildland Fire Decision Support Systems platform(s). The map should be in a compatible format with standardized symbology and mapping criteria used by the fire management agencies. waiting for precedent action
Criteria Deadline year
By 2021, MSP RAA Map in 75% of GIS wildland fire decision support systems for local, state and federal firefighting agencies 2021
Code Obj. code Statement
ALTFIR-3 MGT-RSUP-RAAM Beginning in 2017, with the help of a wildfire coordinator, prepare a regional Resource Avoidance Area map (RAA Map) that identifies MSP species/vegetation communities and other at-risk resources to be avoided on Conserved Lands by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The coordinator should work with Preserve owner managers and their responding (local, state and federal) fire agencies to develop the regional RAA Map in a compatible format with fire agencies' Wildland Fire Decision Support Systems.
ALTFIR-3 MGT-RSUP-RAAM Beginning in 2017, with the help of a wildfire coordinator, prepare a regional Resource Avoidance Area map (RAA Map) that identifies MSP species/vegetation communities and other at-risk resources to be avoided on Conserved Lands by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The coordinator should work with Preserve owner managers and their responding (local, state and federal) fire agencies to develop the regional RAA Map in a compatible format with fire agencies' Wildland Fire Decision Support Systems.
regional PRE 2019, 2020, 2021 View map

MGT-PRP-PFMGTPL ALTFIR-5

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

Beginning in 2019, conduct an inventory of preserve fire management plans and identify elements to include in standardized preserve fire management plans. Prepare a guidebook for preserve fire management plans that, at a minimum, specifies overall pre-fire, fire suppression and post-fire management actions and includes the RAAM that identifies MSP species/habitats and other at-risk resources to be avoided by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The guidebook should identify standard pre-fire, fire suppression, and post-fire actions for specific MSP species and vegetation communities to be incorporated into Preserve Fire Management Plans.

Action Statement Action status Projects
PRP-1 Create an inventory of fire management plans completed for preserves in the MSPA, identify preserves without plans. On hold
PRP-2 The guidebook should be developed collaboratively with input from land owners and managers, fire management agencies, scientists, and other stakeholders. Evaluate strengths and weaknesses of existing fire management plans to inform guidebook recommendations. On hold
PRP-3 Submit project metadata, inventory and guidebook to MSP web portal. On hold
Criteria Deadline year
Completed inventory and preserve fire management plan guidebook by 2021 2021
Code Obj. code Statement
ALTFIR-1 MGT-PRP-IGNPL Starting in 2019, prepare a Wildfire Ignition Reduction Plan detailing measures to reduce wildfire threat to Conserved Lands and at-risk resources in the MSPA. The plan should include: a review of wildfire ignitions and methods for reducing risk; analyses and spatially explicit recommendations for decreasing ignitions along roadways; recommended Project Activity Levels (PAL) for land managers to minimize ignitions from power equipment; analyses of ignition "hotspots" and ignition probabilities relative to at-risk resources with specific management actions to reduce risks; and specifications for establishing a "Fire Watch Program" to reduce ignitions and improve early fire suppression.
ALTFIR-1 MGT-PRP-IGNPL In 2017 and 2018, prepare a Wildfire Ignition Reduction Plan detailing measures to reduce wildfire threat to Conserved Lands and at-risk resources in the MSPA. The plan should include: a review of wildfire ignitions and methods for reducing risk; analyses and spatially explicit recommendations for decreasing ignitions along roadways; recommended Project Activity Levels (PAL) for land managers to minimize ignitions from power equipment; analyses of ignition "hotspots" and ignition probabilities relative to at-risk resources with specific management actions to reduce risks; and specifications for establishing a "Fire Watch Program" to reduce ignitions and improve early fire suppression.
ALTFIR-1 MGT-PRP-IGNPL In 2018 and 2019, prepare a Wildfire Ignition Reduction Plan detailing measures to reduce wildfire threat to Conserved Lands and at-risk resources in the MSPA. The plan should include: a review of wildfire ignitions and methods for reducing risk; analyses and spatially explicit recommendations for decreasing ignitions along roadways; recommended Project Activity Levels (PAL) for land managers to minimize ignitions from power equipment; analyses of ignition "hotspots" and ignition probabilities relative to at-risk resources with specific management actions to reduce risks; and specifications for establishing a "Fire Watch Program" to reduce ignitions and improve early fire suppression.
ALTFIR-3 MGT-RSUP-RAAM Beginning in 2017, with the help of a wildfire coordinator, prepare a regional Resource Avoidance Area map (RAA Map) that identifies MSP species/vegetation communities and other at-risk resources to be avoided on Conserved Lands by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The coordinator should work with Preserve owner managers and their responding (local, state and federal) fire agencies to develop the regional RAA Map in a compatible format with fire agencies' Wildland Fire Decision Support Systems.
ALTFIR-3 MGT-RSUP-RAAM Beginning in 2017, with the help of a wildfire coordinator, prepare a regional Resource Avoidance Area map (RAA Map) that identifies MSP species/vegetation communities and other at-risk resources to be avoided on Conserved Lands by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The coordinator should work with Preserve owner managers and their responding (local, state and federal) fire agencies to develop the regional RAA Map in a compatible format with fire agencies' Wildland Fire Decision Support Systems.
regional and/or local PRE 2018, 2019, 2020, 2021 View map

MGT-RSUP-WFRAP ALTFIR-6

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

Beginning in 2018, coordinate and establish a Wildland Fire Resource Advisor Program (WFRAP) for locally owned (non-federal and non-state) Conserved Lands to integrate local Resource Advisors (RAs) with federal and state agencies and provide unified guidance on avoidance/protective measures for MSP and other rare species and communities to Incident Command personnel during fire events.
Action Statement Action status Projects
RSUP-1 Using the federal model as a guide, the regional wildfire coordinator should work with land managers and fire agencies to develop a WFRAP specific to MSP locally-owned lands and train land managers to be RAs. Procedures should be established for local RAs to work with federal and state advisors to communicate a unified message to Incident Command personnel during fire events. Available for implementation
RSUP-2 RAs should be encouraged to participate in fire safety organizations, such as the California Wildland Fire Coordinating Group to foster coordination and learn from the experiences and expertise of fire management personnel. Available for implementation
Criteria Deadline year
Establish WFRAP by 2021 for all locally-owned lands with trained RAs 2021
Code Obj. code Statement
ALTFIR-4 MGT-IMP-RAAM Starting in 2019, coordinate and integrate MSP Resource Avoidance Areas (RAA) Map into local state and federal management agencies GIS Wildland Fire Decision Support Systems.
ALTFIR-5 MGT-PRP-PFMGTPL Beginning in 2019, conduct an inventory of preserve fire management plans and identify elements to include in standardized preserve fire management plans. Prepare a guidebook for preserve fire management plans that, at a minimum, specifies overall pre-fire, fire suppression and post-fire management actions and includes the RAAM that identifies MSP species/habitats and other at-risk resources to be avoided by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The guidebook should identify standard pre-fire, fire suppression, and post-fire actions for specific MSP species and vegetation communities to be incorporated into Preserve Fire Management Plans.
ALTFIR-5 MGT-PRP-PFMGTPL Beginning in 2019, conduct an inventory of preserve fire management plans and identify elements to include in standardized preserve fire management plans. Prepare a guidebook for preserve fire management plans that, at a minimum, specifies overall pre-fire, fire suppression and post-fire management actions and includes the RAAM that identifies MSP species/habitats and other at-risk resources to be avoided by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The guidebook should identify standard pre-fire, fire suppression, and post-fire actions for specific MSP species and vegetation communities to be incorporated into Preserve Fire Management Plans.
ALTFIR-9 MGT-IMP-WFRAP Implement WFRAP for local (non-federal/non-state) lands and work with federal and state RAs to provided unified guidance on avoidance/ protective measures for MSP species and communities to Incident Command personnel during fire events.
local PRE 2019, 2020, 2021 View map

MGT-IMP-FMGTPL ALTFIR-8

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

Beginning in 2019, implement highest priority proactive management actions identified through monitoring (Objective FSP-8) to reduce risk of fire for most at-risk MSP rare plant and animal occurrences.
Action Statement Action status Projects
IMP-1 Implement invasive plant control and to reduce risk of post-fire non-native plant invasion at high priority MSP rare plant and animal occurrences. waiting for precedent action Fairbanks Ranch/Rancho Santa Fe Invasive Removal and Stream Enhancement
IMP-2 Submit project metadata and datasets to MSP Web Portal waiting for precedent action
Criteria Deadline year
Pre-fire management implemented for =2 very high priority MSP species occurrences by 2021 2021
Code Obj. code Statement
ALTFIR-7 MGT-PRP-FMGTPL In 2017 and 2018, identify MSP rare plant and animal species occurrences at high risk of impacts from fire, including MSP species that do not have species-specific fire recommendations to reduce threat risk prior to fire events and during fire suppression activities.
regional and/or local SUPP 2019, 2020, 2021 View map

MGT-IMP-WFRAP ALTFIR-9

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

Implement WFRAP for local (non-federal/non-state) lands and work with federal and state RAs to provided unified guidance on avoidance/ protective measures for MSP species and communities to Incident Command personnel during fire events.
Action Statement Action status Projects
IMP-1 Implement the WFRAP specific to MSP locally-owned preserves with trained RAs integrated into fire incident management teams to provide simple, unified message to IC concerning protection of natural resources. Wildfire coordinator will be available as a resource to assist in communicating regional MSP priorities among land managers. On hold
Criteria Deadline year
WFRAP implemented during fires on locally-owned lands from 2019-2021 2021
Code Obj. code Statement
ALTFIR-4 MGT-IMP-RAAM Starting in 2019, coordinate and integrate MSP Resource Avoidance Areas (RAA) Map into local state and federal management agencies GIS Wildland Fire Decision Support Systems.
ALTFIR-5 MGT-PRP-PFMGTPL Beginning in 2019, conduct an inventory of preserve fire management plans and identify elements to include in standardized preserve fire management plans. Prepare a guidebook for preserve fire management plans that, at a minimum, specifies overall pre-fire, fire suppression and post-fire management actions and includes the RAAM that identifies MSP species/habitats and other at-risk resources to be avoided by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The guidebook should identify standard pre-fire, fire suppression, and post-fire actions for specific MSP species and vegetation communities to be incorporated into Preserve Fire Management Plans.
ALTFIR-5 MGT-PRP-PFMGTPL Beginning in 2019, conduct an inventory of preserve fire management plans and identify elements to include in standardized preserve fire management plans. Prepare a guidebook for preserve fire management plans that, at a minimum, specifies overall pre-fire, fire suppression and post-fire management actions and includes the RAAM that identifies MSP species/habitats and other at-risk resources to be avoided by fire suppression activities, such as equipment staging, dozer line construction, retardant drops,and overland travel. The guidebook should identify standard pre-fire, fire suppression, and post-fire actions for specific MSP species and vegetation communities to be incorporated into Preserve Fire Management Plans.
ALTFIR-6 MGT-RSUP-WFRAP Beginning in 2018, coordinate and establish a Wildland Fire Resource Advisor Program (WFRAP) for locally owned (non-federal and non-state) Conserved Lands to integrate local Resource Advisors (RAs) with federal and state agencies and provide unified guidance on avoidance/protective measures for MSP and other rare species and communities to Incident Command personnel during fire events.
ALTFIR-6 MGT-RSUP-WFRAP Beginning in 2018, coordinate and establish a Wildland Fire Resource Advisor Program (WFRAP) for locally owned (non-federal and non-state) Conserved Lands to integrate local Resource Advisors (RAs) with federal and state agencies and provide unified guidance on avoidance/protective measures for MSP and other rare species and communities to Incident Command personnel during fire events.
regional and/or local POST 2017, 2018, 2019, 2020, 2021 View map

MON-IMP-FMGT ALTFIR-10

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

Monitor recovery of at-risk MSP species and vegetation communities against the threat of invasive plants the first 3 years following a fire event as identified in post-fire plant and wildlife surveys.
Action Statement Action status Projects
IMP-1 Conduct post fire surveys for invasive plants (Levels 1-4) at MSP plant and animal occurrences and vegetation communities starting the first spring following fire and as needed thereafter to identify priority areas for invasive plant control On hold
IMP-2 Submit project metadata, datasets and postfire management recommendations to MSP Web Portal. On hold
Criteria Deadline year
Invasive plant surveys conducted 1-3 year after wildfire with management recommendations submitted 2021
Code Obj. code Statement
ALTFIR-11 MGT-IMP-FMGT Implement invasive plant control at burned priority sites identified during pre- and post-fire surveys to prevent expansion of invasive plants at priority MSP plant and animal occurrences and vegetation communities.
ALTFIR-12 MON-SURV-FMGT Conduct focused surveys for at-risk MSP plant and animal species for 1-3 years following wildfires and determine their distribution and status. Identify unburned (occupied or unoccupied) refugia within and adjacent to the fire perimeter.
regional POST 2017, 2018, 2019, 2020, 2021 View map

MGT-IMP-FMGT ALTFIR-11

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

Implement invasive plant control at burned priority sites identified during pre- and post-fire surveys to prevent expansion of invasive plants at priority MSP plant and animal occurrences and vegetation communities.
Action Statement Action status Projects
IMP-1 Conduct invasive plant control at priority sites with threats from non-native plants for 2-3 years post-fire or until invasive plants are controlled. On hold
Criteria Deadline year
Post-fire invasive plant control prevents expansion of nonnative plants at priority plant and animal occurrences and vegetation communities 2021
Code Obj. code Statement
ALTFIR-10 MON-IMP-FMGT Monitor recovery of at-risk MSP species and vegetation communities against the threat of invasive plants the first 3 years following a fire event as identified in post-fire plant and wildlife surveys.
ALTFIR-12 MON-SURV-FMGT Conduct focused surveys for at-risk MSP plant and animal species for 1-3 years following wildfires and determine their distribution and status. Identify unburned (occupied or unoccupied) refugia within and adjacent to the fire perimeter.
regional and/or local POST 2017, 2018, 2019, 2020, 2021 View map

MON-SURV-FMGT ALTFIR-12

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

Conduct focused surveys for at-risk MSP plant and animal species for 1-3 years following wildfires and determine their distribution and status. Identify unburned (occupied or unoccupied) refugia within and adjacent to the fire perimeter.
Action Statement Action status Projects
SURV-1 Submit project metadata, monitoring data and reports to MSP Web Portal On hold
Criteria Deadline year
Fire impacts and refugia documented for prioritized at-risk MSP plant and animal species following significant fires in 2017-2021 2021
Code Obj. code Statement
ALTFIR-10 MON-IMP-FMGT Monitor recovery of at-risk MSP species and vegetation communities against the threat of invasive plants the first 3 years following a fire event as identified in post-fire plant and wildlife surveys.
ALTFIR-12 MON-SURV-FMGT Conduct focused surveys for at-risk MSP plant and animal species for 1-3 years following wildfires and determine their distribution and status. Identify unburned (occupied or unoccupied) refugia within and adjacent to the fire perimeter.

Altered hydrology

Goal: Reduce the impact of urban runoff and aseasonal flow on the highest priority MSP species and riparian habitat so that species can presist over the long term (>100 years) in areas upstream and downstream of urban land uses.

regional NFO 2017, 2018, 2019, 2020 View map

MON-RES-STIC ALTHYD-1

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

Continue USGS research study using STIC sensors to measure water temperature and presence in chosen stream channels. The final report should include an analysis investigating the relationship between upstream urban land uses and the number of days with water present. The data should be available in a format that will aid the creation of a hydrologic management plan.
Action Statement Action status Projects
RES-1 Monitor STIC sites on a regular basis to capture stream data and necessary covariate data. In progress Urban Aseasonal Flow Study
RES-2 Analyze data and covariates to invesigate the relationship between stream conditions and watershed land use. In progress Urban Aseasonal Flow Study
RES-3 Submit project metadata and report to the MSP Web Portal. waiting for precedent action Urban Aseasonal Flow Study
Criteria Deadline year
Final report of STIC data and analysis 2021
local NFO 2017, 2018, 2019, 2020, 2021 View map

MGT-IMP-BMP ALTHYD-3

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

Beginning in 2017, implement BMPs identified in the literature and approved management plans for altered hydrology to improve conditions for MSP species.
Action Statement Action status Projects
IMP-1 Submit Metadata, data, and management actions to MSP web portal. available for implementation

San Diego ambrosia Ambrosia pumila

Goal: Maintain or enhance existing San Diego ambrosia occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in chaparral vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
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-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 (Table 2-2.1). 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 =3 small occurrences on Conserved Lands (Table 2-2.1) 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 = 20% absolute cover within the occurrence
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 View map

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
Code Obj. code Statement
AMBPUM-1 MON-IMP-IMG Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (Table 2-2.1) using the regional rare plant "IMG" monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
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 =3 small occurrences on Conserved Lands (Table 2-2.1) 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 = 20% absolute cover within the occurrence
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.

Arroyo toad Anaxyrus californicus

Goal: Protect and enhance existing significant occurrences of arroyo toad to self-sustaining levels and re-establish occurrences in locations where they previously existed to ensure persistence over the long-term (>100 years).

local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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 View map

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 2017, 2018, 2019, 2020, 2021 SO View map

MON-RES-GEN ANACAL-3

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

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.
Action Statement Action status Projects
RES-1 Continue to collect genetic samples during surveys for arroyo toad for use in examining the genetic relationship of arroyo toad in western San Diego County. waiting for precedent action
RES-2 Analyze the genetic samples to evaluate the degree of genetic variation within and between populations and to possibly identify genetic bottlenecks or barriers. waiting for precedent action
RES-3 Prepare management recommendations based upon the genetic analyses that maintain or enhance gene flow and genetic diversity and that identifies source populations. waiting for precedent action
RES-4 Submit project metadata, datasets, and Arroyo Toad Genetics Study report to the MSP Web Portal. Unknown
Criteria Deadline year
Genetic samples collected from studies completed through 2021; Genetic Analysis and Report Completed 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).
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 2017, 2018, 2019 SO View map

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 western pond turtle, primarily young) within the known western pond turtle habitat.
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-2 MGT-IMP-IMG Beginning in 2018, conduct routine management actions 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 western pond turtle, primarily young) within the known western pond turtle 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 View map

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 western pond turtle, primarily young) within the known western pond turtle habitat.
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-2 MGT-IMP-IMG Beginning in 2018, conduct routine management actions 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 western pond turtle, primarily young) within the known western pond turtle 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.
ANACAL-5 MGT-PRP-MGTPL In 2017, continue to convene with the working group of land managers, scientists, and local biologists knowledgeable in arroyo toad to review existing conditions of known occurrences on Conserved Lands and to prepare a plan for management of arroyo toad which considers each site
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 View map

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 PRE 2018, 2019 SO View map

MGT-PRP-RESCPL ANACAL-8

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

Beginning in 2018, establish program and permits to allow emergency management actions for the arroyo toad during or immediately following wildfire events, such as implementation of emergency rescue and temporary translocation, to protect from potential loss or extirpation.
Action Statement Action status Projects
PRP-1 Develop protocols, monitoring standards, and permit process for the rescue of Southwestern pond turtles during wildfire events. Available for implementation
Criteria Deadline year
Wildfire rescue program established for Arroyo toad in 2018 2021
regional SUPP 2019, 2020, 2021 SO View map

MGT-IMP-RESCPL ANACAL-9

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

Beginning in 2019, implement arroyo toad rescue program during wildfire events to protect from loss and/or extirpation.
Action Statement Action status Projects
IMP-1 Submit management data and reports to MSP web portal waiting for precedent action
Criteria Deadline year
Wildfire rescue program implemented for Arroyo toad 2021
regional POST 2019, 2020, 2021 SO View map

MON-IMP-RESCPL ANACAL-10

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

Beginning in 2019, monitor the effectiveness of arroyo toad rescue programs following wildfire events, including both translocation or re-introduction efforts.
Action Statement Action status Projects
IMP-1 Submit monitoring data and report to MSP web portal waiting for precedent action
Criteria Deadline year
Monitoring of post fire rescue programs for Arroyo toad implemented 2021
regional POST 2017, 2018, 2019, 2020, 2021 SO View map

MGT-IMP-FMGT ANACAL-11

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

From 2017 to 2021, implement post fire management actions to ensure the recovery of arroyo toad at occupied sites following wildfire events, including invasive plant and animal control, debris/sediment removal, erosion control or other management actions as needed following a fire.
Action Statement Action status Projects
IMP-1 Implement needed management actions as determined through BAER or other post fire surveys. waiting for precedent action
Criteria Deadline year
Post fire management actions implemented following wildfire events 2021
regional POST 2017, 2018, 2019, 2020, 2021 SO View map

MON-IMP-FMGT ANACAL-12

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

From 2017 to 2021, monitor stream conditions and the effectiveness of management actions implemented to assist in recovery of arroyo toad for 3 years following wildfire events.
Action Statement Action status Projects
IMP-1 Monitor stream flows and water quality post fire, document recovery of arroyo toad populations and habitat, and effectiveness of any management actions for first 3 years after fire. waiting for precedent action
Criteria Deadline year
Monitoring of post fire management actions, stream conditions, and population status for arroyo toads implemented for 3 years post fire 2021

Pallid bat Antrozous pallidus

Goal: Protect pallid bat diurnal, nocturnal, and maternity roosts from destruction and human disturbance and enhance foraging habitat within commuting distance of nocturnal and maternity roosts to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and improve chances of persistence over the long-term (>100 years).

local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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
Annual IMG monitoring of Pallid bat completed 2021
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-1 MON-RES-SPEC In 2017, 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 View map

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
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.
ANTPAL-2 MON-IMP-IMG Beginning in 2017, inspect the vicinity of pallid 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 SL View map

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
PRP-2 Develop a management plan for pallid bat that prioritizes management actions for the next five years. waiting for precedent action
PRP-3 Identify areas where pallid bat and Townsend?s big-eared bat management can be complimentary. waiting for precedent action
PRP-4 Submit management plan to MSP web portal waiting for precedent action
Criteria Deadline year
Management Plan for Pallid bat prepared by 2018 2021
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-1 MON-RES-SPEC In 2017, 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 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.
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.
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.

Aphanisma Aphanisma blitoides

Goal: Maintain or enhance existing aphanisma occurrence(s) and establish new occurrences, as needed, to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and improve chances of persistence over the long term (>100 years) in coastal bluff, coastal dune and coastal sage scrub vegetation communities.

regional and/or local NFO 2017, 2019, 2021 SL View map

MON-IMP-IMG APHBLI-1

Management units: 1, 7

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.
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
Code Obj. code Statement
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-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-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
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 =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 = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL View map

MGT-IMP-IMG APHBLI-2

Management units: 1, 7

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.
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 less than or equal 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
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-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-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 =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 = 20% absolute cover within the occurrence
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 2019 SL View map

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
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-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
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 =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 = 20% absolute cover within the occurrence

Golden eagle Aquila chrysaetos canadensis

Goal: Expand and then maintain a self-sustaining golden eagle population to ensure long term persistence (>100 years) on Conserved Lands in the MSPA by: improving reproductive success through protection of active and inactive nest sites from human disturbance; reducing anthropogenic mortality; managing large mosaics of grassland and open shrublands for optimal prey availability, especially during drought; and by minimizing human impacts to foraging eagles.

regional NFO 2017, 2018, 2019 SO View map

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
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
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
RES-6 Submit project metadata, datasets, and report with management recommendations to the MSP Web Portal. in progress
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-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 Table of Occurrences) 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 Table of Occurrences). 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-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.
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 Table of Occurrences). 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 View map

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
RES-2 Submit project metadata, datasets, and Golden Eagle Genetics Study report to the MSP Web Portal. in progress
Criteria Deadline year
Golden Eagle Genetic Study with Report Completed by 2020 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-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 Table of Occurrences) 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-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 Table of Occurrences). 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.
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 Table of Occurrences). 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.

Western burrowing owl Athene cunicularia hypugaea

Goal: Increase the abundance of nesting burrowing owls to ensure that there are multiple (=2) interbreeding self-sustaining nodes (primarily utilizing natural burrow systems) on Conserved Lands that will provide for burrowing owl persistence in the MSPA over the long-term (>100 years).

regional NFO 2017, 2018, 2019, 2020, 2021 SL View map

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 NFO 2017, 2018, 2019, 2020, 2021 SL View map

MON-RES-GEN ATHCUN-2

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

As part of the burrowing owl research study, collect genetic samples to determine origin of owls and genetic population structure compared to other populations in California, Mexico, and the western U.S.
Action Statement Action status Projects
RES-1 Continue to collect genetic samples during surveys for burrowing owl for use in examining the genetic relationship of burrowing owl in California, Mexico, and the western U.S. waiting for precedent action
RES-2 Analyze the genetic samples to evaluate the degree of genetic variation within and between populations and to possibly identify genetic bottlenecks or barriers. waiting for precedent action
RES-3 Prepare management recommendations based upon the genetic analysis that maintain or enhance gene flow and genetic diversity and that identifies source populations. waiting for precedent action
RES-4 Submit project metadata, datasets, and Burrowing Owl Genetics Study report to the MSP Web Portal. Unknown
Criteria Deadline year
Genetic samples collected from studies completed through 2021; Genetic Analysis and Report Completed by 2021. 2021
regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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 View map

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 and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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 View map

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

Encinitas baccharis Baccharis vanessae

Goal: Maintain or enhance existing Encinitas baccharis occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in chaparral vegetation communities.

regional and/or local NFO 2017, 2019, 2021 SO View map

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
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-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.
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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
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-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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
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 View map

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
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 and/or Local NFO 2019, 2020, 2021 SO View map

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
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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
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 View map

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
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 =3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
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 POST 2018, 2019, 2020, 2021 SO View map

MON-RES-SPEC BACVAN-9

Management units: 4, 5, 8

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.
Action Statement Action status Projects
RES-1 Submit project metadata, datasets, analyses, and report to the MSP Web Portal. On hold
Criteria Deadline year
Encinitas Baccharis Fire Study Completed and Report Submitted by 5 Years Post Fire 2021

San Diego goldenstar Bloomeria clevelandii

Goal: Maintain or enhance existing San Diego goldenstar occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and improve chances of persistence over the long term (>100 years) in chaparral, coastal sage scrub, grassland, and vernal pool/alkali playa vegetation communities.

local NFO 2017, 2018, 2019, 2020, 2021 SS View map

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
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.
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.

San Diego fairy shrimp Branchinecta sandiegonensis

Goal: Protect, enhance, and restore San Diego fairy shrimp occupied and historically occupied habitat to create resilient, self-sustaining populations that provide for persistence over the long-term (>100 years).

local NFO 2018, 2019, 2020, 2021 SL View map

MON-IMP-MONPL BRASAN-1

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

Beginning in 2018, conduct annual qualitative surveys during the wet season to determine the presence of San Diego fairy shrimp in vernal pools on Conserved Lands. Every 3 years conduct dry season quantitative cyst soil sampling at a rotating panel of vernal pools to determine the density of San Diego fairy shrimp cysts, as identified by genetic analysis. Use methods and protocols specified in the City of San Diego Vernal Pool Management and Monitoring Plan (VPMMP; 2015) . Determine whether the pools fall into Level 1 (stable), Level 2 (enhancement) or Level 3 (restoration) management categories based on the presence of shrimp among pools in each complex and track increases or declines in cyst densities over 3 monitoring years to determine if movement is triggered between management categories as identified in the VPMMP. If there is sufficient decline in San Diego fairy shrimp cyst density to trigger an increase in management levels as identified in the VPMMP, then more intensive monitoring is required to determine topographic or hydrologic disturbances as described in the VPMMP.
Action Statement Action status Projects
IMP-1 Submit project metadata, datasets, and monitoring reports with management and Monitoring recommendations to the MSP Web Portal. Available for implementation
Criteria Deadline year
Annual Qualitative Surveys Conducted for San Diego Fairy Shrimp and Quantitative Cyst Sampling Every 3 Years with Reports Completed 2021

Thread-leaved brodiaea Brodiaea filifolia

Goal: Maintain or enhance existing Thread-leaved brodiaea occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in grassland and vernal pool vegetation communities.

regional and/or local NFO 2017, 2019, 2021 SS View map

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
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-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the "IMG" monitoring at thread-leaved brodiaea occurrences on Conserved Lands. 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-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the IMG monitoring at thread-leaved brodiaea occurrences on Conserved Lands. 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.
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 =4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SS View map

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
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-1 MON-IMP-IMG Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (Table 2.xxx) 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-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.
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 =4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence
Regional NFO 2019 SS View map

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.
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 =4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to = 20% absolute cover within the occurrence

Orcutt's brodiaea Brodiaea orcuttii

Goal: Maintain or enhance existing Orcutt's brodiaea occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in chaparral, grassland, oak woodland, southern interior cypress forests, and vernal pool vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
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-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 =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 = 20% absolute cover within the occurrence
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 View map

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
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
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-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 =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 = 20% absolute cover within the occurrence
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 View map

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
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-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.
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 =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 = 20% absolute cover within the occurrence
regional and/or local NFO 2017, 2018, 2019 SO View map

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.

Santa Rosa basalt brodiaea Brodiaea santarosae

Goal: Maintain existing Santa Rosa brodiaea occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and improve chances of persistence over the long term (>100 years) in grassland and vernal pool/alkali playa habitats.

local NFO 2019, 2020, 2021 SS View map

MGT-IMP-IMG BROSAN-2

Management units: 8

Beginning in 2019, conduct routine management actions as identified through the IMG monitoring in 2018 at Santa Rosa 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 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. 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
Code Obj. code Statement
BROSAN-1 MON-IMP-IMG In 2018, inspect extant Santa Rosa brodiaea 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.
BROSAN-1 MON-IMP-IMG In 2018, inspect extant Santa Rosa brodiaea 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. .

Coastal cactus wren Campylorhynchus brunneicapillus sandiegensis

Goal: Protect, enhance, and restore suitable cactus scrub habitat for coastal cactus wrens to increase effective population size in each genetic cluster at a short term sustainable level (e.g. 50-100 wrens), rehabilitate habitat destroyed by wildfire, improve habitat quality to maintain populations during drought, enhance connectivity within and between genetic clusters to increase genetic diversity and rescue small populations, and manage anthropogenic predation risk to ensure the long term persistence (>100 years) of cactus wrens on Conserved Lands in the MSPA.

regional and/or local POST 2017, 2018, 2019, 2020, 2021 SO View map

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
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 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 Table of Occurrences) 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-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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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 Table of Occurrences). 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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 View map

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-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 Table of Occurrences); 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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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-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 Table of Occurrences). 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 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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 View map

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-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 Table of Occurrences); 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-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 Table of Occurrences) 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 Table of Occurrences). 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-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 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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, 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 Table of Occurrences) 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-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 View map

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-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 Table of Occurrences); 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 Table of Occurrences) 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-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-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 Table of Occurrences). 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 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-7 MGT-IMP-IEX In 2017, 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 Table of Occurrences) 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-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 Table of Occurrences). 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 NFO 2017, 2018, 2019 SO View map

MON-RES-GEN CAMBRU-5

Management units: 2, 3, 4, 6

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.
Action Statement Action status Projects
RES-1 Collaborate with the Natural Community Coalition to repeat the 2012 Southern California Coastal Cactus Wren Genetics Study (Barr et al. 2013, 2015) for the Coastal Orange County-Camp Pendleton, San Diego/El Cajon, Otay, and San Pasqual genetic clusters. Evaluate whether the clusters with low effective population sizes and potential inbreeding have changed their levels of genetic diversity in the intervening 6 years with management to increase cactus scrub and improve connectivity, from translocating wrens between genetic clusters, or from population declines during a long and intense drought. in progress
RES-2 Analyze genetic and reproduction data from Orange County and San Diego County studies to determine if reproduction may be adversely affected by inbreeding or low genetic diversity. If lack of genetic diversity and inbreeding show signs of depressing productivity, then evaluate and prioritize specific management recommendations to increase gene flow, such as switching eggs or translocating individuals between genetic clusters over the short term and restoring habitat to expand populations and improve connectivity within and between genetic clusters over the long term. in progress
RES-3 Submit project metadata, datasets, analyses, and report with specific management recommendations to the MSP Web Portal. in progress
Criteria Deadline year
Genetic Study Completed and Report Submitted 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-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 Table of Occurrences); 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-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 Table of Occurrences) 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-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 Table of Occurrences). 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 Table of Occurrences). 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-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-7 MGT-IMP-IEX In 2017, 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 Table of Occurrences) 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 PRE 2017, 2018, 2019, 2020, 2021 SO View map

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 Otay River Valley Cactus Wren Habitat Restoration and Enhancement , 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 Otay River Valley Cactus Wren Habitat Restoration and Enhancement , 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
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-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 Table of Occurrences); 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-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 Table of Occurrences). 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-7 MGT-IMP-IEX In 2017, 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 Table of Occurrences) 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 View map

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
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
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
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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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 Table of Occurrences). 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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 Table of Occurrences). 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 View map

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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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 Table of Occurrences). 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-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 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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-7 MGT-IMP-IEX In 2017, 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 Table of Occurrences) 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 PRE 2017, 2018, 2019, 2020, 2021 SO View map

MGT-IMP-FMGT CAMBRU-9

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

Implement prefire management to reduce potential severity and impacts from future fire at prioritized cactus wren occurrences and habitats most at risk from wildfire.
Action Statement Action status Projects
IMP-1 Implement management actions to reduce severity of potential fires through opening up dense cactus scrub habitats by trimming and thinning shrubs to maintain open scrub, maintaining bare ground buffers around large intact cactus patches, and by reducing nonnative grasses and herbs that can carry wildfire into cactus patches. Design management actions to avoid significant impacts to CSS vegetation or to other MSP species. Available for implementation
IMP-2 As opportunities arise, implement management actions to reduce potential fire impacts in conjunction with other ongoing enhancement and restoration projects for cactus wrens. Available for implementation
IMP-3 Submit project metadata and management actions to the MSP Web Portal. Available for implementation
Criteria Deadline year
By 2021, Implement =1 Management Action to Reduce Impacts from Future Fire at Prioritized Wren Occurrences 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-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 Table of Occurrences); 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-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 Table of Occurrences) 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-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 Table of Occurrences). 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 Table of Occurrences). 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-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.
regional and/or local POST 2017, 2018, 2019, 2020, 2021 SO View map

MON-IMP-FMGT CAMBRU-10

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

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.
Action Statement Action status Projects
IMP-1 Prepare postfire habitat monitoring protocols and sampling design to determine the status of coastal cactus wrens and characterize cactus scrub recovery following wildfire. Use the monitoring results to identify management actions to ensure postfire recovery of high quality cactus scrub at occupied cactus wren sites and at unoccupied cactus scrub sites important for wren population expansion and connectivity within and between genetic clusters. On hold
IMP-2 Submit project metadata, cactus wren postfire survey and habitat monitoring data, annual reports with management recommendations, and a final report documenting project methods and results to the MSP Web Portal. On hold
Criteria Deadline year
At Least 3 Years of Postfire Monitoring of Cactus Wrens and Habitats with Annual Management Recommendations 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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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-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 Table of Occurrences). 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 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-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-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 Table of Occurrences). 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.
regional and/or local POST 2017, 2018, 2019, 2020, 2021 SO View map

MGT-IMP-FMGT CAMBRU-11

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

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.
Action Statement Action status Projects
IMP-1 Implement management actions to restore cactus scrub habitat destroyed by wildfire. These management actions may include planting large >1m cactus to create nesting and roosting habitat for immediate postfire use by cactus wrens, planting pads and segments to improve habitat over the longer term, and to seed or plant native shrubs and forbs as needed to enhance habitat suitability and increase available arthropod food resources (use recommendations from the Coastal Cactus Wren Demography, Vegetation and Arthropod Study). Control invasive nonnative plants to =20% absolute cover to reduce postfire invasion of nonnative plants and to allow postfire recovery of native plants by reducing competition for water and light. Control erosion and human use impacts while habitat is recoverying. On hold
IMP-2 Submit project metadata and management actions to the MSP Web Portal. On hold
Criteria Deadline year
At Least 3 Years of Postfire Management in Priority Cactus Wren Habitats 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 Table of Occurrences). In 2018 and 2021, expand surveys to include the San Pasqual Valley/Lake Hodges genetic cluster.
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 Table of Occurrences). 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-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 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 and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 and San Diego/El Cajon 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-5 MON-RES-GEN From 2017-2019, in conjunction 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 Cacus Wren Genetics Study (Barr et al. 2013, 2015). Determine if genetic diversity and effective population size have changed in the Otay and San Diego/El Cajon genetic clusters (see Table of Occurrences) 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-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-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-7 MGT-IMP-IEX In 2017, 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 Table of Occurrences) 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-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.

Western snowy plover Charadrius nivosus nivosus

Goal: Protect, enhance, and restore occupied and historically occupied habitat to create resilient, self-sustaining populations that provide for persistence over the long term (>100 years). ​

regional NFO 2018, 2019 SL View map

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 View map

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

chaparral

Goal: Maintain, enhance and restore chaparral on Conserved Lands in the MSPA that supports or has the potential to support VF species (i.e., Del Mar manzanita, felt-leaved monardella, Lakeside ceanothus, Nuttall's scrub oak, Otay manzanita, Rainbow manzanita, wart-stemmed ceanothus, California newt, Bell's sage sparrow) and to incidentally benefit a diverse array of other species (e.g., Encinitas baccharis, Jennifer's monardella, Orcutt's hazardia, mountain lion) so that the vegetation community has high ecological integrity, and these species are resilient to environmental stochasticity, catastrophic disturbances and threats, such as very large wildfires and prolonged droughts, and will be likely to persist over the long term (>100 years).

Regional NFO 2017, 2018, 2019 View map

MON-PRP-MONPL CHAPAR-1

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

In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
Action Statement Action status Projects
PRP-1 Establish a vegetation monitoring working group of scientists, wildlife agencies, land managers, and other stakeholders to participate in developing the vegetation monitoring plan. The group should also include interested parties from outside the MSPA, such as representatives from other multiple species plans in Orange and Riverside Counties and from San Diego County military bases, to create a regional monitoring program with greater efficiencies in effort and a broader inference across southern California. In progress
PRP-2 Submit project metadata, datasets, analyses, and Chaparral, Grassland and Coastal Sage Scrub Vegetation Monitoring Plan to the MSP web portal In progress
Criteria Deadline year
Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan completed by 2019 2021
Code Obj. code Statement
CHAPAR-2 MON-DEV-MAP In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.
CHAPAR-3 MON-IMP-MONPL In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the vegetation monitoring plan. In 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
Regional NFO 2017, 2018, 2019, 2020, 2021 View map

MON-DEV-MAP CHAPAR-2

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

In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.
Action Statement Action status Projects
DEV-1 Submit project metadata, datasets, analyses, and Ecological Integrity Classification Map to the MSP web portal In progress 2017-2019 Developing a Map of Ecological Integrity Using Remote Sensing
Criteria Deadline year
Ecological Integrity Map created in 2017 and updated as needed 2018-2021 2021
Code Obj. code Statement
CHAPAR-1 MON-PRP-MONPL In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
CHAPAR-3 MON-IMP-MONPL In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the vegetation monitoring plan. In 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
POLPOL-1 MON-IMP-MONPL In 2021, 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.
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.
POLPOL-1 MON-IMP-MONPL In 2021, 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 =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.
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.
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.
POLPOL-2 MON-RES-SPEC In 2021, 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 NFO 2018, 2019, 2020, 2021 View map

MON-IMP-MONPL CHAPAR-3

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

In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the vegetation monitoring plan. In 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
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
Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan implemented 2018-2021 2021
Code Obj. code Statement
CHAPAR-1 MON-PRP-MONPL In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
CHAPAR-2 MON-DEV-MAP In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.

Salt marsh bird's-beak Chloropyron maritimum ssp. maritimum

Goal: Maintain or enhance existing salt marsh bird's-beak occurrences and create salt marsh to establish new occurrences to reduce risk of population loss to rising sea levels and to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in salt marsh vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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 =3 small occurrences, and establish =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-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-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 View map

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
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-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 and/or Local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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 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-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 =3 small occurrences, and establish =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-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 View map

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-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-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 View map

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-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-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 =3 small occurrences, and establish =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 View map

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-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 =3 small occurrences, and establish =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-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.

Orcutt's spineflower Chorizanthe orcuttiana

Goal: Maintain or enhance existing Orcutt's spineflower occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in chaparral vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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 (Table 2-1.17). 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-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt
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 =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 = 20% absolute cover within the occurrence
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 View map

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
IMP-2 Submit project metadata and management data to the MSP Web Portal. in progress
Criteria Deadline year
Routine Management Completed as Needed Based Upon Monitoring Recommendations 2021
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG In 2017, conduct annual surveys of all Orcutt
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 =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 = 20% absolute cover within the occurrence
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 View map

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
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
CHOORC-1 MON-IMP-IMG In 2017, conduct annual surveys of all Orcutt
CHOORC-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.
CHOORC-4 MGT-IMP-IEX In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt
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-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 =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 = 20% absolute cover within the occurrence
regional NFO 2019 SL View map

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
Code Obj. code Statement
CHOORC-1 MON-IMP-IMG Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
CHOORC-1 MON-IMP-IMG In 2017, conduct annual surveys of all Orcutt
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 (Table 2-1.17). 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-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
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-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 =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 = 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.

Northern harrier Circus cyaneus

Goal: Protect, enhance, and restore northern harrier occupied and historically occupied habitat to create resilient, self-sustaining populations that provide for persistence over the long-term (>100 years).

regional NFO 2019 SO View map

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
local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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
local NFO 2017, 2018, 2019, 2020, 2021 SO View map

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

San Miguel savory Clinopodium chandleri

Goal: Maintain or enhance existing San Miguel savory occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and improve chances of persistence over the long term (>100 years) in chaparral, coastal sage scrub and oak woodland vegetation communities.

local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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 =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 = 20% absolute cover within the occurrence
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 View map

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-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.
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 =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 = 20% absolute cover within the occurrence
regional NFO 2019, 2020 SL View map

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-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-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.

Climate change

Goal: The climate change management goal for the MSPA is to maintain and enhance the long-term ecological integrity, resilience and viability of ecosystems, MSP species, and vegetation communities on Conserved Lands and to facilitate range shifts in species and vegetation communities as necessary for long term persistence in the region.

regional NFO 2017, 2018, 2019, 2020, 2021 View map

MON-DEV-MODL CLICHN-1

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

In 2017, begin developing habitat suitability models for plant and animals species and vegetation communities under current and future climate change scenarios. Extend the modeling to consider the influence of other types of threats, such as changing fire regimes, land use and invasive species. Evaluate potential future conditions across the MSPA to identify where species and vegetation communities may be expected to persist, where they may shift in response to changing environmental conditions, and where threats may be greatest. Identify climate refugia and areas where climate change impacts may be the greatest. Obtain sea level modeling models and maps to incorporate into coastal climate change evaluations. The results of these modeling efforts will be considered in developing species and vegetation monitoring and management plans.
Action Statement Action status Projects
DEV-1 Submit project metadata, modeling data, model predictions and reports to MSP Web Portal In progress
Criteria Deadline year
Complete climate change models for =10 MSP species by 2021 2021
regional and/or local NFO 2018, 2019 View map

MON-IMP-WSTA CLICHN-2

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

Beginning in 2018, design and start assembling a network of automated remote sensing weather stations and soil moisture/temperature sensors on Conserved Lands across the MSPA. Prioritize establishing weather and soil monitoring stations at permanent long-term vegetation monitoring plots.
Action Statement Action status Projects
IMP-1 Establish a working group of land owners, land managers, wildlife agencies, scientists and other stakeholders to design and integate existing and planned weather stations into a monitoring network across the MSPA. On hold
IMP-2 Submit project metadata and remotes sensing weather station and soil probe data to the MSP web portal. On hold
Criteria Deadline year
Weather and Soil Station Network designed and =5 new stations established 2021

coastal sage scrub

Goal: Maintain, enhance and restore coastal sage scrub on Conserved Lands in the MSPA that supports or has the potential to support VF species (i.e., cliff spurge, Palmer's goldenbush, San Diego barrel cactus, snake cholla, Blaineville's horned lizard, California gnatcatcher, San Diego black-tailed jackrabbit) and to incidentally benefit a diverse array of other species (e.g., San Diego thornmint, Hermes copper, Quino checkerspot, coastal cactus wren) so that the vegetation community has high ecological integrity, and these species are resilient to environmental stochasticity, catastrophic disturbances and threats, such as very large wildfires, invasive plants and prolonged drought, and will be likely to persist over the long term (>100 years).

Regional NFO 2017, 2018, 2019 View map

MON-PRP-MONPL COSASC-1

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

In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
Action Statement Action status Projects
PRP-1 Establish a vegetation monitoring working group of scientists, wildlife agencies, land managers, and other stakeholders to participate in developing the vegetation monitoring plan. The group should also include interested parties from outside the MSPA, such as representatives from other multiple species plans in Orange and Riverside Counties and from San Diego County military bases, to create a regional monitoring program with greater efficiencies in effort and a broader inference across southern California. In progress
PRP-2 Submit project metadata, datasets, analyses, and Chaparral, Coastal Sage Scrub, and Grassland Vegetation Monitoring Plan to the MSP web portal In progress
Criteria Deadline year
Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan completed by 2019 2021
Code Obj. code Statement
COSASC-2 MON-DEV-MAP In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.
COSASC-3 MON-IMP-MONPL In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the monitoring plan. From 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
Regional NFO 2017, 2018, 2019, 2020, 2021 View map

MON-DEV-MAP COSASC-2

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

In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.
Action Statement Action status Projects
DEV-1 Submit project metadata, datasets, analyses, and Ecological Integrity Classification Map to the MSP web portal In progress 2017-2019 Developing a Map of Ecological Integrity Using Remote Sensing
Criteria Deadline year
Ecological Integrity Map created in 2017 and updated as needed 2018-2021 2021
Code Obj. code Statement
COSASC-1 MON-PRP-MONPL In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
COSASC-3 MON-IMP-MONPL In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the monitoring plan. From 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
POLPOL-1 MON-IMP-MONPL In 2021, 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.
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.
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.
POLPOL-1 MON-IMP-MONPL In 2021, 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 =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.
POLPOL-2 MON-RES-SPEC In 2021, 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.
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 NFO 2018, 2019, 2020, 2021 View map

MON-IMP-MONPL COSASC-3

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

In 2018, conduct pilot monitoring to collect data and develop any recommendations for finalizing the monitoring plan. From 2019 to 2021, implement the final Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan.
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
Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan implemented 2018-2021 2021
Code Obj. code Statement
COSASC-1 MON-PRP-MONPL In 2017, prepare a long-term monitoring plan for the mosaic of chaparral, coastal sage scrub and grassland vegetation communities that focuses on tracking community composition, structure and ecological integrity over time in relation to climate (i.e., drought) and disturbance from fire. 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 landscape-scale ecological integrity classification map to develop a sampling frame and the sampling design with permanent sampling plots spanning north to south and east to west environmental gradients across the MSPA. Evaluate how the vegetation integrity classes characterize other aspects of the ecosystem 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, invasive plants). A draft monitoring plan should be prepared in 2017, tested in the field with a pilot study in 2018, and finalized by 2019.
COSASC-2 MON-DEV-MAP In 2017, develop a landscape-scale map classifying ecological integrity of shrublands across the MSPA based upon shrub cover and density and invasive nonnative annual grasses using remote imagery (e.g., satellite and high resolution aerial imagery, LIDAR) and vegetation data collected during 2015-2016 California gnatcatcher regional and postfire monitoring. Verify and revise the mapping as needed using field data collected in 2018-2020 as part of the Chaparral, Coastal Sage Scrub and Grassland Monitoring Program and from related VF species monitoring (e.g., California gnatcatcher regional and postfire monitoring). Revise the integrity classification map as needed to respond to changes in vegetation based upon wildfires, drought or other large-scale disturbances.
regional NFO 2019, 2020 View map

MGT-PRP-BMPPL COSASC-4

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

Beginning in 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at 200 acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.
Action Statement Action status Projects
PRP-1 Work with land managers, wildlife agencies, and scientists to determine: methods of landscape-scale invasive plant control to test in coastal sage scrub and grassland ecosystems; locations for testing methods; monitoring targets including MSP species, native plant and animal taxa, and ecological processes; and review of results and development of long-term management and monitoring methods. See COSASC-5 actions for additional information to include in the plan. on hold
Criteria Deadline year
Plan to Test Landscape-scale Invasive Plant Control of Coastal Sage Scrub and Grassland Ecosystems Completed in 2020 2021
Code Obj. code Statement
COSASC-5 MGT-DEV-BMPPL In 2020-2021, begin implementing and testing the plan for landscape-scale invasive plant control of coastal sage scrub and grassland ecosystems at 3 or more selected sites with extensive (at least 200 acres) coastal sage scrub and grasslands with large nonnative grass component, using livestock that are most suitable and feasible to manage for the grazing study, effective at controlling invasive nonnative annual grasses, and that are least likely to impact native plant and animal species. Test management methods for enhancing coastal sage scrub to reduce invasive plants and to increase native forb, grass and shrub cover and bare ground. Test management techniques for nonnnative grassland to improve habitat for MSP species such as Quino checkerspot, burrowing owl, golden eagle, grasshopper sparrow, black-tailed jackrabbit and American badger. Incorporate layered treatments of different control methods in the experimental design.
COSASC-5 MGT-DEV-BMPPL In 2020-2021, begin implementing and testing the plan for landscape-scale invasive plant control of coastal sage scrub and grassland ecosystems at 3 or more selected sites with extensive (=200 acres) coastal sage scrub and grasslands with large nonnative grass component, using livestock that are most suitable and feasible to manage for the grazing study, effective at controlling invasive nonnative annual grasses, and that are least likely to impact native plant and animal species. Test management methods for enhancing coastal sage scrub to reduce invasive plants and to increase native forb, grass and shrub cover and bare ground. Test management techniques for nonnnative grassland to improve habitat for MSP species such as Quino checkerspot, burrowing owl, golden eagle, grasshopper sparrow, black-tailed jackrabbit and American badger. Incorporate layered treatments of different control methods in the experimental design
GRASSL-4 MGT-PRP-BMPPL Beginning on 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at Work on < 200 acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.
GRASSL-4 MGT-PRP-BMPPL Beginning on 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at less than 200 acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.
GRASSL-4 MGT-PRP-BMPPL Beginning on 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at =200 acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.
GRASSL-4 MGT-PRP-BMPPL Beginning on 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at Work on (< 200) acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.
GRASSL-4 MGT-PRP-BMPPL Beginning on 2019, prepare a plan to test the use of grazing, prescribed fire and other methods of landscape-scale control of invasive grasses and forbs in grassland and coastal sage scrub vegetation communities as BMPs to promote MSP species, native plants and animals, and natural ecosystem processes. The plan should determine the effects of different techniques on natural resources at less than 200 acre treatment areas at 3 different sites in the MSPA. Development of the study plan's experimental approach should include a review of the literature on the effects of grazing, prescribed fire, and other methods of invasive plant control on coastal sage scrub and grassland ecosystems to develop a conceptual model for management and monitoring. The plan should detail how to test different plant control methods over at least 3 years and should include the specific monitoring questions, objectives, and monitoring targets, a statistically valid experimental design with monitoring methods, sampling locations, and standardized protocols. The plan should include annual monitoring to determine the benefits and impacts of each method on natural resources and to track financial costs, logistics and sustainability of invasive plant control.

Otay tarplant Deinandra conjugens

Goal: Maintain or enhance existing Otay tarplant occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in native and non native grassland vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SS View map

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
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-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions identified through the annual "IMG" monitoring at Otay tarplant occurrences on Conserved Lands (Table 2-3.3) . 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-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 (Table 2.3-3). 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-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 = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SS View map

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
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-1 MON-IMP-IMG In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (Table 2-3.3) 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 ?20% relative cover and thatch to <5 cm tall and native plants = 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
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-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 (Table 2.3-3). 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 = 20% absolute cover within the occurrence
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 View map

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 ?20% relative cover and thatch to <5 cm tall and native plants = 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
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 = 20% absolute cover within the occurrence
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 and/or Local NFO 2019, 2020, 2021 SS View map

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 = 20% absolute cover within the occurrence
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 View map

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 = 20% absolute cover within the occurrence
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 and/or Local NFO 2014, 2015, 2016, 2017, 2018, 2019, 2020, 2021 SS View map

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.

Orcutt's birds-beak Dicranostegia orcuttiana

Goal: Maintain or enhance existing Orcutt's bird's-beak occurrences and establish new occurrences, as needed, to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in coastal sage scrub vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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
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 =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 = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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
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 =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 = 20% absolute cover within the occurrence
Regional NFO 2019 SL View map

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
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 =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 = 20% absolute cover within the occurrence
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 SL View map

MGT-IMP-IEX DICORC-5

Management units: 3

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.
Action Statement Action status Projects
IMP-1 Conduct invasive plant control and distribute seed to enhance Orcutt's bird's-beak occurrence. 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 and management data to the MSP Web Portal. in progress
Criteria Deadline year
By 2019, Orcutt's Bird's-beak Occurrence Enhanced and Report Submitted 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-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 =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 = 20% absolute cover within the occurrence
Regional and/or Local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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'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-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 20% absolute cover within the occurrence
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
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 20% absolute cover within the occurrence
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 = 20% absolute cover within the occurrence
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-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 =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 = 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.

Stephens' kangaroo rat Dipodomys stephensi

Goal: Protect, enhance, and restore Stephens’ kangaroo rat occupied habitat and historically occupied habitat and the landscape connections between them to create resilient, self-sustaining populations that provide for persistence over the long-term (>100 years).

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SO View map

MON-IMP-IMG DIPSTE-1

Management units: 5, 9

Inspect extant Stephens’ kangaroo rat occurrences on Conserved Lands (see occurrence table) using the regional 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. 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 in 2018 with Management Recommendations 2018
Code Obj. code Statement
DUDVIS-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the "IMG" monitoring conducted in 2016 and 2021 at sticky dudleya 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.
DUDVIS-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016 and 2021 at sticky dudleya 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.
DUDVIS-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016 and 2021 at sticky dudleya 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.
DUDVIS-2 MGT-IMP-IMG Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016 and 2021 at sticky dudleya 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 SO View map

MGT-IMP-IMG DIPSTE-2

Management units: 5, 9

Conduct routine management actions as identified through the IMG monitoring at Stephens' kangaroo rat 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.
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
Code Obj. code Statement
DIPSTE-1 MON-IMP-IMG Inspect extant Stephens’ kangaroo rat occurrences on Conserved Lands (see Table of Occurrences) using the regional "IMG" monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
DIPSTE-1 MON-IMP-IMG Inspect extant Stephens’ kangaroo rat occurrences on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.

Blochman's dudleya Dudleya blochmaniae

Goal: Maintain or enhance existing Blochman's dudleya occurrences and re-establish historic occurrences, as needed, to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in coastal sage scrub vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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 (Table 2-1XX). 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-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 ≤ 20% absolute cover within the occurrence
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
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 = 20% absolute cover within the occurrence
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 = 20% absolute cover within the occurrence
local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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 (Table 2-1XX) 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 (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 ≤ 20% absolute cover within the occurrence
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
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 = 20% absolute cover within the occurrence
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 = 20% absolute cover within the occurrence
Regional NFO 2019 SL View map

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
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
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 = 20% absolute cover within the occurrence
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 = 20% absolute cover within the occurrence
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 ≤ 20% absolute cover within the occurrence

Short-leaved dudleya Dudleya brevifolia

Goal: Maintain or enhance existing Short-leaved dudleya occurrences to ensure multiple conserved occurrences with self sustaining populations to increase resilience to environmental and demographic stochasticity, maintain genetic diversity, and ensure persistence over the long term (>100 years) in chaparral vegetation communities.

regional and/or local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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
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-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-2 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-3 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.
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.
DUDBRE-4 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 (Table 2-1.13). 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.
local NFO 2017, 2018, 2019, 2020, 2021 SL View map

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