47 1st Street, Suite 1
Redlands, CA 92373-4601
(909) 915-5900
“Experience the Jericho Difference” jericho-systems.com October 15, 2019
Crystal Martinez
Andresen Architecture
17087 Orange Way
Fontana, CA 92335
RE: Biological Resources Assessment and Jurisdictional Delineation TD Management Trucking Facility, Locust Avenue and Stone Hurst Drive City of Rialto, CA
Dear Crystal:
Jericho Systems, Inc. (Jericho) is pleased to provide this letter report that details the results of a general Biological Resources Assessment (BRA) that includes habitat suitability assessments for nesting birds, Burrowing owl (Athene cunicularia) [BUOW], California gnatcatcher (Polioptila californica) [CAGN], raptors, small mammals such as the San Bernardino Kangaroo Rat (Dipodomys merriami parvus) [SBKR] and Los Angeles Pocket mouse (Perognathus longimembris brevinasus) [LAPM] and a Jurisdictional Waters Delineation (JD) for the proposed parcel located at the southwest corner of the intersection of Locust Avenue and Stonehurst Drive, in the city of Rialto, CA.
This report is designed to address potential effects of any development to designated Critical Habitats and/or any species currently listed or formally proposed for listing as endangered or threatened under the federal Endangered Species Act (ESA) and the California Endangered Species Act (CESA), or species designated as sensitive by the California Department of Fish and Wildlife (CDFW), or the California Native Plant Society (CNPS). Attention was focused sensitive species known to occur locally. This report also addresses resources protected under the Migratory Bird Treaty Act, federal Clean Water Act (CWA) regulated by the U.S. Army Corps of Engineers (USACE) and Regional Water Quality Control Board (RWQCB) respectively; and Section 1602 of the California Fish and Game Code (FCG) administered by the CDFW.
SITE LOCATION
The Project site is in northwestern Rialto, in San Bernardino County, approximately 0.5-mile north of the Foothill (SR-210). The Project site is a vacant and unimproved rectangular-shaped site located at the southwest intersection of Locust Avenue and West Stonehurst Drive. Vehicle access from along either of these streets.
ENVIRONMENTAL SETTING
The site is rectangular shape of vacant and unimproved land on approximately 3.5-acres (APNs:1133-08- 01 & 02). The site has mature native shrubs and has been heavily impacted by human activities. The subject parcel is undeveloped and surrounded on all sides by industrial development. The surrounding local area sits at the base of the Cajon Pass, where high winds are common meteorological events within the region. The local is characterized as Mediterranean an average annual rainfall of approximately 17 Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
inches. Hydrologically, the Project site is within the Colton Hydrologic Sub-Area (HSA 801.44) which comprises a 17,765-acre drainage area within the larger Middle Santa Ana River Watershed (HUC 180702030804). The subject parcel is situated in a developing area of the Inland Valleys ecoregion.
METHODS
As stated above, the objective of this document is to determine whether the Project area supports special status or otherwise sensitive species and/ or their habitat, and to address the potential effects associated with the Proposed project on those resources. The species and habitats addressed in this document are based on database information and field investigation.
Prior to conducting the field study, species and habitat information was gathered from the reports related to the specific project and relevant databases for the Devore, Fontana, San Bernardino North and South USGS quadrangles to determine which species and/or habitats would be expected to occur on site. These sources include:
• U.S. Fish and Wildlife (USFWS) threatened and endangered species occurrence GIS overlay; • USFWS Information for Planning and Consultation System (IPaC); • California Natural Diversity Database (CNDDB) Rarefind 5; • CNDDB Biogeographic Information and Observation System (BIOS); • California Native Plant Society Electronic Inventory (CNPSEI) database; • Calflora Database;
• USDA Natural Resources Conservation Service (NRCS) Web Soil Survey; • USFWS National Wetland Inventory;
• Environmental Protection Agency (EPA) Water Program “My Waters” data layers • USFWS Designated Critical Habitat Maps
We also reviewed other available technical information on the biological resources of the site, including previous trapping surveys and discussed recent findings with researchers in the field.
Jericho biologist Todd White conducted a general biological resources assessment on July 30, 2019, with an emphasis on special-status species known to occur in the area. Mr. White has an advanced degree and many years of experience surveying biological resources within Southern California. Mr. White conducted the systematic and comprehensive survey during calm weather, between the hours of 4:30 p.m. and 8:30 p.m. Weather conditions during the survey consisted of partly cloudy skies with temperatures ranging from 85 degrees Fahrenheit (° F) to 94° F and variable <5 mph wind.
Wildlife species were detected during field surveys by sight, calls, tracks, scat, or other sign. In addition to species observed, expected wildlife usage of the site was determined per known habitat preferences of regional wildlife species and knowledge of their relative distributions in the area. The focus of the faunal species surveys was to identify potential habitat for special status wildlife within the project area.
Disturbance characteristics and all animal sign encountered on the site are recorded in the results section.
The site was also evaluated for the presence of jurisdictional waters, i.e. waters of the U.S. as regulated by the USACE and RWQCB, and/or streambed and associated riparian habitat as regulated by the CDFW. Evaluation of potential federal jurisdiction followed the regulations set forth in 33CFR part 328 and the USACE guidance documents and evaluation of potential State jurisdiction followed guidance in the Fish and Game Code and A Review of Stream Processes and Forms in Dryland Watersheds (CDFW, 2010).
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
RESULTS
The database searches were conducted within a 3-mile radius of the Project and identified 85 sensitive species (36 plant, 43 animal, 6 invertebrate) and 5 sensitive habitats within the Devore, Fontana, San Bernardino North and South USGS 7.5-minute series quadrangles (Attachment B: Figure 3 and Figure 4).
A full summary of these results is outlined in Attachment A. The database searches indicated the presence of State- and/or federally listed threatened or endangered species within the vicinity of the project site.
Habitat on site consists of highly-disturbed coastal sage scrub mixed with non-native grasses and native and non-native annuals and perennials. Native species on site include telegraph weed (Heterotheca grandiflora), California buckwheat (Eriogonum fasciculatum), deerweed (Lotus scoparius), common phacelia (Phacelia distans), common sunflower (Helianthus annuus), slender buckwheat (Eriogonum gracile), and common fiddleneck (Amsinckia intermedia). The non-native vegetation present within the project area consists of red brome (Bromus rubens), ripgut brome (Bromus diandrus), redstem filaree (Erodium cicutarium), summer mustard (Hirschfeldia incana), tocalote (Centaurea mellitensis) and tree- of-heaven (Ailanthus altissima).
Wildlife species observed or otherwise detected on site during the surveys included: mourning dove (Zenaida macroura), California towhee (Melozone fusca), house finch (Haemorhous mexicanus), Say’s phoebe (Sayornis saya), desert cottontail (Sylvilagus audobonii). Active small mammal burrows were found scattered throughout the site. There are burrows on site that are potentially suitable for BUOW.
San Bernardino Kangaroo Rat (SBKR)
The SBKR is one of several kangaroo rat species in its range. The Dulzura kangaroo rat (Dipodomys simulans), the Pacific kangaroo rat (D. agilis) and the Stephens kangaroo rat (D. stephensi) can occur in areas occupied by the SBKR, but these other species have a wider habitat range.
The habitat of the SBKR is confined to primary and secondary alluvial fan scrub habitats, with sandy soils deposited by fluvial (water) rather than aeolian (wind) processes. Burrows are dug in loose soil, usually near or beneath shrubs. SBKR, are confined to inland valley scrub communities, and more particularly, to scrub communities occurring along rivers, streams and drainage. Most of these drainages have been historically altered as a result of flood control efforts and the resulting increased use of river resources, including mining, off-road vehicle uses and road and housing development. This increased use of river resources has resulted in a reduction in both the amount and quality of habitat available for the SBKR. The past habitat losses and potential future losses prompted the emergency listing of the SBKR as an endangered species.
Documented occurrences of SBKR in the vicinity of the Project site (primarily along the Lytle Creek corridor located 1 mile to the northeast) and Critical Habitat for SBKR is mapped near the Project site.
The Project site is small and has been landlocked by industrial development on all sides since 2014. The isolation of the Project site from other occupied areas renders it unsuitable for SBKR. No further investigation is warranted.
Los Angeles Pocket Mouse (LAPM)
The LAPM is one of two pocket mice found in this area of San Bernardino County. Both the LAPM and the San Diego pocket mouse occupy similar habitats, but the San Diego pocket mouse has a wider range Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
extending south into San Diego County. The habitat of the LAPM is confined to lower elevation grasslands and coast sage scrub habitats, in areas with soils composed of fine sands. The present known distribution of this species extends from Rancho Cucamonga east to Morongo and south to the San Diego County border. LAPM forages in open ground and underneath shrubs. Pocket mice in general dig burrows in loose soil, although this has not been completely documented for this subspecies. The LAPM is listed as a Critical Species of Concern by the CDFW.
The Project site is small and has been landlocked by industrial development on all sides since 2014. The isolation of the Project site from other occupied areas renders it unsuitable for LAPM. No further investigation is warranted.
California gnatcatcher(CAGN)
CAGN is a federally listed Threatened Species year-round residents of the CSS vegetative community in southern California. It is a small thrush-like songbird approximately 4 to 5 inches in length with dark, blue-gray plumage above and gray-white plumage below. Nest building begins during the second or third week of March. The range and distribution of the CAGN is closely aligned with coastal scrub vegetation.
This vegetation is typified by low 3 feet, shrub and sub-shrub species that are often drought deciduous.
The coastal scrub plant communities that overlap the range of the gnatcatcher include Venturan, Diegan, and Riversidean coastal sage scrub communities, and Martirian and Vizcainan coastal succulent scrub communities. The density of CAGN is highest in high-quality habitat and decreased as habitat quality decreased.
As late as the mid-1940s the CAGN was considered locally common and by the mid-1960s, a noticeable decline had begun. The CAGN was listed as Threatened in 1992. According to the “Final Critical Habitat mapping Unit #12" for San Bernardino County, this site is not located within designated critical habitat for the CAGN.
The site contains no habitat potentially suitable for CAGN.
Burrowing owl (BUOW)
BUOW are known to occur locally within suitable habitat areas. BUOW is a ground-dwelling owl typically found in arid prairies, fields, and open areas where vegetation is sparse and low to the ground.
The BUOW depends on the presence of mammal burrows, i.e. ground squirrel burrows to provide shelter from predators, inclement weather and to provide a nesting place. They are also known to make use of human-created structures, such as cement culverts and pipes, for burrows. They feed primarily on insects but will also take small rodents, birds, and reptiles. They are active during the day and night, generally observed in the early morning hours or at twilight. The breeding season for BUOW is February 1 through August 31. The BUOW is not listed under the State or Federal Endangered Species Act but is considered both a State and federal SSC. The BUOW is a protected by the international treaty under the Migratory Bird Treaty Act of 1918 and by State law under the California Fish and Game Code (CDFG Code #3513 & #3503.5).
Per the definition provided in the 2012 CDFG Staff Report on Burrowing Owl Mitigation, “Burrowing owl habitat generally includes, but is not limited to, short or sparse vegetation (at least at some time of year), presence of burrows, burrow surrogates or presence of fossorial mammal dens, well-drained soils, and abundant and available prey.” The Project site contains potentially suitable habitat for this species for the following reasons:
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
• Vegetation is sparse or low to the ground
• Several burrows on site are small mammal burrows that are of the appropriate size shape or aspect for BUOW
• Soils are sandy and friable
No evidence of BUOW was found in the survey area. Several burrows of appropriate shape size or aspect for BUOW, however no BUOW pellets, feathers or whitewash were found on site. No BUOW individuals were observed. Therefore, BUOW are considered absent from the site at the time of surveys.
Nesting Birds and Raptors
The site is not suitable for use by raptors. The project site and immediate surrounding areas do contain habitat suitable for nesting birds in general, including the shrubs on site.
Nesting birds are protected under the MBTA which provides protection for nesting birds that are both residents and migrants whether they are considered sensitive by resource agencies. The MBTA makes it unlawful to take, possess, buy, sell, purchase, or barter any migratory bird listed under 50 CFR 10, including feathers or other parts, nests, eggs, or products, except as allowed by implementing regulations (50 CFR 21). The direct injury or death of a migratory bird, due to construction activities or other construction-related disturbance that causes nest abandonment, nestling abandonment, or forced fledging would be considered take under federal law. The USFWS, in coordination with the CDFW administers the MBTA. CDFW’s authoritative nexus to MBTA is provided in FGC Sections 3503.5 which protects all birds of prey and their nests and FGC Section 3800 which protects all non-game birds that occur naturally in the State.
Jurisdiction Waters
The site drains from northwest to southeast, with only surface flow onto the property from Stonehurst Drive. The Site has no historically documented jurisdictional waters on or near the vicinity.
There are no drainages on site. No aspect of the site presents any evidence of jurisdictional waters. None of the following indicators are present on site: riparian vegetation, facultative, facultative wet or obligate wet vegetation, harrow marks, sand bars shaped by water, racking, rilling, destruction of vegetation, defined bed and bank, distinct line between vegetation types, clear natural scour line, meander bars, mud cracks, staining, silt deposits, litter- organic debris. No jurisdictional waters occur on site.
CONCLUSIONS AND RECOMMENDATIONS
BUOW
There is low potential for BUOW due to the size and quality of suitable habitat. A pre-construction site survey is recommended within 30 days of any planned earth moving activities or construction activities take place.
CAGN
Habitat conditions on site are not suitable for CAGN. The Site supports highly disturbed and poor quality habitat for CAGN, and the area is small and heavily impacted. No further actions are recommended.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
SBKR/LAPM
Habitat conditions on site are not suitable for SBKR or LAPM. The Site supports highly disturbed and poor quality habitat for either species, and the Project site is isolated from any suitable habitat for these species. No further actions are recommended.
Nesting Birds
The vegetation on site does have a potential to support nesting birds. Therefore, to reduce the potential impacts to nesting birds, the following is recommended:
Bird nesting season generally extends from February 1 through September 15 in southern California and specifically, April 15 through August 31 for migratory passerine birds. To avoid impacts to nesting birds (common and special status) during the nesting season, a qualified Avian Biologist will conduct pre‐construction Nesting Bird Surveys (NBS) prior to project‐related disturbance to nestable vegetation to identify any active nests. If no active nests are found, no further action will be required.
If an active nest is found, the biologist will set appropriate no‐work buffers around the nest which will be based upon the nesting species, its sensitivity to disturbance, nesting stage and expected types, intensity and duration of disturbance. The nests and buffer zones shall be field checked weekly by a qualified biological monitor. The approved no‐work buffer zone shall be clearly marked in the field, within which no disturbance activity shall commence until the qualified biologist has determined the young birds have successfully fledged and the nest is inactive.
Please do not hesitate to contact me at 909-915-5900 should you have any questions or require further information.
Sincerely,
Shay Lawrey, President
Ecologist/Regulatory Specialist
Attachments:
Attachment A – Table of Documented Occurrences
Attachment B – Figures
Attachment C – Site Photos
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
ATTACHMENT A – TABLE
OF DOCUMENTED
OCCURRENCES
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Attachment A – Table of Documented Occurences
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Agelaius tricolor tricolored
blackbird
None/
Threatened
Highly colonial species, most numerous in Central Valley & vicinity. Largely endemic to California. Requires open water, protected nesting substrate, and foraging area with insect prey within a few km of the colony.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Aimophila
ruficeps
canescens
southern
California
rufous-crowned
sparrow
None/ None
Resident in Southern California coastal sage scrub and sparse mixed chaparral. Frequents relatively steep, often rocky hillsides with grass and forb patches.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Ambrosia
monogyra
singlewhorl
burrobrush None/ None Chaparral, Sonoran desert scrub. Sandy soils. 5-475 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Anniella
stebbinsi
southern
California
legless lizard
None/ None
Generally south of the Transverse Range, extending to northwestern Baja California. Occurs in sandy or loose loamy soils under sparse vegetation. Disjunct populations in the Tehachapi and Piute Mountains in Kern County. Variety of habitats; generally in moist, loose soil. They prefer soils with a high moisture content.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Arenaria
paludicola marsh sandwort Endangered/
Endangered
Marshes and swamps. Variety of habitats; generally in moist, loose soil. They prefer soils with a high moisture content. Growing up through dense mats of Typha, Juncus, Scirpus, etc. in freshwater marsh. Sandy soil. 3-170 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Arizona elegans
occidentalis
California
glossy snake None/ None
Patchily distributed from the eastern portion of San Francisco Bay, southern San Joaquin Valley, and the Coast, Transverse, and Peninsular ranges, south to Baja California. Generalist reported from a range of scrub and grassland habitats, often with loose or sandy soils.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Artemisiospiza
belli belli
Bell's sage
sparrow None/ None
Nests in chaparral dominated by fairly dense stands of chamise.
Found in coastal sage scrub in south of range. Nest located on the ground beneath a shrub or in a shrub 6-18 inches above ground.
Territories about 50 yds apart.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Aspidoscelis
hyperythra
orange-throated
whiptail None/ None
Inhabits low-elevation coastal scrub, chaparral, and valley-foothill hardwood habitats. Prefers washes and other sandy areas with patches of brush and rocks. Perennial plants necessary for its major food: termites.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Aspidoscelis
tigris stejnegeri coastal whiptail None/ None
Found in deserts and semi-arid areas with sparse vegetation and open areas. Also found in woodland & riparian areas. Ground may be firm soil, sandy, or rocky.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Astragalus
hornii var.
hornii
Horn's milk-
vetch None/ None Meadows and seeps, playas. Lake margins, alkaline sites. 75-350 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Athene
cunicularia burrowing owl None/ None
Open, dry annual or perennial grasslands, deserts, and scrublands characterized by low-growing vegetation. Subterranean nester, dependent upon burrowing mammals, most notably, the California ground squirrel.
The habitat onsite is suitable for
this species. Potential to occur is
low to moderate.
Baeolophus
inornatus oak titmouse None/ None Oak woodlands. Cavity nester.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Batrachoseps
gabrieli
San Gabriel
slender
salamander
None/ None
Known only from the San Gabriel Mtns. Found under rocks, wood, and fern fronds, and on soil at the base of talus slopes. Most active on the surface in winter and early spring.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Berberis nevinii Nevin's
barberry
Endangered/
Endangered
Chaparral, cismontane woodland, coastal scrub, riparian scrub. On steep, N-facing slopes or in low grade sandy washes. 90-1590 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Bombus crotchii Crotch bumble
bee None/ None
Coastal California east to the Sierra-Cascade crest and south into Mexico. Food plant genera include Antirrhinum, Phacelia, Clarkia, Dendromecon, Eschscholzia, and Eriogonum.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Brodiaea
filifolia
thread-leaved
brodiaea
Threatened/
Endangered
Chaparral (openings), cismontane woodland, coastal scrub, playas, valley and foothill grassland, vernal pools. Usually associated with annual grassland and vernal pools; often surrounded by shrubland habitats. Occurs in openings on clay soils. 15-1030 m
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Buteo swainsoni Swainson's
hawk
None/
Threatened
Breeds in grasslands with scattered trees, juniper-sage flats, riparian areas, savannahs, & agricultural or ranch lands with groves or lines of trees. Requires adjacent suitable foraging areas such as grasslands, or alfalfa or grain fields supporting rodent populations.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Calochortus
palmeri var.
palmeri
Palmer's
mariposa-lily None/ None Meadows and seeps, chaparral, lower montane coniferous forest.
Vernally moist places in yellow-pine forest, chaparral. 195-2530 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Calochortus
plummerae
Plummer's
mariposa-lily None/ None
Coastal scrub, chaparral, valley and foothill grassland, cismontane woodland, lower montane coniferous forest. Occurs on rocky and sandy sites, usually of granitic or alluvial material. Can be very common after fire. 60-2500 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Carex comosa bristly sedge None/ None
Marshes and swamps, coastal prairie, valley and foothill grassland.
Lake margins, wet places; site below sea level is on a Delta island. - 5-1010 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Carolella
busckana
Busck's
gallmoth None/ None No information.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Castilleja
lasiorhyncha
San Bernardino
Mountains
owl's-clover
None/ None
Meadows and seeps, pebble plain, upper montane coniferous forest, chaparral, riparian woodland. Mesic to drying soils in open areas of stream and meadow margins or in vernally wet areas. 1140-2320 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Catostomus
santaanae
Santa Ana
sucker
Threatened/
None
Endemic to Los Angeles Basin south coastal streams. Habitat generalists, but prefer sand-rubble-boulder bottoms, cool, clear water, and algae.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Centromadia
pungens ssp.
laevis
smooth tarplant None/ None
Valley and foothill grassland, chenopod scrub, meadows and seeps, playas, riparian woodland. Alkali meadow, alkali scrub; also in disturbed places. 5-1170 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Chaetodipus
fallax fallax
northwestern
San Diego
pocket mouse
None/ None
Sandy, herbaceous areas, usually in association with rocks or coarse gravel. Sandy, herbaceous areas, usually in association with rocks or coarse gravel.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Chaetodipus
fallax pallidus
pallid San
Diego pocket
mouse
None/ None
Desert border areas in eastern San Diego County in desert wash, desert scrub, desert succulent scrub, pinyon-juniper, etc. Sandy, herbaceous areas, usually in association with rocks or coarse gravel.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Charina
umbratica
southern rubber
boa
None/
Threatened
Found in vicinity of streams or wet meadows; requires loose, moist soil for burrowing; seeks cover in rotting logs, rock outcrops, and under surface litter.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Chloropyron
maritimum ssp.
maritimum
salt marsh
bird's-beak
Endangered/
Endangered
Marshes and swamps, coastal dunes. Limited to the higher zones of salt marsh habitat. 0-10 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Chorizanthe
parryi var.
parryi
Parry's
spineflower None/ None
Coastal scrub, chaparral, cismontane woodland, valley and foothill grassland. Dry slopes and flats; sometimes at interface of 2 vegetation types, such as chaparral and oak woodland. Dry, sandy soils. 90-1220 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Chorizanthe
xanti var.
leucotheca
white-bracted
spineflower None/ None Mojavean desert scrub, pinyon and juniper woodland, coastal scrub (alluvial fans). Sandy or gravelly places. 365-1830 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Cicindela
tranquebarica
viridissima
greenest tiger
beetle None/ None Inhabits the woodlands adjacent to the Santa Ana River basin.
Usually found in open spots between trees.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Coccyzus
americanus
occidentalis
western
yellow-billed
cuckoo
Threatened/
Endangered
Riparian forest nester, along the broad, lower flood-bottoms of larger river systems. Nests in riparian jungles of willow, often mixed with cottonwoods, with lower story of blackberry, nettles, or wild grape.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Coleonyx
variegatus
abbotti
San Diego
banded gecko None/ None Coastal & cismontane Southern California. Found in granite or rocky outcrops in coastal scrub and chaparral habitats.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crotalus ruber red-diamond
rattlesnake None/ None
Chaparral, woodland, grassland, & desert areas from coastal San Diego County to the eastern slopes of the mountains. Occurs in rocky areas and dense vegetation. Needs rodent burrows, cracks in rocks or surface cover objects.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Cuscuta
obtusiflora var.
glandulosa
Peruvian
dodder None/ None Marshes and swamps (freshwater). Freshwater marsh. 15-280 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Diadophis
punctatus
modestus
San Bernardino
ringneck snake None/ None
Most common in open, relatively rocky areas. Often in somewhat moist microhabitats near intermittent streams. Avoids moving through open or barren areas by restricting movements to areas of surface litter or herbaceous veg.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Dipodomys
merriami parvus
San Bernardino
kangaroo rat
Endangered/
None
Alluvial scrub vegetation on sandy loam substrates characteristic of alluvial fans and flood plains. Needs early to intermediate seral stages.
The Project site is isolated from
any area occupied by this
species. Potential to occur is
low.
Dipodomys
stephensi
Stephens'
kangaroo rat
Endangered/
Threatened
Primarily annual & perennial grasslands, but also occurs in coastal scrub & sagebrush with sparse canopy cover. Prefers buckwheat, chamise, brome grass and filaree. Will burrow into firm soil.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Dodecahema
leptoceras
slender-horned
spineflower
Endangered/
Endangered
Chaparral, cismontane woodland, coastal scrub (alluvial fan sage scrub). Flood deposited terraces and washes; associates include Encelia, Dalea, Lepidospartum, etc. Sandy soils. 200-765 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Eremophila
alpestris actia
California
horned lark None/ None
Coastal regions, chiefly from Sonoma County to San Diego County.
Also main part of San Joaquin Valley and east to foothills. Short- grass prairie, "bald" hills, mountain meadows, open coastal plains, fallow grain fields, alkali flats.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Eriastrum
densifolium ssp.
sanctorum
Santa Ana
River
woollystar
Endangered/
Endangered
Coastal scrub, chaparral. In sandy soils on river floodplains or terraced fluvial deposits. 180-705 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Euchloe hyantis
andrewsi
Andrew's
marble
butterfly
None/ None
Inhabits yellow pine forest near Lake Arrowhead and Big Bear Lake, San Bernardino Mtns, San Bernardino Co, 5000-6000 ft. Hostplants are Streptanthus bernardinus & Arabis holboellii var pinetorum; larval foodplant is Descurainia richardsonii. Roosts in crevices in cliff faces, high buildings, trees and tunnels.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Eumops perotis
californicus
western mastiff
bat None/ None
Many open, semi-arid to arid habitats, including conifer & deciduous woodlands, coastal scrub, grasslands, chaparral, etc. Roosts in crevices in cliff faces, high buildings, trees and tunnels.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Euphydryas
editha quino
quino
checkerspot
butterfly
Endangered
Sunny openings within chaparral & coastal sage shrublands in parts of Riverside & San Diego counties. Hills and mesas near the coast.
Need high densities of food plants Plantago erecta, P. insularis, and Orthocarpus purpurescens.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Falco
columbarius merlin None/ None
Seacoast, tidal estuaries, open woodlands, savannahs, edges of grasslands & deserts, farms & ranches. Clumps of trees or windbreaks are required for roosting in open country.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Fimbristylis
thermalis
hot springs
fimbristylis None/ None Meadows and seeps (alkaline). Near hot springs. 115-1585 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Galium
californicum
ssp. primum
Alvin Meadow
bedstraw None/ None
Chaparral, lower montane coniferous forest. Grows in shade of trees and shrubs at the lower edge of the pine belt, in pine forest-chaparral ecotone. Granitic, sandy soils. 1460-1830 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Gila orcuttii arroyo chub None/ None
Native to streams from Malibu Creek to San Luis Rey River basin.
Introduced into streams in Santa Clara, Ventura, Santa Ynez, Mojave & San Diego river basins. Slow water stream sections with mud or sand bottoms. Feeds heavily on aquatic vegetation and associated invertebrates.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Glaucomys
oregonensis
californicus
San Bernardino
flying squirrel None/ None
Known from black oak or white fir dominated woodlands between 5200 - 8500 ft in the San Bernardino and San Jacinto ranges. May be extirpated from San Jacinto range. Needs cavities in trees/snags for nests and cover. Needs nearby water.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Helianthus
nuttallii ssp.
parishii
Los Angeles
sunflower None/ None Marshes and swamps (coastal salt and freshwater). 35-1525 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Horkelia
cuneata var.
puberula
mesa horkelia None/ None Chaparral, cismontane woodland, coastal scrub. Sandy or gravelly sites. 15-1645 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Imperata
brevifolia
California
satintail None/ None
Coastal scrub, chaparral, riparian scrub, mojavean desert scrub, meadows and seeps (alkali), riparian scrub. Mesic sites, alkali seeps, riparian areas. 3-1495 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Lasiurus
xanthinus
western yellow
bat None/ None
Found in valley foothill riparian, desert riparian, desert wash, and palm oasis habitats. Roosts in trees, particularly palms. Forages over water and among trees.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Laterallus
jamaicensis
coturniculus
California
black rail
None/
Threatened
Inhabits freshwater marshes, wet meadows and shallow margins of saltwater marshes bordering larger bays. Needs water depths of about 1 inch that do not fluctuate during the year and dense vegetation for nesting habitat.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Lepidium
virginicum var.
robinsonii
Robinson's
pepper-grass None/ None Chaparral, coastal scrub. Dry soils, shrubland. 4-1435 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Lepus
californicus
bennettii
San Diego
black-tailed
jackrabbit
None/ None
Intermediate canopy stages of shrub habitats & open shrub / herbaceous & tree / herbaceous edges. Coastal sage scrub habitats in Southern California.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Lilium parryi lemon lily None/ None
Lower montane coniferous forest, meadows and seeps, riparian forest, upper montane coniferous forest. Wet, mountainous terrain; generally in forested areas; on shady edges of streams, in open boggy meadows & seeps. 625-2930 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Lycium parishii Parish's desert-
thorn None/ None Coastal scrub, Sonoran desert scrub. -3-570 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Malacothamnus
parishii
Parish's bush-
mallow None/ None Chaparral, coastal sage scrub. In a wash. 305-455 m The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Monardella
pringlei
Pringle's
monardella None/ None Coastal scrub. Sandy hills. 300-400 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Nasturtium
gambelii
Gambel's water
cress Endangered
Marshes and swamps. Freshwater and brackish marshes at the margins of lakes and along streams, in or just above the water level. 5-305 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Neotoma lepida
intermedia
San Diego
desert woodrat None/ None
Coastal scrub of Southern California from San Diego County to San Luis Obispo County. Moderate to dense canopies preferred. They are particularly abundant in rock outcrops, rocky cliffs, and slopes.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Nyctinomops
femorosaccus
pocketed free-
tailed bat None/ None
Variety of arid areas in Southern California; pine-juniper woodlands, desert scrub, palm oasis, desert wash, desert riparian, etc. Rocky areas with high cliffs.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Oncorhynchus
mykiss irideus
pop. 10
steelhead -
southern
California DPS
Endangered
Federal listing refers to populations from Santa Maria River south to southern extent of range (San Mateo Creek in San Diego County).
Southern steelhead likely have greater physiological tolerances to warmer water and more variable conditions.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Onychomys
torridus ramona
southern
grasshopper
mouse
None/ None
Desert areas, especially scrub habitats with friable soils for digging.
Prefers low to moderate shrub cover. Feeds almost exclusively on arthropods, especially scorpions and orthopteran insects.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Opuntia
basilaris var.
brachyclada
short-joint
beavertail None/ None Chaparral, Joshua tree woodland, Mojavean desert scrub, pinyon- juniper woodland. Sandy soil or coarse, granitic loam. 425-1800 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Perognathus
longimembris
brevinasus
Los Angeles
pocket mouse None/ None
Lower elevation grasslands and coastal sage communities in and around the Los Angeles Basin. Open ground with fine, sandy soils.
May not dig extensive burrows, hiding under weeds and dead leaves instead.
The shrub component on site is
potentially suitable for this
species. Potential to occur is low
to moderate.
Phrynosoma
blainvillii
coast horned
lizard None/ None
Frequents a wide variety of habitats, most common in lowlands along sandy washes with scattered low bushes. Open areas for sunning, bushes for cover, patches of loose soil for burial, and abundant supply of ants and other insects
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Polioptila
californica
californica
coastal
California
gnatcatcher
Threatened/
None
Obligate, permanent resident of coastal sage scrub below 2500 ft in Southern California. Low, coastal sage scrub in arid washes, on mesas and slopes. Not all areas classified as coastal sage scrub are occupied.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Rana muscosa
southern
mountain
yellow-legged
frog
Endangered/
Endangered
Federal listing refers to populations in the San Gabriel, San Jacinto and San Bernardino mountains (southern DPS). Northern DPS was determined to warrant listing as endangered, Apr 2014, effective Jun 30, 2014. Always encountered within a few feet of water. Tadpoles may require 2 - 4 yrs to complete their aquatic development.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Rhaphiomidas
terminatus
abdominalis
Delhi Sands
flower-loving
fly
Endangered
Found only in areas of the Delhi Sands formation in southwestern San Bernardino & northwestern Riverside counties. Requires fine, sandy soils, often with wholly or partly consolidated dunes & sparse vegetation. Oviposition req. shade.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Rhinichthys
osculus ssp. 3
Santa Ana
speckled dace None/ None
Headwaters of the Santa Ana and San Gabriel rivers. May be extirpated from the Los Angeles River system. Requires permanent flowing streams with summer water temps of 17-20 C. Usually inhabits shallow cobble and gravel riffles.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Ribes
divaricatum var.
parishii
Parish's
gooseberry None/ None Riparian woodland. Salix swales in riparian habitats. 65-300 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Riversidian
Alluvial Fan
Sage Scrub
Riversidian
Alluvial Fan
Sage Scrub
None/ None Habitat
Historically present, heavily
altered and impacted. Does not
exist on site.
Schoenus
nigricans black bog-rush None/ None Marshes and swamps. Often in alkaline marshes. 120-1525 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Senecio
aphanactis
chaparral
ragwort None/ None Chaparral, cismontane woodland, coastal scrub. Drying alkaline flats. 20-855 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Setophaga
petechia yellow warbler None/ None
Riparian plant associations in close proximity to water. Also nests in montane shrubbery in open conifer forests in Cascades and Sierra Nevada. Frequently found nesting and foraging in willow shrubs and thickets, and in other riparian plants including cottonwoods, sycamores, ash, and alders.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Sidalcea
neomexicana
salt spring
checkerbloom None/ None Playas, chaparral, coastal scrub, lower montane coniferous forest, Mojavean desert scrub. Alkali springs and marshes. 3-2380 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Southern
Cottonwood
Willow Riparian
Forest
Southern
Cottonwood
Willow
Riparian Forest
None/ None Habitat Habitat does not exist on site.
Southern
Riparian Forest
Southern
Riparian Forest None/ None Habitat Habitat does not exist on site.
Southern
Riparian Scrub
Southern
Riparian Scrub None/ None Habitat Habitat does not exist on site.
Southern
Sycamore Alder
Riparian
Woodland
Southern
Sycamore
Alder Riparian
Woodland
None/ None Habitat Habitat does not exist on site.
Spea hammondii western
spadefoot None/ None
Occurs primarily in grassland habitats, but can be found in valley- foothill hardwood woodlands. Vernal pools are essential for breeding and egg-laying.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Sphenopholis
obtusata
prairie wedge
grass None/ None
Cismontane woodland, meadows and seeps. Open moist sites, along rivers and springs, alkaline desert seeps. 15-2625 m. Open moist sites, along rivers and springs, alkaline desert seeps. 15-2625 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Streptanthus
bernardinus
Laguna
Mountains
jewelflower
None/ None
Chaparral, lower montane coniferous forest. Clay or decomposed granite soils; sometimes in disturbed areas such as streamsides or roadcuts. 1440-2500 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Streptanthus
campestris
southern
jewelflower None/ None Chaparral, lower montane coniferous forest, pinyon and juniper woodland. Open, rocky areas. 605-2590 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Symphyotrichum
defoliatum
San Bernardino
aster None/ None
Meadows and seeps, cismontane woodland, coastal scrub, lower montane coniferous forest, marshes and swamps, valley and foothill grassland. Vernally mesic grassland or near ditches, streams and springs; disturbed areas. 3-2045 m.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Taxidea taxus American
badger None/ None
Most abundant in drier open stages of most shrub, forest, and herbaceous habitats, with friable soils. Needs sufficient food, friable soils and open, uncultivated ground. Preys on burrowing rodents.
Digs burrows.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Scientific Name Common
Name
Federal/State
Ranking Habitat Potential to Occur
Thamnophis
hammondii
two-striped
gartersnake None/ None
Coastal California from vicinity of Salinas to northwest Baja California. From sea to about 7,000 ft elevation. Highly aquatic, found in or near permanent fresh water. Often along streams with rocky beds and riparian growth.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Vireo bellii
pusillus
least Bell's
vireo
Endangered/
Endangered
Summer resident of Southern California in low riparian in vicinity of water or in dry river bottoms; below 2000 ft. Nests placed along margins of bushes or on twigs projecting into pathways, usually willow, Baccharis, mesquite.
The habitat onsite is unsuitable
for this species. Potential to
occur is low.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
ATTACHMENT B
FIGURES
^_
Service Layer Credits: Esri, HERE, Garmin, (c) OpenStreetMap contributors, and the GIS user community
Copyright:© 2013 National Geographic Society, i-cubed
0 2.5 5 7.5 101.25
Miles
^_
Regional Overview
Site Vicinity
Figure 1 - Regional Overview
Site Vicinity
TD Management Trucking Facility
Locust Avenue and Stone Hurst Drive
City of Rialto, CA
Date: 10/21/2019
Legend
^_ Site Vicinity
O
Service Layer Credits: Esri, HERE, Garmin, (c) OpenStreetMap contributors Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS, 0 0.15 0.3 0.45 0.60.075
Miles
Figure 2
Site Location
TD Management Trucking Facility
Locust Avenue and Stone Hurst Drive
City of Rialto, CA
Imagery Date: 8/6/2017
1 inch = 833 feet
O
Date: 10/21/2019
Legend
Site Location
^_
Service Layer Credits: Esri, HERE, Garmin, (c) OpenStreetMap contributors Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS, 0 0.9 1.8 2.7 3.60.45
Miles
Figure 3
3-mile CNDDB Occurrences
TD Management Trucking Facility
Locust Avenue and Stone Hurst Drive
City of Rialto, CA
Imagery Date: 8/6/2017
1 inch = 4,717 feet
O
Date: 10/21/2019
Legend
^_
Site Location
3-mile Buffer
California glossy snake
Crotch bumble bee
Parry's spineflower
Plummer's mariposa-lily
Riversidian Alluvial Fan Sage Scrub
San Bernardino kangaroo rat
San Diego desert woodrat
Santa Ana River woollystar
burrowing owl
coast horned lizard
coastal California gnatcatcher
mesa horkelia
northwestern San Diego pocket mouse
singlewhorl burrobrush
southern California legless lizard
Service Layer Credits: Esri, HERE, Garmin, (c) OpenStreetMap contributors Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS, 0 0.9 1.8 2.7 3.60.45
Miles
Figure 4
USFWS-Designated Critical Habitat
TD Management Trucking Facility
Locust Avenue and Stone Hurst Drive
City of Rialto, CA
Imagery Date: 8/6/2017
1 inch = 4,717 feet
O
Date: 10/21/2019
Legend
Site Location
3-mile Buffer
San Bernardino Merriam's Kangaroo Rat Critical Habitat
Service Layer Credits: Esri, HERE, Garmin, (c) OpenStreetMap contributors Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS,0 0.01 0.02 0.03 0.040.005 Miles
Figure 5
Soils
TD Management Trucking Facility
Locust Avenue and Stone Hurst Drive
City of Rialto, CA
Imagery Date: 8/6/2017
1 inch = 68 feet
O
Date: 10/21/2019
Legend
Site Location
Soils
SoC; Soboba gravelly loamy sand, 0 to 9 percent slopes
TvC; Tujunga gravelly loamy sand, 0 to 9 percent slopes
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
ATTACHMENT C
SITE PHOTOS
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Photo 1. View looking
east along north side of
parcel bordering
Stonehurst Drive.
Photo 2. View looking
southeast diagonally
from north side of
parcel bordering
Stonehurst Drive..
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Photo 3. View looking
north from the southeast
corner of the property
along Locust Ave.
Photo 4. Looking
diagonally from
northeast corner of
property towards the
southwest corner.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Photo 5. View east
down south edge of
property line towards
Locust Ave.
Photo 6. UAV view
looking east from
western side of
property.
Crystal Martinez
BRA/JD – T&D Management - Rialto
October 15, 2019
Photo 7. UAV view
looking west from
eastern side of property.
Photo 8. UAV view
looking southeast from
northeast corner of
property.