Appendix H Tables APPENDIX H Species Tables

TABLE H-1 Special-Status Species Potentially Occurring within the Fountaingrove Lodge Study Area USFWS/ CDFG/ Scientific Name Common Name CNPS Suitable Habitat for the Species Flowering Period Potential to Occur peninsulare var. Franciscan onion None/None/1B.2 Cismontane woodland, valley and foothill grassland/clay, volcanic, often May-June Very low. Nearest known locality near Kenwood, about 10 miles SE of project area (CalFlora franciscanum serpentinite. 100-300m 2007, Jepson On-line Interchange 2007).

Amorpha californica var. Napa false indigo None/None/1B.2 Broadleaved upland forest, , cismontane woodland; often shaded April – July Moderate. Nearest known localities < 5 miles NE of project area at Pepperwood Preserve napensis slopes. 150-200m. (CNDDB 2007, DeNevers 2003).

Amsinckia lunaris bent-flowered None/None/1B.2 Coastal bluff scrub, cismontane woodland, valley and foothill grassland. March-June Low. A wide-ranging species. Nearest known locality near Kenwood, about 10 miles SE of project fiddleneck 3-500m. area (CalFlora 2007, Jepson On-line Interchange 2007).

Anomobryum julaceuma slender silver-moss None/None/List 2.2 Broadleaved upland forest, lower montane coniferous forest, north coast March-June Very Low. Nearest known locality < 5 miles E of the project area, near the intersection of coniferous forest. 100-1000m. Calistoga and St. Helena roads (Norris and Shevock 2004).

Astragalus claranus Clara Hunt's FE/ None/1B.1 Cismontane woodland, valley foothill grassland, chaparral; sometimes on March-May Very Low. Nearest known locality is about 6 miles NE of the project area, near Alpine School on milk-vetch serpentine. 75-275m St. Helena Road (CNDDB 2007, Best et al. 1996). Survey window for this species is very limited, generally first 2 weeks in April.

Balsamorhiza macrolepis big-scale balsamroot None/None/1B.2 Valley and foothill grassland, cismontane woodland; sometimes on March-June Very low. Nearest known locality is about 5 miles S of project area, on Taylor Mt. (CNDDB 2007). var. macrolepis serpentine. 90-1400m

Brodiaea californica var. narrow-anthered None/None/1B.2 Broadleafed upland forest, chaparral, lower mountain coniferous forest, May-July Very Low. Several localities known from within 5 miles of project area (CNDDB 2007, CalFlora leptandra brodiaea cismontane woodland. Gravelly clay or serpentine soils. 110-915m. 2007, Best et al. 1996).

Erigeron biolettii streamside daisy None/None/List 3 Broadleaved upland forest, Cismontane woodland, North Coast coniferous June-October Low. A wide-ranging species. Nearest known location is on Hood Mountain, about 7 miles SE of forest/rocky, mesic. 300-1100m project area (CalFlora 2007, Jepson On-line Interchange 2007). In rocky areas, not typically found near . Blooming time in Sonoma County is usually July-Sept.

Fritillaria liliacea fragrant fritillary None/None/1B.2 Coastal scrub, valley and foothill grasslands, coastal prairie, often on February- April Moderate. A wide-ranging species. Nearest known locality < 5 miles S of project area on Taylor serpentine although various soils reported, usually clay, in grassland. 3-410m Mt. (CNDDB 2007, Best et al. 1996).

Hemizonia congesta ssp. Hayfield tarplant None/None/ List 3 Coastal scrub, valley and foothill grassland. 25-455m April-October Very low. Nearest known localities within 10 miles of project area. (CNPS 2007, Best et al. 1996). leucocephala

Layia septentrionalis Colusa layia None/None/1B.2 Chaparral, cismontane woodland, valley and foothill grassland. 100-1095m April-May Very low. Nearest known locality on Mt. Hood, about 7 miles SE of project area (CNDDB 2007).

Leptosiphon jepsonii Jepson's leptosiphon None/None/1B.2 Chaparral, cismontane woodlands, usually volcanic. 100-500m. April - May Very Low. Nearest known locality at Pepperwood Preserve, < 5 miles NE of project area (CNDDB 2007, DeNevers 2003).

Lessingia hololeuca woolly-headed None/None/ 3.? Broadleaved upland forest, coastal scrub, lower montane conifer forest, June-October Very Low. Nearest known locality “hills east of Santa Rosa,” (E.E. Greene, 1988, type locality); lessingia valley and foothill grassland; often on serpentine or clay soils. 15-305m other localities within 10 miles of project area (Best et al. 1996, Jepson On-line Interchange 2007.

Micropus amphibolus Mt. Diablo None/None/3.2 Broadleaved upland forest, chaparral, cismontane woodland, valley and March-May Very Low. A wide-ranging species. Nearest known locality < 10 miles from project area (Best et cottonweed foothill woodland. 45-825m al. 1996, Jepson On-line Interchange 2007).

Monardella villosa ssp. robust monardella None/None/1B.2 Broadleaved upland forest, chaparral, cismontane woodland, valley and June-July Very Low. Nearest known location is > 10 miles NW of project area, near Healdsburg (historic globosa foothill grasslands, in openings. 30-300m record from late 1800s) (CNDDB 2007).

Trifolium amoenum Showy Indian FE/SE/1B.1 Coastal bluff scrub, valley and foothill grassland; sometimes on serpentine April-June Very Low. Historically a wide-ranging species. Presumed extinct until rediscovered in 1993 near soil. 5-415m Occidental (CNDDB 2007). Reintroductions are being attempted in the Santa Rosa Plain.

Viburnum ellipticum oval-leaved viburnum None/None/ 2.3 Chaparral, cismontane woodland, lower montane coniferous forest. May-June Very Low. A wide-ranging species. Nearest known locations are 5-10 miles NE of project area, 215-1400m along Mark West Springs Road and at Pepperwood Preserve (Best et al. 1996, CNDDB 2007, DeNevers 2003).

PDX/080870002.DOC H-1 APPENDIX H SPECIES TABLES

TABLE H-1 Special-Status Plant Species Potentially Occurring within the Fountaingrove Lodge Study Area Notes: 1. List of potentially occurring special-status plant species compiled from Santa Rosa, Healdsburg, Cotati, Mark West Springs, Kenwood, Glen Ellen, Two Rock, Sebastapol, Calistoga USGS quadrangle search of CNDDB, USFWS Species List, and CNPS Inventory (see source information below). Status Codes: Federal Status FE – Federally listed as endangered FT – Federally listed as threatened State Status CE – State listed as endangered CT – State listed as threatened CR – State listed as rare California Native Plant Society (CNPS) Status 1A – presumed extinct in California 1B – Plants rare, threatened, or endangered in California and elsewhere 2 – Plants rare, threatened, or endangered in California, but more common elsewhere 3 – Plants about which we need more information – a review list 4 – Plants of limited distribution – a watch list CNPS threat code extensions: 1 -- Seriously endangered in California. 2 -- Fairly endangered in California. 3 -- Not very endangered in California. ? -- Not determined. Sources: Best, C., J. T. Howell, W. Knight, I. Knight and M. Wells. 1996. A flora of Sonoma County. California Native Plant Society, Sacramento, California. CalFlora: Information on California plants for education, research, conservation. 2007. Berkeley, California. The CalFlora Database. Available at: http://www.calflora.org/ California Department of and Game. 2007. Information on California Rare, Threatened, and ; Fully Protected Species, and Species of Special concern. Through the California Department of Fish and Game, Habitat Conservation Planning Branch, Species Account website. Available at: http://www.dfg.ca.gov/hcpb/species/search_species.shtml California Natural Diversity Database (CNDDB). 2006. RareFind3. California Department of Fish and Game, Sacramento. California Native Plant Society (CNPS). 2007. Inventory of Rare and Endangered Plants of California. Online edition, v7-07a. California Native Plant Society. Sacramento, CA. Available at: http://cnps.web.aplus.net/cgi-bin/inv/inventory.cgi DeNevers, G. 2003. Draft Pepperwood Flora, Second Edition. California Academy of Sciences, Park, . Norris, D. and J. Shevock. 2004. Contributions toward a bryoflora of California: I. A Specimen-based Catalog of Mosses. Madrono 51(1):1-131. U.S. Department of , 1972. Soil survey of Sonoma County, California. Forest Service and Soil Conservation Service in cooperation with University of California Agricultural Experiment Station. , D.C. U.S. Fish and Service. 2007. Information on California Endangered Plants from the Sacramento U.S. Fish and Wildlife Service Endangered Plants website. Available at: http://www.fws.gov/sacramento/es/plant_spp_accts/acctplant.htm

H-2 PDX/080870002.DOC APPENDIX H SPECIES TABLES

TABLE H-2 Special-status Plant Species without Suitable Habitat Evaluated for the Fountaingrove Lodge Project Scientific Name Common Name USFWS/ CDFG/ CNPS Suitable Habitat for the Species Flowering Period Potential to Occur Alopecurus aequalis var. Sonoma alopecurus FE/None/List 1B.1 Wet areas, and (freshwater), riparian scrub. May-July Moderate. Known to occur at Pitkin about 5 miles north of Sebastopol. Fewer than 10 sonomensis 5-365m populations believed to remain (CNPS, 2007; USFWS, 2007). No suitable habitat within study area. Arctostaphylos canescens Sonoma manzanita None/None/List 1B.2 Chaparral, lower montane coniferous forest. 180-1675m. February-April Threatened by development. No suitable habitat within study area. ssp. sonomensis Arctostaphylos densiflora Vine Hill manzanita None/SE/ List 1B.1 Chaparral; valley and foothill grassland, acidic, sandy soil. 5-120m February-April Low. Known from only one extant occurrence on the Sonoma Barren near Forestville (CNPS, 2007). No suitable habitat within study area. Arctostaphylos Rincon manzanita None/None/List 1B.1 Chaparral, highly restricted to endemic red rhyolites in Sonoma February – April Very Low. Suitable habitat unlikely in project area. Known from fewer than ten occurrences. No red stanfordiana ssp. decumbe County. 75-310m. rhyolites mapped within project boundary (USDA, 1972). Seriously threatened by development, road construction, vehicles, and viticulture. No suitable habitat within study area. bakeri Sonoma sunshine FE/ SE/ List 1B.1 Vernal pools and swales, valley and foothill grasslands. Endemic March-May Low. Project located north of historic range for this species (USFWS, 2007). No vernal pools or to vernal pools and swales in the Santa Rosa Plain and Sonoma swales known to occur within the project boundary. No suitable habitat within study area. Valley. 10-110m Calamagrostis crassiglumis Thurber's reed grass None/None/List 2.1 Coastal scrub, freshwater marsh. Usually in marshy swales May-July Low. Known in California from fewer than 10 occurrences. Nearest known location at Pitkin Marsh surrounded by grassland or coastal scrub. 10-45m north of Sebastopol (CNPS, 2007; CNDDB, 2006). No suitable habitat within study area. Campanula californica harebill None/None/1.B.2 Bogs, fens, closed-cone coniferous forest, coastal prairie, June-October No suitable habitat within study area. meadows, freshwater marsh, north coast coniferous forest. 1-405m Carex albida white sedge FE/ SE/ List 1B.1 Freshwater marsh, bogs and fens, meadows and seeps. 15-90m May-June Low. Known from only one confirmed extant location at Pitkin Marsh, about 5 miles north of Sebastopol (CNDDB 2006). No suitable habitat within study area. Castilleja uliginosa Pitkin Marsh Indian None/SE/ List 1A Freshwater marsh, wet meadow. 60m June-July Low. Last seen at Pitkin Marsh, about 5 miles north of Sebastopol, in 1988. Presumed extinct in paintbrush California (CDFG, 2007; CNDDB 2006). No suitable habitat within study area. confusus Rincon Ridge None/None/List 1B.1 Closed cone coniferous forest chaparral, Cismontane woodland, February – June Very Low. Suitable habitat unlikely in project area. No volcanic or serpentine soils mapped within ceanothus known from volcanic or serpentine soils, dry shrubby slopes. project boundary (USDA, 1972). Threatened by development. No suitable habitat within study area. 75-1065m. Ceanothus divergens Calistoga ceanothus None/None/List 1B.2 Chaparral, cismontane woodland. 170-950m. February-March No suitable habitat within study area. Ceanothus foliosus var. Vine Hill ceanothus None/None/List 1B.1 Chaparral; sandy acidic soil. 45-305m March-May Very Low. Suitable habitat unlikely in project area. Nearly extirpated. Nearly extirpated in SON Co.; vineatus confirmed from only two occurrences. Known from only two occurrences in Sonoma County (one at Vine Hill Preserve, north of Sebastopol) and one historic occurrence in Mendocino County (CNPS 2007; CNDDB, 2006). No suitable habitat within study area. Ceanothus purpureus holly-leaved ceanothus None/None/List 1B.2 Chaparral, rocky, volcanic slopes. 120-640m. February – June Very Low. Suitable habitat unlikely in project area. Threatened by agriculture, residential development, and alteration of fire regimes No known volcanic soils mapped within project boundary (USDA, 1972). No suitable habitat within study area. Ceanothus sonomensis Sonoma ceanothus None/None/List 1B.2 Coastal prairie; sandy soil. 10-305m June-August Low. Thought extinct, but rediscovered in 1980 at Point Reyes National Seashore. Nearest occurrence to project area (Sebastopol) is believed to be extirpated. Known from approximately ten occurrences; only one occurrence known from NAP Co. Seriously threatened by development. (CNPS, 2007; CNDDB 2006). No suitable habitat within study area. parryi ssp. pappose tarplant None/None/1B.2 Coastal prairie, meadows and seeps, coastal salt marsh, valley May-Nov No suitable habitat within study area. parryi and foothill grassland. 2-420m valida Sonoma spineflower FE/ SE/ List 1B Coastal prairie. 10-50m. No suitable habitat within study area. Clarkia imbricata Vine Hill clarkia FE/SE/List 1B.1 Chaparral, valley and foothill grassland; acidic sandy loam soil. June-August Low. Known from two extant populations, one of which is introduced. Third natural occurrence has 50-75m been extirpated. All three occurrences within Vine Hill area of Sebastopol. (CNPS 2007; CNDDB 2006) No suitable habitat within study area. Cordylanthus tenuis ssp. Pennell's bird's-beak FE/None/List 1B.2 Closed-Cone coniferous forest, Chaparral, in open or disturbed June – Sept Very Low. Suitable habitat unlikely within project area. Known from fewer than five occurrences capillaris areas on serpentine, within forest or chaparral. 45-305m (CNPS, 2007). No suitable habitat within study area. luteum yellow larkspur FE/None/ List 1B Chaparral, coastal prairie, coastal scrub; rocky north facing slopes. March-May Very low. Suitable habitat unlikely within project area. Known from only four occurrences. Nearest 0-100m location to project area, near Graton, has not been seen since 1925 (CNPS, 2007; CNDDB 2006). No suitable habitat within study area. Downingia pusilla dwarf downingia None/None/List 2.2 Valley and foothill grassland, vernal pools. 1-445m March-May High. A wide-ranging species. Threatened by urbanization, development, agriculture, , vehicles, and industrial forestry. Known to occur at several locations in the vicinity of the project area (Windsor) (CNDDB 2006). No suitable habitat within study area.

PDX/080870002.DOC H-3 APPENDIX H SPECIES TABLES

TABLE H-2 Special-status Plant Species without Suitable Habitat Evaluated for the Fountaingrove Lodge Project Scientific Name Common Name USFWS/ CDFG/ CNPS Suitable Habitat for the Species Flowering Period Potential to Occur Erigeron serpentinus serpentine daisy None/None/List 1B.3 Serpentine shrubland. 210m May-August Very Low. Suitable habitat unlikely within project area. No serpentine mapped in project boundary (USDA, 1972). Known only from The Cedars and along Porter Creek (CNPS, 2007; CNDDB, 2006, Best et al, 1996). No suitable habitat within study area. Eryngium constancei Loch Lomond FE/SE/List 1B.1 Vernal pools. 460-855m April-June No suitable habitat within study area. thistle Gilia capitata ssp. woolly-headed gilia None/None/List 1B.1 Coastal scrub. 15-155m May-July Known from only three occurrences near Tomales and Salt Pt. SP. Threatened by urbanization, tomentosa road maintenance, and . No suitable habitat within study area. Horkelia tenuiloba thin-lobed horkelia None/None/List 1B.2 Coastal scrub, chaparral, in sandy soils and mesic openings. May-July Low. Historical occurrences need field work. Known from Pitkin Marsh and Vine Hill Area north of 45-500m Sebastopol (CNPS, 2007; CNDDB 2006; Best et al 1996). No suitable habitat within study area. Burke's goldfields FE/SE/List 1B.1 Vernal pools, meadows and seeps, most often in vernal pools and April-June Moderate. Several occurrences in vicinity of project area near Windsor, at the Sonoma County swales. 15-580m Airport, Shiloh Road and Starr Road (CNPS, 2007; CNDDB 2006). No suitable habitat within study area. Lasthenia conjugens Contra Costa goldfields None/ None/List 1B Cismontane woodland, playas, valley and foothill grassland, and March-June No suitable habitat within study area. vernal pools. 0-470m Lastheniamacrantha ssp Baker’s goldfields None/None/1B.2 Closed-cone coniferous forest, coastal scrub. 60-520m April-October No suitable habitat within study area. bakeri Legenere limosa Legenere None/None/List 1B.1 Vernal pools. 1-880m April-June Very Low. Suitable habitat unlikely within project area. Many historical occurrences extirpated. Threatened by grazing, and development. No occurrences recorded within 5 miles of project area (CNDDB 2006). No suitable habitat within study area. Lilium pardalinum ssp. Pitkin Marsh lily FE/SE/List 1B.1 Cismontane woodlands, meadows and seeps, marshes and June-July Low. Known from only 3 recorded locations, all from the Sebastopol and Cunningham areas of pitkinense swamps (freshwater). 33-65m Sonoma County (CDFG, 2007). No suitable habitat within study area. Sebastopol FE/SE/List 1B.1 Meadows and seeps, valley and foothill grassland, vernal pools/ April-May Low. Graton is the northernmost location of this species’ historic range. No occurrences recorded meadowfoam vernally mesic, seasonal in the vicinity of the Laguna de within 5 miles of project site (CNPS, 2007; CNDDB, 2006). No suitable habitat within study area. Santa Rosa. 15-305m Lupinus sericatus Cobb Mountain lupine None/None/List 1B.2 Chaparral, cismontane woodland, lower montane coniferous forest. March-June No suitable habitat within study area. 180-1525m Microseris paludosa marsh microseris None/None/List 1B.2 Closed-cone coniferous forest, cismontane woodland, coastal April-May Moderate. Nearest recorded location in the vicinity of Old Redwood Road north of Windsor (historic, scrub, valley and foothill grassland. 5-300m non-specific) (CNPS 2007; CNDDB 2006). No suitable habitat within study area. Navarretia leucocephala Baker's navarretia None/None/List 1B.1 Cismontane woodlands, lower montane coniferous forest, May-July Moderate. Widespread occurrences in vicinity of project site, near Windsor (CNDDB, 2006). No ssp. bakeri meadows and seeps, valley and foothill grasslands, vernal pools/ suitable habitat within study area. mesic. 5-1,740m Navarretia leucocephala many-flowered FE/SE/List 1B.2 Vernal pools; volcanic ash flow. 30-950m May-June Low. No known vernal pools in project area. Known from approximately seven occurrences (CNPS ssp. plieantha navarretia 2007; CNDDB 2006). No suitable habitat within study area. Penstemon newberryi var. Sonoma beardtongue None/None/List 1B.3 Chaparral. 700-1370m April-August No suitable habitat within study area. sonomensis Plagiobotrys strictus Calistoga pop-corn FE/ST/1B.1 Broadleaf upland forest, meadows and seeps, valley and foothill May-June No suitable habitat within study area. grassland, vernal pools. 90-160m North Coast None/ST/List 1B.1 Broadleaf upland forest, meadows and seeps, marshes and April-June Moderate. A wide-ranging species. Nearest recorded observance is in Freestone area, although semaphore grass swamps (freshwater), North coast coniferous forest, vernal may be extirpated from this site (CNPS, 2007; CNDDB 2006). No suitable habitat within study area. pool/mesic. 10-635m Poa napensis Napa bluegrass FE/SE/List 1B Broadleafed upland forest, Meadows and seeps, North Coast April-August No suitable habitat within study area. coniferous forest/open areas, mesic. 10-671m. Potentilla hickmanii Hickman's cinquefoil FE/SE/List 1B.1 Coastal bluff scrub, closed-cone coniferous forest, meadows and April-August No suitable habitat within study area. seeps, marshes and swamps. 10-135m Rhynchospora alba white beaked-rush None/None/List 2.2 Bogs and fens, meadows and seeps, marshes and swamps July-August Low. Unconfirmed in recent years from nearest known location at Pitkin Marsh, about 5 miles north (freshwater). 60-2,040 of Sebastopol (CNDDB 2006). No suitable habitat within study area. Rhynchospora californica California beaked-rush None/None/List 1B.1 Bogs and fens, lower montane coniferous forest, meadows and May-July Low. Nearest known locations are Perry Marsh and Pitkin Marsh north of Sebastopol. Observed at seeps, marshes and swamps (freshwater). 45-1,010m Perry Marsh in 1945, but not found during recent searches. Last observed at Pitkin marsh in 1977 (CNDDB 2006). No suitable habitat within study area.

H-4 PDX/080870002.DOC APPENDIX H SPECIES TABLES

TABLE H-2 Special-status Plant Species without Suitable Habitat Evaluated for the Fountaingrove Lodge Project Scientific Name Common Name USFWS/ CDFG/ CNPS Suitable Habitat for the Species Flowering Period Potential to Occur Rhynchospora capitellata brownish beaked-rush None/None/List 2.2 Lower montane coniferous forest, meadows and seeps, marshes July-August Low. Unconfirmed in recent years from nearest known locations at Perry Marsh and Pitkin Marsh, and swamps (freshwater), upper montane coniferous forests. north of Sebastopol (CNDDB 2006). No suitable habitat within study area. 455-2,000m Rhynchospora globularis round-headed None/None/List 2.1 Marshes and swamps (freshwater). 45-60m July-August Low. Known from Sonoma County in two locations, Pitkin and Perry Marshes north of Sebastopol. var. globularis beaked-rush Last seen in Perry Marsh in 1945. Last seen in Pitkin Marsh in 1987 (CNDDB 2006). No suitable habitat within study area. hickmanii ssp Marin checkerbloom None/None/1B.3 Chaparral. 50-430m May-June No suitable habitat within study area. viridis Sidalcea oregana ssp. Kenwood Marsh FE/SE/List 1B.1 Freshwater marshes and swamps, specifically edges of freshwater June-September No suitable habitat within study area. valida checkerbloom marshes. 115-150m Trifolium buckwestiorum Santa Cruz clover None/None/List 1B.1 Broadleafed upland forest, Cismontane woodland, Coastal prairie/ April-October No suitable habitat within study area. margins. 105-610m Trifolium depauperatum saline clover None/None/List 1B.2 Marshes and swamps, valley and foothill grassland, vernal pools in April – June Low. Many sites likely extirpated. Historic occurrences in project vicinity (Santa Rosa and var. hydrophilum mesic, alkaline sites. 0-300m. Occidental) extirpated (CNPS, 2007; CNDDB, 2006). No suitable habitat within study area. Notes: 1. List of potentially occurring special-status plant species compiled from Santa Rosa, Healdsburg, Cotati, Mark West Springs, Kenwood, Glen Ellen, Two Rock, Sebastapol, Calistoga USGS quadrangle search of CNDDB, USFWS Species List, and CNPS Inventory (see source information below). Status Codes: Federal Status FE – Federally listed as endangered FT – Federally listed as threatened State Status CE – State listed as endangered CT – State listed as threatened CR – State listed as rare California Native Plant Society (CNPS) Status 1A – Plants presumed extinct in California 1B – Plants rare, threatened, or endangered in California and elsewhere 2 – Plants rare, threatened, or endangered in California, but more common elsewhere 3 – Plants about which we need more information – a review list 4 – Plants of limited distribution – a watch list CNPS threat code extensions: 1 -- Seriously endangered in California. 2 -- Fairly endangered in California. 3 -- Not very endangered in California. ? -- Not determined. Sources: Best, C., J. T. Howell, W. Knight, I. Knight and M. Wells. 1996. A flora of Sonoma County. California Native Plant Society, Sacramento, California. CalFlora: Information on California plants for education, research, conservation. 2007. Berkeley, California. The CalFlora Database. Available at: http://www.calflora.org/ California Department of Fish and Game. 2007. Information on California Rare, Threatened, and Endangered Species; Fully Protected Species, and Species of Special concern. Through the California Department of Fish and Game, Habitat Conservation Planning Branch, Species Account website. Available at: http://www.dfg.ca.gov/hcpb/species/search_species.shtml California Natural Diversity Database (CNDDB). 2006. RareFind3. California Department of Fish and Game, Sacramento. California Native Plant Society (CNPS). 2007. Inventory of Rare and Endangered Plants of California. Online edition, v7-07a. California Native Plant Society. Sacramento, CA. Available at: http://cnps.web.aplus.net/cgi-bin/inv/inventory.cgi DeNevers, G. 2003. Draft Pepperwood Flora, Second Edition. California Academy of Sciences, Golden Gate Park, San Francisco. Norris, D. and J. Shevock. 2004. Contributions toward a bryoflora of California: I. A Specimen-based Catalog of Mosses. Madrono 51(1):1-131. U.S. Department of Agriculture, 1972. Soil survey of Sonoma County, California. Forest Service and Soil Conservation Service in cooperation with University of California Agricultural Experiment Station. Washington, D.C. U.S. Fish and Wildlife Service. 2007. Information on California Endangered Plants from the Sacramento U.S. Fish and Wildlife Service Endangered Plants website. Available at: http://www.fws.gov/sacramento/es/plant_spp_accts/acctplant.htm

PDX/080870002.DOC H-5 APPENDIX H SPECIES TABLES

TABLE H-3 Wildlife Species Potentially Occurring within the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur

Fish

Lavinia symmetricus Navarro roach None/CSC Habitat generalist, found in warm intermittent streams as well as Russian and it tributaries. Very Low. Piner Creek, an intermittent creek that crosses the southern navarroensis cold well-aerated streams. portion of the study area is a tributary to the Russian River and could be a potentially suitable habitat. Considered unlikely to occur due to potential fish barriers down and uncertain use of intermittent creeks by this species; however, it could be a potential seasonal inhabitant.

Amphibians

Rana boylii Foothill yellow-legged None/CSC Rocky streams in a variety of habitats, including valley-foothill Found throughout most of California’s Coastal Range Low. Unlikely to occur based on quality of habitat. Species unlikely to hardwood or hardwood-conifer, valley-foothill riparian, ponderosa and Sierra range into . occur during the dry season; however, potential seasonal inhabitant for pine, mixed conifer, coastal scrub, mixed chaparral, and wet breeding or could use Piner Creek, an intermittent creek that crosses the meadow types southern portion of the study area, as a migration corridor between permanent water sources during the wet season.

Rana aurora draytonii1 California red-legged FT3/CSC Humid forests, woodlands, grasslands, and streamsides with Ranges along the coast from Mendocino County in Low. Species unlikely to occur during the dry season; however, potential frog2 plant cover. Most common in lowlands or foothills. Frequently south to northern Baja California, seasonal inhabitant for breeding or could use Piner Creek, an intermittent found in woods adjacent to streams. Breeding habitat is in and inland through the northern into creek that crosses the southern portion of the study area, as a migration permanent water sources the foothills of the mountains, south to corridor between permanent water sources during the wet season. Tulare county, and possibly Kern county. A narrow range overlap with Rana aurora occurs in Mendocino

Reptiles

Emys (=Clemmys) Northwestern pond None/CSC Inhabits ponds, marshes, , streams and irrigation ditches Washington State to central California. Low. Possible seasonal inhabitant or migrant. Piner Creek, an intermittent marmorata marmorata4 turtle with aquatic vegetation. Upland sandy banks or grassy open creek that crosses the southern portion of the study area could be used as fields. Known to migrate considerable distances overland. a migration corridor between more permanent water sources at Fountaingrove Lake and an unnamed impoundment west of study area.

Emys (=Clemmys) Western pond turtle None /CSC Inhabits ponds, marshes, rivers, streams and irrigation ditches Washington, Oregon, California, Nevada and Idaho Low. Possible seasonal inhabitant or migrant. Piner Creek, an intermittent Marmorata 4 with aquatic vegetation. Upland sandy banks or grassy open from sea level to around 5000 feet. creek that crosses the southern portion of the study area could be used as fields. Known to migrate considerable distances overland. a migration corridor between more permanent water sources at Fountaingrove Lake and an unnamed impoundment west of study area.

Birds

*Accipiter cooperii Cooper’s hawk None/CSC Mixed forest habitat such as riparian, oak woodland, and conifer. Wide spread throughout California. Moderate. Potentially suitable nesting sites within mixed oak woodland, (Nesting) foraging habitat found throughout the study area. Year-round resident within this region.

Accipiter striatus Sharp-shinned hawk None/CSC Dense wooded habitats including, riparian deciduous and mixed Found throughout California. Moderate. Suitable nesting within mixed oak woodland, foraging habitat (Nesting) conifer habitats with north facing slopes. found throughout the study area. Potential year-round resident in this region.

Haliaeetus Bald eagle (Nesting FT, FPD /SE/CFP Requires large bodies of water for foraging on fish and water Throughout northern California, Oregon and Low. No suitable nesting habitat within the study area. Potential nesting leucocephalus and Wintering) birds. Nests and roosts in large old growth trees or snags in Washington north. habitat within ½ mile of site at Fountaingrove Lake. conifer and redwood forests. Courtship and nesting occurs January through August.

Elanus leucurus White-tailed kite None/CFP Forages in undisturbed, open grasslands, meadows, farmlands Fairly common resident with a large range west of the Moderate. Suitable nesting and foraging habitat occurs in various and emergent wetlands/Nests at top of dense oak, willow, or Sierra Nevada. locations within the study area. Potential nesting trees within study area. other tree stand; usually 6-20 m above ground and near open foraging area

Pandion haliaetus Osprey (Nesting) None /CSC Forages along ocean shore, bays, fresh-water lakes, and large Breeds from across Canada, southward locally Low to Moderate. No known nesting structures occur within the study streams. Nests built in tops of large trees within 15 miles of good and along coasts to Mexico and Caribbean. area. Potential suitable nesting locations could occur within ½ mile of the fish producing bodies of water. study area in proximity to Fountaingrove Lake.

PDX/080870002.DOC H-7 APPENDIX H SPECIES TABLES

TABLE H-3 Wildlife Species Potentially Occurring within the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur

*Asio otus Long-eared owl None/CSC Dense stands of oak woodlands, riparian woodland near meadow Found throughout the northern hemisphere. Their Moderate. Potential nesting habitat occurs within the mixed oak woodland (Nesting) edges range extends throughout temperate in portions of the study area. The study area and proximity to Fountaingrove Lake also provides open foraging habitat for this species.

Athene cunicularia Burrowing owl None/CSC Open, annual or perennial grasslands, deserts and scrubland, Present in North America, and breed across the Low. Potential open grassland habitat in portions of the study area. with low growing vegetation. Subterranean nester, dependent on grassland regions of southern Alberta, Saskatchewan Limited burrow components required by this species (i.e., man-made burrowing . and Manitoba. They occur in all states west of the structures or ground burrowing structures). Mississippi Valley, breed south through the western and mid-western States.

*Selasphorus rufus Rufous BCC/None Breeds in forested and brushy habitats. Found in montane Breeds from southern Alaska southward to very Low. Potential nesting habitat exists within the study area. Unknown if this (Nesting) meadows and disturbed areas on migration. Winters in oak northern California, south central Idaho, and western species breeds in this region. forests with scattered pines and junipers, and in brush and Montana. Winters from southern California, through scrublands in Mexico. Mexico, and along northern Gulf Coast. Frequent vagrant to eastern states.

*Contopus cooperi Olive-sided flycatcher BCC/None Breeds in montane and northern coniferous forests, at forest Breeds from central Alaska across Canada to Low. Potential nesting habitat within the study area. Unknown if this (Nesting) edges and openings, such as meadows and ponds. Winters at Newfoundland and south to the northern species breeds in this region. forest edges and clearings where tall trees or snags are present. in the East, and south through the Mountain West to western Texas and Baja California.

*Dendroica petechia Yellow warbler None/CSC Riparian, open to medium density woodlands and forest with a Throughout the Untied States, common to uncommon Moderate. Potentially suitable nesting habitat within the mixed oak brewsteri (Nesting) heavy brush understory. resident in the northern portion of California, more woodland or riparian portions of the study area. common in southern California

*Icteria viren Yellow-breasted chat None/CSC Nest in low, dense riparian thickets Dense second-growth, and Breeds across eastern United States and southern Low. Potential nesting habitat exists within the riparian portion of the study (Nesting) brush: including willow, blackberry and wild grape. Canada from Iowa to New York, southward to Texas area. Dense vegetation component is limited within the study area. and northern Florida. Also in scattered regions across West from southern Canada to very northern Mexico.

*Lanius ludovicianus Loggerhead shrike None/CSC Open habitat with sparse and trees, suitable perches, Southern Canada through the lower 48 states to Low. Suitable nesting habitat within the mixed oak woodland and coyote (Nesting) bare ground, and low or sparse herbaceous cover. southern Mexico. brush is found in portions of the study area. Good foraging habitat occurs in the open grassland and adjacent golf course habitats. However, oak woodland habitats are not typical habitat for this species.

Mammals

Antrozous pallidus Pallid bat None/CSC Inhabits rocky, outcrop areas where they commonly roost in rock Pallid bat ranges from to Texas. Moderate. Potential for cavities and snags to provided suitable roosting crevices, caves, and mine tunnels but they also roost in the attics habitat within the mixed oak woodland habitat portions of the study area. of houses, under the eaves of barns, behind signs, in hollow trees.

*Corynorhinus Pacific western None/CSC Occurs in a variety of habitats, from desert to deciduous Found throughout California, but details of distribution Low. Potential for cavities and snags in conjunction with maternity townsendii townsendii (Townsend’s) and coniferous forests at a wide range of elevations. Also occurs unknown. Species found in all but subalpine and alpine colonies. Undocumented use of oak woodland snags and cavities in this big-eared bat in abandoned mines and both unoccupied and actively used old habitats. Year long resident. habitat. buildings It is probable that hollow cavities in large trees or snags may constitute an important undocumented resource for maternity colonies of this species.

Myotis thysanodes Fringed myotis None/None Roosts in rock crevices, buildings, tree bark, snags, mines and Widespread in California occurring in all but the Central Moderate. Potential for cavities and snags to provided suitable roosting caves. Trees are the most important daytime roosts for this Valley. and maternity roosts (breeding colony) habitat within the mixed oak species. woodland habitat portions of the study area.

*Myotis yumanensis Yuma myotis None/None Day roosts are found in cavities in buildings, trees, mines, caves, Found throughout most of California at lower elevations Moderate. Potential for cavities and snags to provided suitable roosting bridges, and rock crevices. Night roosts are usually associated in a wide variety of habitat. Due to the presence of and maternity roosts (breeding colony) habitat within the mixed oak with buildings, bridges and other open man-made structure. mature trees on site suitable habitat exists for this woodland habitat portions of the study area. species.

H-8 PDX/080870002.DOC APPENDIX H SPECIES TABLES

TABLE H-3 Wildlife Species Potentially Occurring within the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur

Taxidea taxus American Badger None/CSC Prefer to live in dry, open grasslands, fields, and pastures. They Throughout the western United States were suitable Very Low. Limited open grassland habitat component required by this are found from high alpine meadows to sea level (or below in habitat occurs. species exists within the study area. Death Valley, California).

The information summarized in this table was compiled from the following sources: California Natural Diversity Data Base, Rarefind (CNDDB) USGS Quads: Calistoga, Cotati, Glen Ellen, Healdsburg, Kenwood, Mark West Springs, Santa Rosa, Sebastopol, Two Rocks. U.S. Fish and Wildlife Endangered and Threatened species that occur or may be affected by the Project. Biological Resource Assessment Report, February 2007, Fountainlodge Santa Rosa, Sonoma County, California. Prepared by WRA Environmental Consultants. All species were addressed within this report were considered and ones with a likelihood of occurring within the study area are included in this table footnoted with * (see below). Species not included in this table, but included in the WRA’s report includes: Pacific western big-eared bat (Corynorhinus townsendii townsendii), Greater mastiff bat (Eumops perotis californicus), Golden eagle (Aquila chrysaeros), Northern Harrier (Circus cyaneus), Prairie falcon (Falco mexicanus), Lon-billed curlew (Numenius americanus), short-eared owl (Asio flammeus), Vaux’s swift (Chaetura vauxi), black swift (Cypseloides niger), Lewis’s woodpecker (Melanerpes lewis), purple martin (Progne subis), bank swallow (Riparia riparia), yellow-breasted chat (Icteria virens), Bell’s sage sparrow (Amphispiza belli), California horned lizard (Phrynosoma coronatum frontale), Western spadefoot toad (Scaphiopus (Spea) hammondii), Federal Status: FT: Federally Threatened. BCC: USWFS Birds of Conservation Concern State Status: CSC: California Species of Special Concern. CFP: California Fully-Protected species. * Wildlife potentially occurring within the project area addressed in the February 2007 Biological Resource Assessment Report, but not included in the CNDDB or FWS Species lists. 1 WRA list the Northern Red-legged frog, study area is outside of range of this species. CNDDB, and USFWS site and show occurrences for California Red-legged frog for this region. The southern range for the Northern red-legged frog (Rana aurora aurora) is in Mendocino County north to Oregon. 2 Rana aurora aurora and Rana aurora draytonii should be recognized as separate species with a narrow band of overlap, range for draytonii extends about 100 km further north in coastal California than previously thought. 3 Federal Listing does not included Humboldt, Trinity, and Mendocino Counties; Glenn, Lake, & Sonoma Counties west of the Central Valley Hydrologic Basin; Sonoma & Marin Counties north and west of the , Sonoma Creek & drainages which flow into the , & north of the Walker Creek drainage which flows to the Pacific Ocean. 4 Unclear distinction between species and subspecies, both species addressed as one species in text, “western pond turtle” (Emys (=Clemmys) marmorata).

PDX/080870002.DOC H-9 APPENDIX H SPECIES TABLES

TABLE H-4 Wildlife Species without Habitat Components within the Study Area, Evaluated for the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur Invertebrates Caecidotea tomalensis Tomales isopod None/None The Tomales isopod inhabits freshwater ponds and Inhabits localized fresh-water ponds and streams with still or near-still No suitable habitat within the study area. streams using dense mats of marsh pennywort water in bay area counties. (Hydrocotyle spp.) and decaying leaves for attaching eggs Hydroporus leechi Leech’s skyline diving None/None Aquatic Previously considered limited to the . Now No suitable habitat within the study area. beetle believed to be distributed widely throughout the western United States. Proposed to remove from potential federal listing action California freshwater FE/SE Slow-moving creeks with undercut banks in association Endemic to Marin, Napa, and Sonoma Counties, in low elevation, low No suitable habitat within the study area. shrimp with roots and grasses in water gradient streams. No suitable habitat found in project impact areas. occidentalis California linderiella None/None Inhabit clear to tea-colored water in seasonal ponds, Widespread species found throughout most of California. One recorded No suitable habitat within the study area. fairy shrimp which range in size from square feet to many acres, and occurrence approximately 4 miles to the northeast. are typically located in grasslands or in depressions of Andrena andrenid None / None Upland areas near vernal pools. Inner Coast Ranges (Contra Costa, Lake, Sonoma, and Yolo No suitable habitat within the study area. blennospermatis bee Counties), also includes Tehama, Solano, San Joaquin, Sacramento, El Dorado, and Placer Counties. Fish Hypomesus pacifica FT/ST For most of their one-year life span, delta smelt live along upstream through the Delta in Contra Costa, Sacramento, No suitable habitat within study area and outside of known the freshwater edge of the mixing zone. They spawn in San Joaquin, Solano and Yolo counties. Their historic range is thought range. shallow, fresh or slightly brackish water upstream of the to have extended from Suisun Bay upstream to at least the city of mixing zone. Sacramento on the and Mossdale on the . Oncorhynchus mykiss Central California FT1/NMFS Found in tributaries to the San Francisco Bay. Pass This ESU includes all naturally spawned populations in coastal No suitable habitat within the upper reaches of Piner Coastal Steelhead ESU through the San Francisco Estuary during migration to drainages from the Russian River basin south to Santa Cruz County, Creek (an intermittent creek). While steelhead have streams for spawning, and during outmigration to the and in the San Francisco/ basin as far east as the Napa been documented in lower reaches, (Sept. 2005 Sonoma ocean. Spawn in small streams and tributaries with cold, River County Water Agency), potential barriers occur to certain clean water flowing over graveled bottoms and deep pools life stages. No documented occurrences in study area. Oncorhynchus mykiss Central Valley FT2/NMFS Found in tributaries to the San Francisco Bay, including This ESU includes all naturally spawned steelhead populations in the No suitable habitat within study area and outside of known Steelhead ESU the south Bay. Pass through the San Francisco Estuary Sacramento and San Joaquin Valley. This ESU occupies stream range. during migration to streams for spawning, and during reaches in its geographical range flowing into the Sacramento and San outmigration to the ocean. Spawn in small streams and Joaquin Rivers and tributaries tributaries with cold, clean water flowing over graveled bottoms and deep pools Oncorhynchus kisutch Central California, FT3/SE4/NMFS Found in the Sacramento and San Joaquin Rivers and This ESU includes all naturally spawned steelhead populations in the No suitable habitat within study area and outside of known Coho salmon ESU tributaries. Out going migration to the San Francisco Bay. Sacramento and San Joaquin Valley. This ESU occupies stream range. reaches in its geographical range flowing into the Sacramento and San Joaquin Rivers and tributaries Oncorhynchus kisutch Central California FE/NMFS California populations found principally in the Klamath, This ESU encompasses all naturally spawned populations in rivers and No suitable habitat within the study area. Coast, coho salmon Trinity, Mad, Noyo, and Eel Rivers. Rare in Sacramento tributaries from San Lorenzo River in Santa Cruz County north to Punta River and tributaries to the San Francisco Bay Gorda in Mendocino County. Coho salmon are limited to very small runs that migrate through the Russian River including its tributaries. Oncorhynchus Central Valley FT5/NMFS/ST Chinook require cool water while they mature in Sacramento River and its tributaries. The ESU is limited to only three No suitable habitat within study area and outside of known tshawytacha spring-run ESU freshwater over the summer. natural populations of spring-run (on Mill, Deer, and Butte Creeks) that range. have consistent spawning runs, one small and largely unknown population on the Yuba River, and a Feather River population Oncorhynchus Central Valley fall/late FC/NMFS/FSC Lower rivers and tributaries, valley floor and foothill reach. Population spawning in the Sacramento and San Joaquin Rivers and No suitable habitat within study area and outside of known tshawytacha fall-run ESU Chinook Upper mainstem rivers including the upper mainstem their tributaries. range. salmon reaches of the Sacramento River and major tributaries (currently blocked by Shasta ), Juveniles require summer cold water flows.

PDX/080870002.DOC H-11 APPENDIX H SPECIES TABLES

TABLE H-4 Wildlife Species without Habitat Components within the Study Area, Evaluated for the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur Oncorhynchus California Coastal FT6/NMFS Found in tributaries to the San Francisco Bay. Pass This ESU includes all naturally spawned populations from the Russian No suitable habitat within the upper reaches of Piner tshawytacha Chinook salmon ESU through the San Francisco Estuary during migration to River watershed north to Redwood Creek in Humboldt County. Creek (an intermittent creek). While steelhead trout have streams for spawning, and during outmigration to the been documented in lower reaches, (Sept. 2005 Sonoma ocean. Spawn in well oxygenated water in swift, shallow County Water Agency), potential barriers occur to certain riffles, or at edges of fast runs with loose gravel life stages. No documented occurrences in study area. Hysterocarpus traskii Russian River tule None/CSC Low elevation streams of the Russian River system, with Russian River and it tributaries. No suitable habitat within the study area. pomo perch clear, flowing water with abundant cover, also require deep (>1 m) pool habitat Critical Fish Habitat Oncorhynchus mykiss Critical Habitat, NMFS Critical Habitat is designated for this ESU in all occupied stream No suitable habitat within the study area. California Coastal reaches in its geographical range, including those adjacent to the study steelhead area. (See Central California Coast Steelhead Species Distribution). Oncorhynchus kisutch Critical Habitat, Central NMFS Critical Habitat is designated for this ESU in all occupied stream No suitable habitat within the study area. California Coast, coho reaches in its geographical range, including those adjacent to the study salmon area. (See Central California Coast Steelhead Species Distribution. Central California Coast, Coho Salmon). Oncorhynchus Critical habitat, Central FC/NMFS No suitable habitat within study area and outside of known tshawytacha Valley fall/late fall –run range. Chinook salmon Oncorhynchus Critical Habitat, NMFS Critical Habitat is designated for this ESU in all occupied stream No suitable habitat within the study area. tshawytacha California Coastal reaches in its geographical range, including those adjacent to the study Chinook Salmon area. (See California Coastal Chinook Salmon). Ambystoma California tiger FT/CSC Breeds in freshwater ponds or vernal pools, in association Historically, the CTS distribution was throughout California’s Not within range of the Central Population. See Sonoma californiense salamander, Central with upland areas with small mammal burrows in oak Sacramento and San Joaquin River Valleys, surrounding foothills and County Population. Population and grassland habitats. westward in the lower elevations of California’s central Coast Current distribution is concentrated in the northern part of their historical range and their populations exist in disjunct vernal pool complexes Ambystoma California tiger FE/CSC Breeds in freshwater ponds or vernal pools, in association The Sonoma County population of CTS is an isolated and genetically No suitable habitat present within the study area. californiense salamander, Sonoma with upland areas with small mammal burrows distinct population of this species in the Santa Rosa Plain. Portions of County Population Marin, Sonoma, and Napa Counties Birds Agelaius tricolor Tricolored blackbird None/CSC Open water with a variety of well protected nesting Sacramento and San Joaquin valleys. The range extends to western No suitable nesting habitat within the study area. (Nesting Colony) substrate with adjacent foraging habitats. foothills of Sierra Nevada, foothills of Coast Ranges, and some coastal areas of northern and southern California. It also breeds at several locations scattered throughout Oregon. Ardea herodias Great blue heron None/ None Colonial nester in tall trees. Found near forage areas such Throughout California were suitable habitat exists. Unlikely habitat for rookery within the study area. No (Rookery) as marshes, lake margins, -flats, rivers, streams and recorded rookery within the study area. wet meadows. Coccyzus americanus Western yellow-billed FC/SE/BCC Nest in riparian forests with willows, cottonwoods, and Current nesting range has contracted to west of the Sierra Nevada in No suitable habitat. Limited riparian habitat within the occidentalis (nesting) cuckoo understory of blackberry, nettles and wild grape the Central Valley of California with a northern limit also in the Central study area is not sufficient. Species needs dense riparian Valley along a small section of the Sacramento River and extending habitat for nesting. southward into northern Mexico. Falco peregrinus American peregrine FD/SE Nest near wetlands, lakes, rivers or other water; Cliffs, It is found on all continents except Antarctica. In most parts of the No suitable nesting habitat occurs within the study area. anatum falcon (Nesting) banks, dunes and human made structures. world, it is absent only in the high mountains, in large tracts of desert or jungle, and on isolated islands in the oceans. The American Peregrine Falcon breeds in Mexico, the United States, and Canada.

H-12 PDX/080870002.DOC APPENDIX H SPECIES TABLES

TABLE H-4 Wildlife Species without Habitat Components within the Study Area, Evaluated for the Fountaingrove Lodge Study Area Regulatory Status Scientific Name Common Name Federal/State Suitable Habitat for the Species Species Distribution Potential to Occur Sternula antillarum California least tern FE/SE/CFP Formerly these terns regularly nested on sandy beaches California coast between Santa Barbara and San Diego, with some No suitable nesting habitat within the study area. (=Sterna, =albifrons) (Nesting Colony) and mudflats near the ocean. Currently nest on mudflats nesting sites documented as far north as San Francisco Bay and as far browni away from the ocean and man-made landfills. These south as southern Baja California. Current breeding range of these terrestrial sites have made the nesting terns and their terns is limited to San Francisco Bay and a few areas along the coast chicks increasingly vulnerable to predation. from San Luis Obispo County to San Diego County Strix occidentalis Northern spotted owl FT/None Prefers mature old-growth forests and densely wooded The distribution of the northern subspecies includes southwestern No suitable nesting habitat within the study area. caurina areas which have large trees with a multilayered canopy British Columbia, western Washington and Oregon, and northwestern enclosure. California south to Marin County. The southeastern boundary of its range is the Pit River area of Shasta County, California Brachyramphus Marbled Murrelet FT/SE Nesting sites are in high elevations, exclusively in old Along the Pacific coast of North America, as far south as northern No suitable nesting habitat within the study area. marmoratus (Nesting) growth forests of 175-600 years in age. Forages in coastal California. In North America, the normal range of the birds is within 70 waters close to shore on small fish and invertebrates. km of salt water, west of the coastal mountains. Mammals

Reithrodontomys Salt-marsh harvest FE/SE/CFP Critically dependent on dense cover, preferred habitat is Found only around the San Francisco, San Pablo and Suisun Bays. No suitable habitat exists in the study area. raviventris mouse pickleweed (Salicornia virginica). In marshes with an The water in the wetlands and marshes of the Sacramento-San upper zone of peripheral halophytes (salt-tolerant plants), Joaquin Delta was probably too fresh to support the mice, therefore the mice use this vegetation to escape the higher , and Collinsville- Antioch area is the eastern limit of their distribution. may even spend a considerable portion of their lives there. Mice also move into the adjoining grasslands during the highest winter tides. The information summarized in this table was compiled from the following sources: California Natural Diversity Data Base, Rarefind (CNDDB) USGS Quads: Calistoga, Cotati, Glen Ellen, Healdsburg, Kenwood, Mark West Springs, Santa Rosa, Sebastopol, Two Rocks. U.S. Fish and Wildlife Endangered and Threatened species that occur or may be affected by the Project. Federal Status: FE: Federally Endangered. FT: Federally Threatened. FSC: Federal Species of Concern. FC: Federal Candidate Species. FPD: Federally proposed for delisting. FD: Federally Delisted. BCC: USFWS Birds of Conservation Concern State Status: SE: California Endangered. ST: California Threatened. CSC: California Species of Special Concern. CFP: California Fully-Protected species. NOAA Status: NMFS: Species under the jurisdiction of the National Oceanic & Atmospheric Administration Fisheries Service. Consult with them directly about these species 1 Federal listing includes all runs in coastal basins from the Russian River in Sonoma Co, south to Soquel Creek in Santa Cruz Co. inclusive. Includes the San Francisco bay basin, but excludes the Sacramento-San Joaquin River basins. 2 Federal listing includes all runs in the Sacramento and San Joaquin Rivers and their tributaries 3 The Federal listing is limited to naturally spawning populations in streams between Punta Gorda, Humboldt County and the San Lorenzo River, Santa Cruz County. 4 The State listing is limited to Coho south of San Francisco Bay. 5 Includes populations spawning in the Sacramento River and its tributaries. 6 Originally proposed as part of a larger Southern Oregon and California Coastal ESU. This new ESU was revised to include only naturally spawned coastal spring and fall Chinook salmon between redwood creek in Humboldt County and the Russian River in Sonoma County.

PDX/080870002.DOC H-13