Evidence of bike use off trail
Photo Credit: Emily Perkins, SDMMP
Goal: The goal for managing human use of preserves is to understand and reduce the impacts of human uses on Conserved Lands where human use is reducing the population levels and/or viability of MSP species populations.
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2017-2021, continue supporting the ongoing research on recreation and wildlife led by Colorado State University and the Wildlife Conservation Society.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Submit project metadata, data, and report to MSP web portal. | In progress |
| Criteria | Deadline year |
|---|---|
| Research data submitted to MSP web portal within one year of project completion. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2017-2021, support jurisdictions to develop and implement local enforcement programs for the protection of natural resources on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RSUP-1 | Provide funding support to jurisdictions to develop and implement local enforcement programs that are suited for Conserved Lands they are responsible for managing. | In progress | |
| RSUP-2 | Submit project metadata, data, and report to MSP web portal. | In progress |
| Criteria | Deadline year |
|---|---|
| =1 Local Enforcement Programs Implemented starting in 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, implement biosecurity measures from existing BMPs (e.g. bleaching equipment between stream surveys, brushing invasive seeds off field boots, etc) during biological surveys and land management activities (e.g. disking, creating fuel breaks) to prevent the unintentional spread of invasive species (i.e. exotic plants and animals) and diseases (e.g. chytrid fungus).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Identify the different types of activities (e.g. biological surveys, disking, fuel breaks, etc) on each preserve that may result in the unintentional introduction of invasive species (i.e. exotic plants and animals) and/or disease (e.g. chytrid fungus) and that can be reasonably controlled using existing BMPs (e.g. bleaching equipment between stream surveys, brushing invasive seeds off field boots, etc). | ||
| IMP-2 | Research and begin implementing available biosecurity BMPs as approproate. |
| Criteria | Deadline year |
|---|---|
| =1 Biosecurity BMP Implemented in the MSPA by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, limit or restrict passive recreation uses within Important Management Areas and/or significant occurrences of MSP species during the breeding season for animals and peak growing season for plants and minimize adverse effects from vegetation trampling, erosion, and trash.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Identify where passive recreation uses may impact Important Management Areas and/or significant occurrences of MSP species on preserves. If possible, implement restrictions on use of these areas during the breeding season and peak growing season for plants. | Furby-North Preserve Unauthorized Control Project, Proctor Valley Off Highway Vehicle (OHV) Barrier, Otay River Valley Cactus Wren Habitat Restoration and Enhancement , Spring Canyon/Goat Mesa Vernal Pool Restoration | |
| IMP-2 | Implement litter control measures, such as closed garbage cans and recycling bins, at preserve access points. | Furby-North Preserve Unauthorized Control Project, Proctor Valley Off Highway Vehicle (OHV) Barrier, Otay River Valley Cactus Wren Habitat Restoration and Enhancement , Spring Canyon/Goat Mesa Vernal Pool Restoration |
| Criteria | Deadline year |
|---|---|
| Restrictions on Passive Recreation Implemented for the Protection of MSP Resources | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
From 2017-2021, establish Recreational Area Patrols to assist in identifying and reporting to land managers and rangers any incompatible uses of the preserve that impact natural resources.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Coordinate with land managers who are implementing Recreational Area Patrols to learn how to create a patrol system for other preserves. | South San Diego County Community Outreach |
| Criteria | Deadline year |
|---|---|
| At least 1 new Recreational Patrol Program Implemented starting in 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
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 | Test project on production server, created by DAM 4/3/19 |
| IMP-2 | Submit project metadata, monitoring datasets and report with management actions to the MSP Web Portal. | waiting for precedent action | Test project on production server, created by DAM 4/3/19 |
| Criteria | Deadline year |
|---|---|
| Fuel Loads and Invasive Grasses Reduced for at Risk Populations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
Beginning in 2017, annually inspect conserved populations of San Diego thornmint (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, occurrence status, habitat and threats data, and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego thornmint occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. | available for implementation | San Diego Thornmint Restoration |
| IMP-2 | Submit project metadata and management data to MSP web portal. | available for implementation | San Diego Thornmint Restoration |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
In 2017, continue refining BMPs developed for San Diego thornmint (CBI 2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal studies at Mission Trails and South Crest) and based on research studies (e.g., seed bulking guidelines, seed transfer zones).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Refine BMPs prepared by CBI in the San Diego Thornmint Adaptive Management Framework (2014) by incorporating results of management experiments to control invasive species that threaten populations (e.g., Brachypodium removal and South County Grasslands projects) and based on research studies (e.g., seed bulking guidelines, seed transfer) | In progress | |
| DEV-2 | Submit project metadata, management datasets and BMP report to MSP web portal. | In progress |
| Criteria | Deadline year |
|---|---|
| BMPs for San Diego Thornmint Prepared by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
In 2018, begin preparing a section for San Diego thornmint the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand occurrences on Conserved Lands based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations to maintain large occurrences and enhance at least 3 small occurrences (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Diego thornmint section in the MSP Rare Plant Management Plan. | waiting for precedent action | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to San Diego thornmint occurrences. | waiting for precedent action | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | waiting for precedent action | |
| PRP-4 | Develop an implementation plan for San Diego thornmint that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | waiting for precedent action | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2019 Completed Section for San Diego Thornmint in the MSP Rare Plant Management Plan. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
In 2018, begin preparing a section for San Diego thornmint in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2016-2017 genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing sources of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the San Diego thornmint section of the MSP Seed Collection, Banking and Bulking Plan. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2019, Completed Section for San Diego thornmint in the MSP Seed Collection Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
In 2019, begin implementing the MSP Seed Collection, Banking and Bulking Plan for San Diego thornmint to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2023, =2 Highest Priority Actions Implemented for San Diego thornmint from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6
In 2017, continue field research into soils and habitat relationships and development of habitat suitability and climate change models for San Diego thornmint and other edaphic endemic plants to better understand habitat requirements and to identify and prioritize geographic areas important for connectivity, restoration, and range shifts due to climate change and other threats.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Test soils at potential expansion sites and compare to occupied reference sites to determine site suitability based on soils. | In progress | Enhancing the Resilience of Edaphic Endemic Plants |
| RES-2 | Prepare habitat suitability models under current environmental conditions and for different scenarios of climate change to delineate potential future habitat. | In progress | Enhancing the Resilience of Edaphic Endemic Plants |
| RES-3 | Collect covariate data on vegetation composition and cover (alliance and association-level mapping), soils, invasive plants and other threats for selected populations. | In progress | Enhancing the Resilience of Edaphic Endemic Plants |
| RES-4 | Prioritize locations for conservation, management, and future surveys based on predicted distributions and environmental correlates. | In progress | Enhancing the Resilience of Edaphic Endemic Plants |
| RES-5 | Submit project metadata, monitoring data and report to MSP web portal. | In progress | Enhancing the Resilience of Edaphic Endemic Plants |
| Criteria | Deadline year |
|---|---|
| Refined Models and Prioritized Future Survey Locations for San Diego Thornmint by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
From 2017-2012, inspect extant Nuttall's acmispon occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 7
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Nuttall's acmispon occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | some occurrences are in progress | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | some occurrences are in progress | Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 7
In 2017, begin preparing a section for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Nuttall's acmispon in the MSP Seed Collection, Banking and Bulking Plan. | Available for implementation | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | Available for implementation | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | Available for implementation | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | Available for implementation | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | Available for implementation | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | Available for implementation |
| Criteria | Deadline year |
|---|---|
| By 2018, Completed Nuttall's Acmispon Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
In 2017, begin preparing a section for Nuttall's acmispon in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the 5 large occurrences and to enhance at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Nuttall's acmispon in the MSP Rare Plant Management Plan. | available for implementation | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Nuttall's acmispon occurrences. | available for implementation | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | available for implementation | |
| PRP-4 | Develop an implementation plan for Nuttall's acmispon that prioritizes management actions for the nex 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | available for implementation | |
| PRP-5 | Submit project metadata, project datasets, and the MSP Rare Plant Management Plan to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| By 2018, Completed Nuttall's Acmispon Section in the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 6, 7
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.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
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 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 3, 4, 5, 6, 9, 10, 11
From 2017-2018, support the existing efforts to restore the El Monte ponds and any other on-going habitat restoration projects for the benefit of nesting tricolored blackbird. This objective to be incorporated into the Tricolored Blackbird Management Plan after 2018.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, data, and annual reports documenting project methods and results to the MSP Web Portal. | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Restoration of El Monte ponds implemented for Tricolored Blackbird | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 9, 10, 11
Beginning in 2017, annually inspect suitable nesting habitat at current and historically occupied sites (see occurrence table) to determine management needs (including need for additional water) taking care not to disturb nesting tricolored blackbirds, and use a regional IMG monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol surveys to determine management needs (including need for additonal water) taking care not to disturb nesting tricolored blackbirds, | available for implementation | Tricolored Blackbird (Agelaius tricolor) Surveys |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | available for implementation | |
| IMP-3 | Submit monitoring data and management recommendations to MSP web portal | available for implementation | Tricolored Blackbird (Agelaius tricolor) Surveys |
| Criteria | Deadline year |
|---|---|
| Annual IMG monitoring of Tricolored Blackbird completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 9, 10, 11
In 2018, prepare a management plan for tricolored blackbird that prioritizes management actions to protect nesting sites from disturbance and enhances habitat using data from annual IMG monitoring.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | Available for implementation | |
| PRP-2 | Develop an implementation plan for tricolored blackbird that prioritizes management actions for the next five years. | Available for implementation | |
| PRP-3 | Submit management plan to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Plan for Tricolored Blackbird prepared by 2019 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
Beginning in 2017, annually inspect San Diego ambrosia occurrences on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at San Diego ambrosia occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. | available for implementation | |
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
In 2020, begin preparing a section for San Diego ambrosia in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat, threats, genetic data, and results of existing restoration efforts. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for San Diego ambrosia in the MSP Rare Plant Management Plan. | on hold | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to San Diego ambrosia occurrences. | on hold | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | on hold | |
| PRP-4 | Develop an implementation plan for San Diego ambrosia that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | on hold | |
| PRP-5 | Submit project metadata, management datasets and the MSP Rare Plant Management Plan to MSP web portal | on hold |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed San Diego Ambrosia Section in the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
In 2021, begin implementing highest priority management actions identified for San Diego ambrosia in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Using BMPs, conduct invasive plant control annually until success criteria are met and then as needed thereafter. | waiting for precedent action | |
| IMP-2 | Submit project metadata, management data and monitoring data to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, >1 High priority Management Actions for San Diego Ambrosia initiated from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
In 2021, monitor the effectiveness of highest priority management actions for San Diego Ambrosia in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
In 2020, begin preparing a section for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for San Diego Ambrosia in the MSP Seed Collection, Banking and Bulking Plan. | On hold | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | On hold | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | On hold | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | On hold | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | On hold | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed San Diego Ambrosia section in the MSP Seed Collection Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 6, 8
In 2021, begin implementing the San Diego Ambrosia section in the MSP Seed Collection, Banking and Bulking Plan to collect and store seed at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, >1 San Diego Ambrosia Seed Collection, Banking and Bulking initiated | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8, 9, 10, 11
In 2020 and 2021 (assuming adequate rainfall levels), conduct comprehensive arroyo toad surveys using USGS survey protocols throughout the MSPA on Conserved Lands in known occupied and potential habitat to determine current distribution and status of arroyo toad, collect data on threats and habitat covariates, and identify management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | Survey known occupied and potantial habitat on Conserved Lands across the MSPA to determine the distribution and abundance of arroyo toad on Conserved Lands. | Available for implementation | |
| SURV-2 | Collect data on threats and identify management needs to support self-sustaining occurrences. | Available for implementation | |
| SURV-3 | Continue to collect genetic samples from all arroyo toads captured. | Available for implementation | |
| SURV-4 | Submit survey data and management recommendations to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Comprehensive surveys completed for Arroyo toad by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2017-2018, finalize the results of research begun in 2015 on pallid bats to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas, and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat, assess threats to bats at all preserves where they occur, and develop management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Submit project metadata, survey data, and report with management recommendations to the MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Pallid Bat Surveys and Reports Completed in 2017. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, inspect the vicinity of pallid bat roosts on an annual basis (see occurrence table), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol surveys to quantify signs of human activity near occupied or potential roosts and to identify other potential threats. Care should be taken to avoid disturbing roosting bats. | available for implementation | Pallid Bat Surveys - Sweetwater Marsh |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | available for implementation | Pallid Bat Surveys - Sweetwater Marsh |
| IMP-3 | Submit monitoring data and management recommendations to MSP web portal | available for implementation | Pallid Bat Surveys - Sweetwater Marsh |
| Criteria | Deadline year |
|---|---|
| Annual IMG monitoring of Pallid bat completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting occurrences from disturbance through fencing, signage, and enforcement.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP web portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2018-2019, prepare a management plan for pallid bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the pallid bat research study.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | available for implementation | Pallid Bat Surveys - Sweetwater Marsh |
| PRP-2 | Develop a management plan for pallid bat that prioritizes management actions for the next five years. | waiting for precedent action | Pallid Bat Surveys - Sweetwater Marsh |
| PRP-3 | Identify areas where pallid bat and Townsend?s big-eared bat management can be complimentary. | waiting for precedent action | Pallid Bat Surveys - Sweetwater Marsh |
| PRP-4 | Submit management plan to MSP web portal | waiting for precedent action | Pallid Bat Surveys - Sweetwater Marsh |
| Criteria | Deadline year |
|---|---|
| Management Plan for Pallid bat prepared by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2020, implement highest priority management actions for pallid bats on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the implementation plan. | waiting for precedent action | |
| IMP-2 | Submit project data and management actions to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions implemented for Pallid bat | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2020, monitor the effectiveness of management actions implemented for pallid bats on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of Implementing Pallid Bat High Priority Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 1, 7
In 2019, survey historic aphanisma locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | On hold | |
| SURV-2 | Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Surveys and Report Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
In 2021, begin preparing a section for aphanisma in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009; KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the aphanisma section of the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Write a seed collection plan section that includes collecting seeds over multiple years and several times within a season, accumulating seeds across populations, and sampling among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from occurrences with <1,000 plants and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan section should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Aphanisma Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
In 2021, begin preparing a section for aphanisma in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences and/or establishment of new occurrences in suitable habitat as needed to achieve at least 3 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the aphanisma section of the MSP Rare Plant Management Plan. | some occurrences are in progress | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to aphanisma populations. | some occurrences are in progress | |
| PRP-3 | Prioritize occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | available for implementation | |
| PRP-3 | Prioritize occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | some occurrences are in progress | |
| PRP-4 | Develop an implementation plan for aphanisma that prioritizes management actions for the next 5 year and details tasks, lead entities, responsibilities, and timelines, budgets. | some occurrences are in progress | |
| PRP-5 | Submit project metadata, project datasets, and MSP Rare Plant Management Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Aphanisma Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California |
| 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 | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California , Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California |
| RES-3 | Analyze golden eagle foraging habitat data and develop objectives with criteria for managing open areas (grasslands and suitable areas in coastal sage scrub and chaparral) to conditions preferred by foraging eagles and that support abundant prey (e.g., black-tailed jack rabbits, ground squirrels). | unknown | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California |
| 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 | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California , Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California |
| RES-5 | Use the GPS and behavioral response data to model potential impacts to foraging eagles under different scenarios of human disturbance at important foraging areas. Prepare management recommendations to reduce human impacts on foraging eagles, including alignment of trails, restriction of activities, and educational outreach. | in progress | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California , Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California |
| RES-6 | Submit project metadata, datasets, and report with management recommendations to the MSP Web Portal. | in progress | Five Year Site Occupancy, Nesting Success, Movement Behavior, and Genetic Structure of Golden Eagles in Western San Diego County, California , Biotelemetry Data for Golden Eagles (Aquila chrysaetos) Captured in Coastal Southern California |
| Criteria | Deadline year |
|---|---|
| Golden Eagle Nesting, Foraging, and Habitat Use Study Report with Management Recommendations Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Pesticides | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8, 9, 10, 11
In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Management Plan for managing golden eagle territories with nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include recommendations for managing important foraging habitat to minimize human disturbance to foraging eagles and to improve habitat quality to enhance prey availability, especially during drought periods. The plan should also include specifications to control human disturbance that could discourage nesting, cause nest abandonment, or adversely affect the survival of nestlings, and for managing unstable nest ledges or tree nest sites that are critical to maintaining a breeding pair in territories with limited nesting sites.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prepare a five year plan for maintaining and enhancing golden eagle foraging habitat in grasslands and suitable areas in open coastal sage scrub and chaparral, and for reducing human impacts to foraging eagles. Use the Golden Eagle Nesting, Foraging, and Habitat Use Study and modeling results to identify important foraging areas for golden eagles on Conserved Lands in the MSPA. Specify management to reduce human disturbance in important foraging habitat and to manage invasive annual grasses to promote abundant prey, such as California ground squirrels and black-tailed jackrabbit. Include a mechanism for updating the management plan with monitoring results and specific management recommendations from the Comprehensive Golden Eagle Monitoring Plan. | waiting for precedent action | |
| PRP-2 | Prioritize for management, those nest ledges and trees that are in territories where alternative nest sites are limited. Prepare a nest restoration plan for each prioritized unstable nest ledge or vulnerable nest tree in consultation with a qualified golden eagle biologist. | waiting for precedent action | |
| PRP-3 | Establish procedures for managing human activities within the nest site protective zone, including rerouting trails, closing trails during the breeding season, educational outreach, and enforcement. | waiting for precedent action | |
| PRP-4 | Submit project metadata and Comprehensive Golden Eagle Management Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Comprehensive Golden Eagle Management Plan Completed by 2022 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8, 9, 10, 11
In 2021, use the results and recommendations from the Golden Eagle Nesting, Foraging, and Habitat Use Study and the Golden Eagle Genetics Study to develop a comprehensive Golden Eagle Monitoring Plan for monitoring golden eagle status and assessing nesting, roosting, and foraging habitat on Conserved Lands within the MSPA (see occurrence table). The plan should include standardized monitoring protocols to track the status of eagles at nesting territories, to monitor use of important foraging areas, and to collect habitat and threats covariate data to inform needed management actions.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Complete a plan to monitor the status and habitat use of eagles over the long term within the MSPA that is based upon the occupancy monitoring study in the Golden Eagle Nesting, Foraging and Habitat Use Study. The plan should include detailed monitoring objectives, statistically valid sampling design, sampling locations, monitoring timeline, and standardized monitoring protocols to record eagles and important habitat and threat attributes. | waiting for precedent action | |
| PRP-2 | Develop a plan to rapidly assess the condition of important golden eagle foraging habitat on Conserved Lands across the MSPA using a standardized protocol, statistically valid sampling design, and designated sampling locations. The protocol should describe monitoring methods to collect specific habitat and threat covariates associated with habitat quality, as identified by the Golden Eagle Nesting, Foraging, and Habitat Use Study. The results of this monitoring will be used to periodically prioritize sites and develop specific recommendations for managing foraging habitat to minimize human disturbance and enhance habitat quality to support abundant eagle prey. | waiting for precedent action | |
| PRP-3 | A golden eagle expert should prepare a protocol, standardized data sheets, and provide periodic training to land managers in how to safely conduct annual nest inspections and determine management needs with minimal disturbance to eagles. The protocol should assess nest sites during the non-breeding season to identify nest ledges that are unstable and nest trees that are vulnerable to loss from threats such as wildfire, pests, and fungal pathogens. | waiting for precedent action | |
| PRP-4 | Submit project metadata, sampling design, sampling locations, protocols and Comprehensive Golden Eagle Monitoring Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Comprehensive Golden Eagle Monitoring Plan Completed by 2022 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Pesticides | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 9
In 2017, finalize the Burrowing Owl Conservation and Management Plan that includes results from the research study and habitat assessments and recommendations for the establishment of at least two nodes and enhancement of existing occurrences to ensure persistence on Conserved Lands and establishment of a captive breeding population as a source for burrowing owls.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult with the Burrowing Owl Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to gather input into prioritized management actions. | completed | |
| PRP-2 | Submit project metadata and Burrowing Owl Conservation and Management Plant to the MSP Web Portal. |
| Criteria | Deadline year |
|---|---|
| Burrowing Owl Management Plan Completed in 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 3, 5
In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2018 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 5
In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2018 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 6
Beginning in 2017, inspect Encinitas baccharis occurrences on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 6
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Encinitas baccharis occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 6
Beginning in 2018, inspect extant San Diego goldenstar occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years, unless an occurrence is small (<100 individuals) or faces a high degree of threat, in which case monitor annually.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 6
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016, 2018, and 2020 at San Diego goldenstar occurrence(s) on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 6, 7, 8
Beginning in 2017, inspect conserved populations of thread-leaved brodiaea in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs. After 2017, repeat monitoring every 2 years.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7, 8
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at thread-leaved brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7, 8
In 2020, begin preparing a section for thread-leaved brodiaea in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize extant occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | some occurrences are in progress | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to thread-leaved brodiaea occurrences. | some occurrences are in progress | |
| PRP-3 | Identify and prioritize sites for re-establishment of historic occurrences or that appear suitable for establishment of new occurrences. Specify the highest priority sites for establishing occurrences on Conserved Lands. | some occurrences are in progress | |
| PRP-4 | Develop an implementation plan for thread-leaved brodiaea that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | some occurrences are in progress | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed Section for Thread-leaved brodiaea in the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7, 8
Beginning in 2021, begin implementing highest priority management actions identified in the thread-leaved brodiaea section of the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 High priority Management Action Implemented for Thread-leaved Brodiaea from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7, 8
Monitor effectiveness of implementation of highest priority management actions identified in the thread-leaved brodiaea section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7, 8
In 2020, begin preparing a section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Thread-leaved brodiaea MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Design a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2021, completed section for Thread-leaved brodiaea in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7, 8
In 2021, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Thread-leaved brodiaea to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Seed should be stored for conservation banking and as source of propagules for enhancement and restoration projects at a permanent, established seed bank. | waiting for precedent action | |
| IMP-2 | Submit project metadata and Thread-leaved brodiaea MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 Highest Priority Action Implemented for Thread-leaved brodiaea from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
From 2017-2021, inspect Orcutt's brodiaea occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's brodiaea occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | Otay Mesa Rare Plants |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation | Otay Mesa Rare Plants |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 7, 8
In 2019, survey historic Orcutt's brodiaea locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | On hold | |
| SURV-2 | Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Surveys and Report Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
In 2020, begin preparing an Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Design the seed collection plan to include recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | |
| PRP-6 | Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed Orcutt's Brodiaea Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
From 2017-2019, collect Orcutt's brodiaea seed for conservation banking and bulk seed for establishment of new occurrences at Cal Terraces/Dennery Canyon and Proctor Valley. In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | some occurrences are in progress | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 Highest Priority Action Implemented for Orcutt's brodiaea from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
In 2020, begin preparing an Orcutt's brodiaea section in the MSP Rare Plant Management Plan to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Rare Plant Management Plan. | some occurrences are in progress | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's brodiaea occurrences. | some occurrences are in progress | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | some occurrences are in progress | |
| PRP-4 | Develop an implementation plan for Orcutt's brodiaea that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | some occurrences are in progress | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed Orcutt's Brodiaea Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
In 2021, begin implementing highest priority management actions identified for Orcutt's brodiaea in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 High Priority Management Action Implemented for Orcutt's Brodiaea from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 8
In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's brodiaea section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 8
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.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2018 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
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 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 5, 6
In 2018, inspect occurrences of alkali playa MSP VF plant species (i.e., Coulter's saltbush, Parish's brittlescale, southern tarplant) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2018 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
Beginning in 2020, implement management actions on Conserved Lands as identified through monitoring and the coordination efforts with the land managers and wildlife agencies.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, management datasets, and report to the MSP web portal. |
| Criteria | Deadline year |
|---|---|
| By 2021, at least 1 Management Actions Implemented for Western Snowy Plover | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
Beginning in 2020, monitor the effectiveness of management actions implemented for western snowy plover on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal. |
| Criteria | Deadline year |
|---|---|
| Monitoring data submitted to MSP web portal within one year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1
Beginning in 2017, annually inspect salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at salt marsh bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1
Prepare a salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from the 2016-2017 genetics study and from 2017-2019 seed collection and banking efforts conducted by San Diego Zoo's Institute for Conservation Research to guide collection and storing of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the salt marsh bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-2 | Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-3 | The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-6 | Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2019, Completed Salt Marsh Bird's-beak Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1
From 2017-2019, collect salt marsh bird's-beak seed for conservation banking. In 2019, begin implementing high priority actions for salt marsh bird's-beak from the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2022, =2 Highest Priority Actions Implemented for Salt Marsh Bird's-beak from the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, conduct annual surveys of all Orcutt's spineflower.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at Orcutt's spineflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | in progress | Otay Mesa Rare Plants |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | in progress | Otay Mesa Rare Plants |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2017, continue efforts begun in 2015 to survey historic Orcutt's spineflower locations to: determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | In progress | |
| SURV-2 | Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. | In progress |
| Criteria | Deadline year |
|---|---|
| Baseline Surveys and Report Completed by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2017, continue BMPs initiated in 2015 to establish 4 new occurrences of Orcutt's spineflower.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Establish 4 new occurrences of Orcutt | in progress | |
| IMP-2 | Use BMPs for site preparation (Bauder 2010a,b). Sites with ice plant or Acacia shrubs should be cleared of these invasive plants and duff and then watched for at least 2 years with suitable growing conditions to determine if there are viable spineflower | in progress | |
| IMP-3 | Maintain newly established occurrences so that there is <20% invasive non-native absolute cover, minimal encroachment of native plants (based upon standards used at the Point Loma Naval Base), and no ground disturbance from erosion or trampling. | in progress | |
| IMP-4 | Use the seed collection and bulking plan to determine seed sources and timing and amount of seeding. | in progress | |
| IMP-5 | Submit project metadata, monitoring and management data to MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| 4 New Occurrences of Orcutt's Spineflower Established by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2019, begin preparing a section for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's spineflower section in the MSP Seed Collection, Banking and Bulking Plan. | On hold | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | On hold | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | On hold | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | On hold | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | On hold | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| By 2020, Completed Section for Orcutt's Spineflower in MSP Seed Collection Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2020, begin implementing high priority actions for Orcutt's spineflower in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2022, =1 Highest Priority Actions Implemented for Orcutt's Spineflower from the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2019, begin preparing a section for Orcutt's spineflower in the MSP Rare Plant Management Plan to maintain large occurrences (>1,000 plants) and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Orcutt's spineflower in the MSP Rare Plant Management Plan. | on hold | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's spineflower occurrences. | on hold | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | on hold | |
| PRP-4 | Develop an implementation plan for Orcutt's spineflower that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | on hold | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| By 2020, Completed Section for Orcutt's Spineflower in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2020, begin implementation of the highest priority management actions for Orcutt's spineflower identified in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2022, =1 High Priority Management Action Initiated for Orcutt's spineflower from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
Monitor the effectiveness of highest priority management actions implemented for Orcutt's spineflower.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
In 2019, conduct a survey for northern harrier and other associated raptors to document the harrier's current distribution and abundance and to assess habitat and threats at survey sites. Prepare site-specific management recommendations based on survey results and habitat assessments.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | Submit monitoring data and management recommendations to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Northern Harrier Surveys and Reports Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
From 2017 to 2021, annually inspect the existing nesting occurrences of northern harrier, taking precautions to avoid disturbance, to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. | Available for implementation | |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | Available for implementation | |
| IMP-3 | Submit monitoring data and management recommendations to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with management recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
From 2017-2021, perform routine management activities such as protecting nesting occurrences from disturbance through fencing, signage, and enforcement.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. | Available for implementation | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
In 2020, prepare a management plan for northern harrier that prioritizes management actions to protect nesting sites from disturbance and enhances habitat using data from annual IMG monitoring.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | Available for implementation | |
| PRP-2 | Develop a management plan for northern harrier that prioritizes management actions for the next five years. | Available for implementation | |
| PRP-3 | Submit management plan to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Plan for Northern Harrier prepared by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
Beginning in 2021, implement the highest priority management actions for northern harrier on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the management plan. | waiting for precedent action | |
| IMP-2 | Submit project data and management actions to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions implemented for Northern Harrier | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 1, 3, 4, 5, 6, 7, 8
Beginning in 2021, monitor the effectiveness of management actions implemented for northern harrier on Conserved Lands
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring completed and data and report submited within 1 year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Pesticides | |
| Urban development | URBDEV |
Management units: 3, 4
Beginning in 2018, inspect San Miguel savory occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional monitoring protocol surveys to assess abundance status and quantify potential threats. | on hold | |
| IMP-2 | Based upon occurrence status and threats, determine if routine management or more intensive management is warranted. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018, and 2020 at San Miguel savory occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. | available for implementation | |
| IMP-2 | Submit monitoring and management data to the SC-MTX website portal. | available for implementation | |
| IMP-2 | Submit monitoring and management data to the SC-MTX website portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4
In 2020, begin implementing high priority actions for San Miguel savory in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2024, =1 Highest Priority Action Implemented for San Miguel Savory from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4
In 2020, begin implementing highest priority management actions identified for San Miguel savory in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2024, =1 High Priority Management Action Implemented for San Miguel Savory Section from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4
In 2020, begin monitoring effectiveness of implementation of highest priority management actions identified in the San Miguel savory section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 2, 3
In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus, and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3
In 2017, begin annual inspections of extant occurrences of Otay tarplant on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record spatial extent, estimate abundance, and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine if routine management or more intensive management is warranted. | some occurrences are in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP web portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3
Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at Otay tarplant occurrences on Conserved Lands (see occurrence table) . Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata, monitoring and management recommendations to the MSP web portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3
In 2017 continue the collaboration with the South County Grasslands Project initiated in 2014 to develop BMPs for landscape-scale restoration of Otay tarplant habitat in MU3 that includes testing methods of seeding and invasive plant control so that nonnative plants and thatch are reduced to less than 20% relative cover and thatch to <5 cm tall and native plants to at least 25% relative cover. These percent cover criteria could be revised based on data collected from an acceptable reference site.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Conduct experiments using mowing, prescribed burns herbicide and potentially grazing to control invasive non-native grasses and forbs at a landscape-scale and to compare drill seeding versus hand broadcast seeding in order to determine economical and effect. | in progress | Regional Grazing Monitoring Plan |
| DEV-2 | Based upon experiment results, develop explicit BMPs for the restoration of Otay tarplant. Submit project metadata, monitoring datasets and BMP report to MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| BMPs Developed for Restoration of Otay tarplant by 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3
In 2018, begin preparing an Otay tarplant section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than or equal to 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Otay tarplant in the MSP Rare Plant Management Plan. | some occurrences are in progress | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Otay tarplant occurrences. | some occurrences are in progress | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | some occurrences are in progress | |
| PRP-4 | Develop an implementation plan for Otay tarplant that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | some occurrences are in progress | |
| PRP-5 | Submit project metadata, project datasets, and the MSP Rare Plant Management Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2019, Completed Otay Tarplant Section in the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3
In 2018, begin preparing a section for Otay tarplant in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for:collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Otay tarplant section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2019, Completed Otay Tarplant Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 3
From 2017 to 2021, inspect Orcutt's bird's-beak occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 3
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Orcutt's bird's-beak occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 3
In 2019, survey historic Orcutt's bird's-beak locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | On hold | |
| SURV-2 | Submit project metadata, habitat mapping, occurrence status, habitat and threats assessments, management recommendations, and report to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Surveys and Report Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 3
In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should include recommendations from 2017-2019 seed collection and bulking efforts conducted by San Diego Zoo's Institute for Conservation Research and from the 2016-2017 genetic study to collect and store seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's bird's-beak section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-2 | Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-3 | The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-6 | Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed Orcutt's Bird's-beak Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 3
From 2017-2019, collect Orcutt's bird's-beak seed for conservation banking and bulk seed for enhancing and expanding the Cal Terraces/Dennery Canyon occurrence (see occurrence table). In 2021, begin implementing high priority actions for Orcutt's bird's-beak in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 Highest Priority Action Implemented for Orcutt'sBird's-beak from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 3
In 2020, begin preparing an Orcutt's bird's-beak section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain large occurrences and expand at least 3 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare management recommendations for re-establishment of historic occurrences or establishment of new occurrences if determined to be necessary for gene flow and for long term persistence. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan. | on hold | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's bird's-beak occurrences. | on hold | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | on hold | |
| PRP-4 | Develop an implementation plan for Orcutt's bird's-beak that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | on hold | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| By 2021, Completed Orcutt's Bird's-beak Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
In 2021, begin implementing highest priority management actions identified for Orcutt's bird's-beak in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2025, =1 High Priority Management Action Implemented for Orcutt's Bird's-beak from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
In 2021, monitor effectiveness of implementation of highest priority management actions identified in the Orcutt's bird's-beak section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
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 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
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 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
Management units: 1, 6
From 2017-2021, inspect Blochman's dudleya occurrences annually on Conserved Lands (see occurrence table) using the IMG regional monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | in progress | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 6
Beginning in 2017, conduct routine management actions identified through the IMG monitoring at Blochman's dudleya occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 2, 6, 7
In 2019, survey historic Blochman's dudleya locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | On hold | |
| SURV-2 | Submit project metadata, habitat mapping, and a report with site prioritizations and recommendations for management based upon occurrence status, habitat and threats assessments to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Surveys and Report Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 2, 6, 7
In 2021, begin preparing a section for Blochman's dudleya in the MSP Seed Collection, Banking and Bulking Plant to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009, KEW 2016) and provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Blochman's dudleya section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Blochman's Dudleya Section in MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 2, 6, 7
In 2021, begin preparing a section for Blochman's dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to at least 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for Blochman's dudleya in the MSP Rare Plant Management Plan. | waiting for precedent action | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Blochman's dudleya populations. | waiting for precedent action | |
| PRP-3 | Use occurrence status and threats data to develop management recommendations to reduce threats and promote resilience of occurrences. | waiting for precedent action | |
| PRP-4 | Develop an implementation plan for Blochman's dudleya that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | waiting for precedent action | |
| PRP-5 | Submit project metadata, project datasets, and MSP Rare Plant Management Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Blochman's Dudleya Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 6, 7
In 2017, continue annual inspections of short-leaved dudleya on Conserved Lands in (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect covariate habitat and threats data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | available for implementation | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every Year with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at short leaved dudleya occurrences on Conserved Lands in (see occurrence table). Depending on the type and level of threat, management should only be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities as needed, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species to at most 20% absolute cover. | available for implementation | Otay Mesa Rare Plants |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation | Otay Mesa Rare Plants |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2021, begin preparing a section for short-leaved dudleya in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the genetic study to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and to provide seed sources for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the short-leaved dudleya section of the MSP Seed Collection, Banking and Bulking Plan. | on hold | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | on hold | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | on hold | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | on hold | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | on hold | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Short-leaved dudleya Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2021, begin preparing a section for short-leaved dudleya in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or expand conserved occurrences based upon an assessment of data on occurrence status habitat and threats. Include recommendations for short-leaved dudleay from MSP Seed Collection, Banking and Bulking Plan, relevant BMPs, and recommendations for monitoring effectiveness of management actions.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for short-leaved dudleya in the MSP Rare Plant Management Plan. | on hold | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to short-leaved dudleya occurrences. | on hold | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | on hold | |
| PRP-4 | Develop an implementation plan for short-leaved dudleya that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | on hold | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Short-leaved dudleya section in the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6
In 2018 and 2020, inspect variegated dudleya occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2018 and 2020 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 2, 3, 4, 6
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring in 2016, 2018 and 2020 at variegated 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.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 6
In 2021, inspect sticky dudleya occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 6
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.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform as needed routine management activities, such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 1, 4, 6, 8, 9, 10, 11
In 2017-2019, continue the 5-year breeding bird study begun by USGS in 2015 of southwestern willow flycatcher in the San Luis Rey River and other drainages to determine the status in the MSPA and impacts to riparian habitat from SHB/Fusarium complex and other threats. Prepare site-specific management recommendations based on survey results.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Submit monitoring data and management recommendations to MSP web portal | In progress |
| Criteria | Deadline year |
|---|---|
| Southwestern Willow Flycatcher Surveys and Reports Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 4, 6, 8, 9, 10, 11
In 2020-2021, prepare a management plan for southwestern willow flycatcher based on survey recommendations and that includes provisions for reducing potential impacts of SHB/Fusarium infestation in occupied or potential habitat. Incorporate SHB/Fusarium monitoring results into the management plan, particularly along the San Luis Rey River.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | Available for implementation | |
| PRP-2 | Develop an implementation plan for southwestern willow flyycatcher that prioritizes management actions for the next five years. | Available for implementation | |
| PRP-3 | Submit management plan to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Plan for Southwestern Willow Flycatcher prepared by end 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 4, 6, 8, 9, 10, 11
Beginning in 2021, implement the highest priority management actions for southwestern willow flycatcher on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the management plan. | waiting for precedent action | |
| IMP-2 | Submit project data and management actions to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions initiated for Southwestern Willow Flycatcher | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 4, 6, 8, 9, 10, 11
Beginning in 2021, monitor the effectiveness of management actions implemented for southwestern willow flycatcher on Conserved Lands
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring completed and data and report submitting within 1 year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
From 2017 to 2021, continue efforts to expand and translocate occurrences of pond turtles to increase to self-sustaining levels in MU3 in the Sweetwater and Otay River Watersheds (at SPER, RJER, and other suitable sites) and identify, expand, and translocate pond turtles in at least 2 other watersheds in the MSPA, including but not limited to the San Diego and San Dieguito Rivers. Translocation efforts may include management of invasive aquatic and plant species, providing access protection, and headstart efforts.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct routine management as needed at the Sycuan Peak ER occurrence of southwestern pond turtle. | In progress | |
| IMP-2 | Conduct routine management as needed at the Rancho Jamul ER translocated occurrence of southwestern pond turtle. | In progress | |
| IMP-3 | Continue to identify, begin management of invasive species, and translocate pond turtle to at least 2 suitable locations in the San Dieguito and San Diego River (e.g. El Monte Ponds, Boulder Creek Preserve) watersheds. | In progress | |
| IMP-4 | Submit monitoring and management data to the regional MSP web portal. | In progress |
| Criteria | Deadline year |
|---|---|
| By 2021, 2 new occurrences translocated in the San Diego and San Dieguito River Watersheds; SPER and RJER occurrences increased by 20% through recruitment from 2017 leve | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
From 2017 to 2021, continue monitoring the effectiveness of southwestern pond turtle translocation experiments at SPER and RJER (see Table of Occurrences) and any additional translocated occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Continue to monitor the expanded and head-started occurrence and/or habitat at SPER and RJER to document success. | In progress | |
| IMP-2 | Monitor other translocated occurrences to document success. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Southwestern Pond Turtle Translocation Monitoring and Reports Completed Annually | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
From 2017 to 2021, biennially inspect the existing occurrences of southwestern pond turtle to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Use regional IMG monitoring protocol to assess status, habitat, and quantify potential threats. | Available for implementation | |
| IMP-2 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | Available for implementation | |
| IMP-3 | Submit monitoring and management data to the regional MSP web portal. | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Surveys Completed every two years with management recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
From 2017 to 2021, conduct routine management actions identified through the IMG regional protocol monitoring, including protecting populations from disturbance, removing invasive plants, and removing aquatic predators and exotic species (which compete and or prey on western pond turtle, primarily young) within the known occupied and suitable habitat.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance, controlling invasive plants, and removing invasive aquatic animals. | some occurrences are in progress | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
Beginning in 2018, prepare a management plan for southwestern pond turtles that includes identification of high priority management actions at sites with self sustaining populations, as well as actions to establish of at least 2 additional pond turtle populations to increase resilience to fire and other threats. Include guidance & prioritizations for next steps for translocations. The plan should include actions to manage threats from hydrology, debris, invasive animals and plants, and fire, and the creation of basking sites.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Develop a southwestern pond turtle management plan using the survey data with information on occurrence status and threats, habitat models, and management needs to determine if an appropriate location | waiting for precedent action | |
| PRP-2 | The plan should prioritize management actions for the next five years and detail tasks, lead entities, responsibilities, timelines, and budgets | waiting for precedent action | |
| PRP-3 | Submit management plan to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management Plan for Southwestern pond turtle completed by 2018. | 2018 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
Beginning in 2019, implement highest priority management actions as identified in the Southwestern pond turtle management plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the management plan. | waiting for precedent action | |
| IMP-4 | Submit project metadata and management data to MSP web portal. | unknown |
| Criteria | Deadline year |
|---|---|
| By 2021, =1 High Priority Management Action Implemented from the Southwestern pond turtle Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 8
Beginning in 2019, monitor the effectiveness of management actions implemented for the Southwestern pond turtle.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and report to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 6, 7
In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, inspect occurrences of coast wallflower on Conserved Lands (see occurrence table) using the regional IMG monitoring protocol to record status and to collect habitat and threats covariate data to determine management needs. After 2017, repeat monitoring every 2 years.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | some occurrences are in progress | Rare Plant Inspect and Manage Monitoring 2014-2026 |
| IMP-2 | Submit project metadata, status, habitat and threats data, and management recommendations to the MSP Web Portal. | some occurrences are in progress | Rare Plant Inspect and Manage Monitoring 2014-2026 |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2017, 2019, and 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring at coastal wallflower occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities, such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species =20% absolute cover. | some occurrences are in progress | |
| IMP-2 | Submit project metadata and management datasets to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 6, 7
In 2019, conduct baseline surveys of historic coast wallflower locations to determine current occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats covariates and determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | Map suitable habitat based on soils, topography, openings in vegetation communities, and general location for existing occurrence expansion and new occurrence establishment. | On hold | |
| SURV-2 | Submit project metadata, occurrence status, habitat mapping and assessment, and report to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| By 2020, Surveys and Report Completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 6, 7
In 2021, begin preparing a section for coast wallflower in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the coast wallflower section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | |
| PRP-2 | Prepare a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | some occurrences are in progress |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Coast Wallflower Section in MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 6, 7
In 2021, begin preparing a section for coast wallflower in the MSP Rare Plant Management Plan that prioritizes management actions to maintain and expand conserved occurrences based upon an assessment of data on occurrence status, habitat and threats. Prioritize management recommendations for re-establishment of historic occurrences or establishment of new occurrences in suitable habitat, as needed, to achieve at least 4 occurrences with self-sustaining populations on Conserved Lands (see occurrence table). Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize extant occurrences for management based upon "IMG" monitoring data and baseline survey assessments of occurrence size, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | on hold | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to coast wallflower occurrences. | on hold | |
| PRP-3 | Identify and prioritize sites for re-establishment of historic occurrences or that appear suitable for establishment of new occurrences. Specify the highest priority sites for establishing occurrences to reach the goal of at least 4 extant occurrences on Conserved Lands. | on hold | |
| PRP-4 | Develop an implementation plan for coast wallflower that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | on hold | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| By 2022, Completed Coast Wallflower Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 6
Beginning in 2018, conduct annual surveys for San Diego button-celery in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
In 2017-2018, develop habitat suitability models for Quino checkerspot, host plants, and nectaring plants under current and future climate change scenarios, and conduct fire risk modeling with different management scenarios to identify potential climate and fire refugia. The results of this modeling will be used to inform development of monitoring and management plans.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Submit project metadata, modeling datasets, results and report to the MSP Web Portal. | In progress |
| Criteria | Deadline year |
|---|---|
| Quino Checkerspot Current and Future Climate Habitat Models and Report Completed in 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
Beginning in 2017, prepare a long-term Quino checkerspot metapopulation monitoring plan to track population distribution, abundance, and phenology, and to assess habitats and threats at checkerspot occurrences (see occurrence table), historically occupied and unoccupied high suitability sites across Conserved Lands in the MSPA. The monitoring plan should build upon previous surveys, habitat assessments and modeling to include specific monitoring questions, the sampling frame within the MSPA, monitoring methods, a statistically valid sampling design, sampling locations, timeline, and standardized protocols for determining the status and abundance of larval and adult butterflies and for assessing habitat and threats at each sampling site to determine management needs. The plan should stipulate that for each survey year, a report be prepared with site-specific management recommendations. The monitoring plan will be piloted with field surveys in 2018 to determine if adjustments need to be made and will be finalized in 2019 and then added to the final management plan in 2021 to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop the monitoring plan. | in progress | |
| PRP-2 | Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. | in progress | |
| PRP-3 | Submit project metadata, datasets and Quino Checkerspot Monitoring Plan to the MSP Web Portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Quino Checkerspot Metapopulation Monitoring Plan Completed in 2019 | 2019 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
In 2018 conduct pilot monitoring to evaluate monitoring methodology and sampling design and locations, and prepare recommendations for any adjustments to the monitoring plan. From 2019 to 2021, implement monitoring annually and submit data with management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring Implemented and Data with Recommendations Submitted Annually | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
In 2017-2018, develop a section for Quino checkerpot nectaring forbs and host plants in the MSP Seed Collection, Banking and Bulking Plan to enhance and restore habitat for the butterfly. The plan should incorporate best science and management practices (e.g., Wall 2009; KEW 2016) to provide guidelines for collecting and providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds to provide source material with consideration of potential genetic consequences; for management oriented research; seed bulking; and out-planting to augment extant occurrences or establish new occurrences of Quino checkerspot.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Quino checkerspot section in the MSP Seed Collection, Banking and Bulking Plan. | on hold | |
| PRP-2 | Design a seed collection plan to collect seeds over multiple years, collect seeds several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines from small occurrences (<1,000 plants) and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | waiting for precedent action | |
| PRP-3 | The seed collection plan should include guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest and based on genetic studies as available. Include provisions for collecting seed from unconserved populations planned for development. | waiting for precedent action | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | waiting for precedent action | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | waiting for precedent action | |
| PRP-6 | Submit project metadata and MSP Seed Collection, Banking and Bulking Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By end 2017, Completed Quino Checkerspot Section in MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
In 2018, begin implementing the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot to collect and store seeds to provide propagules as needed for management oriented research, existing population enhancement and establishment of new butterfly occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for butterfly habitat enhancement, expansion, and restoration projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2021, =1 Highest Priority Action Implemented for Quino checkerspot from the MSP Seed Collection, Banking, and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
In 2017, begin developing an interim 5 year Quino Checkerspot Management Plan that focuses on habitat enhancement and restoration and fire management, and includes the information from the MSP Seed Collection, Banking and Bulking Plan for Quino checkerspot, at known occupied and historically occupied sites. In 2021, update and finalize the management plan with results from the captive rearing and translocation projects and combine with the monitoring plan to create a comprehensive Quino Checkerspot Management and Monitoring Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop prioritized management actions. | waiting for precedent action | |
| PRP-2 | Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. | waiting for precedent action | |
| PRP-3 | Submit project metadata and management and monitoring plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Quino Checkerspot Management and Monitoring Plan Completed in 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
Beginning in 2018, implement highest priority management actions for Quino checkerspot on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the Quino Checkerspot Management Plan. | waiting for precedent action | Quino Habitat Restoration |
| IMP-2 | Submit project metadata and management data to MSP web portal | waiting for precedent action | Quino Habitat Restoration |
| Criteria | Deadline year |
|---|---|
| =1 Management actions implemented for Quino checkerspot by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
From 2018 to 2021, monitor the effectiveness of management actions implemented for Quino checkerspot on Conserved Lands
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, monitoring data and reports to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness Monitoring Completed within 1 Year of Management Actions | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
From 2017 to 2021, support existing efforts by the wildlife agencies to collect eggs and captive rear larvae to use in reestablishing and augmenting wild Quino checkerspot populations. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the captive rearing. | in progress | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Captive Rearing Implemented and Report Submitted by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
From 2017 to 2021, support existing efforts by the wildlife agenices to translocate captive bred Quino checkerspot larvae to historically occupied habitat.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the translocation project. | in progress | |
| IMP-1 | Support the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers, San Diego Zoo Global and other stakeholders to implement the translocation project. | in progress | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Translocation Implemented by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 3, 4, 6, 9
From 2017 to 2021, support efforts by the wildlife agencies to monitor the effectivenss of translocated captive bred Quinoo checkerspot larvae. Use results to finalize the Quino Checkerspot Management and Monitoring Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring data and reportto MSP web portal | in progress |
| Criteria | Deadline year |
|---|---|
| Translocation Monitoring Completed and Report Submitted by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Loss of ecological integrity | ECOINT |
| Urban development | URBDEV |
Management units: 1, 3, 6, 7
In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7
In 2021, inspect occurrences of coastal sage scrub MSP VF plant species (cliff spurge, Palmer's goldenbush, San Diego barrel cactus and snake cholla) on Conserved Lands using the regional IMG monitoring protocol to record abundance and collect habitat and threat covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | On hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2018, inspect Orcutt's hazardia occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs. After 2018, repeat monitoring every 2 years.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
Beginning in 2017, conduct routine management actions identified through 2016, 2018 and 2020 IMG monitoring of Orcutt's hazardia occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2017, begin preparing an Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should incorporate best science and management practices (Wall 2009, KEW 2016) and recommendations from the 2014 genetic study to provide guidance for collecting and storing seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's hazardia section in the MSP Seed Collection, Banking and Bulking Plan. | Available for implementation | |
| PRP-2 | Design the seed collection plan to include recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | Available for implementation | |
| PRP-3 | The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. | Available for implementation | |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | Available for implementation | |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | Available for implementation | |
| PRP-6 | Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | Available for implementation |
| Criteria | Deadline year |
|---|---|
| By 2018, Completed Orcutt's Hazardia Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2018, begin implementing high priority actions for Orcutt's hazardia in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2022, =1 Highest Priority Action Implemented for Orcutt's hazardia from the MSP Seed Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2017, begin preparing an Orcutt's hazardia section in the MSP Rare Plant Management Plan that prioritizes management actions to maintain or enhance occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, and other stakeholders to provide input and recommendations for the Orcutt's brodiaea section in the MSP Rare Plant Management Plan. | available for implementation | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to Orcutt's hazardia occurrences. | available for implementation | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | available for implementation | |
| PRP-4 | Develop an implementation plan for Orcutt's hazardia that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | available for implementation | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| By 2018, Completed Orcutt's Hazardia Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2018, begin implementing highest priority management actions identified for Orcutt's hazardia in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2022, =1 High Priority Management Action Implemented for Orcutt's Brodiaea from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 6, 7
In 2018, begin monitoring effectiveness of implementation of highest priority management actions identified in the Orcutt's hazardia section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7
In 2018, develop a long-term San Diego Black-tailed Jackrabbit Monitoring Plan to track their distribution and status, habitat associations and level of threats in coastal sage scrub and grassland vegetation communities across the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the jackrabbit and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Submit project metadata and San Diego Black-tailed Jackrabbit Monitoring Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| San Diego Black-tailed Jackrabbit Monitoring Plan completed in 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7
In 2019, begin implementing long-term San Diego black-tailed jackrabbit monitoring as specified in the San Diego Black-tailed Jackrabbit Monitoring Plan. Prepare a report detailing jackrabbit and habitat and threat assessment results and with site specific vegetation management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| San Diego Black-tailed Jackrabbit Monitoring and Report completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 4, 5, 8
If extant occurrences of heart-leaved pitcher sage are discovered on Conserved Lands in 2017-2021, inspect the occurrences and repeat monitoring every 2 years. Use a regional monitoring protocol to record population 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 | Rare Plant Inspect and Manage Monitoring 2014-2026 |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | Available for implementation | Rare Plant Inspect and Manage Monitoring 2014-2026 |
| Criteria | Deadline year |
|---|---|
| If Extant Occurrences Found on Conserved Lands, Surveys Completed Every 2 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 4, 5, 8
If heart-leaved pitcher sage occurrences are found on Conserved Lands, conduct routine management actions identified through the IMG monitoring. 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 less than 20% absolute cover. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| If Extant Occurrences Found on Conserved Lands, Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 2, 3, 4, 6, 10, 11
From 2017 to 2019, continue Hermes Copper translocation experiments begun in 2014 to test the effectiveness of releasing eggs and larvae to repopulate the Hollenbeck Canyon Wildlife Area (see Table of Occurrences) where the original population was extirpated by fire.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Continue releasing Hermes copper eggs at Hollenbeck Canyon Wildlife Area where the butterfly was extirpated in 2017, to see if translocation success can be improved under normal rainfall conditions. Nine of 14 larvae emerged in 2015 from translocated eggs and 1 adult was observed in 2016, despite the prolonged and intense drought. | In progress |
| Criteria | Deadline year |
|---|---|
| Hermes Copper Translocation Experiments Completed in 2019 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
From 2017 to 2021, continue monitoring the effectiveness of Hermes Copper translocation experiments begun in 2014 at Hollenbeck Canyon Wildlife Area (see Table of Occurrences). Extend the monitoring for 2 years after the last egg is translocated to determine whether a population has been established.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets, analyses and report with management recommendations to the MSP Web Portal. | In progress |
| Criteria | Deadline year |
|---|---|
| Hermes Copper Translocation Monitoring and Reports Completed Annually | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
In 2017, continue development of BMPs begun in 2013 for captive rearing Hermes Copper at the San Diego Zoo. Attempt to determine optimal conditions for rearing Hermes copper in captivity to provide a source of butterflies for translocations to re-establish populations at sites where the butterfly has been extirpated or to establish new populations in suitable habitat.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Submit project metadata, datasets, and report with management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Hermes Copper Captive Rearing Experiments and Report Completed by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
In 2017, complete a 5 year Hermes Copper Management Plan that includes the results from butterfly surveys and habitat assessments and genetic, marking and translocation studies to develop a management strategy and to identify and prioritize site specific management actions. The plan should employ the modeling results to identify potential fire and climate refugia that may be suitable sites for future translocations and provide specific recommendations for reducing fire risk at occurrences at highest risk.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Work with the Butterfly Working Group consisting of species experts, scientists, wildlife agencies, land managers and other stakeholders to develop prioritized management actions. | completed | |
| PRP-2 | Include fire risk and climate change modeling results to provide management recommendations in relation to fire and climate refugia and to reduce fire risk at occurrences. | completed | |
| PRP-3 | Submit project metadata and Herme's Copper Management Plant to the MSP Web Portal. | completed |
| Criteria | Deadline year |
|---|---|
| Hermes Copper Management Plan Completed in 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
In 2018, begin implementing high priority management actions from the Hermes Copper Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, management datasets, and report to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| By 2021, =1 High Priority Management Action Implemented from the Hermes Copper Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
Beginning in 2018, monitor effectiveness of implementation of highest priority management actions identified in the Hermes Copper Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined and Report Completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 4, 6, 10, 11
For at least the first 3 years following a wildfire, use a standardized survey protocol to determine the status of Hermes copper occurrences impacted by fire. Use a standardized postfire protocol to collect vegetation and other covariates important in characterizing Hermes copper habitat recovery following a fire. Postfire monitoring should include collecting habitat recovery data at unoccupied sites that are important for enhancing connectivity or for future population expansion. Identify and prioritize management actions to recover Hermes copper populations and important habitat patches.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Prepare and implement a postfire habitat monitoring protocol and sampling design to determine the status of Hermes copper and characterize coastal sage scrub, host plant (spiny redberry), and nectar plant (California buckwheat) recovery following wildfire. Use the monitoring results to identify management actions to facilitate postfire recovery of high quality habitat at occupied sites and at unoccupied sites important for Hermes copper population expansion and connectivity between occurrences. | On hold | |
| IMP-2 | Submit project metadata, Hermes copper 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 Hermes Copper and Habitats with Annual Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 2, 3, 4, 6, 10, 11
For at least the first 3 years following a fire, implement management actions identified by postfire monitoring as necessary to protect and rehabilitate high quality habitat to allow for recovery of Hermes copper occurrences impacted by wildfire.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Implement management actions to restore coastal sage scrub, host plants (spiny redberry) and nectaring plants (California buckwheat) at Hermes copper habitats destroyed by wildfire. These management actions may include planting host plants, nectaring plants, and controlling invasive plants to 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 Hermes Copper Habitats | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 4, 6
From 2017-2021, inspect willowy monardella occurrences annually on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| 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 Annually with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 4, 6
Beginning in 2017, conduct routine management actions identified through the annual IMG monitoring at willowy monardella occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species =20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 4, 6
In 2019, survey historic willowy monardella locations to determine occurrence status; survey and delineate potentially suitable habitat for new occurrences; survey existing occurrences to identify the potential for enhancement and expansion; and at all sites collect data on occurrence status, habitat and threats and determine management needs. Conduct a hydrological evaluation at each site to determine the current hydrology and risk to existing or potential occurrences from erosion and flooding. Prioritize all evaluated sites based on feasibility of maintaining a sustainable population over the long term and recommend management needed to reduce threats to existing and potential new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | At each extant occurrence, map the extent of the occurrence, collect data on abundance, map adjacent suitable habitat for potential occurrence expansion, collect covariate data on threats including estimates of cover of invasive non-native plants and trampling. | on hold | |
| SURV-2 | Submit project metadata, habitat mapping, and a report with site prioritizations and recommendations for management based upon occurrence status, habitat and threats assessments and hydrological evaluations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys and Report Completed by 2019 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 6
In 2020, begin preparing a section for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan that incorporates best science and management practices (Wall 2009, KEW 2016) to preserve genetic diversity and rescue occurrences in case of catastrophic disturbance. The plan should also include recommendations from the 2016-2017 genetic study and the 2019 baseline surveys and hydrological evaluation to guide collection and storage of seeds over the long term at a permanent, established conservation seed bank (e.g., Institute for Conservation Research Native Plant Seed Bank, Rancho Santa Ana Botanic Garden Seed Conservation Program) and for providing a source of seeds for management purposes. The plan should include recommendations for: collecting and storing seeds for conservation banking; management oriented research; rescuing occurrences after catastrophic disturbances; and seed bulking and out-planting to augment extant occurrences or to establish new occurrences with consideration of genetic implications for population sustainability.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, MCAS Miramar, and other stakeholders to provide input and recommendations for the willowy monardella section in the MSP Seed Collection, Banking and Bulking Plan. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-2 | Prepare the seed collection plan to incorporate genetic study results and with recommendations to collect seeds over multiple years and several times within a season, accumulate seeds across populations, and to sample among habitats and ecological niches. Include guidelines for collecting and storing seeds along maternal lines and to provide propagules to be used in management experiments, enhancement of existing occurrences, and establishment of new occurrences. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-3 | The seed collection plan should have guidelines for collecting seeds from occurrences of sufficient size to accommodate harvest. Include provisions for collecting seed from unconserved populations planned for development. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-4 | Include protocols and guidelines for collecting voucher specimens and submitting to the San Diego Natural History Museum (McEachern et al. 2007). | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-5 | Include guidelines for testing seeds for viability and to obtain information on dormancy and germination rates. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| PRP-6 | Submit project metadata and the MSP Seed Collection, Banking and Bulking Plan to MSP Web Portal. | some occurrences are in progress | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2020, Completed Willowy Monardella Section in the MSP Seed Collection, Banking and Bulking Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 6
In 2021, begin implementing high priority actions for willowy monardella in the MSP Seed Collection, Banking and Bulking Plan to collect and store seeds at a permanent seed bank and to provide propagules as needed for management oriented research, existing population enhancement and establishment of new occurrences.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Bulk seed at a qualified facility for enhancement, expansion, establishment or transplantation projects using seed from genetically appropriate donor accessions in the propagation seed bank collection. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| IMP-2 | Maintain records for collected seed to document donor and receptor sites, collection dates and amounts. Submit seed collection, storage and bulking data to the MSP Web Portal. | waiting for precedent action | California Plant Rescue (CaPR) - San Diego Zoo Wildlife Alliance's Native Plant Seed Bank |
| Criteria | Deadline year |
|---|---|
| By 2024, =2 Seed Collection, Banking and Bulking Action Completed for Willowy Monardella | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 6
In 2020, begin preparing a section for willowy monardella in the MSP Rare Plant Management Plan that prioritizes management actions to maintain the large occurrence and enhance at least 4 small occurrences on Conserved Lands (see occurrence table) based upon an assessment of data on occurrence status, habitat and threats. Prepare prioritized management recommendations to re-establish historic occurrences or new occurrences in suitable habitat, if determined to be necessary for gene flow and to maintain self sustaining populations for the long term persistence of the species in the MSPA. Minimum criteria for enhancement are to reduce invasive annual nonnative plants and thatch to less than 20% absolute cover within the occurrence.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Consult the San Diego County Rare Plant Working Group made up of plant ecologists, geneticists, rare plant experts, land managers, restoration practitioners, seed banking and bulking practitioners, wildlife agencies, MCAS Miramar, and other stakeholders to provide input and recommendations for the willowy monardella section in the MSP Rare Plant Management Plan. | waiting for precedent action | |
| PRP-2 | Develop a conceptual model that identifies management actions to effectively reduce threats to willowy monardella occurrences. | waiting for precedent action | |
| PRP-3 | Prioritize occurrences for management based upon an assessment of occurrence status, the potential for management to significantly reduce identified threats, and the availability of adjacent suitable habitat for occurrence expansion. | waiting for precedent action | |
| PRP-4 | Develop an implementation plan for willowy monardella that prioritizes management actions for the next 5 years and details tasks, lead entities, responsibilities, and timelines, budgets. | waiting for precedent action | |
| PRP-5 | Submit project metadata and MSP Rare Plant Management Plan to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2020, Completed Willowy Monardella Section in MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 6
In 2021, begin implementing highest priority management actions identified for willowy monardella in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management datasets, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| By 2024, =2 High Priority Management Action Implemented for Willowy Monardella from the MSP Rare Plant Management Plan | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 6
In 2021, monitor effectiveness of implementation of highest priority management actions identified in the willowy monardella section in the MSP Rare Plant Management Plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, management effectiveness datasets, analyses, and report to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Effectiveness of High Priority Management Actions Determined | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 2, 3, 6
Beginning in 2018, conduct annual surveys for spreading navarretia in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 4, 5
In 2020, inspect chaparral nolina occurrence(s) 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.
| 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-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, occurrence status, habitat and threats data, and management recommendations to the MSP Web Portal. |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2020 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 4, 5
Beginning in 2020, conduct routine management actions as identified through the 2016 and subsequent IMG monitoring at chaparral nolina 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 routine management activities such as protecting occurrences from disturbance through enforcement and controlling invasive non-native plant species. | on hold | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 3
Beginning in 2018, conduct annual surveys for California Orcutt grass in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4
Beginning in 2018, inspect Gander's ragwort occurrences on Conserved Lands (see occurrence table) every 3 years using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Modify IMG protocol to improve mapping and estimating abundance of large occurrences with difficult to delineate boundaries. In 2018 focus on mapping occurrence boundaries. | on hold | |
| IMP-3 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Every 3 Years with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 3, 4
Beginning in 2017, conduct routine management actions identified through the IMG monitoring in 2016 and subsequent years at Gander's ragwort 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 less than 20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management datasets to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 1, 7
In 2021, develop a long-term Wandering Skipper Monitoring Plan to track their distribution and status, habitat associations and level of threats in salt marsh vegetation on Conserved Lands in the MSPA. The plan should integrate with the Salt Marsh Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the butterfly and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Submit project metadata and Wandering Skipper Monitoring Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Wandering Skipper Monitoring Plan completed by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 7
In 2019, develop a regional, long-term monitoring plan to integrate habitat assessment and threat evaluations into the Belding's savannah sparrow population monitoring conducted by the California Department of Fish and Wildlife on Conserved Lands in the MSPA. Develop a sampling design and standardized protocol to assess habitat and threats at occupied, historically occupied and suitable unoccupied habitats for the sparrow. Design the habitat and threats assessment to inform regional salt marsh vegetation monitoring. The purpose of the plan is to use habitat and threat monitoring data to develop site specific management recommendations to maintain, enhance or restore Belding's savannah sparrow habitat.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Coordinate with the California Department of Fish and Wildlife, U.S. Fish and Wildlife Service, scientists and land managers to develop a habitat and threats assessment monitoring protocol to integrate into ongoing regional Belding's savannah sparrow population monitoring. | On hold | |
| PRP-2 | Submit project metadata and Belding's Savannah Sparrow Habitat and Threat Assessment Monitoring Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Belding's Savannah Sparrow Habitat and Threat Assessment Monitoring Plan completed by 2019 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 7
In 2020 or 2021, depending on timing of Belding's savannah sparrow population monitoring implemented by the California Department of Fish and Wildlife, conduct habitat and threats assessment as specified in the Belding's Savannah Sparrow Habitat and Threat and Assessment Monitoring Plan and in conjunction with sparrow population monitoring on Conserved Lands in the MSPA.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Belding's Savannah Sparrow Habitat and Threat Monitoring and Report completed by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2018, develop a long-term Blainville's Horned Lizard Monitoring Plan to track their distribution and status, habitat associations and level of threats in chaparral, coastal sage scrub and grassland vegetation communities across Conserved Lands in the MSPA. The plan should integrate with the Chaparral, Coastal Sage Scrub and Grassland Vegetation Monitoring Plan to include sampling at long-term vegetation monitoring plots. The monitoring plan should build upon previous surveys, habitat assessments and modeling to develop specific questions, monitoring methods, a statistically valid sampling design, sampling locations, and standardized protocols for determining the status and abundance of the lizard and for assessing habitat and threats at each sampling site to determine vegetation management needs. The plan should include guidelines for data analysis and preparation of a report with monitoring results and vegetation management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Submit project metadata and Blainville's Horned Lizard Monitoring Plan to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Blainville's Horned Lizard Monitoring Plan completed in 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2019, begin implementing long term Blainville's horned lizard monitoring as specified in the Blainville's Horned Lizard Monitoring Plan. Prepare a report detailing lizard and habitat and threat assessment results and with site specific vegetation management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, datasets, analyses and monitoring report with management recommendations to the MSP Web Portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Blainville's Horned Lizard Monitoring and Report completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Human uses of the Preserves | HUMUSE |
| Invasive animals | INVANI |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2017-2018, finalize the results of research begun in 2015 on Townsend's big-eared bat to identify nocturnal, diurnal, and maternity roosts, foraging areas, and water sources associated with roosts in order to identify seasonal and annual changes in use and important foraging areas and monitor reproductive status. Collect habitat covariates associated with roosting and foraging habitat and assess threats to bats at all preserves where they occur and develop management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Submit project metadata, survey data, and report with management recommendations to the MSP web portal. | In progress |
| Criteria | Deadline year |
|---|---|
| Townsend's Big-Eared Bat Surveys and Reports Completed in 2018. | 2018 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, annually inspect the vicinity of Townsend's big-eared bat roosts on an annual basis (see Table of Occurrences), taking care not to disturb bats, and use a regional monitoring protocol to collect covariate data on human activities and other threats to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol surveys to quantify signs of human activity near occupied or potential roosts and to identify other potential threats. Care should be taken to avoid disturbing roosting bats. | In progress | |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | Unknown | |
| IMP-3 | Submit monitoring data and management recommendations to the MSP web portal. | Unknown |
| Criteria | Deadline year |
|---|---|
| Annual monitoring of Townsend's big-eared bat completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2017, perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement. | Available for implementation | |
| IMP-2 | Submit project metadata and management data to MSP web portal | Unknown |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
In 2018-2019, prepare a management plan for Townsend's big-eared bat that prioritizes management actions to protect roosts from disturbance, ensures sufficient roosts for seasonal temperature requirements and for reproduction, and enhances foraging habitat using data from annual roost monitoring and recommendations from the Townsend's big-eared bat research study.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | available for implementation | |
| PRP-2 | Identify areas where Townsends big-eared bat and pallid bat management can be complimentary. | available for implementation | |
| PRP-3 | Develop a plan for Townsends big-eared bat that prioritizes management actions for the next five years and details tasks, lead entities, responsibilities, and timelines, budgets. | available for implementation | |
| PRP-4 | Submit management plan to MSP web portal | available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Plan for Townsend's big-eared bat prepared by 2018 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2020, implement highest priority management actions for Townsend
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the implementation plan. | waiting for precedent action | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions implemented for Townsend's big-eared bat | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11
Beginning in 2020, monitor the effectiveness of management actions implemented for Townsend's big-eared bats on Conserved Lands
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit metadata, monitoring data and reports to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring data submitted to MSP web portal within one year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 6
Beginning in 2018, conduct annual surveys for San Diego mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3
Beginning in 2018, conduct annual surveys for Otay mesa mint in occupied, historically occupied and potentially suitable vernal pools to determine cover clases in each basin and cover of each nonnative species using a standardize protocol as defined in the VPMMP (City of San Diego 2015). Nonnative cover classes will be combined to determine if management triggers for Level 1, 2 or 3 management are met. Management recommendations will be made, noting individual nonnative species that pose a threat to direct specific management actions. Management actions will be implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8
In 2020, implement regional and subregional California gnatcatcher monitoring initiated in 2016 to determine the percent area occupied (PAO) by California gnatcatcher in modeled high and very high suitability habitat on Conserved Lands and military lands in the MSPA as part of a larger monitoring program for southern California. Over the next 15 years, determine trends in California gnatcatcher PAO and in their colonization and extinction rates and be able to detect at least 30% change in PAO. Identify associations between habitat and threat correlates with gnatcatcher PAO and with extinction and colonization rates and develop biologically meaningful thresholds for management and to specify management criteria and recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | When the results of the 2016 California gnatcatcher surveys become available, coordinate with the regional California gnatcatcher survey group made up of wildlife agencies, land managers and scientists, to determine when the next round of regional surveys should be implemented. It is anticipated that the surveys are likely to be held in 2020. Based on the monitoring results and group recommendations, adjust the habitat model and sampling frame as necessary to better predict suitable habitat in the northern extent of the range. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets, analyses and reports to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Regional and Subregional California Gnatcatcher Surveys completed and report submitted by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 7, 8
In 2020, implement California gnatcatcher postfire monitoring conducted in 2015 and 2015 to: determine whether there has been further recovery of California gnatcatchers in areas burned in 2003, 2007 and 2014 (i.e., PAO>10%); evaluate if there is a difference in PAO between areas burned in 2003, 2007 and 2014; investigate the relationship between gnatcatcher PAO and vegetation composition, cover and structure; and evaluate the composition, cover and structure of coastal sage scrub in areas with different fire frequencies and patterns of vegetation recovery based upon time since fire, spatial distribution, previous land use, and environmental conditions. Use the regional gnatcatcher and vegetation monitoring protocols to monitor postfire recovery of gnatcatchers and vegetation at sampling points surveyed in 2016. Analyze gnatcatcher and vegetation data to develop overall and site specific vegetation management recommendations for postfire recovery of coastal sage scrub vegetation to support California gnatcatchers.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Submit project metadata, monitoring datasets, analyses and reports to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Postfire California Gnatcatcher Surveys completed and report submitted by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered fire regime | ALTFIR |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 4, 5, 8, 9, 10
In 2017, finalize efforts begun in 2016, using available regional mountain lion movement data, to develop quantitative models of mountain lion movement in the MSPA to validate likely movement patterns and to assist with linkage and land protection prioritization.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| RES-1 | Project metadata, data, and report submitted to MSP web portal | completed | Mountain Lion Connectivity and Genetics Study- North San Diego County, Mountain Lion Critical Linkage Evaluation in MSPA |
| Criteria | Deadline year |
|---|---|
| Mountain lion connectivity model completed by 2017 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
In 2017-2018, guided by information from telemetry studies and mountain lion movement modelling, prioritize potential mountain lion crossing locations for SR 78, SR 76, SR 79, I-15, and other priority roads. For each priority crossing location, conduct detailed linkage assessments to identify existing impediments to successful crossings and recommendations for wildlife crossing infrastructure improvement (culvert maintenance, undercrossing construction, fencing, etc.) and habitat/land protection needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| EVAL-1 | Use telemetry and modelling data to inform important wildlife crossing locations along SR 78, SR 76 and SR 79 where follow up surveys will be conducted to identify specific locations and recommendations for wildlife crossing infrastructure improvements. | in progress | Mountain Lion Connectivity and Genetics Study- North San Diego County |
| EVAL-2 | At each location, detailed field assessments will be performed to identify existing impediments to successful crossings, specific recommendations for wildlife crossing infrastructure improvements, and land protection needs in the area defined in order to provide for long term successful connectivity between protected lands for mountain lions and other wildlife. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| EVAL-3 | Project metadata, data, and reports submitted to MSP web portal. | in progress | Mountain Lion Connectivity and Genetics Study- North San Diego County |
| Criteria | Deadline year |
|---|---|
| By 2019, linkage evaluations completed for mountain lion crossing locations for SR 76, SR 79, SR 78 and other priority roads | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2017 and based on linkage assessment results, prepare Linkage Implementation Plan that outlines specific locations and recommendations for improving mountain lion and deer connectivity across SR 78, 76, 79 and other priority roads in MU s 5, 8, 9, and 10.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Linkage Implementation Plans will identify the locations and design criteria for needed wildlife crossing infrastructure for priority roads and highways in MUs 5, 8, 9, and 10, including locations for road under/overcrossings and barrier fences to funnel lions and other wildlife to crossing locations for priority highways and roads | waiting for precedent action | |
| PRP-2 | Submit data and reports to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Mountain lion and deer linkage implementation plan completed for MU 5, 8, 9 and 10 by 2019 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2019, implement linkage enhancement actions outlined in linkage evaluations and linkage implementation plans
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | As funding becomes available, implement priority wildlife crossing improvements for MU 5, 8, 9, 10 and other priority roads. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions to improve connectivity for mountain lions and deer implemented | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2019, monitor implementation and effectiveness of linkage enhancements actions for mountain lions and other species, including mule deer.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit Metadata, data, and report to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring data submitted to MSP web portal within one year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2017, support efforts by UC Davis Wildlife Health Center and others to test the effectiveness of various methods to deter mountain lions and other native predators from preying on livestock/domestic animals in locations where depredation permits have been issued in recent past, with the goal of reducing depredation permits by 50%.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Research existing predator deterrent systems for their applicability to southern California wildlife communities. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| DEV-2 | Implement quantitative pilot study to evaluate effectiveness of various methods in deterring native predators from taking livestock. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| DEV-3 | From these studies, establish a set of "Best Practices" for protecting livestock from native predators. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| DEV-4 | Support efforts in the development of outreach materials to livestock owners on proper husbandry and native predator deterrence techniques to protect livestock from native predators. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| DEV-5 | Submit project metadata, data, and BMPs to MSP web portal. | in progress | Mountain Lion Road Crossing and Deterrent Methods Evaluations |
| Criteria | Deadline year |
|---|---|
| Best Practices for Reducing native predator take of domestic livestock developed and disseminated to landowners. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2019, implement Best Management Practices for deterring mountain lions and other predators from preying on livestock/domestic animals with the goal of reducing depredation permits by 50%.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit Metadata, data, and management actions to MSP web portal. | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| BMPs implemented to reduce mountain lion predation on domestic animals | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 5, 8, 9, 10
Beginning in 2019, monitor the effectiveness of BMPs implemented to deter mountain lions and other predators from preying on livestock/domestic animals.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| DEV-1 | Implement field studies to assess effectiveness of BMPs in reducing livestock predation by mountain lions and other native predators | Unknown | |
| DEV-2 | Monitor rate of depredation permits to evaluate if BMPs are having desired effect on reducing lion mortalities. | Unknown | |
| DEV-3 | Submit project metadata, monitoring data and results to MSP web portal. | Unknown |
| Criteria | Deadline year |
|---|---|
| Monitoring effectiveness of BMPs implemented within one year of management actions | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 3, 4, 5, 8, 9, 10
In 2020, develop a long-term monitoring strategy that integrates BMPs to document mountain lion population, connectivity and distribution within the MSPA. Monitoring plan will incorporate, as feasible: 1) possible non invasive methods for monitoring genetic connectivity (scat, hair snares, tracks, etc.), 2) methods for integrating camera trap data from various sources to answer questions regarding lion movement and distribution, and 3) a regional database to track information on lion mortalities and cause (vehicle strikes, depredation permits, illegal take, etc.) to identify problem areas and to inform management actions.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Work with UCD to evaluate the feasibility of various mountain lion DNA testing methods (scat, hair snare, etc.) for use in future long term monitoring of genetic connectivity | Unknown | |
| PRP-2 | Identify and collate data from various relevant camera trap studies (SDTT, UCD-WHC, USGS, Feral Pig Study, land managers) and evaluate how data could be integrated as part of a long term monitoring strategy for documenting mountain lion movement and distribution within the MSPA. | Unknown | |
| PRP-3 | Identify existing sources for lion mortality data, conduct outreach, and work to develop a system for collating and integrating lion mortality data from various sources into the MSP Database. | Unknown |
| Criteria | Deadline year |
|---|---|
| Monitoring plan for documenting mountain lion connectivity are developed and integrated with available track and camera data from other sources to identify the level of | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 3, 4, 5, 8, 9, 10
In 2021, implement monitoring actions as identified in the Mountain lion monitoring plan.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, data, and reports to MSP web portal | Unknown |
| Criteria | Deadline year |
|---|---|
| Monitoring program for mountain lions implemented by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Loss of connectivity | LOSCON |
| Urban development | URBDEV |
Management units: 1, 7
From 2017 to 2021, continue the existing captive rearing and release efforts for Rideway's rail implememted by the wildlife agencies.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Implement management actions specified by the wildlife agencies for recovery of light-footed Ridgway's rail. | in progress |
| Criteria | Deadline year |
|---|---|
| Wildlife Agency specified management actions completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 7
From 2017 to 2021, annually inspect the existing occurrences of Ridgway's rail to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. | available for implementation | |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | available for implementation | |
| IMP-3 | Submit monitoring data and management recommendations to MSP web portal | available for implementation |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with management recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 1, 7
From 2017-2021, perform routine management activities such as protecting occurrences from disturbance through fencing, signage, and enforcement.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. | available for implementation | |
| IMP-2 | Submit project metadata and management data to MSP web portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Urban development | URBDEV |
Management units: 3
In 2021, inspect small-leaved rose occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2021 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 3
Beginning in 2017, conduct routine management actions as identified through the IMG monitoring conducted in 2016 and 2021 at the small-leaved rose 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 to less than 20% absolute cover. | on hold | |
| 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 to less than 20% absolute cover. | available for implementation | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | on hold | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | available for implementation |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 2, 3, 4, 5, 6
Beginning in 2018, conduct annual surveys for western spadefoot in vernal pools to determine distribution and status and to assess habitat conditions and threats. Management recommendations will be made and implemented annually as part of the general vernal pool habitat management objectives for different management levels (ML1, ML2, ML3).
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Annual Surveys Completed with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 7
From 2017-2021, annually conduct predator control at breeding least tern colonies before and during the nesting season to improve fledgling success. Include tracking of predator-tern interactions to provide real-time data to improve control efforts during the breeding season.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct predator control prior to breeding and during the breeding season to control the various taxa (e.g. mammals, reptiles, birds, inverebrates) that prey on adult, nestling, and fledgling least terns. | in progress | |
| IMP-2 | Submit data and reports to MSP web portal. | in progress |
| Criteria | Deadline year |
|---|---|
| Predator Control Implemented and Reports Completed Annually | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
From 2017-2021, monitor the effectiveness of predator control at least tern colonies and monitor overall tern predator status and trend to identify larger issues potentially affecting other MSP species and to improve management effectiveness.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal | available for implementation |
| Criteria | Deadline year |
|---|---|
| Monitoring completed and data and report submitted within 1 year of management actions being completed. | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
From 2017 to 2021, continue the existing survey efforts for California least tern implemented by the wildlife agencies and military.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | Submit monitoring data and management recommendations to MSP web portal | In progress |
| Criteria | Deadline year |
|---|---|
| Least Tern Surveys and Reports Completed Annually | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
From 2017 to 2021, annually inspect the existing nest sites for California least tern, taking precautions to avoid disturbance during the nesting season, to identify necessary management actions in order to support the expansion of the occurrence to self sustaining levels.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Conduct regional IMG monitoring protocol survey locations and habitat, assess status, and quantify potential threats. | Available for implementation | |
| IMP-2 | Based upon threat evaluation, determine if routine management or more intensive management is warranted. | Available for implementation | |
| IMP-3 | Submit monitoring data and management recommendations to MSP web portal | Available for implementation |
| Criteria | Deadline year |
|---|---|
| Surveys Completed Annually with management recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 7
From 2017-2021, perform routine management activities such as invasives removal, sand replenishment, nest prep, and protecting occurrences from disturbance through fencing, signage, and enforcement.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform management activities protecting occurrences from disturbance through fencing, signage, and enforcement. | Available for implementation | Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern |
| IMP-2 | Submit project metadata and management data to MSP web portal. | Available for implementation | Adaptive Management of Coastal Sand Dunes in Mission Bay to Benefit Native Plants and the CA Least Tern |
| Criteria | Deadline year |
|---|---|
| Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Climate change | CLICHN |
| Herbivory/predation | |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 3
Beginning in 2018, conduct annual qualitative surveys during the wet season to determine the presence of Riverside 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 Riverside 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 Riverside Fairy Shrimp and Quantitative Cyst Sampling Every 3 Years with Reports Completed | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
Management units: 3, 8
In 2019, inspect Parry's tetracoccus occurrences on Conserved Lands (see occurrence table) using the regional rare plant IMG monitoring protocol to record abundance and collect habitat and threats covariate data to determine management needs.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Based upon occurrence status and threats, determine management needs including whether routine management or more intensive management is warranted. | on hold | |
| IMP-2 | Submit project metadata, monitoring datasets and management recommendations to the MSP Web Portal. | on hold |
| Criteria | Deadline year |
|---|---|
| Surveys Completed in 2019 with Management Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 3, 8
Beginning in 2020, conduct routine management actions identified through the 2019 IMG monitoring at Parry's tetracoccus occurrences on Conserved Lands (see occurrence table). Depending on the type and level of threat, management should be conducted as needed, not necessarily every year, and using BMPs with precautions to do no harm.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Perform routine management activities such as protecting occurrences from disturbance through fencing and enforcement and controlling invasive non-native plant species to less than 20% absolute cover. | On hold | |
| IMP-2 | Submit project metadata and management data to the MSP Web Portal. | On hold |
| Criteria | Deadline year |
|---|---|
| Routine Management Completed as Needed Based Upon Monitoring Recommendations | 2021 |
| Threat Name | Threat Code |
|---|---|
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Urban development | URBDEV |
Management units: 1, 6, 8
In 2017-2019, conduct surveys for least Bell's vireo and habitat assessment to compare population status and recovery in the MSPA before, during, and after SHB/Fusarium complex in infested habitat over time at the Tijuana River Valley and other sites, if funding available, such as Camp Pendelton and San Luis Rey River. Prepare site-specific management recommendations based on survey results and habitat assessments.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| SURV-1 | Submit monitoring data and management recommendations to MSP web portal | In progress |
| Criteria | Deadline year |
|---|---|
| Least Bell's Vireo Surveys and Reports Completed by 2020 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11
In 2020, if least Bell's vireo survey results indicate management is needed to reduce impacts from SHB/Fusarium infestation, then develop a management plan that incorporate SHB/Fusarium monitoring and management and prioriotize management recommendations.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| PRP-1 | Prioritize management actions, focusing on reducing threats and expanding occurrences in areas most likely to remain viable over the long-term in the context of future land development. | waiting for precedent action | |
| PRP-2 | Develop a management plan for least Bell's vireo that prioritizes management actions for the next five years. | waiting for precedent action | |
| PRP-3 | Submit management plan to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management Plan for Least Bell's Vireo Completed by 2021 | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11
Beginning in 2021, implement the highest priority management actions for least Bell's vireo on Conserved Lands.
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Management actions to be determined by the management plan. | waiting for precedent action | |
| IMP-2 | Submit project data and management actions to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Management actions implemented for Least Bell's Vireo | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
Management units: 1, 2, 3, 4, 5, 6, 8, 10, 11
Beginning in 2021, monitor the effectiveness of management actions implemented for least Bell's vireo on Conserved Lands
| Action | Statement | Action status | Projects |
|---|---|---|---|
| IMP-1 | Submit monitoring data and reports to MSP web portal | waiting for precedent action |
| Criteria | Deadline year |
|---|---|
| Monitoring completed and data and report submitted within 1 year of management actions | 2021 |
| Threat Name | Threat Code |
|---|---|
| Altered hydrology | ALTHYD |
| Climate change | CLICHN |
| Human uses of the Preserves | HUMUSE |
| Invasive plants | INVPLA |
| Parasitism/disease | |
| Urban development | URBDEV |
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Anstine-Audubon Nature Preserve Fencing Project
The goal of this project was to install 855 linear feet of lodge pole fencing along the northern boundary of San Diego Audubon Society’s (SDAS’s) 11.6-acre Anstine-Audubon Nature Preserve (Anstine) in Vista, CA to combat hazardous and non-hazardous dumping and illegal trespassing. The addition of fencing along the northern portion of the property, adjacent to Hidden Lake Lane, will protect the fragile riparian, oak woodland, and endangered coastal sage scrub habitats on the preserve. Urban Corps of San Diego, with SDAS oversight, successfully installed an 855-foot long, five-foot high lodge pole wooden fence along with three access gates on the property in the planned one-year project.
Project Start Date: March 7, 2023
Project Completion Date: January 18, 2024
This project was fully funded by SANDAG TransNet EMP Land Management Grant #S1125499
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Bat Community Monitoring 2002-2019
We compiled bat survey data from sampling sites throughout San Diego County in southern California from 2002-2019. Survey methods included ANABAT bat detectors, the unaided ear, day roost surveys and exit counts, and night roost surveys. All surveys were led by or included D. Stokes. Surveys were conducted with permission from private landowners and public land managers in areas where species were historically known or had the potential to occur based on habitat preferences. The study area in which surveys were conducted, San Diego County, spans a wide array of habitat types, including woodland, forest, coastal sage scrub, chaparral, and desert habitats, and apart from the desert, is generally characterized by a moderate Mediterranean climate. Elevation across San Diego County ranges from sea level along the coast to nearly 2,000 m in the mountains.
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Carlsbad Wildlife Movement Analysis
A study of wildlife movement within the Carlsbad's NCCP plan, known as the Habitat Management Plan (HMP). The HMP is the only approved subarea plan of the sub regional Multiple Habitat Conservation Plan (MHCP). A key objective of the HMP is to maintain functional wildlife corridors and habitat linkages within the city and to the region. An inventory of possible wildlife movement corridors and constraints, and an initial monitoring of key locations, is necessary to provide a baseline assessment of animal movement within the city and to begin evaluating the MHCP and HMP objectives. This Wildlife Movement Analysis Final Report is a summary of the methods and results of an inventory of potential wildlife movement corridors and pinch points within the City of Carlsbad.
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Coastal Cactus Wren Conservation Network
The Coastal Cactus Wren Conservation Network is an ad hoc group of more than 100 individuals representing research institutions, land management agencies, local government, non-profit conservation organizations and wildlife agencies. Members work together to exchange research and management information to develop best practices, policies, and programs that promote conservation and recovery of this bird throughout its range (Ventura, Los Angeles, San Bernardino, Orange, Riverside, and San Diego counties). This information will inform publication of a regional conservation strategy for the coastal cactus wren.
Cactus wrens (Campylorhynchus brunneicapillus) are distributed across the arid regions of the southwestern United States and northern and central Mexico (Hamilton et al. 2011). While the desert populations are fairly abundant, populations of coastal cactus wrens have declined dramatically over the past 30 years, with extirpation and genetic isolation affecting many locations as a result of habitat loss, habitat fragmentation, edge effects of development, and catastrophic fires (Solek and Szijj 2004). The coastal population is unique in that it occurs exclusively within the coastal sage scrub plant community, ranging from Ventura County south into San Diego County, U.S.A. and northwestern Baja California, Mexico. The firestorms of 2007 impacted several strongholds for the coastal cactus wren in Orange and San Diego counties. The significant loss of habitat and birds was the impetus for formation of the Coastal Cactus Wren Network.
For more information on the Coastal Cactus Wren Conservation Network, please see the document titled &quot;Coastal Cactus Wren Working Group Regional Goals, Objectives, and Strategies&quot;.
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Furby-North Preserve Unauthorized Control Project
Currently there are multiple unauthorized trails on the Property. The Property is surrounded on all sides by heavy urbanization, and local residents frequently hike through using the northern access road or unauthorized trails. Off-road vehicle use, specifically motorcycles, is also a problem within the Property. Failure to control access to the unauthorized trails on the Property will cause further loss of on-site sensitive vegetation communities including maritime succulent scrub, Diego coastal sage scrub and vernal pools. In addition, special status species observed on-site including the coastal California gnatcatcher and coastal cactus wren could be affected by unauthorized use of the Property. This one-year project will add signage, fencing, and gates on the Property to prevent unauthorized access into and across the Property and allow for future active restoration of the unauthorized trails as outlined in the Resource Management Plan. The County will coordinate with the SANDAG enforcement program to increase patrols and enforce County regulations on the Property once signs are intellect, The County also will coordinate with Earth Discovery Institute to develop a public outreach program with the San Ysidro School District,including, but not limited to, the distribution of flyers discussing general ecology using the proposed project as an example of how good stewardship results in positive biological changes The message will encourage school children to participate in the conservation effort of their local flora and fauna and thus reduce trespassing across the Property. The County will provide on-site monitoring during installation and post-installation of fencing, gates, and signs to document the effectiveness.
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Golden Eagle (Aquila chrysaetos) Monitoring and Management Plan
Golden eagles (Aquila chrysaetos) face many threats in southern California. To reduce these threats and successfully conserve this species in western San Diego County, MSP Roadmap 2021-2026 objectives include the development and implementation of a Management Strategic Plan for Golden Eagles in San Diego County and a Monitoring Strategic Plan for Golden Eagles in San Diego County. These plans include general sections with background information and rationale for prioritizing and developing monitoring and management recommendations. Previously, the U.S. Geological Survey (USGS) in collaboration with local, State, and other Federal agencies has conducted a multi-year research study of golden eagles to address questions regarding habitat use, movement behavior, nest occupancy, genetic population structure, and human impacts on eagles. From 2016-17, occupancy analyses were conducted and it was concluded that estimates of occupancy were greatest at sample sites with more rugged terrain conditions, lower human development, and lower amounts of scrubland vegetation cover (Weins et al. 2022). Tracking data from the last 10 years in the Western Unites States have shown eagles exhibit long-distance, nonroutine movements that were responsive to the updraft potential of the spatial and temporal landscape they encountered (Poessel et al. 2022). For the development of both Plans, chapters will be shaped based on the latest scientific information regarding occupancy, natal nesting success, juvenile dispersal, movement and biotelemetry, home range estimation, habitat use, and prey availability. Site-based threats assessment will be used to determine the best management practices. These plans are developed with input and guidance provided by the San Diego Golden Eagle working group, which includes include landowners and managers, scientists, species experts, and representatives from non-profit organizations, government, and wildlife agencies. Occurrence-specific management recommendations will be based on working group input and multiple years of data on Golden Eagle population status, habitat associations, and threats. These are living documents as the plans will be updated when new information becomes available or management actions are completed, and new recommendations are needed.
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Harbison's Dun Skipper Surveys and Monitoring
SANDAG-funded surveys for Harbison's dun skipper adults were conducted to assess year to year variation in population size. Field visits were used to document use including plants used for nectar sources, as well as obtain non-lethal genetic samples. A rapid habitat assessment was conducted at each site which included general woodland tree species composition, condition of San Diego sedge plants, and recording potential threats to the Harbison's dun skipper.
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Hodges Reservoir-Bernardo Bay Cactus Wren Habitat Restoration Grant Project
This project restored habitat for the California Species of Special Concern, the coastal cactus wren (Campylorhynchus brunneicapillus), near the Hodges Reservoir-Bernardo Bay. This included a 20 acre restoration of cactus burned in the 2007 Witch Creek Fire. Additionally, unauthorized trails were closed off and the soil was stabilized to minimize erosion and filter runoff into source water reservoir. The purpose of this restoration project was to re-establish cactus wren habitat and connectivity to eastern core habitat areas.
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Human impact to vernal pool complexes in Southern California
The flagship species for San Diego County's vernal pools is the federally endangered San Diego fairy shrimp (Branchinecta sandiegonensis: SDFS). For this species, the most critical
management issues are likely to involve population connectivity. Degradation of the landscape, direct damage (often by vehicles), creation of new basins (most often road ruts) and increasing biotic connectivity (beyond historic levels) are also important factors. The specific goals of this study were focused in three areas: landscape genetics in the San Diego fairy shrimp B. sandiegonensis; hybridization between B. sandiegonensis and B. lindahli; and conservation, management and recovery of B. sandiegonensis. This was a project jointly funded by SANDAG and a CDFW Section 6 grant.
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MSCP Wildlife Corridor Monitoring
A CBI study evaluating several MSCP habitat linkages and corridors critical to regional wildlife movement in the MSCP preserve. The study evaluated the functionality of the linkages, the large mammals and mesopredators using the linkages, constraints to animal movement, and underpass function.
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Ocean Beach Estuary Enhancement Project
The project includes efforts to reduce threats to SO and SL species in the San Diego River estuary and allow human recreational use to coexist with high-quality habitat. The San Diego River estuary contains biologically valuable salt marsh and coastal dune habitats, which are increasingly rare in the region. Several SO and SL species occur in this project area including: salt marsh bird's beak, Nuttall's acmispon, western snowy plover, light-footed Ridgway's rail, and California least tern. The project will utilize management actions to minimize threats and encourage responsible human recreation including: improving access control through physical barriers to reduce threats of trampling, trash and illegal use, managing invasive weeds and planting native species to encourage pollinators of target native plant species, increasing community awareness through community education, and facilitating community investment with hands-on, meaningful volunteer projects, docent-led programs, and outreach, and growing a robust stewardship program to augment limited staff capacity for long-term maintenance of habitat and improvements.
This project is partially funded by SANDAG TransNet EMP Land Management Grant #S1125510
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Open Space Enforcement Program (CDFW and County Sheriff)
Illegal activities, such as off-road riding, trespassing, vandalism, and littering have complicated efforts to preserve and manage open space lands in the region of San Diego. Despite passive enforcement efforts, open space violations continued to persist on both publicly owned lands and privately owned properties and are believed to be adversely affecting the species and habitats that the open space lands were intended to preserve.
To address this issue, the San Diego Association of Governments in association with its partners, developed an Open Space Enforcement Program to coordinate and implement an aggressive multi-agency enforcement effort for conservation and management of the open space in the region. Through a cooperative approach, the California Department of Fish and Wildlife and San Diego County Sheriff's Department Off-Road Enforcement Team (ORET) participated in a Pilot Program to advance the following goals:
1. Prevent/reduce habitat damage
2. Reduce/prevent take of MHCP and MSCP covered species
3. Reduce preserve management and remediation costs
4. Support volunteer patrol activities on preserves
CDFW Game Wardens primarily focused on increasing law enforcement patrols in open space areas for illegal activity to control damage of property and the environment. Game Wardens enforced state law and local ordinances against violators in the targeted areas to help reduce and deter criminal activities on open space lands in the region. The ORET developed an open space enforcement plan and conducted enforcement actions that have a nexus and contributed to the protection of open spaces throughout the region. A majority of the ORET's efforts focused on areas previously identified, while the remainder of their effort focused on response to specific and often one-time requests for open space enforcement response. To the extent possible, the ORET and DFG collaborated on developing joint operational plans and information sharing to enhance the logistical and tactical effectiveness of the Program.
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Otay Ranch Preserve Enhancement Project
The goal of the project is to restore and increase the quality of habitat for Quino checkerspot butterfly (MSP Category SL [Species at risk of loss from the Management Strategic Plan Area]) near Minnewawa Truck Trail through seasonal road closure, seeding, and planting within suitable Quino habitat. This program addresses the immediate needs of Quino within the Otay Ranch Preserve (ORP) Dulzura Parcels where loss and degradation of existing Quino habitat has occurred due to vehicles, an increase of invasive plants, and drought. The objectives to reach these goals include 1) container plant installation, 2) seeding, 3) watering, 4) erosion control, 5) removable bollard and sign installation, 6) photographic monitoring, 7) quarterly reports, 8) final report. The methodologies used in this proposal are like those used to successfully restore 6 acres of Quino habitat in the ORP San Ysidro Parcels (CDFW Local Area Assistance Grant), 14.28 acres located in the ORP Salt Creek Parcels for the City of Chula Vista Quino Checkerspot Recovery Program, and 5 acres on USFWS Refuge property for the Quino Checkerspot Augmentation Project. This project is consistent with the management and monitoring approach prescribed in SDMMP’s Management and Monitoring Strategic Plan (MSP Vol. 2D, Page V2D.2-6).
This project is partially funded by SANDAD TransNet Land Management Grant #S1125469.
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Otay River Valley Cactus Wren Habitat Restoration and Enhancement
The goal of this three-year project (#5004730) is to increase the amount of suitable habitat and improve connectivity for the coastal cactus wren along Otay River Valley through restoration and enhancement of degraded habitat areas. This project will complement the existing coastal cactus wren habitat restoration project proposed by the City of Chula Vista within the Otay River Valley and Salt Creek as part of the current Transnet EMP grant cycle. The coastal cactus wren restoration program in the Otay River Valley and Salt Creek area address the immediate needs of the coastal cactus wren where loss and degradation of existing wren habitat has occurred due to historical cattle grazing, increase of invasive plant species, unauthorized off-road vehicle use, drought, and vegetation succession processes. Activities included in this program include invasive species control with follow-up herbicide treatments, shrub thinning, collecting and planting coast cholla and coast prickly pear cuttings, native grass and forb seed collection and redistribution, vegetation monitoring, and focus cactus wren monitoring. An additional grant (#5004944) was awarded the first year of project implementation that provided access control fencing to the #5004730 project. Activities for the proposed project include the installation of t-post barbless wire fencing around the 3.5 acre CACW restoration area, in addition to installing 8 signs stating "Habitat Restoration Area - No Trespassing." This project would fulfill the immediate need for access control to the CACW restoration area, deterring off-road vehicles, bikers, equestrians, and other trails users from entering the project site. By providing funding for access control to this restoration and enhancement site, it will increase the success of EMP Grant #5004730.
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Otay Water District San Miguel Habitat Management Area Perimeter Fencing Restoration and Threat Reduction Project
The San Miguel Habitat Management Area (HMA) is an approximate 240-acre biological preserve and mitigation bank that was created by the Otay Water District in 1994. The HMA has recently experienced increased illegal entrance and creation of trails throughout the area. The uptick began during the pandemic when people were in search of more outdoor recreation opportunities. Mountain bikers and hikers are drawn to the surrounding USFWS refuge trail system that is open to the public. The HMA's perimeter fencing and gate locks are frequently cut by trail users illegally passing through the HMA to access between the USFWS refuge trail system and the local residential community, causing significant damage and threatening the viability of species and their habitats on the HMA including the coastal California gnatcatcher and burrowing owl. The Project will implement a variety of education-orientated and land management deterrent strategies to reduce these threats. This includes a public outreach and education campaign consisting of coordination with USFWS and SDGE; participation in local community meetings; and removal of HMA trails from apps. Deterrent efforts include installation of new gates, installation of vegetation to close off trails, installation of camera stations, and coordination with local law enforcement to implement enforcement actions.
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Proctor Valley Off Highway Vehicle (OHV) Barrier
Installation of the original Proctor Valley off-road barrier segments began in the southwest section of the valley in 2009 on City of San Diego, Public Utilities property and was partially funded by a Land Management Grant (#5001137). Subsequent project proposals submitted to SANDAG EMP, as well as other funding sources, resulted in additional OHV barrier sections installed on CDFW property (2010-2011; #5001327), followed in 2014, via a submission by Chaparral Lands Conservancy (and partners) for a project intended to complete the barrier along the remaining open space stretches of Proctor Valley Road (LMG #5001971). This last section included privately owned lands and CDFW's RJER Proctor Valley East unit. The section of barrier fence included in this project was originally planned for installation in 2014, as part of the EMP funded Proctor Valley Vehicle Barriers Project (Chaparral Lands Conservancy). However, that project ran out of funds following unexpected steep increases in the price of steel.
Implementation of the CDFW project (#5004941) is consistent with the implementation of the Fire and Wildlife Action Plan (FWA) assigned to golden eagle, Quino checkerspot butterfly and Hermes copper butterfly via the limitation of access to OHV activities, thus reducing wildfire risk (and preventing other impacts) to their habitats. This project will also maintain large (>300 acres) open areas within golden eagle territories to meet foraging habitat conditions preferred by eagles. This project was intended to reduce/prevent wildfires and other impacts from unauthorized activities on conserved lands in Proctor Valley. There is an urgent need to control access and prevent impacts before such pressures lead to increased unauthorized access. With the installation of the new OHV barrier section, CDFW staff can focus limited resources on management actions necessary to prevent unauthorized vehicle intrusion from adjacent private lands, now that direct access from Proctor Valley Road has been eliminated.
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Quarry Creek Preserve Fencing Project
SDHC will install additional fencing to prevent trespassers from entering vulnerable areas of the preserve that have historically been disturbed by trespassers and encampments. This project was partially funded by SANDAG TransNet EMP Land Management Grant #S1125500.
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Quino Habitat Restoration
The County of San Diego proposes to reduce a threat to the Quino checkerspot butterfly by increasing and improving habitat on a County-owned site that had previously supported a hundred or more butterflies. The Quino is threatened by development pressure, invasion by non-native grasslands (NNG) and forbs, and, likely, changes to climate and long-term drought. It is considered an MSP Category SL (species at risk of loss). The County intends to significantly enhance improve Quino habitat conditions and connectivity by: 1) identifying and closing roads/portions of road on the site to vehicular activity; 2) preventing off-road vehicle activity that may be bifurcating and destroying Quino habitat; 3) fencing and signing these areas to be restored; 4) controlling and removing invasive NNG that compete with plantago erecta, the primary Quino habitat and food source seeding areas with primarily native plant species required for Quino survival; 5) documenting site condition improvements as well as any beneficial effect for Quino,
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Rare Plant Inspect and Manage Monitoring 2014-2026
From 2014-2026, a Management and Monitoring Strategic Plan (MSP Roadmap) monitoring objective for 30 rare plant species is to inspect occurrences to determine management needs. The inspect and manage (IMG) objective is implemented to document the status of rare plant occurrences and assess habitats and threats to develop specific management recommendations. IMG monitoring is implemented by a combination of land managers and contracted biologists in coordination with the SDMMP. Available rare plant data is posted below. New annual updates are typically posted in March. Based upon an evaluation of these data, a 2014-2026 monitoring schedule has been developed for the 30 rare plant species (attached below). Coordinating data collection across the region allows analyses of species and population trends over time and provides a better understanding of the association between habitat and threat covariates and population dynamics.
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San Diego National Wildlife Refuge: Mother Miguel Mountain
This three-year project will protect sensitive species, including Mexican flannelbush, and critical habitat on the southwestern slope of Mother Miguel Mountain, while managing public access in a manner that will create within those who visit the site an awareness and appreciation of the need to respect the habitats and species present on the Refuge.
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San Diego River Channel
This project will take place on 148 acres of the San Diego River Biological Corridor between Santee border to Channel Road in Lakeside. The largest threat to the river is illegal lodging. Homeless individuals and groups in Lakeside always want to use the San Diego River Channel for illegal lodging and we are starting to get hunters in the riverbed as well. Although everyone makes their best effort to ensure that we remove the camps, it is done on an ad hoc basis without regular staff support. Recently, there has been an uptick in illegal lodging in the riverbed. This ls due to their use of a large culvert that drains into the river as as well as the removal of other illegal lodging locations in other areas of the river in other communities. All of the communities along the river are working hard to remove this population, which just creates a shuffle of individuals and camps between areas and communities. We have also had reports of hunters in he river. This needs be be stopped. With homeless comes trash, the cutting of fences, the removal of hazardous waste including sanitary issues, as well as needles and drug paraphernalia.
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San Diego RiverBlitz
Volunteer citizen science teams hike segments of the urban San Diego River to collect data about trash, homeless encampments, and invasive plants. This data is collected using a data mapping app called Mappler.
RiverBlitz takes place twice annually, allowing for year-over-year comparisons of point-in-time data.
On-going surveys and data mapping efforts supplement the RiverBlitz program, allowing the San Diego River Park Foundation to initiate real-time responses to trash and invasive plant species.
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San Dieguito Citizen Science Monitoring Program
The San Dieguito River Valley Conservancy (SDRVC) developed the San Dieguito Citizen Science Monitoring Program as a sustainable, cost-effective, and scientifically valid approach to gather critical data on lands within the San Dieguito River Park Focused Planning Area. This program seeks to fill knowledge gaps on the diversity, population, movements and spatial ecology of species within the watershed to better inform future land acquisitions, adaptive land management, habitat and species restoration, educational initiatives and future research. One of the main objectives of this program is to gather data that is consistent and shared with other regional planning efforts being coordinated by the San Diego Management & Monitoring Program. Data collected is submitted to regional databases and will help meet the management goals and objectives identified in the Management & Monitoring Strategic Plan. Annual expert-led surveys are carried out by volunteer citizen scientists following approved protocols and encourage community involvement and engagement.
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SDMMP Summary of Achievements 2008-2024
As a program, SDMMP has regionally monitored 52 species and regionally surveyed 68 species across all taxa; monitored and/or mapped 8 vegetation communities; and modeled, assessed, and mapped 8 threats and stressors. Additionally, the SDMMP has completed 27 genetic studies, 80 research studies, 18 habitat models, and interacted with more than 75 partner groups. The table provided breaks down management and monitoring tasks that have been completed by species, vegetation community, and threats.
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South San Diego County Community Outreach
In 2011, Earth Discovery Institute (EDI) received a TransNet EMP Land Management Grant Contract #5001968. That grant allowed EDI to establish a Community Outreach Coordination program that has assisted the USFWS, CDFW, EHC, BLM, TNC, and CBI with interpretive and volunteer conservation events and environmental education aimed at improving public knowledge about and stewardship of South County preserved Lands. This one-year project will extend conservation outreach and environmental education. Two follow-up grants (#5001770 and #5004737) assisted in funding the project. Interpretive and habitat conservation events will support land management goals and agencies. Long-term stewardship will be built through student involvement. Access control and management will be supported by volunteer patrols. Quarterly newsletters will feature volunteer efforts and MSP priority species and habitats. The EDI website will provide access to habitat information as well as an incident reporting mechanism.
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Spring Canyon/Goat Mesa Vernal Pool Restoration
The vernal pools at the Spring Canyon/Goat Mesa complex (J16-J18) and surrounding open space have suffered considerable off-road damage over the years. This damage has resulted in changes in hydrologic, flow patterns, and inundation characteristics. This vernal pools complex was identified by the adopted Recovery Plan for Vernal Pools of Southern California (USFWS 1998) as necessary to stabilize populations of the following endangered and threatened MSP species: E. aristulatum, P. nudiuscula, N. fossalis, O. californica, B. sandiegonensis, and S. wootoni. The Management Strategic Plan (MSP) for Conserved Lands in Western San Diego County (SDMMP) also lists other MSP species historically found onsite, including D. variegata, M. minimus, S. hammondii, and A cunicularia. Minimization of illegal off-road vehicle use is the primary goal. The main objective to reach the goal is to use to fence off as many of the key access points and areas of frequent off-road vehicle use throughout the City open space to protect the habitat for the endangered and threatened species that exist onsite. This will be done by hiring a fence contractor to provide all supplies and install the fence. This project was partially funded by SANDAG TransNet EMP Land Management Grant #5004945 .
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SR 94 Wildlife Infrastructure Plan
Proposed road improvements to SR 94 provide an opportunity to mitigate the potential barrier effects of the highway. This project identifies where improvements to existing infrastructure on SR-94 could improve connectivity across the South County preserves, using Best Management Practices from the scientific literature; recommends wildlife movement monitoring to identify where new crossings are needed; and identifies where additional conservation would enhance the integrity of South County linkages. The review prioritizes infrastructure improvements of 35 existing undercrossings inspected by wildlife experts in the field along 14.6 miles of SR-94 where the highway bisects conserved lands. The majority of the recommendations for infrastructure improvement focus on increasing the diameter, and thus the openness ratio (cross-sectional area divided by length), of the undercrossing itself, removing vegetation and debris blocking the undercrossing, restoring habitat in the approach to the undercrossing, and installing fencing to both (1) keep animals off the highway and (2) funnel wildlife to the undercrossings.
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West Bernardo Mountain HMA Enhancement & Restoration
Project goals are to enhance and restore coastal sage scrub and cactus scrub habitat on the southwest slope of Bernardo Mountain near Lake Hodges. Partially funded by the SANDAG TransNet Environmental Mitigation Program. Contract Number: S1125508
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Wildlife Response to Human Recreation on NCCP Reserves in San Diego County
Adaptive land protection and management strategies are fundamental to accomplishing the stated species and habitat conservation goals of federal Habitat Conservation Plan (HCP) and California Natural Community Conservation Plan (NCCP) efforts. In San Diego County, the current NCCP reserve system includes more than 200,000 acres of protected lands, which are monitored and managed by multiple jurisdictions. The Wildlife Agencies (FWS and DFW, collectively), environmental groups, and reserve managers would like an improved understanding of how various threats and stressors may be affecting reserve performance for the benefit of 103 plant and animal species. The intent of this applied research project was to complement the existing species and habitat monitoring efforts in San Diego County by developing a program to assess the possible effects of human recreation on wildlife populations. Specific objectives for first phase of this project were to: (1) Develop recommendations for research studying the effects of recreation on wildlife species; and (2) Test methods for monitoring recreation and complete a pilot field study.
The second phase of this study was to implement a well designed study that integrates species monitoring with recreation monitoring to systematically assess recreation's direct and indirect effects on sensitive wildlife species, to improve the understanding of the trade-offs inherent in multiple-use management of reserves, and to ensure that NCCP reserves are providing the required levels of protection and achieving the goals of the NCCP program.
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