Biological Resources Assessment

1434 Grove Street

Healdsburg,

Prepared For: City of Healdsburg

August 20, 2019

ECORP Consulting, Inc. has assisted public and private land owners with environmental regulation compliance since 1987. We offer full service capability, from initial baseline environmental studies through environmental planning review, permitting negotiation, liaison to obtain legal agreements, mitigation design, and monitoring and compliance reporting.

Citation: ECORP Consulting, Inc. (ECORP). 2019. Biological Resources Assessment for the 1434 Grove Street Project. Prepared for City of Healdsburg, California. August. Biological Resources Assessment for the 1434 Grove Street Project

CONTENTS

1.0 INTRODUCTION ...... 1 1.1 Project Location and Description...... 1 1.2 Purpose of this Biological Resources Assessment ...... 1 2.0 REGULATORY SETTING ...... 3 2.1 Federal Regulations ...... 3 2.1.1 Endangered Act ...... 3 2.1.2 Migratory Bird Treaty Act ...... 5 2.1.3 Clean Water Act ...... 5 2.2 State and Local Regulations ...... 6 2.2.1 California Endangered Species Act ...... 6 2.2.2 Native Protection Act ...... 6 2.2.3 California Fish and Game Code Special Protections for Birds ...... 6 2.2.4 Lake or Streambed Alteration Agreements ...... 7 2.2.5 Porter-Cologne Water Quality Act ...... 7 2.2.6 California Environmental Quality Act...... 7 2.2.7 City of Healdsburg General Plan 2030 ...... 10 3.0 METHODS ...... 10 3.1 Literature Review ...... 10 3.2 Field Surveys Conducted ...... 11 3.3 Special-Status Species Considered for the Project ...... 11 4.0 RESULTS ...... 11 4.1 Site Characteristics and Land Use ...... 11 4.2 Vegetation Communities ...... 12 4.3 Soils ...... 12 4.4 Potential Waters of the U.S...... 15 4.4.1 Wetlands ...... 15 4.4.2 Other Waters...... 15 4.4.3 Wildlife ...... 15 4.5 Evaluation of Special-Status Species Identified in the Literature Search ...... 16 4.5.1 Special-Status ...... 26 4.5.2 Special-Status Animals ...... 26 4.5.3 Birds ...... 30 4.5.4 Mammals ...... 31 4.6 Wildlife Movement/Corridors ...... 31

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4.7 Critical Habitat ...... 32 5.0 RECOMMENDATIONS ...... 32 5.1 Waters of the U.S...... 32 5.2 Special-Status Plants ...... 32 5.3 Special-Status Invertebrate ...... 34 5.4 Special-Status Fish ...... 34 5.5 Special-Status Amphibians ...... 34 5.6 Special-Status Reptiles ...... 35 5.7 Special-Status Birds and MBTA-Protected Birds (including Raptors)...... 35 5.8 Special-Status Mammals ...... 35 5.9 Tree/Riparian Impacts ...... 36 6.0 REFERENCES ...... 37

LIST OF TABLES

Table 1. Potential Waters of the U.S...... 15 Table 2. Potentially Occurring Special-Status Species ...... 16

LIST OF FIGURES

Figure 1. Project Location and Vicinity ...... 2 Figure 2. Natural Resources Conservation Service Soil Types ...... 13 Figure 3. Aquatic Resources Delineation ...... 14 Figure 4. Site Plan ...... 33

LIST OF ATTACHMENTS

Attachment A – Representative Site Photographs Attachment B - Plant List Attachment C – Special-Status Species Searches (9-Quad CNPS Search, 9-Quad CNNDB Search, and Project Area IPaC Search)

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LIST OF ACRONYMS AND ABBREVIATIONS

ARD Aquatic Resources Delineation BRA Biological Resources Assessment CDFW California Department of Fish and Wildlife CEQA California Environmental Quality Act CESA California Endangered Species Act (a.k.a. California ESA) CFR Code of Federal Regulations BA Biological assessment BCC Birds of conservation concern BO Biological opinion BRA Biological resources assessment CC California Coastal CCC Central California Coast CDFW California Department of Fish and Wildlife CEQA California Environmental Quality Act CFR Code of Federal Regulations CNDDB California Natural Diversity Database CNPS California Native Plant Society CRPR California Rare Plant Rank CWA Clean Water Act ESA Endangered Species Act ESU Evolutionarily Significant Unit FR Federal Register MBTA Migratory Bird Treaty Act msl Mean sea level NMFS National Marine Fisheries Service NOAA National Oceanic and Atmospheric Administration NPDES National Pollutant Discharge Elimination System NPPA Native Plant Protection Act NRCS Natural Resources Conservation Service Project ±1.839-acre 1434 Grove Street Industrial Project RWQCB Regional Water Quality Control Board SSC Species of special concern USACE U.S. Army Corps of Engineers USC U.S. Code USEPA U.S. Environmental Protection Agency USFWS U.S. Fish and Wildlife Service USGS U.S. Geological Survey

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1.0 INTRODUCTION

At the request of the City of Healdsburg, ECORP Consulting, Inc. conducted a biological resources assessment (BRA) for the ±1.839-acre Industrial 1434 Grove Street Project (Project) located in the City of Healdsburg, Sonoma County, California. The purpose of the assessment was to collect information on the biological resources present or with the potential to occur in the Project Study Area, assess potential biological impacts related to Project activities, and identify potential mitigation measures to inform and support the Project’s California Environmental Quality Act (CEQA) documentation for biological resources.

1.1 Project Location and Description

The Project is located east of Highway 101 at 1434 Grove Street, north of Dry Creek Road and adjacent to Foss Creek (Figure 1. Project Location and Vicinity). The site corresponds to an unsectioned portion of the Rancho Sotoyome Land Grant within the “Geyserville” and “Jimtown”, California” 7.5-minute quadrangles (U.S. Geological Survey [USGS] revised 1997; 1993, respectively). The approximate center of the site is located at latitude 38.629284° (NAD27) and longitude -122.874841° (NAD27) within the Russian Watershed (Hydrologic Unit Code #18010110) Watershed (Natural Resources Conservation Service [NRCS], et al. 2017).

The Project parcel (Assessor’s Parcel Number 089-071-012) is located within the ‘I’ (Industrial) land use designation in the Healdsburg 2030 General Plan and in the ‘I’ (Industrial) zoning district. The Project includes construction of a new one-story, 15,424-square foot building for industrial uses, a covered masonry trash enclosure, construction of a driveway and an uncovered parking lot, and construction of a bioretention basin. The Project site includes a portion of Foss Creek along the western boundary that will not be impacted by the proposed Project.

1.2 Purpose of this Biological Resources Assessment

The purpose of this BRA is to assess the potential for occurrence of special-status plant and animal species and their habitats and sensitive habitats such as wetlands and riparian communities within the Project Study Area. This assessment includes a preliminary analysis of impacts on biological resources anticipated to result from the Project as presently defined. The mitigation recommendations presented in this assessment are based on a preliminary impact analysis, a review of existing literature, and the results of the site reconnaissance, the aquatic resources delineation, and the early season rare plant surveys for the Project.

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(AMM)-amyers 3/19/2019

APN Boundary - 1.85 acres

Sonoma County, California Unsectioned portion of the Rancho Sotoyome Landgrant; MDBM Latitude (NAD83): 38.629284° Longitude (NAD83): -122.874841° Watershed: Russian (18010110) I Scale in Feet 0 1,000 2,000 Geyserville (1987 (rev. 1997) NAD27 and Jimtown (1993 NAD27) CA 7.5-minute Topographic Quadrangle US Geological Survey Location: N:\2019\2019-040 1434Grove Street\MAPS\Location_Vicinity\GroveSt_LnV_20190319.mxd Map Date: 3/19/2019 iService Layer Credits: Copyright:© 2018 Garmin Copyright:© 2013 National Geographic Society, i-cubed Figure 1. Project Location and Vicinity 2019-040 1434 Grove Street Biological Resources Assessment for the 1434 Grove Street Project

For the purposes of this assessment, special-status species are defined as plants or animals that:

 are listed, proposed for listing, or candidates for future listing as threatened or endangered under the federal Endangered Species Act (ESA);

 are listed or candidates for future listing as threatened or endangered under the California ESA;

 meet the definitions of endangered or rare under § 15380 of the CEQA Guidelines;

 are identified as a species of special concern (SSC) by the California Department of Fish and Wildlife (CDFW);

 are birds identified as birds of conservation concern (BCC) by the U.S. Fish and Wildlife Service (USFWS);

 are considered by the California Native Plant Society (CNPS) to be "rare, threatened, or endangered in California", “plants about which more information is needed”, or “plants of limited distribution – a watch list” (i.e., species with a California Rare Plant Rank [CRPR] of 1B, 2, 3, or 4);

 are plants listed as rare under the California Native Plant Protection Act (NPPA) (California Fish and Game Code, § 1900 et seq.); or

 are fully protected in California in accordance with the California Fish and Game Code, §§ 3511 (birds), 4700 (mammals), 5050 (amphibians and reptiles), and 5515 (fishes).

2.0 REGULATORY SETTING

2.1 Federal Regulations

2.1.1 Endangered Species Act

The ESA protects plants and animals that are listed as endangered or threatened by USFWS and the National Marine Fisheries Service (NMFS). Section 9 of ESA prohibits, without authorization, the taking of listed wildlife, where take is defined as “harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, collect, or attempt to engage in such conduct” [50 Code of Federal Regulations (CFR) 17.3]. For plants, this statute governs removing, possessing, maliciously damaging, or destroying any listed plant under federal jurisdiction and removing, cutting, digging up, damaging, or destroying any listed plant in any other area in knowing violation of state law [16 U.S. Code (USC) 1538].

Under Section 7 of ESA, federal agencies are required to consult with USFWS and/or NMFS if their actions, including permit approvals and funding, could adversely affect a listed (or proposed) species (including plants) or its critical habitat. Through consultation and the issuance of a biological opinion (BO), USFWS and NMFS may issue an incidental take statement allowing take of the species that is incidental to an otherwise authorized activity provided the activity will not jeopardize the continued existence of the species. Section 10 of ESA provides for the issuance of incidental take permits where no other federal actions are necessary provided a habitat conservation plan is developed.

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Section 7 Consultation

Section 7 of ESA mandates that all federal agencies consult with USFWS and/or NMFS to ensure that federal agencies’ actions do not jeopardize the continued existence of a listed species or adversely modify critical habitat for listed species. If direct and/or indirect effects will occur to critical habitat that appreciably diminish the value of critical habitat for both the survival and recovery of a species, the adverse modifications will require formal consultation with USFWS or NMFS. If adverse effects are likely, the federal lead agency must prepare a biological assessment (BA) for the purpose of analyzing the potential effects of the proposed project on listed species and critical habitat to establish and justify an "effect determination." Often a third-party, non-federal applicant drafts the biological assessment for the lead federal agencies. The USFWS/NMFS reviews the BA; if it concludes that the project may adversely affect a listed species or its habitat, it prepares a BO. The BO may recommend "reasonable and prudent alternatives" to the project to avoid jeopardizing or adversely modifying habitat.

Critical Habitat

Critical Habitat is defined in Section 3 of ESA as:

1. the specific areas within the geographical area occupied by a species, at the time it is listed in accordance with the ESA, on which are found those physical or biological features essential to the conservation of the species and that may require special management considerations or protection; and

2. specific areas outside the geographical area occupied by a species at the time it is listed, upon a determination that such areas are essential for the conservation of the species.

For inclusion in a Critical Habitat designation, habitat within the geographical area occupied by the species at the time it was listed must first have features essential to the conservation of the species (16 USC 1533). Critical Habitat designations identify, to the extent known and using the best scientific data available, habitat areas that provide essential life cycle needs of the species (areas on which are found the primary constituent elements). Primary constituent elements are the physical and biological features that are essential to the conservation of the species and that may require special management considerations or protection. These include but are not limited to the following:

1. Space for individual and population growth and for normal behavior

2. Food, water, air, light, minerals, or other nutritional or physiological requirements

3. Cover or shelter

4. Sites for breeding, reproduction, or rearing (or development) of offspring

5. Habitats that are protected from disturbance or are representative of the historic, geographical, and ecological distributions of a species

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2.1.2 Migratory Bird Treaty Act

The Migratory Bird Treaty Act (MBTA) implements international treaties between the United States and other nations devised to protect migratory birds, any of their parts, eggs, and nests from activities such as hunting, pursuing, capturing, killing, selling, and shipping, unless expressly authorized in the regulations or by permit. As authorized under the MBTA, USFWS issues permits to qualified applicants for the following types of activities: falconry, raptor propagation, scientific collecting, special purposes (rehabilitation, education, migratory game bird propagation, and salvage), take of depredating birds, taxidermy, and waterfowl sale and disposal. The regulations governing migratory bird permits can be found in 50 CFR part 13 General Permit Procedures and 50 CFR part 21 Migratory Bird Permits. The State of California has incorporated the protection of non-game birds in § 3800, migratory birds in § 3513, and birds of prey in § 3503.5 of the California Fish and Game Code.

2.1.3 Clean Water Act

The purpose of the federal Clean Water Act (CWA) is to “restore and maintain the chemical, physical, and biological integrity of the nation’s waters.” Section 404 of the CWA prohibits the discharge of dredged or fill material into Waters of the United States without a permit from the USACE. The definition of Waters of the U.S. includes rivers, streams, estuaries, the territorial seas, ponds, lakes, and wetlands. Wetlands are defined as those areas “that are inundated or saturated by surface or ground water at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions” [33 CFR 328.3 7b]. The U.S. Environmental Protection Agency (USEPA) also has authority over wetlands, including the authority to veto permits issued by USACE under CWA Section 404(c).

Projects involving activities that have no more than minimal individual and cumulative adverse environmental effects may meet the conditions of one of the Nationwide Permits already issued by USACE (Federal Register [FR] 82:1860, January 6, 2017). If impacts on wetlands could be substantial, an individual permit is required. A Water Quality Certification or waiver pursuant to Section 401 of the CWA is required for Section 404 permit actions; this certification or waiver is issued by the Regional Water Quality Control Board (RWQCB).

U.S. Fish and Wildlife Service Birds of Conservation Concern

The 1988 amendment to the Fish and Wildlife Conservation Act mandates USFWS “identify species, subspecies, and populations of all migratory nongame birds that, without additional conservation actions, are likely to become candidates for listing under ESA.” To meet this requirement, USFWS published a list of BCC (USFWS 2008) for the United States. The list identifies the migratory and nonmigratory bird species (beyond those already designated as federally threatened or endangered) that represent USFWS’ highest conservation priorities. Depending on the policy of the lead agency, projects that result in substantial impacts to BCC may be considered significant under CEQA.

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2.2 State and Local Regulations

2.2.1 California Endangered Species Act

The California ESA (California Fish and Game Code §§ 2050-2116) protects species of fish, wildlife, and plants listed by the state as endangered or threatened. Species identified as candidates for listing may also receive protection. Section 2080 of the California ESA prohibits the taking, possession, purchase, sale, and import or export of endangered, threatened, or candidate species, unless otherwise authorized by permit. Take is defined in Section 86 of the California Fish and Game Code as “hunt, pursue, catch, capture, or kill, or attempt to hunt, pursue, catch, capture, or kill.” The California ESA allows for take incidental to otherwise lawful projects under permits issued by CDFW.

Fully Protected Species

The State of California first began to designate species as “fully protected” prior to the creation of the federal and the California ESAs. Lists of fully protected species were initially developed to provide protection to those animals that were rare or faced possible extinction and included fish, amphibians and reptiles, birds, and mammals. Most fully protected species have since been listed as threatened or endangered under the federal and/or California ESAs. Fully protected species are identified in the California Fish and Game Code § 4700 for mammals, § 3511 for birds, § 5050 for reptiles and amphibians, and § 5515 for fish.

These sections of the California Fish and Game Code provide that fully protected species may not be taken or possessed at any time, including prohibition of CDFW from issuing incidental take permits for fully protected species under the California ESA. CDFW will issue licenses or permits for take of these species for necessary scientific research or live capture and relocation pursuant to the permit and may allow incidental take for lawful activities carried out under an approved Natural Community Conservation Plan within which such species are covered.

2.2.2 Native Plant Protection Act

The NPPA of 1977 (California Fish and Game Code §§ 1900-1913) was established with the intent to “preserve, protect and enhance rare and endangered plants in this state.” The NPPA is administered by CDFW. The Fish and Game Commission has the authority to designate native plants as “endangered” or “rare”. The NPPA prohibits the take of plants listed under the NPPA, but the NPPA contains a number of exemptions to this prohibition that have not been clarified by regulation or judicial rule. In 1984, the California ESA brought under its protection all plants previously listed as endangered under NPPA. Plants listed as rare under NPPA are not protected under the California ESA, but are still protected under the provisions of NPPA. The Fish and Game Commission no longer lists plants under NPPA, reserving all listings to the California ESA.

2.2.3 California Fish and Game Code Special Protections for Birds

In addition to protections contained within the California ESA and California Fish and Game Code § 3511 described above, the California Fish and Game Code includes a number of sections that specifically protect certain birds.

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Section 3800 states that it is unlawful to take nongame birds, such as those occurring naturally in California that are not resident game birds, migratory game birds, or fully protected birds, except when in accordance with regulations of the California Fish and Game Commission or a mitigation plan approved by CDFW for mining operations.

Section 3503 prohibits the take, possession, or needless destruction of the nest or eggs of any bird.

Section 3503.5 protects birds of prey (which includes eagles, hawks, falcons, kites, ospreys, and owls) and prohibits the take, possession, or destruction of any birds and their nests

Section 3505 makes it unlawful to take, sell, or purchase egrets, ospreys, and several exotic nonnative species, or any part of these birds.

Section 3513 specifically prohibits the take or possession of any migratory nongame bird as designated in the MBTA.

2.2.4 Lake or Streambed Alteration Agreements

Section 1602 of the California Fish and Game Code requires individuals or agencies to provide a Notification of Lake or Streambed Alteration to CDFW for “any activity that may substantially divert or obstruct the natural flow or substantially change the bed, channel, or bank of any river, stream, or lake.” CDFW reviews the proposed actions and, if necessary, proposed measures to protect affected fish and wildlife resources. The final proposal mutually agreed upon by CDFW and the applicant is the Lake or Streambed Alternation Agreement.

2.2.5 Porter-Cologne Water Quality Act

The RWQCB implements water quality regulations under the federal CWA and the Porter-Cologne Water Quality Act. These regulations require compliance with the National Pollutant Discharge Elimination System (NPDES), including compliance with the California Storm Water NPDES General Construction Permit for discharges of stormwater runoff associated with construction activities. General Construction Permits for projects that disturb one or more acres of land require development and implementation of a Storm Water Pollution Prevention Plan. Under the Porter-Cologne Water Quality Act, the RWQCB regulates actions that would involve “discharging waste, or proposing to discharge waste, with any region that could affect the water of the state” [Water Code 13260(a)]. Waters of the State are defined as “any surface water or groundwater, including saline waters, within the boundaries of the state” [Water Code 13050 (e)]. The RWQCB regulates all such activities, as well as dredging, filling, or discharging materials into Waters of the State, that are not regulated by USACE due to a lack of connectivity with a navigable water body. The RWQCB may require issuance of a Waste Discharge Requirements for these activities.

2.2.6 California Environmental Quality Act

In accordance with CEQA Guidelines § 15380, a species or subspecies not specifically protected under the federal or California ESAs or NPPA may be considered endangered, rare, or threatened for CEQA review purposes if the species meets certain criteria specified in the Guidelines. These criteria include definitions similar to definitions used in ESA, the California ESA, and NPPA. Section 15380 was included in the CEQA

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Guidelines primarily to address situations in which a project under review may have a significant effect on a species that has not been listed under ESA, the California ESA, or NPPA, but that may meet the definition of endangered, rare, or threatened. Animal species identified as SSC by CDFW and plants identified by the CNPS as rare, threatened, or endangered may meet the CEQA definition of rare or endangered.

Species of Special Concern

SSC are defined by the CDFW as a species, subspecies, or distinct population of an animal native to California that are not legally protected under ESA, the California ESA, or the California Fish and Game Code, but currently satisfies one or more of the following criteria:

 The species has been completely extirpated from the state or, as in the case of birds, it has been extirpated from its primary seasonal or breeding role;

 The species is listed as federally (but not state) threatened or endangered, or meets the state definition of threatened or endangered but has not formally been listed;

 The species has or is experiencing serious (noncyclical) population declines or range retractions (not reversed) that, if continued or resumed, could qualify it for state threatened or endangered status;

 The species has naturally small populations that exhibit high susceptibility to risk from any factor that if realized, could lead to declines that would qualify it for state threatened or endangered status, and

 SSC are typically associated with habitats that are threatened.

Depending on the policy of the lead agency, projects that result in substantial impacts to SSC may be considered significant under CEQA.

California Rare Plant Ranks

The CNPS maintains the Inventory of Rare and Endangered Plants of California (CNPS 2019), which provides a list of plant species native to California that are threatened with extinction, have limited distributions, and/or low populations. Plant species meeting one of these criteria are assigned to one of six CRPRs. The rank system was developed in collaboration with government, academia, non- governmental organizations, and private sector botanists, and is jointly managed by CDFW and the CNPS. The CRPRs are currently recognized in the California Natural Diversity Database (CNDDB). The following are definitions of the CNPS CRPRs:

 Rare Plant Rank 1A – presumed extirpated in California and either rare or extinct elsewhere

 Rare Plant Rank 1B – rare, threatened, or endangered in California and elsewhere

 Rare Plant Rank 2A – presumed extirpated in California, but more common elsewhere

 Rare Plant Rank 2B – rare, threatened, or endangered in California but more common elsewhere

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 Rare Plant Rank 3 – a review list of plants about which more information is needed

 Rare Plant Rank 4 – a watch list of plants of limited distribution

Additionally, CNPS has defined Threat Ranks that are added to the CRPR as an extension. Threat Ranks designate the level of threat on a scale of 1 through 3, with 1 being the most threatened and 3 being the least threatened. Threat Ranks are generally present for all plants ranked 1B, 2B, or 4, and for the majority of plants ranked 3. Plant species ranked 1A and 2A (presumed extirpated in California), and some species ranked 3, which lack threat information, do not typically have a Threat Rank extension. The following are definitions of the CNPS Threat Ranks:

 Threat Rank 0.1 – Seriously threatened in California (over 80 percent of occurrences threatened/high degree and immediacy of threat)

 Threat Rank 0.2 – Moderately threatened in California (20-80 percent occurrences threatened/moderate degree and immediacy of threat)

 Threat Rank 0.3 – Not very threatened in California (<20 percent of occurrences threatened/low degree and immediacy of threat or no current threats known)

Factors, such as habitat vulnerability and specificity, distribution, and condition of occurrences, are considered in setting the Threat Rank; and differences in Threat Ranks do not constitute additional or different protection (CNPS 2019).

Depending on the policy of the lead agency, substantial impacts to plants ranked 1A, 1B, or 2, and 3 are typically considered significant under CEQA Guidelines § 15380. Significance under CEQA is typically evaluated on a case-by-case basis for plants ranked 4 and at the discretion of the CEQA lead agency.

California Environmental Quality Act Significance Criteria

Sections 15063-15065 of the CEQA Guidelines address how an impact is identified as significant. Generally, impacts to listed (rare, threatened, or endangered) species are considered significant. Assessment of "impact significance" to populations of non-listed species (e.g., SSC) usually considers the proportion of the species’ range that will be affected by a project, impacts to habitat, and the regional and population level effects.

Specifically, § 15064.7 of the CEQA Guidelines encourages local agencies to develop and publish the thresholds that the agency uses in determining the significance of environmental effects caused by projects under its review. However, agencies may also rely upon the guidance provided by the expanded Initial Study checklist contained in Appendix G of the CEQA Guidelines. Appendix G provides examples of impacts that would normally be considered significant.

An evaluation of whether or not an impact on biological resources would be substantial must consider both the resource itself and how that resource fits into a regional or local context. Substantial impacts would be those that would diminish, or result in the loss of, an important biological resource, or those that would obviously conflict with local, state, or federal resource conservation plans, goals, or regulations. Impacts are sometimes locally important but not significant under CEQA. The reason for this is that

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Biological Resources Assessment for the 1434 Grove Street Project although the impacts would result in an adverse alteration of existing conditions, they would not substantially diminish or result in the permanent loss of an important resource on a population-wide or region-wide basis.

2.2.7 City of Healdsburg General Plan 2030

The City of Healdsburg’s Natural Resources Element of their General Plan (City of Healdsburg 2015) provides goals, policies and measures to protect and improve the City’s natural resources including plant and wildlife resources. Goals that could pertain to biological resources within the Project include:

GOAL NR-A: Improve water quality and flows in the Russian River, Dry Creek and Foss Creek to protect the city’s water supply, recreation, fish and wildlife.

GOAL NR-B: Conservation and restoration of Healdsburg’s native plants and wildlife, ecosystems and waterways.

GOAL NR-C: Preservation and enhancement of Healdsburg’s natural setting.

GOAL NR-D: Maintenance of the economic viability of agriculture in the Healdsburg area while providing for the planned development of Healdsburg.

GOAL NR-E: Reduce greenhouse gas emissions and increase energy efficiency communitywide.

GOAL NR-F: Protection and improvement of air quality in the Healdsburg area.

GOAL NR-G: Continuation of existing mineral extraction activities in an environmentally-sensitive manner.

Policies and Implementation Measures for these goals are detailed in the Natural Resources Element of their General Plan (City of Healdsburg 2015).

3.0 METHODS

3.1 Literature Review

The following resources were reviewed to determine the special-status species that had been previously documented within or in the vicinity of the Project Study Area:

 CDFW CNDDB data for the for the “Ukiah, California” 7.5-minute quadrangle and the nine surrounding USGS quadrangles (CDFW 2019);

 USFWS list of species and other resources under the USFWS jurisdiction that are known or expected to be on or near the Project area (USFWS 2019a);

 NMFS list of species and other resources under NMFS jurisdiction that are known or expected to be on or near the Project area (NMFS 2019a); and

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 CNPS’ electronic Inventory of Rare and Endangered Plants of California was queried for the “Geyserville and Jimtown, California” 7.5-minute quadrangles and the nine surrounding USGS quadrangles (CNPS 2019).

3.2 Field Surveys Conducted

ECORP senior biologist Tom Scofield conducted a reconnaissance-level site assessment on March 12, 2019. ECORP’s staff biologist, Clay DeLong, conducted an aquatic resources delineation and early season rare plant survey on April 23, 2019, and ECORP’s staff botanist, Casey Peters, conducted a late season rare plant survey on August 13, 2019. The findings of these surveys have been incorporated into this BRA.

An arborist survey was conducted for the Project site by James McNair and Associates and is summarized in an Arborist Report for the Project (McNair and Associates).

3.3 Special-Status Species Considered for the Project

Based on species occurrence information from the literature review and field observations, a list of special-status and CNDDB-tracked plant and animal species considered to have the potential to occur within the Project was generated and is summarized in Section 4.0. Each of the species that were considered as potentially occurring within the Project or vicinity was evaluated based on the following criteria:

 Present - Species was observed during field surveys or is known to occur within the Project based on documented occurrences within the CNDDB or other literature.

 Potential to Occur - Habitat (including soils and elevation requirements) for the species occurs within the Project.

 Low Potential to Occur - Marginal or limited amounts of habitat occurs and/or the species is not known to occur within the vicinity of the Project based on CNDDB records and other available documentation.

 Absent - No suitable habitat (including soils and elevation requirements) and/or the species is not known to occur within the vicinity of the Project based on CNDDB records and other documentation.

4.0 RESULTS

4.1 Site Characteristics and Land Use

The Project is located on level terrain and is situated at an elevational range between approximately 140 to 150 feet above mean sea level (msl). The Project site is currently unimproved and bordered by railroad tracks to the east, Foss Creek to the west, a recently constructed industrial building to the north, and undeveloped property to the south. The general vicinity of the Project is largely developed with industrial and commercial uses.

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The site is located in the northern coast range subregion of the California Floristic Province (Baldwin et al. 2012). This area is characterized by a Mediterranean climate, which is comprised of hot and dry summer months and cold and wet winter months. The annual precipitation for Healdsburg is approximately 42.13 inches (with the wettest period during October-April), and average daily temperatures range from 47.2˚ - 73.7 ˚F(National Oceanic and Atmospheric Administration [NOAA] 2019). Representative site photographs are provided in Attachment A.

4.2 Vegetation Communities

The Project area includes a densely wooded oak woodland located along the riparian edge of Foss Creek on the west side of the Project. There is also a remnant portion of oak woodland on the eastern side of the Project adjacent to a railroad easement. The dominant tree species occurring onsite include coast live oak (Quercus agrifolia), valley oak (Quercus lobata), native willow (Salix laevigata, and nonnative plum (Prunus spp.).

The Project also includes patches of ruderal/nonnative grassland and weedy vegetation along the edges of the riparian area and existing gravel parking areas. Plants found in this habitat include wild oats (Avena fatua), mustard (Brassica sp.), ripgut brome (Bromus diandrus), yellow star-thistle (Centaurea solstitialis), filaree (Erodium botrys), and prickly lettuce (Lactuca serriola). Vegetation found in the riparian understory include many of the ruderal/nonnative grassland species described above and also included poison oak (Toxicodendron diversilobum), Himalayan blackberry (Rubus armeniacus), and fennel (Foeniculum vulgare).

The eastern boundary near the railroad easement supports seasonal wetlands associated with a drainage swale and low-lying depressional areas that pond water. Vegetation observed in these areas were largely comprised of species found in wetlands including Italian ryegrass (Festuca perennis), Mediterranean barley (Hordeum marinum ssp. gussoneanum), toad rush (Juncus bufonius), hairy hawkbit (Leontodon saxatilis), Himalayan blackberry, Carex species (sedge), and curly dock (Rumex crispus). A comprehensive list of all plant species encountered during field surveys of the Project is provided in Attachment B.

4.3 Soils

According to the Web Soil Survey (NRCS 2019), one soil unit, or type, has been mapped within the Project, (ZaA) Zamora silty clay loam, 0 to 2 percent slopes (Figure 2. Natural Resources Conservation Service Soil Types). A very small area of (210) urban land is mapped along the edge of the highway.

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PeC Map Features

APN Boundary - 1.85 acres Sonoma County GIS Parcel - Boundary is Approximate Series Designation - Series Description

ZaA - Zamora silty clay loam, 0 to 2 percent slopes

ZaA

Tracks (JDS/AMM)-amyers 3/19/2019

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Sources: ESRI, Sonoma County ECORP: N:\2019\2019-0401434 Grove Street\MAPS\Soils_and_Geology\GroveSt_NRCS_20190319.mxd Map Date: 3/19/2019 Scale in Feet Figure 2. Natural Resources Conservation I Service Soil Types 0 70 2019-040 1434 Grove Street 38.629465/-122.875315 142 38.629462/-122.874572 Map Features A 143 A Property Boundary - 1.85 acres

139 A Reference Coordinate (NAD83) Three-criteria Sample Points 141 H! Upland Point H! 139 Waters Point 140 1 140 Aquatic Resources - 0.129 ac. * Wetlands 139 Seasonal Wetland Swale - 0.002 ac. 138 4N H! 136 Other Waters H! 135 3 134 Creek - 0.127 ac. H! 129 H! 1 2N Photo Source: Sonoma County Pictometry, 2018 Boundary Source: Munselle Civil Engineering Delineator: C. DeLong SWS-1 Coordinate System: NAD 1983 StatePlane California II FIPS 0402 Feet 133 1 Subject to U.S. Army Corps of Engineers verification. This exhibit depicts information and data produced in 139 accord with the wetland delineation methods described in the 1987 Corps of Engineers Wetland Delineation 140 138 Manual and the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Arid West Region 141 Version 2.0 as well as the Updated Map and Drawing Standards for the South Pacific Division Regulatory 142 137 Program as amended on February 10, 2016, and conforms to Sacramento District specifications. However, feature boundaries have not been legally surveyed and may be subject to minor adjustments if more accurate locations are required. SWS-2 * The acreage value for each feature has been rounded to the nearest 1/1000 decimal. Summation of these 130 values may not equal the total potential Waters of the U.S. acreage reported.

CREEK-1 138 138

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129 Tracks 132

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138 (JDS)-JSwager 5/3/2019

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38.627959/-122.875115 A 135 A 38.627955/-122.874461 ECORP: N:\2019\2019-0401434 Grove Street\MAPS\Jurisdictional_Delineation\GroveSt_ARD_20190502.mxd Map Date: 5/3/2019 Scale in Feet Figure 3. Aquatic Resources Delineation

0 60 I 2019-040 1434 Grove Street Biological Resources Assessment for the 1434 Grove Street Project

4.4 Potential Waters of the U.S.

A total of 0.129 acre of aquatic resources have been mapped within the Project Area (Table 1). A discussion of the aquatic resources is presented below, and aquatic resources delineation map is provided in Figure 3. Potential Waters of the U.S, which. included two types: seasonal wetland and perennial creek (Foss Creek). These features are described below.

Table 1. Potential Waters of the U.S.

Type Acreage1 Wetlands Seasonal Wetland Swale 0.002 Other Waters Perennial Creek (Foss Creek) 0.127 Total 0.129 1Acreages represent a calculated estimation and are subject to modification following the U.S. Army Corps of Engineers verification process.

4.4.1 Wetlands

Seasonal Wetland

Approximately 0.002 acre of seasonal wetland occurs within the Project along the eastern boundary (Figure 3). Seasonal wetlands are ephemerally wet due to accumulation of surface runoff and rainwater within low-lying areas. Inundation periods tend to be relatively short and they are commonly dominated by nonnative annual and sometimes perennial hydrophytic species.

4.4.2 Other Waters.

Perennial Creek (Foss Creek)

Approximately 0.127-acre of perennial creek (a portion of Foss Creek) occurs within the Project (Figure 3). Perennial creeks are characterized by year-round flows, The limits of this feature were delineated at the ordinary high-water mark, which was identified based on water marks, scour, shifts in vegetation, sediment deposits, and drift deposits. Foss Creek is primarily comprised of open water, with mature riparian occurring along the banks.

4.4.3 Wildlife

Wildlife use onsite is expected to be minimal due to the highly disturbed nature of the Project site, and close proximity to the surrounding developed areas. Bird species found within the Project site during this assessment included red-shouldered hawk (Buteo lineatus), common raven (Corvus corax), Anna’s hummingbird (Calypte anna) northern mockingbird (Mimus polyglottos), oak titmouse (Baeolophus inornatus), western bluebird (Sialia mexicana), black phoebe (Sayornis nigricans), European starling (Sturnus vulgaris), white-crowned sparrow (Zonotrichia leucophrys), yellow-rumped warbler (Setophaga coronata), and Brewer’s blackbird (Euphagus cyanocephalus).

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4.5 Evaluation of Special-Status Species Identified in the Literature Search

There are no special-status species previously documented within the Project site boundaries (CDFW 2019, Attachment C), but 21 special-status species are known to occur within the vicinity of the Project (CDFW 2019, USFWS 2019a, CNPS 2019). These species are: Sonoma sunrise (Blennosperma bakeri), bristly sedge Carex comosa), Pappose tarplant (Centromadia parryi ssp. Parryi), dwarf downingia (Downingia pusilla), congested-headed hayfield tarplant (Hemizonia congesta ssp. Congesta), Burke’s goldfields (Lasthenia burkei), Sebastopol meadowfoam (Limnanthes vinculans), Baker’s navarretia (Navarretia leucocephala ssp. bakeri), marsh checkerbloom (Sidalcea oregana ssp. hydrophila), California freshwater shrimp (Syncaris pacifica), hardhead (Mylopharodon conocephalus), Coho salmon (Oncorhynchus kisutch), Chinook salmon (Oncorhynchus tshawytscha), Steelhead (Oncorhynchus mykiss irideus), California giant salamander (Dicamptodon ensatus), California red-legged frog (Rana draytonii), foothill yellow-legged frog (Rana boylii), North Western pond turtle (Emys marmorata), burrowing owl (Athene cunicularia), White- tailed kite (Elanus leucurus), and Pallid bat (Antrozous pallidus).

These species and other special-status species that were evaluated are presented in Table 2, which lists all of the special-status plants and wildlife species identified in the literature review as potentially occurring within the Project. Included in these tables are the listing status for each species, a brief habitat description, and a determination on the potential to occur within the Project site. Following the table are brief descriptions and discussions of each special-status species that have the potential to occur in the Project.

Several species came up in the database and literature searches (Attachment B) but are not included in Table 2 because they are only tracked by the CNDDB and possess no special status or because the identified sensitive habitats are not located within the Project area. They are not discussed further in this report.

Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Plants Franciscan onion 1B.2 Clay, volcanic, and April – June Absent – no suitable often serpentinite soil in habitat. Allium peninsulare var. cismontane woodlands, franciscanum and valley and foothill grasslands 171’ – 1,001’). Rincon Ridge manzanita 1B Chaparral and February – Absent – no suitable cismontane woodlands May habitat. Arctostaphylos (240’ – 1214’). stanfordiana ssp. decumbens

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Napa false indigo 1B Openings of broad- April – July Absent – no suitable leafed upland forest, habitat and outside of Amorpha californica var. chaparral, and elevation range. napensis cismontane woodland (394’ – 6562’). Sonoma sunshine FE CE 1B Valley and foothill June – Low potential to occur – grassland September ruderal zones that Blennosperma bakeri (98’ – 1,657’). support non-native annual grassland plant species provide marginally suitable habitat. Narrow-anthered brodiaea 1B.2 Volcanic soils in broad- May – July Absent – outside of leafed upland forest, elevation range. Brodiaea leptandra chaparral, cismontane woodland, lower montane coniferous forest, valley and foothill grassland (361’ – 3,002’). The Cedars manzanita CR 1B.2 Prefers serpentinite February – Absent – no suitable seeps in chaparral and May habitat and outside of Arctostaphylos bakeri ssp. closed-cone coniferous elevation range. sublaevis forest (607’ – 2,493’). Konocti manzanita 1B Serpentinite seeps, February – Absent – no suitable closed-cone coniferous May habitat and outside of Arctostaphylos manzanita forest, and chaparral elevation range. ssp. elegans (607’ – 2493’). Bristly sedge 2B.1 Coastal prairies, May - Low Potential to occur – marshes and swamps, September seasonal wetland swale Carex comosa including lake margins, provides marginally and in Valley and suitable habitat. foothill grassland (0’ – 2,051’). The Cedars fairy-lantern 1B.2 Serpentinite soils in May – Absent – no suitable closed-cone coniferous August habitat and outside of raichei forest, and chaparral elevation range. (656’ – 1608’). Mt. Saint Helena morning- 4.2 Serpentinite soils in April - June Absent – outside of glory chaparral, lower elevation range. montane coniferous Calystegia collina ssp. forest, and Valley and oxyphylla foothill grassland (915’ – 3314’). Dwarf soaproot 1B Serpentinite soils in May - Absent – no suitable chaparral August habitat and outside of Chlorogalum pomeridianum (1001’ – 3281’). elevation range. var. minus

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Serpentine cryptantha 1B Serpentinite soils in April - June Absent – no suitable chaparral habitat and outside of Cryptantha dissita (1296’ – 1903’). elevation range. Holly-leaved ceanothus 1B Volcanic, rocky soils in February - Absent – no suitable chaparral and June habitat and outside of Ceanothus purpureus cismontane woodland elevation range. (394’ – 3000’). Pappose tarplant 1B Often in alkaline soils in May - Low Potential to occur – chaparral, coastal November seasonal wetland swale Centromadia parryi ssp. prairie, meadows and provides marginally parryi seeps, marshes and suitable habitat. coastal salt swamps, and vernally mesic Valley and foothill grasslands (0’ – 1378’). Rincon Ridge ceanothus 1B Volcanic or serpentinite February – Absent – no suitable soils in closed-cone June habitat. Ceanothus confusus coniferous forest, chaparral, and cismontane woodland (246’ – 3494’). Pennell's bird's-beak FE 1B Serpentinite soils in June - Absent – no suitable closed-cone coniferous September habitat. Cordylanthus tenuis ssp. forest and chaparral capillaris (148’ – 1001’). Dwarf downingia 2B.2 Mesic areas in Valley March – Low Potential to occur – and foothill grassland, May seasonal wetland swale Downingia pusilla and vernal pools. provides marginally Species appears to suitable habitat. have an affinity for slight disturbance (i.e., scraped depressions, ditches, etc.) (Baldwin et al. 2012, CDFW 2019) (3’ – 1,460’). Brandegee's eriastrum 1B Volcanic, sandy soil in April - Absent – no suitable chaparral and August habitat and outside of Eriastrum brandegeeae cismontane woodland elevation range. (1394’ – 2756’). Greene's narrow-leaved 1B Serpentinite and May - Absent – no suitable daisy volcanic soils in September habitat. chaparral greenei (262’ – 3297’). Serpentine daisy 1B Serpentinite soils in May - Absent – no suitable seeps and chaparral August habitat. Erigeron serpentinus (197’ – 2198’).

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite The Cedars buckwheat 1B Serpentinite soils in June - Absent – no suitable closed-cone coniferous September habitat and outside of Eriogonum cedrorum forests (1198’ – 1804’). elevation range. Fragrant fritillary 1B.2 Cismontane woodland, February - Absent – no suitable coastal prairie, coastal April habitat. Fritillaria liliacea scrub, and valley and foothill grassland, often on serpentinite substrates (10’ – 1,345’). Congested-headed hayfield 1B.2 Sometimes roadsides, April - Low Potential to occur – tarplant and valley and foothill November ruderal areas provide grasslands potentially suitable Hemizonia congesta ssp. (66’ – 1,837’). habitat. congesta Glandular western flax 1B.2 Usually in serpentinite May - Absent – no suitable soils in chaparral, August habitat and outside of Hesperolinon cismontane woodland, elevation range. adenophyllum and Valley and foothill grassland (492’ – 4,314’). Thin-lobed horkelia 1B Mesic, sandy openings May - Absent – no suitable of broad-leafed upland August habitat onsite. Horkelia tenuiloba forests, chaparral, valley and foothill grassland (164’ – 1,640’). Small groundcone 2B North coast coniferous April - Absent – no suitable forest (295’ – 2904’). August habitat onsite. Kopsiopsis hookeri Burke's goldfields FE CE 1B.1 Mesic sites within April - June Low Potential to occur – meadows and seeps seasonal wetland swale Lasthenia burkei and vernal pools provides marginally (49’ – 1,969’). suitable habitat. Colusa layia 1B.2 Sandy or serpentinite April - May Absent – no suitable soils in chaparral, habitat and outside of Layia septentrionalis cismontane woodland, elevation range. and valley and foothill grasslands (329’ – 3,592’) Jepson's leptosiphon 1B.2 Usually volcanic soils of March - Absent – no suitable chaparral, cismontane May habitat and outside of Leptosiphon jepsonii woodland, valley and elevation range. foothill grasslands (328’ – 1640’)

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Sebastopol meadowfoam FE CE 1B Vernally mesic areas in April - May Low Potential to occur – meadows and seeps, seasonal wetland swale Limnanthes vinculans Valley and foothill provides marginally grasslands, and vernal suitable habitat. pools (49’ – 1,009’). Cobb Mountain lupine 1B Broad-leafed upland March - Absent – no suitable forest, chaparral, June habitat and outside of Lupinus sericatus cismontane woodland, elevation range. and lower montane coniferous forests (902’ – 5003’). Marsh microseris 1B.2 Closed-cone coniferous April - June Absent – no suitable forest, cismontane habitat. Microseris paludosa woodland, coastal scrub, and Valley and foothill grassland (16’-1,165’). Baker's navarretia 1B.1 Vernal pools and mesic April - July Low Potential to occur – areas within seasonal wetland swale Navarretia leucocephala cismontane woodlands, provides marginally ssp. bakeri lower montane suitable habitat. coniferous forests, meadows and seeps, and Valley and foothill grasslands (15’ – 5,700’). Few-flowered navarretia FE CT 1B.1 Volcanic ash flow May - June Absent – no suitable vernal pools habitat and outside of Navarretia leucocephala (1,312’ – 2,805’). elevation range. ssp. pauciflora Many-flowered navarretia FE CE 1B.2 Volcanic ash flow May - June Absent – no suitable vernal pools habitat. Navarretia leucocephala (98’ – 3,117’). ssp. plieantha

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Geysers panicum CE 1B Geothermally-altered June – Absent – no suitable soil, sometimes August habitat and outside of Panicum acuminatum var. streamsides within elevation range. thermale closed-cone coniferous forests, riparian forests, and Valley and foothill grassland (1001’ – 8104’). White-flowered rein orchid 1B Sometimes occurs in March - Absent – no suitable serpentinite soils, September habitat. Piperia candida broad-leafed upland forest, lower mountain coniferous forest, and North Coast coniferous forest (98’ – 4298’) Purple-stemmed 1B Broad-leafed upland May - June Absent – no suitable checkerbloom forest and coastal habitat. prairie (49’ – 279’). Sidalcea malviflora ssp. purpurea Marsh checkerbloom 1B Mesic environments June - Low Potential to occur – within meadows, seeps, August seasonal wetland swale Sidalcea oregana ssp. and riparian forest provides marginally hydrophila (3609’ – 7546’). suitable habitat. Freed's jewelflower 1B Serpentinite soils within May – July Absent – no suitable chaparral and habitat and outside of brachiatus cismontane woodland elevation range. ssp. hoffmanii (1407’ – 4003’) Dorr's Cabin jewelflower 1B Serpentinite soils within June Absent – no suitable closed-cone coniferous habitat and outside of forest, chaparral elevation range. ssp. hirtiflorus (607’ – 2690’). Morrison's jewelflower 1B Serpentinite, rocky, and May, Absent – no suitable talus soils within August - habitat and outside of Streptanthus morrisonii Chaparral September elevation range. ssp. morrisonii (394’ – 1919’). Socrates Mine jewelflower 1B Usually occurs in May - June Absent – no suitable serpentinite soils within habitat and outside of closed-cone coniferous elevation range. ssp. brachiatus forest and chaparral (1788’ – 3281’).

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Hoffman's bristly 1B Rocky soils within March – Absent – no suitable jewelflower chaparral, cismontane July habitat and outside of woodland, and elevation range. Streptanthus glandulosus serpentinite soils within ssp. hoffmanii Valley and foothill grasslands (394’ – 1558’). Santa Cruz clover 1B.1 Gravelly sites and on April - Absent – no suitable the margins of October habitat and outside of Trifolium buckwestiorum broadleaved upland elevation range. forest, cismontane woodland, and coastal prairie (344’ – 2,001’). Methuselah's beard lichen 4.2 On tree branches, N/A Absent – no suitable usually old growth habitat and outside of Usnea longissima hardwoods and conifers elevation range. within broadleaf upland forest and North Coast coniferous forest (164’ – 4790’). Invertebrates California freshwater FE CE Small, perennial coastal N/A Potential – Foss Creek shrimp streams. Excellent provides potential habitat habitat conditions for this species. Syncaris pacifica include streams with exposed live tree roots and overhanging riparian vegetation that provide refuge during high stream flows. Fish Russian River tule perch SSC Cool, well oxygenated NA Absent - The distribution water within low- of this species is limited Hysterocarpus traskIi pomo elevation lakes, to the lower reaches of streams, and estuarine Dry Creek and the environments. Prefer to Russian River and is not occupy deep pools that expected to occur in have overhanging Foss Creek. vegetative cover. Navarro roach SSC Predominantly in small NA Absent - Navarro roach warm streams, but also are confined to the Lavinia symmetricus found in larger colder Navarro River and its navarroensis streams. tributaries.

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Gualala roach SSC Predominantly in small NA Absent - Gualala roach warm streams, but also are confined to the Lavinia symmetricus found in larger colder Gualala River and its parvipinnis streams. tributaries. Hardhead SSC Relatively undisturbed NA Potential – Foss Creek streams at low to mid provides potential habitat Mylopharodon elevations in the for this species. conocephalus Sacramento-San Joaquin and Russian River drainages. In the San Joaquin River, scattered populations found in tributary streams, but only rarely in the valley reaches of the San Joaquin River. Coho salmon - central FE CE Rivers, streams, NA Potential – Foss Creek California coast ESU creeks. provides potential habitat for this species. Oncorhynchus kisutch Chinook salmon - California FT Rivers, streams, NA Potential – Foss Creek coast ESU creeks. provides potential habitat for this species. Oncorhynchus tshawytscha Steelhead - central FT Rivers, streams, NA Potential – Foss Creek California coast DPS creeks. provides potential habitat for this species. Oncorhynchus mykiss irideus Amphibians California giant salamander SSC Wet coastal forests in NA Potential – Foss Creek or near clear, cold provides potential habitat Dicamptodon ensatus permanent and semi- for this species. permanent streams and seepages. California red-legged frog FT - SSC Lowlands and foothills NA Low Potential to Occur – at waters with dense Foss Creek provides a Rana draytonii shrubby or emergent potential movement riparian vegetation. corridor for this species Adults must have but does not provide aestivation habitat to suitable breeding habitat. endure summer dry down.

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Foothill yellow-legged frog CC SSC Inhabits lakes, ponds, N/A Potential – Foss Creek meadow streams, provides potential habitat Rana boylii isolated pools, and for this species. sunny riverbanks in the Sierra Nevada Mountains. Waters that do not freeze to the bottom and which do not dry up are required. Occurs from 984' above sea level to over 12,000' above sea level. Red-bellied newt SSC Streams and rivers NA Absent – lack of suitable within coastal coastal woodland habitat Taricha rivularis woodlands and and outside of elevation redwood forest along range. the coast of northern California. Elevational range from 150-450 meters. Reptiles North Western pond turtle SSC Requires basking sites NA Potential – Foss Creek and upland habitats up provides potential habitat Emys marmorata to 0.5 km from water for for this species. egg laying. Uses ponds, streams, detention basins, and irrigation ditches. Birds Burrowing owl BCC, Nests in burrows or NA Low potential to occur – SSC burrow surrogates in ruderal areas provide Athene cunicularia open, treeless, areas marginally suitable within grassland, habitat. No burrows steppe, and desert observed onsite. biomes. Often with other burrowing mammals (e.g., prairie dogs, California ground squirrels). May also use human-made habitat such as agricultural fields, golf courses, cemeteries, roadside, airports, vacant urban lots, and fairgrounds.

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite White-tailed kite CFP Nesting occurs within NA Low potential to occur – trees in low elevation riparian woodland Elanus leucurus grassland, agricultural, provides potentially wetland, oak woodland, suitable nesting habitat. riparian, savannah, and Disturbances associated urban habitats. with adjacent commercial operations, however, likely preclude this species from nesting in the Project. Purple martin SSC In California, breeds N/A Absent – The Project along coast range, lacks potential nesting Progne subis Cascade-northern snag habitat and Sierra Nevada region disturbances associated and isolated population with adjacent commercial in Sacramento. Nesting operations, however, habitat includes likely preclude this montane forests, species from nesting in Pacific lowlands with the Project. dead snags; the isolated Sacramento population nests in weep holes under elevated highways/bridges. Winters in South America. Mammals Pallid bat SSC Crevices in rocky NA Potential to occur – outcrops and cliffs, riparian woodland Antrozous pallidus caves, mines, trees provides potential (e.g., basal hallows of roosting habitat for this redwoods, cavities of species. oaks, exfoliating pine and oak bark, deciduous trees in riparian areas, and fruit trees in orchards). Also roosts in various human structures such as bridges, barns, porches, bat boxes, and human-occupied as well as vacant buildings (WBWG 2017).

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Table 2. Potentially Occurring Special-Status Species

Status Bloom Period/ Approx. Common Name CESA/ Survey Potential To Occur (Scientific Name) ESA NPPA Other Habitat Description Dates Onsite Status Codes FESA Federal Endangered Species Act CESA California Endangered Species Act FE Federal ESA listed, Endangered. FT Federal ESA listed, Threatened BCC U. S. Fish and Wildlife Service Bird of Conservation Concern (USFWS, 2008 CE California ESA or NPPA listed, Endangered. CR California ESA or NPPA listed, Rare. CT California ESA NPPA listed, Threatened CC Candidate for California ESA listing as Endangered or Threatened. CFP Fish and Game Code of California Fully Protected Species (§3511-birds, §4700-mammals, §5050-reptiles/amphibians). SSC California Department of Fish and Game Species of Special Concern (CDFG, updated August 2004). 1B California Rare Plant Rank/Rare or Endangered in California and elsewhere. 2B Plants rare, threatened, or endangered in California but more common elsewhere. 4 CRPR/Plants of Limited Distribution – A Watch List. 0.1 Threat Rank/Seriously threatened in California (over 80% of occurrences threatened / high degree and immediacy of threat) 0.2 Threat Rank/Moderately threatened in California (20-80% occurrences threatened / moderate degree and immediacy of threat) CNDDB Species that is tracked by CDFW's Natural Diversity Database but does not have any of the above special-status designations otherwise.

4.5.1 Special-Status Plants

Based on the literature review and habitat types recorded in the Project, nine special-status plant species were identified as having a low potential to occur within the Project (Table 1). Several species identified in the database search were determined to be absent due to the absence of suitable habitat and/or because the Project is outside the range of the species.

A focused early rare plant survey (conducted by ECORP on April 24, 2019) found no potentially occurring early season special-status plants. Accordingly, potentially occurring early blooming plant species including: bristly sedge, Pappose tarplant, dwarf downingia, congested-headed hayfield tarplant, Burke’s goldfield, Sebastopol meadowfoam, and Baker’s navarretia are considered not to occur in the Project.

A second focused late season rare plant survey will be conducted in June 2019 to address two potentially occurring late season blooming rare plant species: Sonoma sunrise and marsh checkerbloom.

4.5.2 Special-Status Animals

Based on the literature review and habitat types recorded in the Project, 12 of the 17 special-status animals are considered to potentially occur within the Project (Table 1).

Invertebrates

One special-status invertebrate (California freshwater shrimp [Syncaris pacifica]) is considered to potentially occur in Foss Creek.

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California Freshwater Shrimp

The California fresh water shrimp is a small fresh water shrimp that occurs in a relatively small range of coastal low elevation, low gradient (low velocity) streams in central California. The species is known to occur in Napa, Sonoma, and Marin counties. Due to habitat loss and degradation in many parts of this coastal stream system and the limited range in which this species occurs, California fresh water shrimp is listed as endangered pursuant to both the federal and California ESAs. This species may occur onsite within Foss Creek.

Fish

Four of the special-status fish species identified in the literature search (hardhead (Mylopharadon conocephalus), Central California Coast Coho salmon, California Coastal Chinook salmon, and Central California Coast steelhead) potentially occur in the Project site in association with Foss Creek.

Hardhead

Hardhead is a relatively large minnow (Family Cyprinidae) that is a California SSC. Hardhead are widely distributed, but declining in abundance, in relatively undisturbed low- to mid-elevation streams throughout the Sacramento-San Joaquin river and Russian River drainages (Moyle 2002). Hardhead may reach lengths of 60 cm or greater (Moyle et al. 2015). Juvenile hardhead typically aggregate and forage at the surface of pools and runs during the day, while adults tend to occur in deeper pools where they forage on invertebrates and aquatic plants. The primary threats to hardhead include dams and diversions, agricultural practices, urbanization, instream mining, stream channel modifications, fisheries management (i.e., historic eradication and harvest as a “rough fish”), and competition from nonnative fish species (Moyle et al. 2015). Foss Creek provides potential habitat for supporting hardhead. Hardhead have the potential to occur within Foss Creek on the Project site.

Coho Salmon (Central California Coast ESU)

The Central California Coast (CCC) Evolutionarily Significant Unit (ESU) of Coho salmon (Oncorhynchus kisutch) was first listed as threatened under the ESA in 1996 (61 FR 56138) and subsequently listed as endangered under the ESA in 2005 (70 FR 37160). The CCC ESU was listed as endangered under the California ESA in March 2005. The CCC ESU includes populations from Punta Gorda, California south to the San Francisco Bay (excluding the Sacramento-San Joaquin river system). Critical Habitat was designated for the CCC ESU under the ESA on May 5, 1999 (64 FR 24049).

Coho salmon are anadromous salmonids, which spend the adult life stage in the ocean, and migrate into their natal freshwater rivers for spawning, egg incubation, and early life stage rearing. Adults enter freshwater to spawn in riffles of coastal streams from September through January. Eggs incubate in the gravel from November through April and alevins (hatchlings) remain within the gravels for two to 10 weeks until their yolk sac is absorbed. Fry emerge from the gravel from March to July and become parr (immature juveniles) over the summer months. After spending their first year rearing in their natal freshwater stream, Coho salmon smolts migrate to the ocean under winter flows in March and April. Adult Coho salmon typically spend two years in the ocean before returning to their natal streams to spawn. The primary threats to CCC ESU Coho salmon are largely human-related and include habitat loss, genetic

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introgression with hatchery-reared fish, overexploitation, and climactic changes (e.g., oceanic conditions) (Moyle 2002). Foss Creek provides potential habitat for supporting CCC ESU Coho salmon but is not designated Critical Habitat for the ESU. Coho salmon have the potential to occur within Foss Creek on the Project site.

Chinook Salmon (California Coastal ESU)

The California Coastal (CC) ESU of Chinook salmon includes naturally spawned populations from rivers south of the Klamath River to the Russian River. The CC ESU was first listed as threatened under the ESA in 1999 (64 FR 50394) and subsequently reaffirmed with the addition of hatchery stocks in 2005 (70 FR 37160). Critical habitat was designated for the CC ESU under the ESA on September 2, 2005 (70 FR 52488). The CC ESU is not listed under the California ESA, nor does it have a special-status designation in California.

Chinook salmon are anadromous salmonids. Adult CC ESU Chinook salmon spend three to five years in the ocean before entering freshwater to spawn in their natal streams from September through January. The timing of spawning and early life stage development is somewhat elastic and dependent upon annual, climatic, and hydrologic conditions. Spawning occurs in the late fall and early winter months and the adults die shortly after spawning. Eggs incubate in the gravel from approximately November through March and alevins (hatchlings) remain within the gravels for two to 10 weeks until their yolk sac is absorbed. Fry emerge from the gravel in late winter or early spring. Some portion of these fish may emigrate toward the ocean as post-emergent fry immediately after gravel emergence, or as smolts up to several weeks or months after emergence. The primary threats to CC ESU Chinook salmon are largely human-related and include habitat loss (e.g., due to dams and other migration barriers) and degradation, alteration of river flows, urbanization, gravel mining, and competition or predation from introduced species (Moyle 2002). Foss Creek provides potential habitat for supporting CC ESU Chinook salmon but is not designated Critical Habitat for the ESU. Chinook salmon have the potential to occur within Foss Creek on the Project site.

Steelhead (Central California Coast ESU)

Steelhead is the anadromous form of rainbow trout. The CCC ESU of steelhead includes populations from coastal streams extending from the Russian River to Aptos Creek, and drainages of San Francisco Bay, San Pablo Bay, and Suisun Bay eastward to Chipps Island, and tributary streams to Suisun Marsh. The CCC ESU was first listed as threatened under the ESA in 1997 (62 FR 43937) and subsequently reaffirmed 2006 (71 FR 834). Critical habitat was designated for the CC ESU under the ESA on September 2, 2005 (70 FR 52488). The CC ESU is not listed under the California ESA nor does it have a special-status designation in California.

Adult steelhead spend one to three years in the ocean before migrating back to their natal streams to spawn, typically from December through March. Spawning occurs shortly after arrival at suitable habitats in their natal stream and eggs incubate for three to four weeks. Fry emerge from the gravel within two to three weeks after hatching. Juveniles spend the first year or two residing in cool, fast-moving, and clear perennial streams before emigrating to the ocean under high winter flows. The primary threats to CCC ESU steelhead include overharvest, degradation and loss of estuarine habitat, hydropower development

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and associated dams, degraded ocean conditions, and hatchery practices (NMFS 2011). Foss Creek provides potential habitat for supporting CCC ESU steelhead but is not designated critical habitat for the ESU. Steelhead have the potential to occur within Foss Creek on the Project site.

Amphibians

Three special-status amphibian species: California giant salamander (Dicamptodon ensatus), California red- legged frog (Rana draytonii), and foothill yellow-legged frog (Rana boylii), potentially occur in the Project site in association with Foss Creek.

California Giant Salamander

The California giant salamander (Dicamptodon ensatus) is listed as federally endangered by the USFWS and is a California state listed endangered species. California giant salamander is a large (to 17 cm snout- vent length [snout-vent length), heavy-bodied salamander occurring in California’s mesic coast forests (Thomson et al. 2016). Adults are terrestrial most of the year, and are found under rocks, debris, bark, and other cover near streams. California giant salamanders occur in the Coast Range from the Point Arena vicinity of Mendocino County, east into Lake and Glenn counties, and south to Santa Cruz County. This species may occur onsite within and adjacent to Foss Creek.

California Red-legged Frog

The California red-legged frog (Rana draytonii) is listed as federally threatened by the USFWS and is a California SSC. Critical Habitat was designated pursuant to the ESA across approximately 1,636,609 acres in 27 counties including Alameda, Butte, Calaveras, Contra Costa, El Dorado, Marin, Napa, Nevada, Placer, Solano, and Yuba counties. The California red-legged frog range extends through Pacific slope drainages and parts of the Central Valley from Shasta County, California, to Baja, Mexico. This area includes the Coast Ranges and the west slope of the Sierra Nevada Mountains at elevations below 1,548 meters (5,000 feet). The current range is greatly reduced, with most remaining populations occurring along the coast from Marin County to Ventura County; and in isolated locations in the foothills of the western slope of the Sierra Nevada. Breeding habitat includes coastal lagoons, marshes, springs, permanent and semi- permanent natural ponds, and ponded and backwater portions of streams. California red-legged frogs also breed in artificial impoundments including stock ponds, irrigation ponds, and siltation ponds. Upland and riparian areas provide important habitat during summer when California red-legged frogs are known to aestivate in dense vegetation, burrows and leaf litter. California red-legged frogs often disperse from breeding habitats to forage and seek upland refugia and are often found within close proximity to a pond or deep pool in a creek where emergent vegetation, undercut banks, or semi-submerged rootballs afford shelter (USFWS 2005). This species may occur onsite within and adjacent to Foss Creek.

Foothill Yellow-Legged Frog

The foothill yellow-legged frog has been proposed for listing as threatened under California’s ESA and is a California SSC. It occurs in the Coast Ranges, from the Oregon border south to the Transverse Mountains in Los Angeles County, west of the Cascade crest in most of northern California, and in the Sierra Nevada foothills south to Kern County, from sea level to 6,000 feet above msl (Stebbins 1985). Foothill yellow-

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legged frogs occupy rocky streams in valley-foothill hardwood, valley-foothill hardwood-conifer, valley- foothill riparian, ponderosa pine, mixed conifer, coastal scrub, mixed chaparral, and wet meadow plant communities. They are rarely found far from water and will often dive into water to take refuge under rocks or sediment when disturbed (Zeiner et al. 1988). This species may occur onsite within and adjacent to Foss Creek.

Reptiles

One special-status reptile species, northern western pond turtle (Actinemys marmorata) was identified as potentially occurring in the Project site in association with Foss Creek.

Northern Western Pond Turtle

The northern western pond turtle is not listed pursuant to either the federal or California ESAs; however, it is designated as an SSC. Western pond turtles occur in a variety of fresh and brackish water habitats including marshes, lakes, ponds, and slow moving streams (Jennings and Hayes 1994). This species is primarily aquatic; however, they typically leave aquatic habitats in the fall to reproduce and to overwinter (Jennings and Hayes 1994). Deep, still water with abundant emergent woody debris, overhanging vegetation, and rock outcrops is optimal for basking and thermoregulation. Although adults are habitat generalists, hatchlings and juveniles and hatchlings require shallow edgewater with relatively dense submergent or short emergent vegetation in which to forage. Northern western pond turtles deposit their eggs within excavated nests in upland areas, with substrates that typically have high clay or silt fractions (Jennings and Hayes 1994). The majority of nesting sites are located within 200 meters (650 feet) of the aquatic sites; however, nests have been documented as far as 400 meters (1,310 feet) from the aquatic habitat. The CNDDB database includes known occurrences of northern western pond turtles within Foss Creek. This species is therefore considered to potentially occur onsite. This species may occur onsite within and adjacent to Foss Creek.

4.5.3 Birds

Two of the three of the special-status bird species identified in the literature search, Western white-tailed kite (Elanus leucurus) and burrowing owl (Athene cunicularia) potentially occur in the Project. While riparian and oak trees occur in the Project, the lack of suitable snags in the onsite trees likely preclude this species from nesting in the Project.

White-tailed Kite

White-tailed kite is not listed pursuant to either the California or federal ESAs; however, the species is fully protected pursuant to Section 3511 of the California Fish and Game Code. This species is a common resident in the Central Valley and the entire length of the California coast, and all areas up to the Sierra Nevada foothills and southeastern deserts (Dunk 1995). In northern California, white-tailed kite nesting occurs from March through early August, with nesting activity peaking from March through June. Nesting occurs in trees within riparian, oak woodland, savannah, and agricultural communities that are near foraging areas such as low elevation grasslands, agricultural, meadows, farmlands, savannahs, and emergent wetlands (Dunk 1995). This species may utilize the onsite trees for nesting.

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Western Burrowing Owl

The Western burrowing owl is not listed pursuant to either the California or federal ESAs; however, it is designated as a BCC by the USFWS and an SSC by the CDFW. Burrowing owls inhabit dry open rolling hills, grasslands, desert floors, and open bare ground with gullies and arroyos, but can also inhabit developed areas such as vacant lots and golf courses. This species typically uses burrows created by fossorial mammals, most notably the California ground squirrel (Spermophilus beecheyi) but may also use manmade structures such as pipes and culverts. This species may utilize onsite ruderal and grassland areas. The observed lack of suitable burrows onsite, likely precludes this species from occurring in the Project.

MBTA Protected Birds

Riparian woodland and other trees found in the Project support potential nesting habitat for birds protected under the MBTA. These could include common species such as northern mockingbird and house finch (Haemorhous mexicanus).

4.5.4 Mammals

One special-status mammal species, Pallid bat, was identified as potentially occurring in the Project site. This species is considered to potentially roost in in trees located in the riparian corridor and in other scattered areas of the Project.

Pallid Bat

The pallid bat is not listed pursuant to either the California or federal ESAs; however, this species is considered an SSC by CDFW. The pallid bat is a large, light-colored bat with long, prominent ears and pink, brown, or grey wing and tail membranes. This species ranges throughout North America from the interior of British Columbia, south to Mexico, and east to Texas. The pallid bat inhabits low elevation (below 6,000 feet) rocky arid deserts and canyonlands, shrub-steppe grasslands, karst formations, and higher elevation coniferous forest (above 7,000 feet). This species roosts alone or in groups in the crevices of rocky outcrops and cliffs, caves, mines, trees, and in various human structures such as bridges, and barns. Pallid bats are feeding generalists that glean a variety of arthropod prey from surfaces as well as capturing insects on the wing. Foraging occurs over grasslands, oak savannahs, ponderosa pine forests, talus slopes, gravel roads, lava flows, fruit orchards, and vineyards. Although this species utilizes echolocation to locate prey, often they use only passive acoustic cues. This species is not thought to migrate long distances between summer and winter sites (WBWG 2017). This species may utilize the onsite trees for roosting.

4.6 Wildlife Movement/Corridors

While wildlife use and wildlife movements through the Project is expected to be minimized due to the developed nature of the lands surrounding the Project, Foss Creek, including its perennial flows and adjacent riparian habitat, provide a movement for a variety of species, including several special status species (see Section 4.5).

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4.7 Critical Habitat

There is no Critical Habitat designated within the Project (CDFW 2019, USFWS 2019b, NMFS 2019).

5.0 RECOMMENDATIONS

This section summarizes possible measures to avoid, minimize, or compensate for potential impacts to biological resources from the proposed Project, including those to Waters of the U.S., special-status plant and wildlife resources, movement corridors, and oak woodland. Mitigation recommendations are provided, but may be revised based on the CEQA analysis and project permitting.

5.1 Waters of the U.S.

The aquatic resources delineation (ARD) field surveys identified potential Waters of the U.S. within the Project Area. An ARD report has been developed but has not been submitted to the USACE for verification. The current proposed Project has been designed to avoid impacts to the potential Waters of the U.S. identified on-site (Figure 4, Site Plan). If these features are verified as Waters of the U.S. by USACE and if disturbance would occur to Waters of the U.S. within the Project, the following measures would be recommended to minimize potential impacts to Waters of the U.S.:

 Authorization to fill wetlands under the Section 404 of the federal CWA (Section 404 Permit) must be obtained from USACE prior to discharging any dredged or fill materials into any Waters of the U.S. Mitigation measures will be developed as part of the Section 404 Permit to ensure no net loss of wetland function and values. To facilitate such authorization, an application for a Section 404 Permit for the Project will be prepared and submitted to USACE, and will include direct, avoided, and preserved acreages to Waters of the U.S. Mitigation for impacts to Waters of the U.S. typically consists of a minimum of a 1:1 ratio for direct impacts; however final mitigation requirements will be developed in consultation with USACE.

 A Water Quality Certification or waiver pursuant to Section 401 of the CWA must be obtained for Section 404 permit actions.

5.2 Special-Status Plants

Following completion of the initial site visit, the Project Area was found to provide potential habitat for nine special-status plants (Section 4.5). These include Sonoma sunrise, bristly sedge, Pappose tarplant, dwarf downingia, congested-headed hayfield tarplant, Burke’s goldfield, Sebastopol meadowfoam, Baker’s navarretia, and marsh checkerbloom. No special-status plants, however, were found during the focused protocol-level special status early and late season plant surveys and none are considered to occur on-site. No further measures pertaining to special-status plants are recommended.

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Map Features

Property Boundary - 1.85 acres

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0 70 I 2019-040 1434 Grove Street

EDGEOFROADTO MAINTAIN 5.0' FROM Biological Resources Assessment for the 1434 Grove Street Project

5.3 Special-Status Invertebrate

Suitable habitat for one special-status invertebrate species, California freshwater shrimp, occurs in the Project site in association with Foss Creek. The Project is currently proposing to avoid Foss Creek. The following measure is recommended to minimize potential impacts to California freshwater shrimp:

 If impacts to Foss Creek are avoided, no further measures are recommended. However, if impacts to Foss Creek will occur for the Project, surveys and/or consultation with USFWS and CDFW will be required for potential impacts to California freshwater shrimp.

5.4 Special-Status Fish

Foss Creek provides suitable habitat for four special-status fish species: hardhead, Central California Coast Coho salmon, California Coastal Chinook salmon, and Central California Coast steelhead, which have a potential to occur in Foss Creek at the Project site. The Project is currently proposing to avoid impacting Foss Creek and riparian vegetation along the stream bank within the Project boundary. The following measures are recommended to minimize potential impacts to special-status fish potentially occurring in Foss Creek:

 Conduct vegetation removal during the dry season construction window (e.g., June through October) to minimize the potential adverse effects on sensitive early life stages of special-status fish.

 Implement Best Management Practices to minimize potential erosion entering Foss Creek.

 If impacts to Foss Creek are avoided, no further measures are recommended. However, if impacts to Foss Creek will occur for the Project, consultation with NMFS will be required for potential impacts to ESA-listed CCC Coho salmon, CC Chinook salmon, and CCC steelhead; consultation with CDFW will be required for potential impacts to California ESA-listed CCC Coho salmon.

5.5 Special-Status Amphibians

Suitable habitat for three special-status amphibian species, California giant salamander, California red- legged frog, and foothill yellow-legged frog, occur in the Project site in association with Foss Creek. The Project is currently proposing to avoid Foss Creek. The following measures are recommended to minimize potential impacts to California giant salamander, California red-legged frog, and foothill yellow-legged frog:

 Conduct a pre-construction clearance survey for California giant salamander, California red- legged frog, and foothill yellow-legged frog within 48 hours of the start of construction. If California red-legged frog are observed, consultation with USFWS will be required. If California giant salamander and/or Foothill yellow-legged frog are observed, consultation with CDFW will be required.

 If impacts to Foss Creek are avoided, no further measures are recommended. However, if impacts to Foss Creek will occur for the Project, surveys and/or consultation with USFWS and CDFW will

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be required for potential impacts to California giant salamander, California red-legged frog, and foothill yellow-legged frog.

5.6 Special-Status Reptiles

Suitable aquatic habitat and marginally suitable upland habitat for one special-status reptile species, northern western pond turtle, is present within the Project site. The following measures are recommended to minimize potential impacts to the northern western pond turtle:

 Conduct a preconstruction clearance survey for northern western pond turtle within 48 hours of the start of construction. If northern western pond turtles are observed in the construction zone, a qualified biologist shall relocate the turtle to a location away from the construction zone.

5.7 Special-Status Birds and MBTA-Protected Birds (including Raptors)

Suitable nesting habitat for two special-status birds is present within the Project Area (Section 4.5). These include white-tailed kite and western burrowing owl. If special-status nesting birds are present, the proposed Project could result in harassment to nesting individuals and may temporarily disrupt foraging activities.

In addition to white-tailed kite and western burrowing owl, all native birds, including raptors, are protected under the federal MBTA. As such, to ensure that there would be no impacts to protected active nests, the following measures would be recommended if construction were to take place during the nesting bird season:

 Conduct a pre-construction nesting bird survey of all suitable habitats in the Project Area within 14 days prior to the commencement of construction during the nesting season (February 1 – August 31). Conduct a pre-construction nesting raptor survey within 500 feet of the Project Area and conduct a pre-construction nesting passerine survey within 100 feet of the Project Area. These surveys may be conducted concurrently. Pre-construction nesting surveys are not recommended for construction activities that begin outside of the nesting season.

 If active nests are found, a no-disturbance buffer around the nests shall be established. The buffer distance shall be established by a qualified biologist in consultation with CDFW and/or USFWS based upon the species. The buffer shall be maintained until the fledglings are capable of flight and become independent of the nest tree (which is to be determined by a qualified biologist). Once the young are independent of the nest, no further measures are recommended.

5.8 Special-Status Mammals

There is one special-status mammal, pallid bat, that could potentially occur within the Project Area (Section 4.5). To ensure that this species is not impacted, the following measures are recommended:

 Conduct pre-construction roosting bat surveys for all suitable roosting habitat (i.e., trees and manmade structures) prior to construction activities. If suitable roosting habitat is identified, a qualified biologist will conduct an evening bat emergence survey that may include acoustic monitoring to determine whether or not bats are present. If pallid bats are found, consultation

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Biological Resources Assessment for the 1434 Grove Street Project

with CDFW prior to initiation of disturbance of suitable roosting habitat will be required. If bats are not found during the preconstruction surveys, no further measures will be necessary.

5.9 Tree/Riparian Impacts

Tree protection procedures are identified in the Project’s Arborist report (MacNair and Associates 2019) and include tree protection and riparian fencing, trunk protection, and soil protection. Additional mitigation recommendations provided in the Arborist report include plantings, improvement of the site through removal of exotic, invasive plant species, and general woodland cleanup. No riparian trees will be removed.

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6.0 REFERENCES

Baldwin, B.G; D.H. Goldman; D.J. Keil; R. Patterson; and T.J. Rosatti, editors. 2012. The Jepson Manual: Vascular Plants of California, Second Edition. University of California Press, Berkeley.

CDFW. 2019. Rarefind 5. Online Version, commercial version dated: 18 March 2019. California Natural Diversity Database. The Resources Agency, Sacramento. Accessed March 2019.

CNPS. 2019. Inventory of Rare and Endangered Plants in California (online edition, v7-17nov 13-12-17). California Native Plant Society. Sacramento, CA. Available online: http://cnps.site.aplus.net/cgi- bin/inv/inventory.cgi. Accessed March 2019.

City of Healdsburg. Healdsburg 2030 General Plan Policy Document. 2015. City of Healdsburg Planning and Building Department

Dunk, J. R. 1995. White-tailed Kite (Elanus leucurus), The Birds of North America Online (A. Poole, Ed.). Ithaca: Cornell Lab of Ornithology; Retrieved from the Birds of North America Online: http://bna.birds.cornell.edu/bna/species/178.

Jennings, M. R., and M. P. Hayes. 1994. Amphibian and reptile species of special concern in California. Final report to the California Department of Fish and Game, Inland Fisheries Division, Rancho Cordova, California 225 pp.

McNair and Associates, 2019. 1434 Grove Street, Healdsburg Arborist Report. March 5 2019.

Moyle, P. B. 2002. Inland Fishes of California. University of California Press, Berkeley and Los Angeles, California.

Moyle, P. B., R. M. Quinones, J. V. Katz., and J. Weaver. Fish Species of Special Concern in California, Third Edition. Sacramento: California Department of Fish and Wildlife.

NMFS. 2019. NMFS Species List accessed 5/17/19. http://www.nwr.noaa.gov/protected_species/species_list/species_lists.html

_____. 2011. North-Central California Coast Recovery Domain. 5-Year Review: Summary and Evaluation of Central California Coastal Steelhead DPS and Northern California Steelhead DPS. Southwest Region and Southwest Fisheries Science Center.

NOAA. 2019. National Environmental Satellite, Data, and Information Service. NOAA’s National Weather Service Site: http://www.wrh.noaa.gov/forecast/wxtables/index.php?lat=38.64409000000006&lon=- 121.15750999999995.

NRCS. 2019. U.S. General Soil Map (gSSURGO). Available online: http://soildatamart.nrcs.usda.gov. Accessed 3/18/19.

NRCS, USGS, and USEPA. 2017. Watershed Boundary Dataset for California. Available online: https://datagateway.nrcs.usda.gov [February 2019].

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Biological Resources Assessment for the 1434 Grove Street Project

Stebbins, R.C. 1985. A field guide to western reptiles and amphibians. Houghton Mifflin Co., Boston. 336p.

Thomson, R. C., Wright, A. N., and Shaffer, H. B. 2016. California Amphibian and Reptile Species of Special Concern. California Department of Fish and Wildlife. University of California Press, Oakland.

USFWS. 2019a. Species List for the "Geyserville, California" 7.5-minute Quadrangle. Internet website: http://www.fws.gov/sacramento/ES_Species/Lists/es_species_lists-overview.htm. Accessed 3/18/19.

_____. 2019b. Species Lists. Available by request online: https://ecos.f ws.gov/ipac/. Accessed April 2019.

_____. 2008. Birds of Conservation Concern 2008. U.S. Fish and Wildlife Service, Division of Migratory Bird Management, Arlington, Virginia. Arlington, Virginia. http://www.fws.gov/migratorybirds/. Accessed

_____. 2005. Revised Guidance on Site Assessments and Field Surveys for the California Red-legged Frog. Appendix: California red-legged frog ecology and distribution. August 2005.

USGS. 1993. “Jimtown, California” 7.5-minute Quadrangle. NAD83 Geological Survey. Denver, Colorado.

_____. 1987. “Geyserville, California” 7.5-minute Quadrangle. NAD83 Geological Survey. Denver, Colorado.

WBWG. 2017. Western Bat Species Accounts. Available on-line at: http://wbwg.org/western-bat-species/

Zeiner, D.C, and W.F. Laudenslayer, Jr., K.E. Mayer, and M. White, Eds. 1988. California’s Wildlife. Volume I Amphibians and Reptiles. Department of Fish and Game, Sacramento, CA, USA.

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LIST OF ATTACHMENTS

Attachment A – Representative Site Photographs

Attachment B – Special-Status Species Searches (9-Quad CNPS Search, 9-Quad CNNDB Search, and Project Area IPaC Search)

Attachment C - Special-Status Species Searches (Quad CNNDB Search, Project Area IPaC Search, and 9-Quad CNPS Search, 9)

ATTACHMENT A

Representative Site Photographs

Central portion of site. March 13, 2019. Eastern portion looking south. March 13, 2019.

Foss Creek. March 13, 2019. Riparian along Foss Creek. March 13, 2019.

Representative Site Photographs 2019-040 1434 Grove Street

ATTACHMENT B

Plant Species List

Plant List

FAMILY NAME Scientific Name Common Name Lactuca serriola* Prickly lettuce Leontodon saxatilis* Hairy hawkbit Matricaria discoidea* Pineapple weed Silybum marianum* Milk thistle Sonchus asper* Prickly sowthistle Sonchus oleraceus* Common sowthistle Tragopogon porrifolius* Goat's beard Hirschfeldia incana* Shortpod mustard Lepidium didymum* Wart-cress Raphanus sativus* Purple wild radish CARYOPHYLLACEAE Spergularia rubra* Purple sandspurry CONVOLVULACEAE Convolvulus arvensis* Field bindweed CYPERACEAE Carex praegracilis Clustered field sedge Cyperus eragrostis Tall flatsedge DIPSACACEAE Dipsacus fullonum* Teasel FABACEAE Acmispon americanus American bird's foot trefoil Cytisus scoparius* Scotch broom Lotus corniculatus* Birdsfoot trefoil Lupinus bicolor Bicolored lupine Medicago polymorpha* Bur clover Trifolium dubium* Shamrock clover Trifolium fragiferum* Strawberry clover Trifolium hirtum* Rose clover Trifolium incarnatum* Crimson clover Vicia benghalensis* Purple vetch Vicia sativa* Common vetch Quercus agrifolia Coast live oak Quercus lobata Valley oak GERANIACEAE Erodium botrys* Broad leaf filaree Geranium dissectum* Cut-leaved geranium FAMILY NAME Scientific Name Common Name HYPERICACEAE Hypericum calycinum* Aaron's beard IRIDACEAE Sisyrinchium bellum Blue-eyed grass JUNCACEAE Juncus balticus ssp. ater Baltic rush Juncus bufonius Toad rush Juncus capitatus* Capped rush Juncus effusus Soft rush LAMIACEAE Mentha spicata* Spearmint Mentha x. piperita Peppermint LYTHRACEAE Lythrum hyssopifolia* Hyssop loosestrife MYRSINACEAE Lysimachia arvensis* Scarlet pimpernel OLEACEAE Fraxinus latifolia Oregon ash ONAGRACEAE Epilobium brachycarpum Panicled willow-herb OROBANCHACEAE Parentucellia viscosa* Yellow parentucellia OXALIDACEAE Oxalis pes-caprae* Sourgrass PLANTAGINACEAE Kickxia elatine* Sharp-leaved fluellin Plantago coronopus* Cut-leaf plantain Plantago lanceolata* English plantain POACEAE Avena fatua* Wild oat Briza maxima* Big quaking grass Bromus diandrus* Ripgut brome Bromus hordeaceus* Soft brome Bromus laevipes Woodland brome Cynodon dactylon* Bermuda grass Festuca bromoides* Brome fescue Festuca perennis* Italian Ryegrass Hordeum marinum ssp. gussoneanum* Mediterranean barley Hordeum murinum ssp. glaucum* Foxtail barley Phalaris aquatica* Harding grass Poa annua* Annual bluegrass Poa pratensis* Kentucky bluegrass Polypogon monspeliensis* Annual rabbit-foot grass FAMILY NAME Scientific Name Common Name POLYGONACEAE Polygonum aviculare ssp. depressum Prostrate knotweed Rumex crispus* Curly dock Rumex pulcher* Fiddle dock ROSACEAE Heteromeles arbutifolia Toyon Prunus cerasifera* Cherry plum Rubus armeniacus* Himalayan blackberry Rubus leucodermis White bark raspberry RUBIACEAE Galium aparine Common bedstraw SALICACEAE Salix laevigata Red willow SAPINDACEAE Aesculus californica California buckeye VITACEAE Vitis californica California wild grape

ATTACHMENT C

Special-Status Species Searches (Quad CNNDB Search, Project Area IPaC Search, and 9-Quad CNPS Search, 9)

3/18/2019 Print View

Query Summary: Quad IS (Cloverdale (3812371) OR Asti (3812278) OR The Geysers (3812277) OR Warm Springs Dam (3812361) OR Geyserville (3812268) OR Jimtown (3812267) OR Cazadero (3812351) OR Guerneville (3812258) OR Healdsburg (3812257))

Print Close

CNDDB Element Query Results CA Scientific Common Taxonomic Element Total Returned Federal State Global State Rare Other Habitats Name Name Group Code Occs Occs Status Status Rank Rank Plant Status Rank Cismontane Allium peninsulare Franciscan woodland, Monocots PMLIL021R1 25 1 None None G5T2 S2 1B.2 null Ultramafic, var. onion franciscanum Valley & foothill grassland Broadleaved SB_RSABG- Amorpha Napa false Rancho Santa upland forest, californica var. Dicots PDFAB08012 76 8 None None G4T2 S2 1B.2 Chaparral, indigo Ana Botanic napensis Garden Cismontane woodland Chaparral, BLM_S- Coastal scrub, Sensitive, Desert wash, CDFW_SSC- Great Basin Species of grassland, Great Special Basin scrub, Concern, Mojavean desert Antrozous pallid bat Mammals AMACC10010 416 6 None None G5 S3 null IUCN_LC- scrub, Riparian pallidus Least woodland, Concern, Sonoran desert USFS_S- scrub, Upper Sensitive, montane WBWG_H- coniferous High Priority forest, Valley & foothill grassland CDFW_SSC- Species of North coast Arborimus Sonoma tree Special coniferous pomo vole Mammals AMAFF23030 222 2 None None G3 S3 null Concern, forest, IUCN_NT- Oldgrowth, Near Redwood Threatened Chaparral, Arctostaphylos The Cedars BLM_S- Closed-cone bakeri ssp. manzanita Dicots PDERI04222 4 4 None Rare G2T2 S2 1B.2 Sensitive coniferous sublaevis forest, Ultramafic Chaparral, Arctostaphylos Konocti Cismontane manzanita manzanita Dicots PDERI04271 69 4 None None G5T3 S3 1B.3 null woodland, ssp. elegans Lower montane coniferous forest

Arctostaphylos Chaparral, stanfordiana Rincon Ridge Dicots PDERI041G4 12 4 None None G3T1 S1 1B.1 null Cismontane ssp. manzanita woodland decumbens Brackish marsh, CDF_S- Estuary, Ardea great blue Sensitive, Freshwater Birds ABNGA04010 155 1 None None G5 S4 null herodias heron IUCN_LC- marsh, Marsh & Least Concern swamp, Riparian forest, Wetland BLM_S- Sensitive, Coastal prairie, CDFW_SSC- Coastal scrub, Species of Great Basin Special grassland, Great Concern, Athene Basin scrub, burrowing owl Birds ABNSB10010 1978 2 None None G4 S3 null IUCN_LC- cunicularia Mojavean desert Least scrub, Sonoran Concern, desert scrub, USFWS_BCC- Valley & foothill Birds of grassland Conservation Concern Blennosperma Sonoma Dicots PDAST1A010 24 2 Endangered Endangered G1 S1 1B.1 SB_RSABG- Valley & foothill https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 1/7 3/18/2019 Print View bakeri sunshine Rancho Santa grassland, Ana Botanic Vernal pool, Garden Wetland Bombus obscure IUCN_VU- Insects IIHYM24380 181 3 None None G4? S1S2 null null caliginosus bumble bee Vulnerable USFS_S- Bombus western Sensitive, Insects IIHYM24250 282 1 None None G2G3 S1 null null occidentalis bumble bee XERCES_IM- Imperiled Broadleaved upland forest, Chaparral, narrow- Cismontane Brodiaea anthered Monocots PMLIL0C022 39 3 None None G3? S3? 1B.2 null woodland, leptandra brodiaea Lower montane coniferous forest, Valley & foothill grassland Chaparral, Calochortus The Cedars BLM_S- Closed-cone Monocots PMLIL0D1L0 9 9 None None G2 S2 1B.2 coniferous raichei fairy-lantern Sensitive forest, Ultramafic Chaparral, Lower montane Calystegia Mt. Saint coniferous collina ssp. Helena Dicots PDCON04032 9 1 None None G4T3 S3 4.2 null forest, oxyphylla morning-glory Ultramafic, Valley & foothill grassland Coastal prairie, Freshwater marsh, Marsh & Carex comosa bristly sedge Monocots PMCYP032Y0 29 1 None None G5 S2 2B.1 null swamp, Valley & foothill grassland, Wetland Chaparral, Cismontane Ceanothus Rincon Ridge BLM_S- woodland, confusus ceanothus Dicots PDRHA04220 33 6 None None G1 S1 1B.1 Sensitive Closed-cone coniferous forest, Ultramafic Chaparral, Ceanothus Calistoga Dicots PDRHA04240 26 1 None None G2 S2 1B.2 BLM_S- Cismontane divergens ceanothus Sensitive woodland, Ultramafic

Ceanothus holly-leaved Chaparral, Dicots PDRHA04160 43 1 None None G2 S2 1B.2 null Cismontane purpureus ceanothus woodland Chaparral, Centromadia Coastal prairie, parryi ssp. pappose Dicots PDAST4R0P2 39 1 None None G3T2 S2 1B.2 BLM_S- Marsh & swamp, parryi tarplant Sensitive Meadow & seep, Valley & foothill grassland BLM_S- Sensitive, Chlorogalum SB_SBBG- dwarf Santa Barbara Chaparral, pomeridianum Monocots PMLIL0G042 31 2 None None G5T3 S3 1B.2 var. minus soaproot Botanic Ultramafic Garden, USFS_S- Sensitive Clear Lake Clear Lake Drainage Drainage Inland CARA2520CA 3 1 None None GNR SNR null null null Resident Trout Resident Waters Stream Trout Stream

SB_RSABG- Chaparral, Cordylanthus Pennell's Rancho Santa Closed-cone tenuis ssp. bird's-beak Dicots PDSCR0J0S2 4 1 Endangered Rare G4G5T1 S1 1B.2 Ana Botanic coniferous capillaris Garden forest, Ultramafic Corynorhinus Townsend's Mammals AMACC08010 628 4 None None G3G4 S2 null BLM_S- Broadleaved townsendii big-eared bat Sensitive, upland forest, CDFW_SSC- Chaparral, Species of Chenopod Special scrub, Great Concern, Basin grassland, IUCN_LC- Great Basin Least scrub, Joshua Concern, tree woodland, USFS_S- Lower montane https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 2/7 3/18/2019 Print View Sensitive, coniferous WBWG_H- forest, Meadow High Priority & seep, Mojavean desert scrub, Riparian forest, Riparian woodland, Sonoran desert scrub, Sonoran thorn woodland, Upper montane coniferous forest, Valley & foothill grassland

Cryptantha serpentine Dicots PDBOR0A0H2 10 4 None None G2 S2 1B.2 BLM_S- Chaparral, dissita cryptantha Sensitive Ultramafic

CDFW_SSC- Aquatic, Species of Meadow & seep, Dicamptodon California Special North coast ensatus giant Amphibians AAAAH01020 234 32 None None G3 S2S3 null Concern, coniferous salamander IUCN_NT- forest, Riparian Near forest Threatened Valley & foothill Downingia dwarf grassland, Dicots PDCAM060C0 132 3 None None GU S2 2B.2 null pusilla downingia Vernal pool, Wetland

Dubiraphia Giuliani's giulianii dubiraphian Insects IICOL5A020 1 1 None None G1G3 S1S3 null null Aquatic riffle beetle

BLM_S- Cismontane Sensitive, woodland, CDFW_FP- Marsh & swamp, Elanus white-tailed Birds ABNKC06010 179 2 None None G5 S3S4 null Fully Riparian leucurus kite Protected, woodland, Valley IUCN_LC- & foothill Least Concern grassland, Wetland Aquatic, Artificial flowing waters, Klamath/North coast flowing waters, BLM_S- Klamath/North Sensitive, coast standing CDFW_SSC- waters, Marsh & Species of swamp, Emys western pond Reptiles ARAAD02030 1360 24 None None G3G4 S3 null Special Sacramento/San marmorata turtle Concern, Joaquin flowing IUCN_VU- waters, Vulnerable, Sacramento/San USFS_S- Joaquin Sensitive standing waters, South coast flowing waters, South coast standing waters, Wetland Broadleaved upland forest, Cismontane woodland, Closed-cone coniferous North Erethizon American Mammals AMAFJ01010 508 5 None None G5 S3 null IUCN_LC- forest, Lower dorsatum Least Concern montane porcupine coniferous forest, North coast coniferous forest, Upper montane coniferous forest

Eriastrum Brandegee's BLM_S- Chaparral, brandegeeae eriastrum Dicots PDPLM03020 6 1 None None G1Q S1 1B.1 Sensitive Cismontane woodland

Erigeron Greene's Chaparral, greenei narrow- Dicots PDAST3M5G0 20 1 None None G3 S3 1B.2 null Ultramafic leaved daisy

Erigeron serpentine Dicots PDAST3M5M0 6 2 None None G2 S2 1B.3 BLM_S- Chaparral, serpentinus daisy Sensitive Ultramafic Eriogonum The Cedars Dicots PDPGN087A0 3 2 None None G1 S1 1B.3 BLM_S- Closed-cone cedrorum buckwheat Sensitive, coniferous SB_RSABG- forest, Rancho Santa Ultramafic https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 3/7 3/18/2019 Print View Ana Botanic Garden Cismontane woodland, Coastal prairie, Fritillaria fragrant USFS_S- liliacea fritillary Monocots PMLIL0V0C0 82 1 None None G2 S2 1B.2 Sensitive Coastal scrub, Ultramafic, Valley & foothill grassland

Hemizonia congested- congesta ssp. headed Dicots PDAST4R065 52 8 None None G5T2 S2 1B.2 null Valley & foothill congesta hayfield grassland tarplant Chaparral, Cismontane Hesperolinon glandular Dicots PDLIN01010 48 2 None None G2G3 S2S3 1B.2 BLM_S- woodland, adenophyllum western flax Sensitive Ultramafic, Valley & foothill grassland

BLM_S- Broadleaved Sensitive, upland forest, Horkelia thin-lobed Dicots PDROS0W0E0 27 2 None None G2 S2 1B.2 SB_RSABG- Chaparral, tenuiloba horkelia Rancho Santa Valley & foothill Ana Botanic grassland Garden AFS_VU- Vulnerable, Aquatic, Hysterocarpus Russian River Fish AFCQK02011 4 4 None None G5T4 S4 null CDFW_SSC- Klamath/North traskii pomo tule perch Species of coast flowing Special waters Concern Kopsiopsis small North coast Dicots PDORO01010 21 1 None None G4? S1S2 2B.3 null hookeri groundcone coniferous forest CDFW_SSC- Species of Cismontane Special woodland, Concern, Lower montane Lasiurus western red blossevillii bat Mammals AMACC05060 128 1 None None G5 S3 null IUCN_LC- coniferous Least forest, Riparian Concern, forest, Riparian WBWG_H- woodland High Priority Broadleaved IUCN_LC- upland forest, Least Cismontane Lasiurus Concern, woodland, cinereus hoary bat Mammals AMACC05030 238 1 None None G5 S4 null WBWG_M- Lower montane Medium coniferous Priority forest, North coast coniferous forest

SB_RSABG- Meadow & seep, Lasthenia Burke's Dicots PDAST5L010 35 5 Endangered Endangered G1 S1 1B.1 Rancho Santa Vernal pool, burkei goldfields Ana Botanic Wetland Garden

Lavinia CDFW_SSC- Aquatic, symmetricus Navarro Fish AFCJB19023 4 1 None None G4T1T2 S2S3 null Species of Sacramento/San navarroensis roach Special Joaquin flowing Concern waters

Lavinia CDFW_SSC- Aquatic, symmetricus Gualala roach Fish AFCJB19025 4 1 None None G4T1T2 S2S3 null Species of Sacramento/San parvipinnis Special Joaquin flowing Concern waters Chaparral, Cismontane Layia Colusa layia Dicots PDAST5N0F0 57 3 None None G2 S2 1B.2 BLM_S- woodland, septentrionalis Sensitive Ultramafic, Valley & foothill grassland SB_RSABG- Rancho Santa Chaparral, Leptosiphon Jepson's Ana Botanic Cismontane jepsonii leptosiphon Dicots PDPLM09140 39 2 None None G3 S3 1B.2 Garden, woodland, SB_USDA-US Ultramafic Dept of Agriculture Meadow & seep, SB_RSABG- Limnanthes Sebastopol Rancho Santa Valley & foothill vinculans meadowfoam Dicots PDLIM02090 46 2 Endangered Endangered G1 S1 1B.1 Ana Botanic grassland, Garden Vernal pool, Wetland IUCN_NT- Linderiella California occidentalis linderiella Crustaceans ICBRA06010 437 1 None None G2G3 S2S3 null Near Vernal pool Threatened https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 4/7 3/18/2019 Print View Lupinus Cobb Dicots PDFAB2B3J0 46 1 None None G2? S2? 1B.2 BLM_S- Broadleaved sericatus Mountain Sensitive upland forest, lupine Chaparral, Cismontane woodland, Lower montane coniferous forest, Ultramafic Cismontane woodland, Closed-cone Microseris marsh Dicots PDAST6E0D0 38 1 None None G2 S2 1B.2 null coniferous paludosa microseris forest, Coastal scrub, Valley & foothill grassland CDFW_SSC- Klamath/North Species of coast flowing Mylopharodon hardhead Fish AFCJB25010 32 1 None None G3 S3 null Special waters, conocephalus Concern, Sacramento/San USFS_S- Joaquin flowing Sensitive waters Cismontane woodland, Lower montane Navarretia coniferous leucocephala Baker's Dicots PDPLM0C0E1 58 3 None None G4T2 S2 1B.1 BLM_S- forest, Meadow navarretia Sensitive & seep, Valley & ssp. bakeri foothill grassland, Vernal pool, Wetland SB_RSABG- Navarretia leucocephala few-flowered Dicots PDPLM0C0E4 10 1 Endangered Threatened G4T1 S1 1B.1 Rancho Santa Vernal pool, ssp. pauciflora navarretia Ana Botanic Wetland Garden

Navarretia many- SB_RSABG- leucocephala flowered Dicots PDPLM0C0E5 8 1 Endangered Endangered G4T1 S1 1B.2 Rancho Santa Vernal pool, ssp. plieantha navarretia Ana Botanic Wetland Garden

Northern Northern Vernal pool, Hardpan Hardpan Herbaceous CTT44110CA 126 1 None None G3 S3.1 null null Wetland Vernal Pool Vernal Pool coho salmon - Oncorhynchus central Fish AFCHA02034 23 9 Endangered Endangered G4 S2? null AFS_EN- Aquatic kisutch pop. 4 California Endangered coast ESU

Oncorhynchus steelhead - Aquatic, mykiss irideus central Fish AFCHA0209G 44 4 Threatened None G5T2T3Q S2S3 null AFS_TH- Sacramento/San pop. 8 California Threatened Joaquin flowing coast DPS waters CDF_S- Sensitive, Pandion osprey Birds ABNKC01010 500 3 None None G5 S4 null CDFW_WL- Riparian forest haliaetus Watch List, IUCN_LC- Least Concern Closed-cone coniferous Panicum Geysers BLM_S- forest, Riparian acuminatum Monocots PMPOA24028 11 5 None Endangered G5T2Q S2 1B.2 forest, Valley & panicum Sensitive var. thermale foothill grassland, Wetland Broadleaved upland forest, white- Lower montane Piperia flowered rein Monocots PMORC1X050 167 1 None None G3 S3 1B.2 BLM_S- coniferous candida orchid Sensitive forest, North coast coniferous forest, Ultramafic CDFW_SSC- Species of Broadleaved Progne subis purple martin Birds ABPAU01010 71 1 None None G5 S3 null Special upland forest, Concern, Lower montane IUCN_LC- coniferous forest Least Concern Rana boylii foothill yellow- Amphibians AAABH01050 2366 69 None Candidate G3 S3 null BLM_S- Aquatic, legged frog Threatened Sensitive, Chaparral, CDFW_SSC- Cismontane Species of woodland, Special Coastal scrub, Concern, Klamath/North https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 5/7 3/18/2019 Print View IUCN_NT- coast flowing Near waters, Lower Threatened, montane USFS_S- coniferous Sensitive forest, Meadow & seep, Riparian forest, Riparian woodland, Sacramento/San Joaquin flowing waters Aquatic, Artificial flowing waters, Artificial standing waters, Freshwater marsh, Marsh & swamp, Riparian forest, Riparian CDFW_SSC- Species of scrub, Riparian California red- Special woodland, Rana draytonii legged frog Amphibians AAABH01022 1515 1 Threatened None G2G3 S2S3 null Concern, Sacramento/San Joaquin flowing IUCN_VU- Vulnerable waters, Sacramento/San Joaquin standing waters, South coast flowing waters, South coast standing waters, Wetland Sidalcea purple- Broadleaved malviflora ssp. stemmed Dicots PDMAL110FL 19 1 None None G5T1 S1 1B.2 null upland forest, purpurea checkerbloom Coastal prairie Sidalcea Meadow & seep, marsh oregana ssp. checkerbloom Dicots PDMAL110K2 35 1 None None G5T2 S2 1B.2 null Riparian forest, hydrophila Wetland

Streptanthus Chaparral, brachiatus Socrates BLM_S- Closed-cone Mine Dicots PDBRA2G072 10 8 None None G2T1 S1 1B.2 coniferous ssp. Sensitive brachiatus jewelflower forest, Ultramafic

Streptanthus Chaparral, brachiatus Freed's Dicots PDBRA2G071 13 1 None None G2T2 S2 1B.2 BLM_S- Cismontane ssp. hoffmanii jewelflower Sensitive woodland, Ultramafic Chaparral, Streptanthus Hoffman's Cismontane glandulosus bristly Dicots PDBRA2G0J4 10 5 None None G4T2 S2 1B.3 BLM_S- woodland, ssp. hoffmanii jewelflower Sensitive Ultramafic, Valley & foothill grassland Chaparral, Streptanthus Dorr's Cabin BLM_S- Closed-cone morrisonii ssp. jewelflower Dicots PDBRA2G0S2 1 1 None None G2T1 S1 1B.2 Sensitive coniferous hirtiflorus forest, Ultramafic

Streptanthus Morrison's BLM_S- Chaparral, morrisonii ssp. jewelflower Dicots PDBRA2G0S3 5 3 None None G2T1? S1? 1B.2 Sensitive Ultramafic morrisonii Aquatic, California Syncaris freshwater Crustaceans ICMAL27010 20 1 Endangered Endangered G2 S2 null IUCN_EN- Sacramento/San pacifica shrimp Endangered Joaquin flowing waters Broadleaved upland forest, CDFW_SSC- Species of North coast Taricha red-bellied Special coniferous rivularis newt Amphibians AAAAF02020 136 29 None None G4 S2 null Concern, forest, Redwood, IUCN_LC- Riparian forest, Least Concern Riparian woodland BLM_S- Broadleaved Sensitive, upland forest, Trifolium Santa Cruz Dicots PDFAB402W0 50 2 None None G2 S2 1B.1 SB_USDA-US Cismontane buckwestiorum clover Dept of woodland, Agriculture Coastal prairie Broadleaved upland forest, North coast Usnea Methuselah's BLM_S- Lichens NLLEC5P420 206 2 None None G4 S4 4.2 coniferous longissima beard lichen Sensitive forest, Oldgrowth, Redwood https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 6/7 3/18/2019 Print View

https://map.dfg.ca.gov/rarefind/view/QuickElementListView.html 7/7 United States Department of the Interior FISH AND WILDLIFE SERVICE Sacramento Fish And Wildlife Office Federal Building 2800 Cottage Way, Room W-2605 Sacramento, CA 95825-1846 Phone: (916) 414-6600 Fax: (916) 414-6713

In Reply Refer To: March 18, 2019 Consultation Code: 08ESMF00-2019-SLI-1402 Event Code: 08ESMF00-2019-E-04507 Project Name: Industrial Project Healdsburg, CA

Subject: List of threatened and endangered species that may occur in your proposed project location, and/or may be affected by your proposed project

To Whom It May Concern:

The enclosed species list identifies threatened, endangered, proposed and candidate species, as well as proposed and final designated critical habitat, under the jurisdiction of the U.S. Fish and Wildlife Service (Service) that may occur within the boundary of your proposed project and/or may be affected by your proposed project. The species list fulfills the requirements of the Service under section 7(c) of the Endangered Species Act (Act) of 1973, as amended (16 U.S.C. 1531 et seq.).

Please follow the link below to see if your proposed project has the potential to affect other species or their habitats under the jurisdiction of the National Marine Fisheries Service: http://www.nwr.noaa.gov/protected_species/species_list/species_lists.html

New information based on updated surveys, changes in the abundance and distribution of species, changed habitat conditions, or other factors could change this list. Please feel free to contact us if you need more current information or assistance regarding the potential impacts to federally proposed, listed, and candidate species and federally designated and proposed critical habitat. Please note that under 50 CFR 402.12(e) of the regulations implementing section 7 of the Act, the accuracy of this species list should be verified after 90 days. This verification can be completed formally or informally as desired. The Service recommends that verification be completed by visiting the ECOS-IPaC website at regular intervals during project planning and implementation for updates to species lists and information. An updated list may be requested through the ECOS-IPaC system by completing the same process used to receive the enclosed list. 03/18/2019 Event Code: 08ESMF00-2019-E-04507 2

The purpose of the Act is to provide a means whereby threatened and endangered species and the ecosystems upon which they depend may be conserved. Under sections 7(a)(1) and 7(a)(2) of the Act and its implementing regulations (50 CFR 402 et seq.), Federal agencies are required to utilize their authorities to carry out programs for the conservation of threatened and endangered species and to determine whether projects may affect threatened and endangered species and/or designated critical habitat.

A Biological Assessment is required for construction projects (or other undertakings having similar physical impacts) that are major Federal actions significantly affecting the quality of the human environment as defined in the National Environmental Policy Act (42 U.S.C. 4332(2) (c)). For projects other than major construction activities, the Service suggests that a biological evaluation similar to a Biological Assessment be prepared to determine whether the project may affect listed or proposed species and/or designated or proposed critical habitat. Recommended contents of a Biological Assessment are described at 50 CFR 402.12.

If a Federal agency determines, based on the Biological Assessment or biological evaluation, that listed species and/or designated critical habitat may be affected by the proposed project, the agency is required to consult with the Service pursuant to 50 CFR 402. In addition, the Service recommends that candidate species, proposed species and proposed critical habitat be addressed within the consultation. More information on the regulations and procedures for section 7 consultation, including the role of permit or license applicants, can be found in the "Endangered Species Consultation Handbook" at: http://www.fws.gov/endangered/esa-library/pdf/TOC-GLOS.PDF

Please be aware that bald and golden eagles are protected under the Bald and Golden Eagle Protection Act (16 U.S.C. 668 et seq.), and projects affecting these species may require development of an eagle conservation plan (http://www.fws.gov/windenergy/ eagle_guidance.html). Additionally, wind energy projects should follow the wind energy guidelines (http://www.fws.gov/windenergy/) for minimizing impacts to migratory birds and bats.

Guidance for minimizing impacts to migratory birds for projects including communications towers (e.g., cellular, digital television, radio, and emergency broadcast) can be found at: http:// www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/towers/towers.htm; http:// www.towerkill.com; and http://www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/towers/ comtow.html.

We appreciate your concern for threatened and endangered species. The Service encourages Federal agencies to include conservation of threatened and endangered species into their project planning to further the purposes of the Act. Please include the Consultation Tracking Number in the header of this letter with any request for consultation or correspondence about your project that you submit to our office.

03/18/2019 Event Code: 08ESMF00-2019-E-04507 3

Attachment(s):

▪ Official Species List

03/18/2019 Event Code: 08ESMF00-2019-E-04507 1

Official Species List This list is provided pursuant to Section 7 of the Endangered Species Act, and fulfills the requirement for Federal agencies to "request of the Secretary of the Interior information whether any species which is listed or proposed to be listed may be present in the area of a proposed action".

This species list is provided by:

Sacramento Fish And Wildlife Office Federal Building 2800 Cottage Way, Room W-2605 Sacramento, CA 95825-1846 (916) 414-6600

03/18/2019 Event Code: 08ESMF00-2019-E-04507 2

Project Summary Consultation Code: 08ESMF00-2019-SLI-1402

Event Code: 08ESMF00-2019-E-04507

Project Name: Industrial Project Healdsburg, CA

Project Type: DEVELOPMENT

Project Description: Construction of a new one-story, 15,424 square foot (SF) building for industrial uses at 1434 Grove Street, Healdsburg, CA

Project Location: Approximate location of the project can be viewed in Google Maps: https:// www.google.com/maps/place/38.62838336100113N122.87585936486722W

Counties: Sonoma, CA

03/18/2019 Event Code: 08ESMF00-2019-E-04507 3

Endangered Species Act Species There is a total of 6 threatened, endangered, or candidate species on this species list.

Species on this list should be considered in an effects analysis for your project and could include species that exist in another geographic area. For example, certain fish may appear on the species list because a project could affect downstream species.

IPaC does not display listed species or critical habitats under the sole jurisdiction of NOAA Fisheries1, as USFWS does not have the authority to speak on behalf of NOAA and the Department of Commerce.

See the "Critical habitats" section below for those critical habitats that lie wholly or partially within your project area under this office's jurisdiction. Please contact the designated FWS office if you have questions.

1. NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an office of the National Oceanic and Atmospheric Administration within the Department of Commerce.

Birds NAME STATUS Northern Spotted Owl Strix occidentalis caurina Threatened There is final critical habitat for this species. Your location is outside the critical habitat. Species profile: https://ecos.fws.gov/ecp/species/1123

Reptiles NAME STATUS Green Sea Turtle Chelonia mydas Threatened Population: East Pacific DPS No critical habitat has been designated for this species. Species profile: https://ecos.fws.gov/ecp/species/6199

Amphibians NAME STATUS California Red-legged Frog Rana draytonii Threatened There is final critical habitat for this species. Your location is outside the critical habitat. Species profile: https://ecos.fws.gov/ecp/species/2891

03/18/2019 Event Code: 08ESMF00-2019-E-04507 4

Crustaceans NAME STATUS California Freshwater Shrimp Syncaris pacifica Endangered No critical habitat has been designated for this species. Species profile: https://ecos.fws.gov/ecp/species/7903

Flowering Plants NAME STATUS Burke's Goldfields Lasthenia burkei Endangered No critical habitat has been designated for this species. Species profile: https://ecos.fws.gov/ecp/species/4338

Pennell's Bird's-beak Cordylanthus tenuis ssp. capillaris Endangered No critical habitat has been designated for this species. Species profile: https://ecos.fws.gov/ecp/species/3175

Critical habitats THERE ARE NO CRITICAL HABITATS WITHIN YOUR PROJECT AREA UNDER THIS OFFICE'S JURISDICTION.

3/18/2019 CNPS Inventory Results

Plant List Inventory of Rare and Endangered Plants 73 matches found. Click on scientific name for details

Search Criteria

Found in Quads 3812371, 3812278, 3812277, 3812361, 3812268, 3812267, 3812351 3812258 and 3812257;

Modify Search Criteria Export to Excel Modify Columns Modify Sort Display Photos

CA Rare Blooming State Global Scientific Name Common Name Family Lifeform Plant Period Rank Rank Rank Allium peninsulare var. perennial (Apr)May- Franciscan onion Alliaceae 1B.2 S2 G5T2 franciscanum bulbiferous herb Jun Amorpha californica var. perennial deciduous Napa false indigo Fabaceae Apr-Jul 1B.2 S2 G4T2 napensis shrub Antirrhinum virga twig-like snapdragon Plantaginaceae perennial herb Jun-Jul 4.3 S3? G3? Arctostaphylos bakeri ssp. perennial evergreen Baker's manzanita Ericaceae Feb-Apr 1B.1 S1 G2T1 bakeri shrub Arctostaphylos bakeri ssp. The Cedars perennial evergreen Ericaceae Feb,Apr,May 1B.2 S2 G2T2 sublaevis manzanita shrub perennial evergreen Howell's manzanita Ericaceae Mar-Apr 4.2 S3 G4 Arctostaphylos hispidula shrub Arctostaphylos manzanita perennial evergreen (Jan)Mar- Konocti manzanita Ericaceae 1B.3 S3 G5T3 ssp. elegans shrub May(Jul) Arctostaphylos Rincon Ridge perennial evergreen Feb- Ericaceae 1B.1 S1 G3T1 stanfordiana ssp. manzanita shrub Apr(May) decumbens Asclepias solanoana serpentine milkweed Apocynaceae perennial herb May-Jul(Aug) 4.2 S3 G3 Astragalus breweri Brewer's milk-vetch Fabaceae annual herb Apr-Jun 4.2 S3 G3 Cleveland's milk- Fabaceae perennial herb Jun-Sep 4.3 S4 G4 Astragalus clevelandii vetch Blennosperma bakeri Sonoma sunshine Asteraceae annual herb Mar-May 1B.1 S1 G1 narrow-anthered perennial Themidaceae May-Jul 1B.2 S3? G3? Brodiaea leptandra brodiaea bulbiferous herb serpentine reed Poaceae perennial herb Apr-Jul 4.3 S3 G3 Calamagrostis ophitidis grass The Cedars fairy- perennial May-Aug 1B.2 S2 G2 Calochortus raichei lantern bulbiferous herb Calyptridium four-petaled Montiaceae annual herb Apr-Jun 4.3 S4 G4 quadripetalum pussypaws Calystegia collina ssp. Mt. Saint Helena perennial Convolvulaceae Apr-Jun 4.2 S3 G4T3 oxyphylla morning-glory rhizomatous herb Calystegia collina ssp. three-fingered perennial Convolvulaceae Apr-Jun 1B.2 S1 G4T1 tridactylosa morning-glory rhizomatous herb Campanula californica swamp harebell Campanulaceae perennial Jun-Oct 1B.2 S3 G3 http://rareplants.cnps.org/result.html?adv=t&quad=3812371:3812278:3812277:3812361:3812268:3812267:3812351:3812258:3812257 1/4 3/18/2019 CNPS Inventory Results rhizomatous herb perennial bristly sedge Cyperaceae May-Sep 2B.1 S2 G5 Carex comosa rhizomatous herb Castilleja ambigua var. annual herb johnny-nip Orobanchaceae Mar-Aug 4.2 S3S4 G4T4 ambigua (hemiparasitic) Rincon Ridge perennial evergreen Rhamnaceae Feb-Jun 1B.1 S1 G1 Ceanothus confusus ceanothus shrub holly-leaved perennial evergreen Rhamnaceae Feb-Jun 1B.2 S2 G2 Ceanothus purpureus ceanothus shrub Centromadia parryi ssp. pappose tarplant Asteraceae annual herb May-Nov 1B.2 S2 G3T2 parryi Chlorogalum perennial dwarf soaproot Agavaceae May-Aug 1B.2 S3 G5T3 pomeridianum var. minus bulbiferous herb Clarkia gracilis ssp. tracyi Tracy's clarkia Onagraceae annual herb Apr-Jul 4.2 S3 G5T3 Collomia diversifolia serpentine collomia Polemoniaceae annual herb May-Jun 4.3 S4 G4 Cordylanthus tenuis ssp. serpentine bird's- annual herb Orobanchaceae Jul-Aug 4.3 S3 G4G5T3 brunneus beak (hemiparasitic) Cordylanthus tenuis ssp. annual herb Pennell's bird's-beak Orobanchaceae Jun-Sep 1B.2 S1 G4G5T1 capillaris (hemiparasitic) serpentine Boraginaceae annual herb Apr-Jun 1B.2 S2 G2 Cryptantha dissita cryptantha California lady's- perennial Apr- Orchidaceae 4.2 S4 G4 Cypripedium californicum slipper rhizomatous herb Aug(Sep) mountain lady's- perennial Orchidaceae Mar-Aug 4.2 S4 G4 Cypripedium montanum slipper rhizomatous herb Downingia pusilla dwarf downingia Campanulaceae annual herb Mar-May 2B.2 S2 GU Brandegee's Polemoniaceae annual herb Apr-Aug 1B.1 S1 G1Q Eriastrum brandegeeae eriastrum Greene's narrow- Asteraceae perennial herb May-Sep 1B.2 S3 G3 Erigeron greenei leaved daisy Erigeron serpentinus serpentine daisy Asteraceae perennial herb May-Aug 1B.3 S2 G2 The Cedars Polygonaceae perennial herb Jun-Sep 1B.3 S1 G1 Eriogonum cedrorum buckwheat Snow Mountain perennial Polygonaceae Jun-Sep 1B.2 S2 G2 Eriogonum nervulosum buckwheat rhizomatous herb Eriogonum ternatum ternate buckwheat Polygonaceae perennial herb Jun-Aug 4.3 S4 G4 perennial fragrant fritillary Liliaceae Feb-Apr 1B.2 S2 G2 Fritillaria liliacea bulbiferous herb Hemizonia congesta ssp. congested-headed Asteraceae annual herb Apr-Nov 1B.2 S2 G5T2 congesta hayfield tarplant hogwallow starfish Asteraceae annual herb Mar-Jun 4.2 S3 G3 Hesperolinon glandular western Linaceae annual herb May-Aug 1B.2 S2S3 G2G3 adenophyllum flax Horkelia tenuiloba thin-lobed horkelia Rosaceae perennial herb May-Jul(Aug) 1B.2 S2 G2 perennial Kopsiopsis hookeri small groundcone Orobanchaceae rhizomatous herb Apr-Aug 2B.3 S1S2 G4? (parasitic) Lasthenia burkei Burke's goldfields Asteraceae annual herb Apr-Jun 1B.1 S1 G1 Layia septentrionalis Colusa layia Asteraceae annual herb Apr-May 1B.2 S2 G2 Jepson's leptosiphon Polemoniaceae annual herb Mar-May 1B.2 S3 G3 http://rareplants.cnps.org/result.html?adv=t&quad=3812371:3812278:3812277:3812361:3812268:3812267:3812351:3812258:3812257 2/4 3/18/2019 CNPS Inventory Results Leptosiphon jepsonii Crystal Springs Asteraceae annual herb Jul-Oct 1B.2 S2 G2 Lessingia arachnoidea lessingia Sebastopol Limnanthaceae annual herb Apr-May 1B.1 S1 G1 Limnanthes vinculans meadowfoam Cobb Mountain Fabaceae perennial herb Mar-Jun 1B.2 S2? G2? Lupinus sericatus lupine Mt. Diablo Asteraceae annual herb Mar-May 3.2 S3S4 G3G4 Micropus amphibolus cottonweed Microseris paludosa marsh microseris Asteraceae perennial herb Apr-Jun(Jul) 1B.2 S2 G2 perennial green monardella Lamiaceae Jun-Sep 4.3 S3 G3 Monardella viridis rhizomatous herb Navarretia leucocephala Baker's navarretia Polemoniaceae annual herb Apr-Jul 1B.1 S2 G4T2 ssp. bakeri Navarretia leucocephala few-flowered Polemoniaceae annual herb May-Jun 1B.1 S1 G4T1 ssp. pauciflora navarretia Navarretia leucocephala many-flowered Polemoniaceae annual herb May-Jun 1B.2 S1 G4T1 ssp. plieantha navarretia Panicum acuminatum var. annual / perennial Geysers panicum Poaceae Jun-Aug 1B.2 S2 G5T2Q thermale herb Perideridia gairdneri ssp. Gairdner's yampah Apiaceae perennial herb Jun-Oct 4.2 S3S4 G5T3T4 gairdneri white-flowered rein (Mar)May- Orchidaceae perennial herb 1B.2 S3 G3 Piperia candida orchid Sep Lobb's aquatic annual herb Ranunculaceae Feb-May 4.2 S3 G4 Ranunculus lobbii buttercup (aquatic) Sidalcea malviflora ssp. purple-stemmed perennial Malvaceae May-Jun 1B.2 S1 G5T1 purpurea checkerbloom rhizomatous herb Sidalcea oregana ssp. marsh checkerbloom Malvaceae perennial herb (Jun)Jul-Aug 1B.2 S2 G5T2 hydrophila Streptanthus barbiger bearded jewelflower Brassicaceae annual herb May-Jul 4.2 S3 G3 Streptanthus brachiatus Socrates Mine Brassicaceae perennial herb May-Jun 1B.2 S1 G2T1 ssp. brachiatus jewelflower Streptanthus brachiatus Freed's jewelflower Brassicaceae perennial herb May-Jul 1B.2 S2 G2T2 ssp. hoffmanii Streptanthus glandulosus Hoffman's bristly Brassicaceae annual herb Mar-Jul 1B.3 S2 G4T2 ssp. hoffmanii jewelflower Streptanthus morrisonii Three Peaks Brassicaceae perennial herb Jun-Sep 1B.2 S1 G2T1 ssp. elatus jewelflower Streptanthus morrisonii Dorr's Cabin Brassicaceae perennial herb Jun 1B.2 S1 G2T1 ssp. hirtiflorus jewelflower Streptanthus morrisonii Kruckeberg's Brassicaceae perennial herb Apr-Jul 1B.2 S1 G2T1 ssp. kruckebergii jewelflower Streptanthus morrisonii Morrison's Brassicaceae perennial herb May,Aug,Sep 1B.2 S1? G2T1? ssp. morrisonii jewelflower Trifolium buckwestiorum Santa Cruz clover Fabaceae annual herb Apr-Oct 1B.1 S2 G2 Methuselah's beard fruticose lichen Parmeliaceae 4.2 S4 G4 Usnea longissima lichen (epiphytic)

http://rareplants.cnps.org/result.html?adv=t&quad=3812371:3812278:3812277:3812361:3812268:3812267:3812351:3812258:3812257 3/4 3/18/2019 CNPS Inventory Results Suggested Citation

California Native Plant Society, Rare Plant Program. 2019. Inventory of Rare and Endangered Plants of California (online edition, v8-03 0.39). Website http://www.rareplants.cnps.org [accessed 18 March 2019].

Search the Inventory Information Contributors Simple Search About the Inventory The Calflora Database Advanced Search About the Rare Plant Program The California Lichen Society Glossary CNPS Home Page California Natural Diversity Database About CNPS The Jepson Flora Project Join CNPS The Consortium of California Herbaria CalPhotos

Questions and Comments [email protected]

© Copyright 2010-2018 California Native Plant Society. All rights reserved.

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