Appendix D CNDBB Species List

20‐09479: Conejo Community Park and Center Scientific Name Suitability/ Status Habitat Requirements Potential to Occur in Project Area Common Name Observations and Lichens

FE/SCE Acanthomintha duttonii , Valley and foothill grassland. serpentinite. No suitable habitat present within the study area and G1/S1 Not Expected San Mateo thorn‐mint 50 ‐ 300 m. annual herb. Blooms Apr‐Jun soil types are not suitable. 1B.1

FT/SCE Chaparral, Coastal scrub, Valley and foothill grassland, Acanthomintha ilicifolia G1/S1 Vernal pools. Clay, openings. 10 ‐ 960 m. annual herb. Not Expected No suitable habitat present within the study area. San Diego thorn‐mint 1B.1 Blooms Apr‐Jun

Acmispon dendroideus var. FT/SCE Coastal bluff scrub, Coastal scrub, Valley and foothill traskiae G4T3/S3 grassland. 15 ‐ 365 m. perennial . Blooms Feb‐ Not Expected No suitable habitat present within the study area. San Clemente Island lotus 1B.3 Aug

Chaparral, Cismontane woodland, Coastal scrub, FE/SCT Cismontane woodland in study area is highly disturbed Allium munzii Pinyon and juniper woodland, Valley and foothill G1/S1 Not Expected and anthropogenically influenced. Study area is outside Munz's onion grassland. mesic, clay. 297 ‐ 1070 m. perennial 1B.1 elevation range for this species. bulbiferous herb. Blooms Mar‐May

FE/SCE Cismontane woodland in study area is highly disturbed Amsinckia grandiflora Cismontane woodland, Valley and foothill grassland. G1/S1 Not Expected and anthropogenically influenced. Study area is outside large‐flowered fiddleneck 270 ‐ 550 m. annual herb. Blooms (Mar)Apr‐May 1B.1 elevation range for this species.

FE/SCE Lower montane coniferous forest, Upper montane Arabis mcdonaldiana No suitable habitat present within the study area and G3/S3 coniferous forest. serpentinite. 135 ‐ 1800 m. perennial Not Expected McDonald's rockcress soil types are not suitable. 1B.1 herb. Blooms May‐Jul

Arctostaphylos montana ssp. FE/SCE Chaparral, Coastal prairie, Coastal scrub. serpentinite No suitable habitat present within the study area and ravenii G3T1/S1 outcrop. 45 ‐ 215 m. perennial evergreen shrub. Not Expected soil types are not suitable. Presidio manzanita 1B.1 Blooms Feb‐Mar

Broadleafed upland forest, Closed‐cone coniferous FT/SCE Upland forest in study area is highly disturbed and Arctostaphylos pallida forest, Chaparral, Cismontane woodland, Coastal G1/S1 Not Expected anthropogenically influenced. No suitable habitat pallid manzanita scrub. siliceous shale, sandy or gravelly. 185 ‐ 465 m. 1B.1 present within the study area. perennial evergreen shrub. Blooms Dec‐Mar FE/SCE Marshes and swamps (freshwater or brackish). sandy, Arenaria paludicola No suitable habitat present within the study area. G1/S1 openings. 3 ‐ 170 m. perennial stoloniferous herb. Not Expected marsh sandwort Study area is outside elevation range for this species. 1B.1 Blooms May‐Aug

Chaparral, Coastal scrub, Valley and foothill grassland. FE/None brauntonii recent burns or disturbed areas, usually sandstone with G2/S2 Not Expected No suitable habitat present within the study area. Braunton's milk‐vetch carbonate layers. 4 ‐ 640 m. perennial herb. Blooms 1B.1 Jan‐Aug

FE/SCT Chaparral (openings), Cismontane woodland, Valley Cismontane woodland in study area is highly disturbed Astragalus claranus G1/S1 and foothill grassland. serpentinite or volcanic, rocky, Not Expected and anthropogenically influenced. No suitable habitat Clara Hunt's milk‐vetch 1B.1 clay. 75 ‐ 275 m. annual herb. Blooms Mar‐May present within the study area.

Astragalus magdalenae var. FT/SCE Desert dunes. 60 ‐ 225 m. perennial herb. Blooms Dec‐ peirsonii G3G4T1/S1 Not Expected No suitable habitat present within the study area. Apr Peirson's milk‐vetch 1B.2

Astragalus pycnostachyus var. FE/SCE Coastal dunes, Coastal scrub, Marshes and swamps No suitable habitat present within the study area. lanosissimus G2T1/S1 (edges, coastal salt or brackish). 1 ‐ 35 m. perennial Not Expected Study area is outside elevation range for this species. Ventura marsh milk‐vetch 1B.1 herb. Blooms (Jun)Aug‐Oct

FE/SCE Coastal bluff scrub (sandy), Coastal dunes, Coastal Astragalus tener var. titi No suitable habitat present within the study area. G2T1/S1 prairie (mesic). often vernally mesic areas. 1 ‐ 50 m. Not Expected coastal dunes milk‐vetch Study area is outside elevation range for this species. 1B.1 annual herb. Blooms Mar‐May

None/None Chaparral, Cismontane woodland, Coastal scrub, Cismontane woodland in study area is highly disturbed Baccharis malibuensis G1/S1 Riparian woodland. 150 ‐ 305 m. perennial deciduous Low potential and anthropogenically influenced. Riparian woodland Malibu baccharis 1B.1 shrub. Blooms Aug is potentially suitable.

FT/SCE Chaparral (maritime), Cismontane woodland. Cismontane woodland in study area is highly disturbed Baccharis vanessae G1/S1 sandstone. 60 ‐ 720 m. perennial deciduous shrub. Not Expected and anthropogenically influenced. No suitable habitat Encinitas baccharis 1B.1 Blooms Aug,Oct,Nov present within the study area. FE/SCE Chaparral, Cismontane woodland, Coastal scrub, Cismontane woodland in study area is highly disturbed Berberis nevinii G1/S1 Riparian scrub. sandy or gravelly. 70 ‐ 825 m. perennial Not Expected and anthropogenically influenced. No suitable habitat Nevin's barberry 1B.1 evergreen shrub. Blooms (Feb)Mar‐Jun present within the study area.

FE/SCE Closed‐cone coniferous forest, Chaparral, Cismontane Cismontane woodland in study area is highly disturbed Berberis pinnata ssp. insularis G5T1/S1 woodland, Coastal scrub. rocky. 75 ‐ 400 m. perennial Not Expected and anthropogenically influenced. No suitable habitat island barberry 1B.2 evergreen shrub. Blooms Feb‐May present within the study area.

FE/SCE Blennosperma bakeri Valley and foothill grassland (mesic), Vernal pools. 10 ‐ No suitable habitat present within the study area. G1/S1 Not Expected Sonoma sunshine 110 m. annual herb. Blooms Mar‐May Study area is outside elevation range for this species. 1B.1

Chaparral (openings), Cismontane woodland, Coastal FT/SCE Cismontane woodland in study area is highly disturbed Brodiaea filifolia scrub, Playas, Valley and foothill grassland, Vernal G2/S2 Not Expected and anthropogenically influenced. No suitable habitat thread‐leaved brodiaea pools. often clay. 25 ‐ 1120 m. perennial bulbiferous 1B.1 present within the study area. herb. Blooms Mar‐Jun

FT/SCE Cismontane woodland, Valley and foothill grassland. Cismontane woodland in study area is highly disturbed Brodiaea pallida G1/S1 vernal streambeds, often serpentinite. 165 ‐ 385 m. Not Expected and anthropogenically influenced. No suitable habitat Chinese Camp brodiaea 1B.1 perennial bulbiferous herb. Blooms May‐Jun present within the study area.

None/None Chaparral, Coastal scrub, Valley and foothill grassland. Calochortus clavatus var. gracilis No suitable habitat present within the study area. G4T2T3/S2S3 320 ‐ 1000 m. perennial bulbiferous herb. Blooms Mar‐ Not Expected slender mariposa lily Study area is outside elevation range for this species. 1B.2 Jun(Nov)

Chaparral, Cismontane woodland, Coastal scrub, Lower None/None Cismontane woodland in study area is highly disturbed Calochortus plummerae montane coniferous forest, Valley and foothill G4/S4 Not Expected and anthropogenically influenced. No suitable habitat Plummer's mariposa lily grassland. granitic, rocky. 100 ‐ 1700 m. perennial 4.2 present within the study area. bulbiferous herb. Blooms May‐Jul

FT/SCT Calochortus tiburonensis Valley and foothill grassland (serpentinite). 50 ‐ 150 m. No suitable habitat present within the study area. G1/S1 Not Expected Tiburon mariposa lily perennial bulbiferous herb. Blooms Mar‐Jun Study area is outside elevation range for this species. 1B.1 FE/SCE Chaparral (openings), Cismontane woodland. gabbroic Cismontane woodland in study area is highly disturbed Calystegia stebbinsii G1/S1 or serpentinite. 185 ‐ 1090 m. perennial rhizomatous Not Expected and anthropogenically influenced. No suitable habitat Stebbins' morning‐glory 1B.1 herb. Blooms Apr‐Jul present within the study area.

FE/SCT Castilleja affinis var. neglecta Valley and foothill grassland (serpentinite). 60 ‐ 400 m. No suitable habitat present within the study area and G4G5T1T2/S1S2 Not Expected Tiburon paintbrush perennial herb (hemiparasitic). Blooms Apr‐Jun soil types are not suitable. 1B.2

Castilleja campestris var. FT/SCE Vernal pools (often acidic). 50 ‐ 750 m. annual herb succulenta G4?T2T3/S2S3 Not Expected No suitable habitat present within the study area. (hemiparasitic). Blooms (Mar)Apr‐May succulent owl's‐clover 1B.2

FT/SCE Coastal bluff scrub, Coastal scrub. rocky, often Castilleja grisea G3/S3 canyons. 10 ‐ 535 m. perennial herb (hemiparasitic). Not Expected No suitable habitat present within the study area. San Clemente Island paintbrush 1B.3 Blooms (Dec)Feb‐Aug

FE/SCE Chenopod scrub, Pinyon and juniper woodland, Valley Caulanthus californicus No suitable habitat present within the study area and G1/S1 and foothill grassland. sandy. 61 ‐ 1000 m. annual herb. Not Expected jewelflower soil types are not suitable. 1B.1 Blooms Feb‐May

FT/SCE Ceanothus ophiochilus Chaparral (gabbroic or pyroxenite‐rich outcrops). 580 ‐ No suitable habitat present within the study area. G1/S1 Not Expected Vail Lake ceanothus 1065 m. perennial evergreen shrub. Blooms Feb‐Mar Study area is outside elevation range for this species. 1B.1

Chaparral, Cismontane woodland. Serpentinite or Cismontane woodland in study area is highly disturbed FE/SCR gabbroic (nutrient‐deficient forms of gabbro‐derived Ceanothus roderickii and anthropogenically influenced. No suitable habitat G1/S1 soils characterized by low concentrations of available Not Expected Pine Hill ceanothus present within the study area and soil types are not 1B.1 K, P, S, Fe, and Zn). 245 ‐ 1090 m. perennial evergreen suitable. shrub. Blooms Apr‐Jun

None/None Marshes and swamps (margins), Valley and foothill Centromadia parryi ssp. australis G3T2/S2 grassland (vernally mesic), Vernal pools. 0 ‐ 480 m. Not Expected No suitable habitat present within the study area. southern tarplant 1B.1 annual herb. Blooms May‐Nov Cercocarpus traskiae FE/SCE Chaparral, Coastal scrub. rocky, sausserite gabbro. 100 ‐ Catalina Island mountain‐ G1/S1 Not Expected No suitable habitat present within the study area. 250 m. perennial evergreen shrub. Blooms Mar‐May mahogany 1B.1

Cismontane woodland in study area is highly disturbed Chlorogalum purpureum var. FT/SCR Cismontane woodland, Valley and foothill grassland. and anthropogenically influenced. No suitable habitat reductum G2T1/S1 305 ‐ 630 m. perennial bulbiferous herb. Blooms Apr‐ Not Expected present within the study area. Study area is outside Camatta Canyon amole 1B.1 May elevation range for this species.

Chloropyron maritimum ssp. FE/SCE Coastal dunes, Marshes and swamps (coastal salt). 0 ‐ No suitable habitat present within the study area. maritimum G4?T1/S1 30 m. annual herb (hemiparasitic). Blooms May‐ Not Expected Study area is outside elevation range for this species. salt marsh bird's‐beak 1B.2 Oct(Nov)

FE/SCR Chloropyron molle ssp. molle Marshes and swamps (coastal salt). 0 ‐ 3 m. annual No suitable habitat present within the study area. G2T1/S1 Not Expected soft bird's‐beak herb (hemiparasitic). Blooms Jun‐Nov Study area is outside elevation range for this species. 1B.2

FE/SCE Chenopod scrub, Valley and foothill grassland. alkaline. Chloropyron palmatum G1/S1 5 ‐ 155 m. annual herb (hemiparasitic). Blooms May‐ Not Expected No suitable habitat present within the study area. palmate‐bracted bird's‐beak 1B.1 Oct

FE/SCT Coastal dunes, Coastal prairie, Coastal scrub. sandy, Chorizanthe howellii No suitable habitat present within the study area. G1/S1 often disturbed areas. 0 ‐ 45 m. annual herb. Blooms Not Expected Howell's spineflower Study area is outside elevation range for this species. 1B.2 May‐Jul

FE/SCE Closed‐cone coniferous forest, Chaparral (maritime), Chorizanthe orcuttiana No suitable habitat present within the study area. G1/S1 Coastal scrub. sandy openings. 3 ‐ 125 m. annual herb. Not Expected Orcutt's spineflower Study area is outside elevation range for this species. 1B.1 Blooms Mar‐May

Chorizanthe parryi var. FC/SCE Coastal scrub (sandy), Valley and foothill grassland. 150 No suitable habitat present within the study area and fernandina G2T1/S1 Not Expected ‐ 1220 m. annual herb. Blooms Apr‐Jul soil types are not suitable. San Fernando Valley spineflower 1B.1 FE/SCE Chorizanthe valida Coastal prairie (sandy). 10 ‐ 305 m. annual herb. No suitable habitat present within the study area and G1/S1 Not Expected Sonoma spineflower Blooms Jun‐Aug soil types are not suitable. 1B.1

Chaparral (openings), Cismontane woodland, Cismontane woodland in study area is highly disturbed FE/SCE Cirsium fontinale var. fontinale Meadows and seeps, Valley and foothill grassland. and anthropogenically influenced. No suitable habitat G2T1/S1 Not Expected Fountain thistle Serpentinite seeps. 45 ‐ 175 m. perennial herb. Blooms present within the study area. Study area is outside 1B.1 (Apr)May‐Oct elevation range for this species.

Cismontane woodland in study area is highly disturbed FE/SCE Chaparral, Cismontane woodland, Coastal scrub, Valley Cirsium fontinale var. obispoense and anthropogenically influenced. No suitable habitat G2T2/S2 and foothill grassland. serpentinite seeps, drainages. 35 Not Expected San Luis Obispo fountain thistle present within the study area and soil types are not 1B.2 ‐ 385 m. perennial herb. Blooms Feb‐Jul(Aug‐Sep) suitable.

Cismontane woodland, Coastal dunes, Coastal scrub, Cismontane woodland in study area is highly disturbed Cirsium scariosum var. FE/SCT Marshes and swamps (brackish), Valley and foothill and anthropogenically influenced. No suitable habitat loncholepis G5T1/S1 Not Expected grassland. mesic, sandy. 4 ‐ 220 m. perennial herb. present within the study area and soil types are not La Graciosa thistle 1B.1 Blooms May‐Aug suitable.

FE/SCE Coastal scrub, Valley and foothill grassland Clarkia franciscana No suitable habitat present within the study area and G1/S1 (serpentinite). 25 ‐ 335 m. annual herb. Blooms May‐ Not Expected Presidio clarkia soil types are not suitable. 1B.1 Jul

FE/SCE Clarkia imbricata Chaparral, Valley and foothill grassland. acidic sandy No suitable habitat present within the study area. G1/S1 Not Expected Vine Hill clarkia loam. 50 ‐ 75 m. annual herb. Blooms Jun‐Aug Study area is outside elevation range for this species. 1B.1

Cismontane woodland in study area is highly disturbed FE/SCR Chaparral (margins, openings), Cismontane woodland, Clarkia speciosa ssp. immaculata and anthropogenically influenced. No suitable habitat G4T1/S1 Valley and foothill grassland. sandy. 25 ‐ 185 m. annual Not Expected Pismo clarkia present within the study area. Study area is outside 1B.1 herb. Blooms May‐Jul elevation range for this species.

FT/SCE Chaparral, Cismontane woodland, Valley and foothill Cismontane woodland in study area is highly disturbed Clarkia springvillensis G2/S2 grassland. granitic. 245 ‐ 1220 m. annual herb. Blooms Not Expected and anthropogenically influenced. No suitable habitat Springville clarkia 1B.2 (Mar)Apr‐Jul present within the study area. Cordylanthus tenuis ssp. FE/SCR Closed‐cone coniferous forest, Chaparral. serpentinite. No suitable habitat present within the study area and capillaris G4G5T1/S1 45 ‐ 305 m. annual herb (hemiparasitic). Blooms Jun‐ Not Expected soil types are not suitable. Pennell's bird's‐beak 1B.2 Sep

FT/SCE conjugens Coastal scrub, Valley and foothill grassland. clay. 25 ‐ G1/S1 Not Expected No suitable habitat present within the study area. Otay tarplant 300 m. annual herb. Blooms (Apr)May‐Jun 1B.1

FE/SCE Deinandra increscens ssp. villosa Coastal bluff scrub, Coastal scrub, Valley and foothill G4G5T2/S2 Not Expected No suitable habitat present within the study area. Gaviota tarplant grassland. 20 ‐ 430 m. annual herb. Blooms May‐Oct 1B.1

None/SCR Deinandra minthornii Chaparral, Coastal scrub. rocky. 280 ‐ 760 m. perennial G2/S2 Not Expected No suitable habitat present within the study area. Santa Susana tarplant deciduous shrub. Blooms Jul‐Nov 1B.2

Upland forest in study area is highly disturbed and FE/SCE Broadleafed upland forest, Coastal scrub, Valley and anthropogenically influenced. No suitable habitat Delphinium bakeri G1/S1 foothill grassland. decomposed shale, often mesic. 80 ‐ Not Expected present within the study area and no CNDDB Baker's larkspur 1B.1 305 m. perennial herb. Blooms Mar‐May occurrences are located within 5 miles of the study area.

FE/SCR Delphinium luteum Chaparral, Coastal prairie, Coastal scrub. rocky. 0 ‐ 100 No suitable habitat present within the study area. G1/S1 Not Expected golden larkspur m. perennial herb. Blooms Mar‐May Study area is outside elevation range for this species. 1B.1

Delphinium parryi ssp. None/None Chaparral (maritime), Coastal dunes. 0 ‐ 200 m. blochmaniae G4T2/S2 Not Expected No suitable habitat present within the study area. perennial herb. Blooms Apr‐Jun dune larkspur 1B.2

Delphinium variegatum ssp. FE/SCE Valley and foothill grassland (coastal). 75 ‐ 500 m. kinkiense G4T2/S2 Not Expected No suitable habitat present within the study area. perennial herb. Blooms Mar‐Apr San Clemente Island larkspur 1B.1 Cismontane woodland in study area is highly disturbed FE/SCE Chaparral, Cismontane woodland, Coastal scrub Dodecahema leptoceras and anthropogenically influenced. No suitable habitat G1/S1 (alluvial fan). sandy. 200 ‐ 760 m. annual herb. Blooms Not Expected slender‐horned spineflower present within the study area and soil types are not 1B.1 Apr‐Jun suitable.

Dudleya blochmaniae ssp. None/None Coastal bluff scrub, Chaparral, Coastal scrub, Valley blochmaniae G3T2/S2 and foothill grassland. rocky, often clay or serpentinite. Not Expected No suitable habitat present within the study area. Blochman's dudleya 1B.1 5 ‐ 450 m. perennial herb. Blooms Apr‐Jun

Cismontane woodland in study area is highly disturbed FT/None and anthropogenically influenced. Soil types are Dudleya cymosa ssp. agourensis Chaparral, Cismontane woodland. rocky, volcanic. 200 ‐ G5T1/S1 Low potential potentially suitable, though no rock outcrops are Agoura Hills dudleya 500 m. perennial herb. Blooms May‐Jun 1B.2 present. Nearest CNDDB observations are at least 3.75 miles southeast of the study area.

FT/SCR Dudleya cymosa ssp. marcescens Chaparral. volcanic, rocky. 150 ‐ 520 m. perennial herb. G5T2/S2 Not Expected No suitable habitat present within the study area. marcescent dudleya Blooms Apr‐Jul 1B.2

FT/SCR Dudleya nesiotica Coastal bluff scrub, Coastal scrub. rocky or gravelly, No suitable habitat present within the study area. G1/S1 Not Expected dudleya clay. 10 ‐ 50 m. perennial herb. Blooms Apr‐Jun Study area is outside elevation range for this species. 1B.1

FT/None Coastal scrub, Valley and foothill grassland. rocky or Dudleya parva G1/S1 gravelly, clay or volcanic. 60 ‐ 450 m. perennial herb. Not Expected No suitable habitat present within the study area. Conejo dudleya 1B.2 Blooms May‐Jun

Cismontane woodland in study area is highly disturbed FT/SCT Chaparral, Cismontane woodland, Coastal scrub, Valley and anthropogenically influenced. Soil types are Dudleya stolonifera G1/S1 and foothill grassland. rocky. 10 ‐ 260 m. perennial Not Expected potentially suitable, though no rock outcrops are Laguna Beach dudleya 1B.1 stoloniferous herb. Blooms May‐Jul present. No CNDDB occurrences are located within 5 miles of the study area.

FE/SCE Dudleya traskiae Coastal bluff scrub, Coastal scrub. rocky. 30 ‐ 110 m. No suitable habitat present within the study area. G1/S1 Not Expected Santa Barbara Island dudleya perennial herb. Blooms Feb,Apr,May,Jul Study area is outside elevation range for this species. 1B.2 Eriastrum densifolium ssp. FE/SCE Chaparral, Coastal scrub (alluvial fan). sandy or No suitable habitat present within the study area and sanctorum G4T1/S1 Not Expected gravelly. 91 ‐ 610 m. perennial herb. Blooms Apr‐Sep soil types are not suitable. Santa Ana River woollystar 1B.1

Cismontane woodland in study area is highly disturbed FE/SCE Chaparral (maritime), Cismontane woodland, Coastal altissimum and anthropogenically influenced. No suitable habitat G1/S1 scrub. sandstone. 80 ‐ 270 m. perennial evergreen Not Expected Indian Knob mountainbalm present within the study area. No CNDDB occurrences 1B.1 shrub. Blooms Mar‐Jun are located within 5 miles of the study area.

FE/SCR Coastal bluff scrub, Closed‐cone coniferous forest, Eriodictyon capitatum No suitable habitat present within the study area and G2/S2 Chaparral (maritime). sandy. 40 ‐ 900 m. perennial Not Expected Lompoc yerba santa soil types are not suitable. 1B.2 evergreen shrub. Blooms May‐Sep

FE/SCE Eriogonum apricum var. apricum Chaparral (openings, Ione soil). 60 ‐ 145 m. perennial No suitable habitat present within the study area. G2T1/S1 Not Expected Ione buckwheat herb. Blooms Jul‐Oct Study area is outside elevation range for this species. 1B.1

Eriogonum apricum var. FE/SCE Chaparral (openings, Ione soil). 90 ‐ 120 m. perennial No suitable habitat present within the study area. prostratum G2T1/S1 Not Expected herb. Blooms Jun‐Jul Study area is outside elevation range for this species. Irish Hill buckwheat 1B.1

None/SCR Chaparral, Coastal scrub, Valley and foothill grassland. Eriogonum crocatum No suitable habitat present within the study area and G1/S1 Conejo volcanic outcrops, rocky. 50 ‐ 580 m. perennial Not Expected conejo buckwheat soil types are not suitable. 1B.2 herb. Blooms Apr‐Jul

Cismontane woodland in study area is highly disturbed FE/SCE Cismontane woodland (often serpentinite, on Eriophyllum latilobum and anthropogenically influenced. No suitable habitat G1/S1 roadcuts), Coastal scrub, Lower montane coniferous Not Expected San Mateo woolly sunflower present within the study area and soil types are not 1B.1 forest. 45 ‐ 330 m. perennial herb. Blooms May‐Jun suitable.

Eryngium aristulatum var. FE/SCE Coastal scrub, Valley and foothill grassland, Vernal parishii G5T1/S1 pools. mesic. 20 ‐ 620 m. annual / perennial herb. Not Expected No suitable habitat present within the study area. San Diego button‐celery 1B.1 Blooms Apr‐Jun FE/SCE constancei Vernal pools. 460 ‐ 855 m. annual / perennial herb. No suitable habitat present within the study area. G1/S1 Not Expected Loch Lomond button‐celery Blooms Apr‐Jun Study area is outside elevation range for this species. 1B.1

Erysimum capitatum var. FE/SCE No suitable habitat present within the study area. angustatum G5T1/S1 Inland dunes. 3 ‐ 20 m. perennial herb. Blooms Mar‐Jul Not Expected Study area is outside elevation range for this species. Contra Costa wallflower 1B.1

FE/SCE Erysimum menziesii Coastal dunes. 0 ‐ 35 m. perennial herb. Blooms Mar‐ No suitable habitat present within the study area. G1/S1 Not Expected Menzies? wallflower Sep Study area is outside elevation range for this species. 1B.1

FE/SCE Chaparral, Lower montane coniferous forest. inland Erysimum teretifolium G1/S1 marine sands. 120 ‐ 610 m. perennial herb. Blooms Not Expected No suitable habitat present within the study area. Santa Cruz wallflower 1B.1 Mar‐Jul

FE/SCR Chaparral, Cismontane woodland. gabbroic or Fremontodendron decumbens No suitable habitat present within the study area. G1/S1 serpentinite, rocky. 425 ‐ 760 m. perennial evergreen Not Expected Pine Hill flannelbush Study area is outside elevation range for this species. 1B.2 shrub. Blooms Apr‐Jul

FE/SCR Closed‐cone coniferous forest, Chaparral, Cismontane Cismontane woodland in study area is highly disturbed Fremontodendron mexicanum G2/S1 woodland. gabbroic, metavolcanic, or serpentinite. 10 ‐ Not Expected and anthropogenically influenced. No suitable habitat Mexican flannelbush 1B.1 716 m. perennial evergreen shrub. Blooms Mar‐Jun present within the study area.

FE/SCR Coastal bluff scrub, Closed‐cone coniferous forest, Galium buxifolium G2G3/S2S3 Coastal scrub. rocky. 5 ‐ 400 m. perennial deciduous Not Expected No suitable habitat present within the study area. box bedstraw 1B.2 shrub. Blooms Mar‐Jul

FE/SCR Chaparral, Cismontane woodland, Lower montane Cismontane woodland in study area is highly disturbed Galium californicum ssp. sierrae G5T1/S1 coniferous forest. gabbroic. 100 ‐ 585 m. perennial Not Expected and anthropogenically influenced. No suitable habitat El Dorado bedstraw 1B.2 herb. Blooms May‐Jun present within the study area. Cismontane woodland in study area is highly disturbed FE/SCT Chaparral (maritime), Cismontane woodland, Coastal Gilia tenuiflora ssp. arenaria and anthropogenically influenced. No suitable habitat G3G4T2/S2 dunes, Coastal scrub. sandy, openings. 0 ‐ 45 m. annual Not Expected Monterey gilia present within the study area. Study area is outside 1B.2 herb. Blooms Apr‐Jun elevation range for this species.

Hesperocyparis abramsiana var. FT/SCE Closed‐cone coniferous forest, Chaparral, Lower abramsiana G1T1/S1 montane coniferous forest. sandstone or granitic. 280 ‐ Not Expected No suitable habitat present within the study area. Santa Cruz cypress 1B.2 800 m. perennial evergreen . Blooms

Hesperocyparis abramsiana var. FT/SCE Closed‐cone coniferous forest, Chaparral, Lower No suitable habitat present within the study area. butanoensis G1T1/S1 montane coniferous forest. Sandstone. 400 ‐ 490 m. Not Expected Study area is outside elevation range for this species. Butano Ridge cypress 1B.2 perennial evergreen tree. Blooms Oct

FT/SCT Hesperolinon congestum Chaparral, Valley and foothill grassland. serpentinite. 5 ‐ No suitable habitat present within the study area and G1/S1 Not Expected Marin western flax 370 m. annual herb. Blooms Apr‐Jul soil types are not suitable. 1B.1

FT/SCE Coastal prairie, Coastal scrub, Valley and foothill Holocarpha macradenia G1/S1 grassland. often clay, sandy. 10 ‐ 220 m. annual herb. Not Expected No suitable habitat present within the study area. Santa Cruz tarplant 1B.1 Blooms Jun‐Oct

FE/SCE Lasthenia burkei Meadows and seeps (mesic), Vernal pools. 15 ‐ 600 m. G1/S1 Not Expected No suitable habitat present within the study area. Burke's goldfields annual herb. Blooms Apr‐Jun 1B.1

FE/SCE Layia carnosa Coastal dunes, Coastal scrub (sandy). 0 ‐ 60 m. annual No suitable habitat present within the study area. G2/S2 Not Expected beach layia herb. Blooms Mar‐Jul Study area is outside elevation range for this species. 1B.1

FE/SCE Lessingia germanorum Coastal scrub (remnant dunes). 25 ‐ 110 m. annual No suitable habitat present within the study area. G1/S1 Not Expected San Francisco lessingia herb. Blooms (Jun)Jul‐Nov Study area is outside elevation range for this species. 1B.1 Bogs and fens, Coastal bluff scrub, Coastal prairie, FE/SCE Lilium occidentale Coastal scrub, Marshes and swamps (freshwater), No suitable habitat present within the study area. G1/S1 Not Expected western lily North Coast coniferous forest (openings). 2 ‐ 185 m. Study area is outside elevation range for this species. 1B.1 perennial bulbiferous herb. Blooms Jun‐Jul

Cismontane woodland in study area is highly disturbed Lilium pardalinum ssp. FE/SCE Cismontane woodland, Meadows and seeps, Marshes and anthropogenically influenced. No suitable habitat pitkinense G5T1/S1 and swamps (freshwater). mesic, sandy. 35 ‐ 65 m. Not Expected present within the study area. Study area is outside Pitkin Marsh lily 1B.1 perennial bulbiferous herb. Blooms Jun‐Jul elevation range for this species.

Limnanthes floccosa ssp. FE/SCE Valley and foothill grassland (mesic), Vernal pools. 46 ‐ californica G4T1/S1 Not Expected No suitable habitat present within the study area. 930 m. annual herb. Blooms Mar‐May Butte County meadowfoam 1B.1

FE/SCE Meadows and seeps, Valley and foothill grassland, Limnanthes vinculans G1/S1 Vernal pools. vernally mesic. 15 ‐ 305 m. annual herb. Not Expected No suitable habitat present within the study area. Sebastopol meadowfoam 1B.1 Blooms Apr‐May

Lithophragma maximum FE/SCE Coastal bluff scrub, Coastal scrub. rocky. 120 ‐ 400 m. San Clemente Island woodland G1/S1 Not Expected No suitable habitat present within the study area. perennial rhizomatous herb. Blooms Apr‐Jun star 1B.1

FE/SCE Lupinus nipomensis Coastal dunes. 10 ‐ 50 m. annual herb. Blooms Dec‐ No suitable habitat present within the study area. G1/S1 Not Expected Nipomo Mesa lupine May Study area is outside elevation range for this species. 1B.1

FE/SCE Lupinus tidestromii Coastal dunes. 0 ‐ 100 m. perennial rhizomatous herb. No suitable habitat present within the study area. G1/S1 Not Expected Tidestrom's lupine Blooms Apr‐Jun Study area is outside elevation range for this species. 1B.1

FE/SCE Malacothamnus clementinus Valley and foothill grassland (rocky). 10 ‐ 275 m. G2G3/S2S3 Not Expected No suitable habitat present within the study area. San Clemente Island bush‐mallow perennial deciduous shrub. Blooms Mar‐Aug 1B.1 Malacothamnus fasciculatus var. FE/SCE Chaparral, Coastal scrub. rocky. 15 ‐ 210 m. perennial nesioticus G4T1/S1 Not Expected No suitable habitat present within the study area. deciduous shrub. Blooms Apr‐Jul Santa Cruz Island bush‐mallow 1B.1

Monardella hypoleuca ssp. None/None Cismontane woodland in study area is highly disturbed Chaparral, Cismontane woodland. 50 ‐ 1525 m. hypoleuca G4T3/S3 Not Expected and anthropogenically influenced. No suitable habitat perennial herb. Blooms (Apr)May‐Aug(Sep‐Dec) white‐veined 1B.3 present within the study area.

None/None Monardella sinuata ssp. gerryi Coastal scrub. Sandy openings. 150 ‐ 245 m. annual G3T1/S1 Not Expected No suitable habitat present within the study area. Gerry's curly‐leaved monardella herb. Blooms Apr‐Jun 1B.1

Potentially suitable riparian forest and woodland habitat is present in the study area. However the FE/SCE Chaparral, Coastal scrub, Riparian forest, Riparian Monardella viminea riparian system in the study area is characterized by a G1/S1 scrub, Riparian woodland. alluvial ephemeral washes. Not Expected willowy monardella perennial stream with steep banks rather than a sandy 1B.1 50 ‐ 225 m. perennial herb. Blooms Jun‐Aug ephemeral wash. No CNDDB occurrences are located within 5 miles of the study area.

FE/SCT No suitable habitat present within the study area and Nasturtium gambelii Marshes and swamps (freshwater or brackish). 5 ‐ 330 G1/S1 Not Expected no CNDDB occurrences are located within 5 miles of Gambel's water cress m. perennial rhizomatous herb. Blooms Apr‐Oct 1B.1 the study area.

Navarretia leucocephala ssp. FE/SCT Vernal pools (volcanic ash flow). 400 ‐ 855 m. annual No suitable habitat present within the study area. pauciflora G4T1/S1 Not Expected herb. Blooms May‐Jun Study area is outside elevation range for this species. few‐flowered navarretia 1B.1

Navarretia leucocephala ssp. FE/SCE Vernal pools (volcanic ash flow). 30 ‐ 950 m. annual plieantha G4T1/S1 Not Expected No suitable habitat present within the study area. herb. Blooms May‐Jun many‐flowered navarretia 1B.2

None/None Chaparral (openings), Coastal scrub (openings), Valley N avarretia ojaiensis G2/S2 and foothill grassland. 275 ‐ 620 m. annual herb. Not Expected No suitable habitat present within the study area. Ojai navarretia 1B.1 Blooms May‐Jul FT/SCE Neostapfia colusana Vernal pools (adobe, large). 5 ‐ 200 m. annual herb. No suitable habitat present within the study area. G1/S1 Not Expected Colusa grass Blooms May‐Aug Study area is outside elevation range for this species. 1B.1

FE/SCE Nitrophila mohavensis Playas (mesic, clay). 425 ‐ 750 m. perennial herb. No suitable habitat present within the study area. G1/S1 Not Expected Amargosa nitrophila Blooms May‐Oct Study area is outside elevation range for this species. 1B.1

None/None Chaparral, Coastal scrub. sandstone or gabbro. 140 ‐ Nolina cismontana G3/S3 1275 m. perennial evergreen shrub. Blooms (Mar)May‐ Not Expected No suitable habitat present within the study area. chaparral nolina 1B.2 Jul

FE/SCE Oenothera deltoides ssp. howellii Inland dunes. 0 ‐ 30 m. perennial herb. Blooms Mar‐ No suitable habitat present within the study area. G5T1/S1 Not Expected Antioch Dunes evening‐primrose Sep Study area is outside elevation range for this species. 1B.1

Cismontane woodland in study area is highly disturbed FE/SCE Chenopod scrub, Cismontane woodland, Valley and and anthropogenically influenced. No suitable habitat Opuntia basilaris var. treleasei G5T1/S1 foothill grassland. sandy or gravelly. 100 ‐ 1450 m. Not Expected present within the study area and no CNDDB Bakersfield cactus 1B.1 perennial stem succulent. Blooms Apr‐May occurrences are located within 5 miles of the study area.

FE/SCE Orcuttia californica G1/S1 Vernal pools. 15 ‐ 660 m. annual herb. Blooms Apr‐Aug Not Expected No suitable habitat present within the study area. California Orcutt grass 1B.1

FT/SCE Orcuttia inaequalis G1/S1 Vernal pools. 10 ‐ 755 m. annual herb. Blooms Apr‐Sep Not Expected No suitable habitat present within the study area. San Joaquin Valley Orcutt grass 1B.1

FE/SCE Orcuttia pilosa Vernal pools. 46 ‐ 200 m. annual herb. Blooms May‐ No suitable habitat present within the study area. G1/S1 Not Expected hairy Orcutt grass Sep Study area is outside elevation range for this species. 1B.1 FT/SCE Orcuttia tenuis Vernal pools. Often gravelly. 35 ‐ 1760 m. annual herb. G2/S2 Not Expected No suitable habitat present within the study area. slender Orcutt grass Blooms May‐Sep(Oct) 1B.1

FE/SCE Orcuttia viscida Vernal pools. 30 ‐ 100 m. annual herb. Blooms Apr‐ No suitable habitat present within the study area. G1/S1 Not Expected Sacramento Orcutt grass Jul(Sep) Study area is outside elevation range for this species. 1B.1

Cismontane woodland in study area is highly disturbed FT/SCR Chaparral, Cismontane woodland. serpentinite or and anthropogenically influenced. No suitable habitat layneae G2/S2 gabbroic, rocky. 200 ‐ 1085 m. perennial herb. Blooms Not Expected present within the study area and no CNDDB Layne's ragwort 1B.2 Apr‐Aug occurrences are located within 5 miles of the study area. Cismontane woodland in study area is highly disturbed FE/SCE Cismontane woodland, Valley and foothill grassland and anthropogenically influenced. No suitable habitat Pentachaeta bellidiflora G1/S1 (often serpentinite). 35 ‐ 620 m. annual herb. Blooms Not Expected present within the study area and no CNDDB white‐rayed pentachaeta 1B.1 Mar‐May occurrences are located within 5 miles of the study area.

FE/SCE Chaparral (openings), Coastal scrub, Valley and foothill Pentachaeta lyonii G1/S1 grassland. rocky, clay. 30 ‐ 690 m. annual herb. Blooms Not Expected No suitable habitat present within the study area. Lyon's pentachaeta 1B.1 (Feb)Mar‐Aug

FE/SCE Lower montane coniferous forest, Upper montane Phlox hirsuta No suitable habitat present within the study area and G1/S1 coniferous forest. serpentinite, talus. 820 ‐ 1500 m. Not Expected Yreka phlox soil types are not suitable. 1B.2 perennial herb. Blooms Apr‐Jun

FE/SCT Meadows and seeps, Valley and foothill grassland, Plagiobothrys strictus No suitable habitat present within the study area. G1/S1 Vernal pools. alkaline areas near thermal springs. 90 ‐ Not Expected Calistoga popcornflower Study area is outside elevation range for this species. 1B.1 160 m. annual herb. Blooms Mar‐Jun

FE/SCE Meadows and seeps, Valley and foothill grassland. Poa napensis No suitable habitat present within the study area. G1/S1 alkaline, near thermal springs. 100 ‐ 200 m. perennial Not Expected Napa blue grass Study area is outside elevation range for this species. 1B.1 herb. Blooms May‐Aug FE/SCE Pogogyne abramsii No suitable habitat present within the study area. G1/S1 Vernal pools. 90 ‐ 200 m. annual herb. Blooms Mar‐Jul Not Expected San Diego mesa mint Study area is outside elevation range for this species. 1B.1

FE/SCE Pogogyne nudiuscula G1/S1 Vernal pools. 90 ‐ 250 m. annual herb. Blooms May‐Jul Not Expected No suitable habitat present within the study area. Otay Mesa mint 1B.1

FE/SCE Valley and foothill grassland (mudstone and Polygonum hickmanii G1/S1 sandstone). 210 ‐ 250 m. annual herb. Blooms May‐ Not Expected No suitable habitat present within the study area. Scotts Valley polygonum 1B.1 Aug

Coastal bluff scrub, Closed‐cone coniferous forest, FE/SCE Potentilla hickmanii Meadows and seeps (vernally mesic), Marshes and No suitable habitat present within the study area. G1/S1 Not Expected Hickman's cinquefoil swamps (freshwater). 10 ‐ 149 m. perennial herb. Study area is outside elevation range for this species. 1B.1 Blooms Apr‐Aug

Cismontane woodland in study area is highly disturbed FE/SCE Cismontane woodland, Valley and foothill grassland. Pseudobahia bahiifolia and anthropogenically influenced. No suitable habitat G2/S2 clay, often acidic. 15 ‐ 150 m. annual herb. Blooms Mar‐ Not Expected Hartweg's golden sunburst present within the study area. Study area is outside 1B.1 Apr elevation range for this species. Cismontane woodland in study area is highly disturbed FT/SCE and anthropogenically influenced. No suitable habitat Pseudobahia peirsonii Cismontane woodland, Valley and foothill grassland. G1/S1 Not Expected present within the study area and no CNDDB San Joaquin adobe sunburst adobe clay. 90 ‐ 800 m. annual herb. Blooms Feb‐Apr 1B.1 occurrences are located within 5 miles of the study area. Cismontane woodland in study area is highly disturbed FE/SCE Cismontane woodland, Valley and foothill grassland, Sedella leiocarpa and anthropogenically influenced. No suitable habitat G1/S1 Vernal pools. vernally mesic depressions in volcanic Not Expected Lake County stonecrop present within the study area. Study area is outside 1B.1 outcrops. 365 ‐ 790 m. annual herb. Blooms Apr‐May elevation range for this species. Cismontane woodland in study area is highly disturbed None/None Chaparral, Cismontane woodland, Coastal scrub. and anthropogenically influenced. No suitable habitat Senecio aphanactis G3/S2 sometimes alkaline. 15 ‐ 800 m. annual herb. Blooms Not Expected present within the study area and no CNDDB chaparral ragwort 2B.2 Jan‐Apr(May) occurrences are located within 5 miles of the study area. FE/SCE Sidalcea oregana ssp. valida Marshes and swamps (freshwater). 115 ‐ 150 m. No suitable habitat present within the study area. G5T1/S1 Not Expected Kenwood Marsh checkerbloom perennial rhizomatous herb. Blooms Jun‐Sep Study area is outside elevation range for this species. 1B.1

FE/SCE Sidalcea pedata Meadows and seeps (mesic), Pebble (Pavement) plain. No suitable habitat present within the study area and G1/S1 Not Expected bird‐foot checkerbloom 1600 ‐ 2500 m. perennial herb. Blooms May‐Aug soil types are not suitable. 1B.1

Streptanthus glandulosus ssp. FE/SCE Valley and foothill grassland (serpentinite). 30 ‐ 150 m. No suitable habitat present within the study area. niger G4T1/S1 Not Expected annual herb. Blooms May‐Jun Study area is outside elevation range for this species. Tiburon jewelflower 1B.1

FT/SCR Swallenia alexandrae Desert dunes. 850 ‐ 1280 m. perennial rhizomatous No suitable habitat present within the study area. G2/S2 Not Expected Eureka Valley dune grass herb. Blooms Apr‐Jun Study area is outside elevation range for this species. 1B.2

FE/SCE Thelypodium stenopetalum Meadows and seeps (mesic, alkaline). 1600 ‐ 2500 m. No suitable habitat present within the study area. G1/S1 Not Expected slender‐petaled thelypodium perennial herb. Blooms May‐Sep Study area is outside elevation range for this species. 1B.1

FE/SCE Closed‐cone coniferous forest (sandy, openings, Trifolium trichocalyx No suitable habitat present within the study area and G1/S1 burned areas). 30 ‐ 305 m. annual herb. Blooms Apr‐ Not Expected Monterey clover soil types are not suitable. 1B.1 Jun

FE/SCR Tuctoria greenei Vernal pools. 30 ‐ 1070 m. annual herb. Blooms May‐ G1/S1 Not Expected No suitable habitat present within the study area. Greene's tuctoria Jul(Sep) 1B.1

Tuctoria mucronata FE/SCE Valley and foothill grassland (mesic), Vernal pools. 5 ‐ No suitable habitat present within the study area. Crampton's tuctoria or Solano G1/S1 Not Expected 10 m. annual herb. Blooms Apr‐Aug Study area is outside elevation range for this species. grass 1B.1 Cismontane woodland in study area is highly disturbed FT/SCT Cismontane woodland, Valley and foothill grassland. and anthropogenically influenced. No suitable habitat Verbena californica G2/S2 mesic, usually serpentinite seeps or creeks. 260 ‐ 400 Not Expected present within the study area and no CNDDB Red Hills vervain 1B.1 m. perennial herb. Blooms May‐Sep occurrences are located within 5 miles of the study area.

FT/SCT Verbesina dissita Chaparral (maritime), Coastal scrub. 45 ‐ 205 m. No suitable habitat present within the study area. G1G2/S1 Not Expected big‐leaved crownbeard perennial herb. Blooms (Mar)Apr‐Jul Study area is outside elevation range for this species. 1B.1

Fish Native to streams from Malibu Creek to San Luis Rey River basin. Introduced into streams in Santa Clara, None/None Gila orcuttii Ventura, Santa Ynez, Mojave & San Diego river basins. G2/S2 Not Expected No suitable habitat present within the study area. arroyo chub Slow water stream sections with mud or sand bottoms. Feeds heavily on aquatic vegetation and associated invertebrates. Reptiles Contra Costa County south to San Diego, within a None/None variety of open .This element represents Potentially suitable soils with areas of deep leaf litter Anniella spp. G3G4/S3S4 California records of Anniella not yet assigned to new Moderate potential and areas of sparse vegetation are present in the study California legless lizard CDFW_SSC‐Species of Special species within the Anniella pulchra complex. Variety of area. Concern habitats; generally in moist, loose soil. They prefer soils with a high moisture content. Generally south of the Transverse Range, extending to Potentially suitable soils with areas of deep leaf litter northwestern Baja California. Occurs in sandy or loose and areas of sparse vegetation are present in the study None/None loamy soils under sparse vegetation. Disjunct Anniella stebbinsi area. The nearest CNDDB occurrence is from 2015 and G3/S3 populations in the Tehachapi and Piute Mountains in High potential legless lizard is located approximately 0.35 miles south of the study Kern County. Variety of habitats; generally in moist, area in a developed area with patches of suitable loose soil. They prefer soils with a high moisture habitat. content.

None/None Found in deserts and semi‐arid areas with sparse A potentially suitable freshwater stream and Aspidoscelis tigris stejnegeri G5T5/S3 vegetation and open areas. Also found in woodland & Moderate potential associated riparian habitat are present in the study coastal whiptail CDFW_SSC‐Species of Special riparian areas. Ground may be firm soil, sandy, or area. Concern rocky. Most common in open, relatively rocky areas. Often in None/None somewhat moist microhabitats near intermittent A potentially suitable freshwater stream and Diadophis punctatus modestus G5T2T3/S2? streams. Avoids moving through open or barren areas Low potential associated riparian habitat are present in the study San Bernardino ringneck snake by restricting movements to areas of surface litter or area. herbaceous veg. A thoroughly aquatic turtle of ponds, marshes, rivers, None/None streams and irrigation ditches, usually with aquatic A potentially suitable freshwater stream and Emys marmorata G3G4/S3 vegetation, below 6000 ft elevation. Needs basking Moderate potential associated riparian habitat are present in the study western pond turtle sites and suitable (sandy banks or grassy open fields) area. upland habitat up to 0.5 km from water for egg‐laying. Frequents a wide variety of habitats, most common in Loose soils and diverse habitats with abundant insects None/None lowlands along sandy washes with scattered low Phrynosoma blainvillii are present in the study area, though the preferred G3G4/S3S4 bushes. Open areas for sunning, bushes for cover, Low potential coast horned lizard habitat of sandy washes with scattered low bushes is patches of loose soil for burial, and abundant supply of not present. ants and other insects. Coastal California from vicinity of Salinas to northwest None/None Baja California. From sea to about 7,000 ft elevation. A potentially suitable freshwater stream and Thamnophis hammondii G4/S3S4 Highly aquatic, found in or near permanent fresh Moderate potential associated riparian habitat are present in the study two‐striped gartersnake water. Often along streams with rocky beds and area. riparian growth. Birds

Highly colonial species, most numerous in Central Though riparian habitat is present in the study area, None/ST Valley & vicinity. Largely endemic to California. the preferred open water and marshes are not present. Agelaius tricolor G2G3/S1S2 Requires open water, protected nesting substrate, and Not Expected The only CNDDB occurrence in 5 miles is from 1995 tricolored blackbird foraging area with insect prey within a few km of the and is restricted to the banks of Lake Sherwood, colony. approximately 3.6 miles south of the study area.

Aimophila ruficeps canescens None/None Resident in Southern California and southern California rufous‐ G5T3/S3 sparse mixed chaparral. Frequents relatively steep, Not Expected No suitable habitat present within the study area. crowned sparrow CDFW_WL‐Watch List often rocky hillsides with grass and forb patches.

Obligate, permanent resident of coastal sage scrub FT/None Polioptila californica californica below 2500 ft in Southern California. Low, coastal sage G4G5T2Q/S2 Not Expected No suitable habitat present within the study area. coastal California gnatcatcher scrub in arid washes, on mesas and slopes. Not all areas classified as coastal sage scrub are occupied.

Colonial nester; nests primarily in riparian and other No suitable habitat present within the study area. None/ST Riparia riparia lowland habitats west of the desert. Requires vertical Nearest CNDDB observation is from 1964, and the G5/S2 Not Expected bank swallow banks/cliffs with fine‐textured/sandy soils near species is considered extirpated as a breeder in streams, rivers, lakes, ocean to dig nesting hole. southern California. Summer resident of Southern California in low riparian FE/SE in vicinity of water or in dry river bottoms; below 2000 Riparian habitat is isolated amid urban development, Vireo bellii pusillus G5T2/S2 ft. Nests placed along margins of bushes or on twigs Low potential however several important species that provide least Bell's vireo projecting into pathways, usually willow, Baccharis, shelter and forage are present in the study area. mesquite. Mammals None/None Coastal scrub of Southern California from San Diego Neotoma lepida intermedia G5T3T4/S3S4 County to San Luis Obispo County. Moderate to dense Not Expected No suitable habitat present within the study area. San Diego desert woodrat CDFW_SSC‐Species of Special canopies preferred. They are particularly abundant in Concern rock outcrops, rocky cliffs, and slopes. Sensitive Natural Communities Modern conversion to MCV2 nomenclature: California None/None Southern Sycamore Alder sycamore woodlands. This community was observed in G4/S4 . Present Riparian Woodland the study area during the January 2021 survey, and is currently ranked G3/S3.

Modern conversion to MCV2 nomenclature: Needle None/None grass ‐ Melic grass grassland. This community was not Valley Needlegrass Grassland G3/S3.1 . Absent observed in the study area during the January 2021 survey.

Modern conversion to MCV2 nomenclature: Valley oak None/None woodland and forest. This community was not Valley Oak Woodland G3/S2.1 . Absent observed in the study area during the January 2021 survey.