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State Route 58 Widening Project - Bakersfield Freeways

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<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> (Rosedale Highway)<br />

BA<br />

Biological Assessment<br />

Rosedale Highway, <strong>Project</strong> Limits Extend from West of Allen Road to <strong>State</strong> <strong>Route</strong><br />

99Kern County, CA<br />

District 06-Kern-<strong>58</strong>- PM 46.1 to 51.7<br />

EA 0600000076<br />

September 22, 2011


For individuals with sensory disabilities, this document is available in Braille, large print, on<br />

audiocassette, or computer disk. To obtain a copy in one of these alternate formats, please call or<br />

write to Caltrans, Attn: Kirsten Helton, Senior Environmental Planner, District 6, 855 M Street,<br />

Suite 200, Fresno, California 93731; (559) 445-6282. Voice, or use the California Relay Service<br />

TTY number: (559) 488-4067.


Summary of Findings, Conclusions and Determinations<br />

Summary of Findings, Conclusions and Determinations<br />

The California Department of Transportation (Caltrans), in cooperation with the City<br />

of <strong>Bakersfield</strong> and the County of Kern, proposes to improve an approximate 5.6-mile<br />

segment of <strong>State</strong> <strong>Route</strong> (SR) <strong>58</strong>, locally known as Rosedale Highway. The project area<br />

is located within unincorporated Kern County and the City of <strong>Bakersfield</strong>; the limits<br />

extend from west of Allen Road to <strong>State</strong> <strong>Route</strong> (SR) 99.<br />

The proposed project would construct two new lanes between Allen Road and SR 99;<br />

this would result in a six lane roadway throughout the project limits (post mile [PM]<br />

46.1 to PM 51.7). Improvements would also include a grade separated rail crossing that<br />

would be constructed between Mohawk Street and Landco Drive. The bridge over<br />

Calloway Canal would be widened; however, the bridge over the Friant-Kern Canal<br />

would not be widened.<br />

The purpose of the proposed project is to improve east-west traffic flow on the local<br />

and regional transportation systems and to improve traffic operations within the<br />

corridor to accommodate planned growth.<br />

The proposed project is part of the Thomas Roads Improvement Program (TRIP),<br />

which includes 10 projects: six road improvement projects in the planning and<br />

environmental review phases, three road projects currently under construction<br />

(Westside Parkway, SR-178 at Fairfax Interchange and 7 th Standard Road) and one<br />

route adoption (West Beltway).<br />

The Biological Study Area (BSA) for the proposed project includes a 5.6-mile-long<br />

section of Rosedale Highway plus a 500-foot buffer area north and south of the<br />

roadway’s centerline.<br />

A list of special-status plant and animal species that have the potential to occur within<br />

a ten-mile query radius of the BSA was established by conducting a literature review<br />

of the United <strong>State</strong>s Fish and Wildlife Service (USFWS) online special-status species<br />

list, the California Department of Fish and Game (CDFG) California Natural Diversity<br />

Database (CNDDB) and the California Native Plant Society (CNPS) species list.<br />

Fourteen federally listed species have been evaluated for their potential to occur in the<br />

BSA. Of these species, the federally listed endangered San Joaquin kit fox (Vulpes<br />

macrotis mutica) has potential to occur in the BSA. The remaining thirteen species are<br />

not expected to occur in the BSA due to the lack of suitable habitat, because they were<br />

not observed during surveys, or because they are not known to occur in the immediate<br />

project vicinity.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment S-1


Summary of Findings, Conclusions and Determinations<br />

Vegetation mapping was conducted on March 21, 2007 by walking the BSA.<br />

Vegetation in the BSA consists of non-native grassland, developed/ornamental,<br />

ruderal/disturbed and open water/waterway.<br />

A survey for wildlife species was conducted on March 21, 2007 to document wildlife<br />

habitat and evaluate the BSA’s potential to support special-status wildlife species that<br />

are known or expected to occur in the BSA.<br />

Surveys for the kit fox, its dens and sign were conducted in May, June and July of<br />

2008. One individual kit fox, four potential kit fox dens and four kit fox signs (scat)<br />

were observed in the BSA.<br />

The proposed project would result in direct and indirect effects to the federally listed<br />

endangered San Joaquin kit fox:<br />

• Direct effects include the permanent loss of 1.21 acres of habitat for the San<br />

Joaquin kit fox (0.18 acre non-native grassland, 1.00 acre ruderal/disturbed, and<br />

0.03 acre open water/waterway) in the BSA that are considered suitable foraging<br />

and denning habitat for the kit fox. Permanent effects to habitat include the removal<br />

of habitat to accommodate the new roadbed, intersection improvements, and<br />

proposed new right-of-way (ROW) limits.<br />

• Temporary effects to habitat include temporary disturbance such as equipment and<br />

materials staging. The proposed project would temporarily affect 6.61 acres of<br />

habitat areas (3.25 acres of non-native grassland, 3.30 acres of ruderal/disturbed<br />

areas, and 0.06 acre of open water/waterway).<br />

• Direct effects would also include the permanent or temporary loss of one potential<br />

kit fox den within the alignment.<br />

• Indirect effects of project implementation may include the potential for an<br />

unintentional increase in vehicular strikes of kit foxes crossing the road. Other<br />

indirect effects could include habitat fragmentation, change in movement corridors,<br />

geographic isolation, and/or altered space use, all of which could result in disrupted<br />

social ecology, reduced fertility, pregnancy rates, prenatal survival, mortality, and<br />

reduced carrying capacity in the vicinity of the BSA.<br />

There is no critical habitat for San Joaquin kit fox within the BSA; therefore no critical<br />

habitat would be affected by the proposed project.<br />

S-2 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Summary of Findings, Conclusions and Determinations<br />

The following Avoidance and Minimization, and Mitigation Measures shall be<br />

implemented prior to project construction to reduce impacts to biological resources:<br />

• Construction activities will adhere to the standard construction and operational<br />

requirements as described in the USFWS Standardized Recommendations for<br />

Protection of the Endangered San Joaquin Kit Fox Prior to or During Ground<br />

Disturbance (USFWS 2011).<br />

• Pre-construction surveys for kit fox will be conducted prior to construction within<br />

the project footprint and temporary construction zone and a 200-foot buffer around<br />

these areas in accordance with USFWS guidelines (2011).<br />

• An employee education program shall be established and implemented prior to<br />

construction. The program shall include, at a minimum, kit fox identification, a<br />

description of suitable habitat for kit fox, and measures to implement in the event<br />

that kit fox is found during construction. The program shall be presented to all<br />

members of the construction crew prior to the start of project construction<br />

activities. All construction personnel are required to sign a form stating they took<br />

the class and understood the materials presented in the class.<br />

• Biological monitors shall regularly inspect the construction site to ensure the<br />

minimization measures are implemented throughout construction.<br />

• Road design modifications that would facilitate safe passage of kit fox and reduce<br />

vehicular-mortalities are proposed and will be evaluated for feasibility during final<br />

project design.<br />

• Compensatory mitigation for effects to non-native grassland, ruderal/disturbed,<br />

and open water/waterway will consist of the purchase of credits through the<br />

Metropolitan <strong>Bakersfield</strong> Habitat Conservation Plan (MBHCP).<br />

• Implementation of the Sump Habitat Program (currently under development),<br />

which includes installation of artificial dens in selected sumps, controlling<br />

vegetation in and around dens, increasing accessibility to sumps through<br />

fence/gate gaps, maintenance procedures to reduce the potential for effects to kit<br />

foxes, and post-construction monitoring of kit fox use of the sumps. The Wildlife<br />

Heritage Foundation, a non-profit land trust, will hold the endowments necessary<br />

to fully fund the Sump Habitat Program and will oversee the conservation<br />

easements.<br />

The project ‘may affect, likely to adversely affect’ the San Joaquin kit fox due to the<br />

direct and indirect impacts on this species resulting from project implementation.<br />

However, with the measures described above from the San Joaquin Kit Fox Effects<br />

Analysis, Mitigation Strategy, and Implementation Plan (Implementation Plan)<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment S-3


Summary of Findings, Conclusions and Determinations<br />

(<strong>Bakersfield</strong> and Caltrans 2010), effects would be avoided and minimized to the extent<br />

practicable.<br />

S-4 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Table of Contents<br />

Table of Contents<br />

Chapter 1. Introduction ................................................................................................ 1<br />

1.1. <strong>Project</strong> History ........................................................................................... 1<br />

1.1.1. Purpose and Need ...................................................................................... 1<br />

1.1.1.1. <strong>Project</strong> Purpose .......................................................................................... 1<br />

1.1.1.2. <strong>Project</strong> Need .............................................................................................. 1<br />

1.2. <strong>Project</strong> Description .................................................................................... 1<br />

1.2.1. <strong>Project</strong> Phasing .......................................................................................... 7<br />

1.2.2. Avoidance and Minimization Measures .................................................... 7<br />

1.3. Summary of Consultation to Date ............................................................. 8<br />

1.4. Document Preparation History ................................................................ 10<br />

Chapter 2. Study Methods .......................................................................................... 11<br />

2.1. Listed and Proposed Species Potentially in the Biological Study Area .. 11<br />

2.2. Studies Required ...................................................................................... 13<br />

2.2.1. Literature Review .................................................................................... 13<br />

2.2.2. Vegetation Mapping ................................................................................ 13<br />

2.2.3. General Wildlife Surveys ........................................................................ 14<br />

2.2.4. Focused Surveys ...................................................................................... 14<br />

2.2.4.1. San Joaquin Kit Fox ................................................................................ 14<br />

2.3. Personnel and Survey Dates .................................................................... 15<br />

2.4. Agency Coordination and Professional Contacts .................................... 16<br />

2.5. Limitations That May Influence Results ................................................. 19<br />

Chapter 3. Results: Environmental Setting ................................................................ 21<br />

3.1. Description of Existing Biological and Physical Conditions ................... 21<br />

3.1.1. Study Area ............................................................................................... 21<br />

3.1.2. Physical Conditions ................................................................................. 21<br />

3.1.3. Biological Conditions in the BSA ........................................................... 25<br />

3.1.3.1. Vegetation Types ..................................................................................... 25<br />

3.1.3.2. Common Animal Species ........................................................................ 26<br />

Chapter 4. Results: Biological Resources, Discussion of Impacts and Mitigation .... 29<br />

4.1. Federally Listed or Proposed Animal Species Occurrences .................... 29<br />

4.1.1. Discussion of San Joaquin Kit Fox (Vulpes macrotis mutica) ................ 29<br />

4.1.1.1. Survey Results ......................................................................................... 31<br />

4.1.1.2. Critical Habitat ........................................................................................ 32<br />

4.1.1.3. Avoidance and Minimization Efforts ...................................................... 32<br />

4.1.1.4. <strong>Project</strong> Impacts ........................................................................................ 33<br />

4.1.1.5. Modifications to the <strong>Project</strong> to Mitigate Effects ...................................... 37<br />

4.1.1.6. Cumulative Effects (FESA)..................................................................... 42<br />

Chapter 5. Conclusions and Determination ............................................................... 45<br />

5.1. Conclusions ............................................................................................. 45<br />

5.2. Determination .......................................................................................... 45<br />

Chapter 6. References ................................................................................................ 47<br />

Appendix A Wildlife Species Observed in the BSA .................................................... 51<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment<br />

i


List of Figures<br />

List of Figures<br />

1 Regional Vicinity ................................................................................................ 5<br />

2A–C <strong>Project</strong> Effects ..................................................................................................... 6<br />

3A–C Biological Study Area ....................................................................................... 23<br />

4 Local Vicinity ................................................................................................... 24<br />

ii<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


List of Tables<br />

List of Tables<br />

1 Listed, Proposed Species, and Critical Habiat Potentially Occuring or<br />

Known to Occur in the <strong>Project</strong> Area ................................................................. 11<br />

2 Vegetation Types and Other Areas Within the BSA ........................................ 25<br />

3 Habitat for San Joaquin Kit Fox That Would be Affected by Each<br />

Phase of Alternative A ...................................................................................... 35<br />

4 Ratios Required to Mitigate for Effects on San Joaquin Kit Fox Habitat ......... 41<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment<br />

iii


List of Abbreviated Terms<br />

List of Abbreviated Terms<br />

A<br />

BA<br />

BO<br />

BMP<br />

BSA<br />

Caltrans<br />

CDFG<br />

CESA<br />

CNDDB<br />

CNPS<br />

ESA<br />

ESRP<br />

FE<br />

FED<br />

FESA<br />

FHWA<br />

FP<br />

FT<br />

GPS<br />

Implementation Plan<br />

MBGP<br />

MBHCP<br />

NFWF<br />

P<br />

PM<br />

ROW<br />

RWQCB<br />

SAFETAE-LU<br />

SE<br />

SJVR<br />

SR<br />

Absent<br />

Biological Assessment<br />

Biological Opinion<br />

Best Management Practices<br />

Biological Study Area<br />

California Department of Transportation<br />

California Department of Fish and Game<br />

California Endangered Species Act<br />

California Natural Diversity Database<br />

California Native Plant Society<br />

Endangered Species Act<br />

Endangered Species Recovery Program<br />

Federally listed endangered<br />

Final Environmental Document<br />

Federal Endangered Species Act<br />

Federal Highway Administration<br />

Fully Protected<br />

Federally listed threatened<br />

Geographic Positioning System<br />

San Joaquin Kit Fox Effects Analysis, Mitigation Strategy,<br />

and Implementation Plan<br />

Metropolitan <strong>Bakersfield</strong> General Plan<br />

Metropolitan <strong>Bakersfield</strong> Habitat Conservation Plan<br />

National Fish and Wildlife Foundation<br />

Present<br />

post mile<br />

right-of-way<br />

Regional Water Quality Control Board<br />

Safe, Accountable, Flexible, Efficient, Transportation<br />

Equity Act: A Legacy for Users<br />

<strong>State</strong>-listed endangered<br />

San Joaquin Valley Railroad<br />

<strong>State</strong> <strong>Route</strong><br />

iv<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


List of Abbreviated Terms<br />

SSC<br />

ST<br />

TRIP<br />

USACE<br />

USC<br />

USFWS<br />

USGS<br />

California Species of Special Concern<br />

<strong>State</strong>-listed threatened<br />

Thomas Roads Improvement Program<br />

U.S. Army Corps of Engineers<br />

U.S. Code<br />

U.S. Fish and Wildlife Service<br />

U.S. Geological Survey<br />

Rosedale Highway <strong>Widening</strong> Biological Assessment<br />

v


List of Abbreviated Terms<br />

This page intentionally left blank<br />

vi<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 1.<br />

Introduction<br />

The purpose of this Biological Assessment (BA) is to provide technical information<br />

and to review the proposed project in sufficient detail to determine to what extent the<br />

proposed project may affect threatened, endangered, or proposed species. This BA is<br />

prepared in accordance with (1) legal requirements found in Section 7(a)(2) of the<br />

federal Endangered Species Act (FESA) (16 United <strong>State</strong>s Code [USC] 1536[c]) and<br />

(2) Federal Highway Administration (FHWA) and Caltrans regulations, policies, and<br />

guidance. The document presents technical information upon which later decisions<br />

regarding project effects are developed.<br />

1.1. <strong>Project</strong> History<br />

1.1.1. Purpose and Need<br />

1.1.1.1. <strong>Project</strong> Purpose<br />

The purpose of the proposed project is:<br />

• To reduce existing and future traffic congestion on <strong>State</strong> <strong>Route</strong> <strong>58</strong> between Allen<br />

Road and <strong>State</strong> <strong>Route</strong> 99 to improve local and regional east-west traffic flow.<br />

1.1.1.2. <strong>Project</strong> Need<br />

The proposed project is needed to serve existing and projected travel demand along<br />

the SR-<strong>58</strong> corridor. The project extends through the urban core area of metropolitan<br />

<strong>Bakersfield</strong>, where SR-<strong>58</strong> is used to access jobs and commercial uses within the City.<br />

The City of <strong>Bakersfield</strong> General Plan and the Kern County General Plan both assume<br />

SR-<strong>58</strong> as a six lane highway through the project study area. This portion of SR-<strong>58</strong> has<br />

traffic congestion, especially during the busiest times of the day. The project has also<br />

been identified in the Safe, Accountable, Flexible, Efficient, Transportation Equity<br />

Act: A Legacy for Users (SAFETEA-LU) legislation as part of the National Corridor<br />

Infrastructure Improvement Program (Section 1302 of the SAFETEA-LU).<br />

1.2. <strong>Project</strong> Description<br />

Caltrans, in cooperation with the City of <strong>Bakersfield</strong> and the County of Kern, proposes<br />

to improve an approximate 5.6-mile segment of SR-<strong>58</strong>, locally known as Rosedale<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 1


Chapter 1 Introduction<br />

Highway. The project area is located within unincorporated Kern County and the City<br />

of <strong>Bakersfield</strong> (Figure 1); the limits extend from west of Allen Road to SR 99(Figures<br />

2A–2C). One Build Alternative and the No Build Alternative have been evaluated.<br />

The City of <strong>Bakersfield</strong> is the lead agency pursuant to the California Environmental<br />

Quality Act and Caltrans is the lead agency for the National Environmental Policy<br />

Act.<br />

The proposed project is part of the TRIP, which includes 10 projects: six road<br />

improvement projects in the planning and environmental review phases, three road<br />

projects currently under construction (Westside Parkway, SR-178 at Fairfax<br />

Interchange and 7 th Standard Road) and one route adoption (West Beltway).<br />

Build Alternative<br />

The Build Alternative would construct two new lanes between Allen Road and SR 99.<br />

East of Gibson Street, the project would modify land striping and the median to<br />

transition to the existing lane configuration. This would result in a six lane roadway<br />

throughout the project limits (post miles 46.1 to 51.7). Cross streets may also be<br />

restriped at their intersections with SR- <strong>58</strong> to improve the traffic operations.<br />

Ultimate improvements would include a grade separated rail crossing that would be<br />

constructed between Mohawk Street and Landco Drive. As part of the first phase of<br />

improvements, the road would be widened to six lanes, the railroad gates would be<br />

installed, and 11-foot turnouts would be provided to allow trucks and busses to move<br />

outside traffic lanes. As part of the final phase of the project, a grade separated rail<br />

crossing (where the road would go over the railroad tracks) would be provided.<br />

The roadway would be designed to local (City and County) standards for the portion<br />

of the project between Allen Road and Mohawk Street. This is the portion of the<br />

project where Caltrans will relinquish the ROW to the local agencies. The standard<br />

cross-section for this portion of the roadway would be 110 feet. Between Mohawk<br />

Street and SR 99, the roadway would be designed to <strong>State</strong> standards. Property would<br />

need to be acquired for this alternative.<br />

Along with the roadway widening, there would also be the following changes along<br />

the roadway:<br />

• Traffic signals and signage would need to be relocated because the roadway would<br />

be wider.<br />

2 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 1 Introduction<br />

• Minor changes, such as restriping approach lanes to provide an additional turn lane<br />

on the side-street approaches to SR- <strong>58</strong>, would be constructed at the cross streets<br />

because SR- <strong>58</strong> would be wider.<br />

• Utilities and drainage facilities would be relocated because of the wider roadway,<br />

including above-ground utilities such as power poles, and storm drain inlets.<br />

• Existing landscaping1 and irrigation would be replaced in the median along the<br />

proposed project alignment if it is damaged by construction.<br />

The depth of construction for the SR-<strong>58</strong> widening is expected to be five feet or less in<br />

all locations except where new bridge columns are required (at the west crossing of<br />

the Calloway Canal and at the proposed overcrossing). In these locations, the<br />

maximum depth of ground disturbance is expected to be about 45 feet from pile<br />

driving (no major excavation).<br />

San Joaquin Valley Railroad Grade Separation<br />

The project proposes a grade separation over the San Joaquin Valley Railroad (rail line<br />

between Mohawk Street and Landco Drive). The proposed grade separation would be<br />

built on the current alignment for SR- <strong>58</strong>. A temporary route on the north side of the<br />

roadway would be provided during construction to maintain roadway function. In this<br />

location, additional ROW would be required. Borrow material would be required for<br />

the grade separation and would be environmentally cleared by the contractor.<br />

No Build Alternative<br />

The No Build Alternative would not provide any improvements to SR-<strong>58</strong>. Without the<br />

proposed widening, the No Build Alternative does not address congestion and traffic<br />

delays that could be expected as traffic volumes increase. Improvements that are<br />

planned for other roadways as part of separate projects would still be built.<br />

Figures 2A–2C show the footprint for the proposed project. All borrow, disposal,<br />

staging, access, and utility relocations would be within the footprint identified in these<br />

figures, or within nearby developed areas. Figures 2A–2C also show potential kit fox<br />

dens and other observations near the project area. Dust-, erosion-, and<br />

sediment-control measures will be developed at a later project design phase, but will<br />

follow standard Best Management Practices (BMPs). Specific construction equipment<br />

will also be determined at a later project design phase, but will follow standard<br />

construction techniques.<br />

1<br />

Due to concerns regarding San Joaquin kit fox crossing the road, any landscaping planted will be<br />

low-level (i.e., less than six inches) that does not require mowing.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 3


Chapter 1 Introduction<br />

There are no interdependent or interrelated projects.<br />

4 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


46<br />

Lost Hills<br />

33<br />

Delano<br />

McFarland<br />

43<br />

Wasco<br />

99<br />

Buttonwillow<br />

Rosedale<br />

<strong>58</strong><br />

155<br />

<strong>Project</strong> Location<br />

Kern River<br />

Kernville<br />

Lake<br />

Isabella<br />

Onyx<br />

Ridgecrest<br />

395<br />

Califor nia Aqueduct<br />

Tupman<br />

5<br />

BAKERSFIELD<br />

Arvin<br />

<strong>58</strong><br />

Keene<br />

14<br />

California City<br />

Taft<br />

Maricopa<br />

99<br />

Lebec<br />

Tehachapi<br />

Los An gel es A queduct<br />

Rosamond<br />

Mojave<br />

Edwards AFB<br />

Boron<br />

Kern<br />

N<br />

D:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\ex_RV_BA_v002.ai<br />

(092211 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\IS-EA\Fig1_RV.pdf<br />

Regional Vicinity<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 060F360<br />

Figure 1


Map Extent<br />

A<br />

B<br />

C<br />

ALLEN RD<br />

OLD FARM RD<br />

JEWETTA AV<br />

VERDUGO LN<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

W JEWETTA AV<br />

Biological Study Area<br />

<strong>Project</strong> Impacts<br />

Grade Separation<br />

Species Location<br />

Kit Fox Observation<br />

Active Kit Fox Den<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Impacts.mxd<br />

Temporary Impacts<br />

Potential Kit Fox Den<br />

Vegetation Types and other Areas Kit Fox Sign<br />

Non-native Grassland<br />

Developed/Ornamental<br />

Ruderal/Disturbed<br />

Open Water/Waterway<br />

(Rev 09-22-11 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig2_<strong>Project</strong>_Effects.pdf<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

<strong>Project</strong> Effects<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 2A


Map Extent<br />

A<br />

B<br />

C<br />

VERDUGO LN<br />

CALLOWAY DR<br />

MAIN PLAZA DR<br />

COFFEE RD<br />

Friant-Kern Canal<br />

Calloway Canal<br />

HENRY LN<br />

PATTON WY<br />

WEAR ST<br />

FRUITVALE AV<br />

Calloway Canal<br />

Emery Ditch<br />

Emery Ditch<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

WEDDING LN<br />

Calloway Canal<br />

Biological Study Area<br />

<strong>Project</strong> Impacts<br />

Grade Separation<br />

Species Location<br />

Kit Fox Observation<br />

Active Kit Fox Den<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Impacts.mxd<br />

Temporary Impacts<br />

Potential Kit Fox Den<br />

Vegetation Types and other Areas Kit Fox Sign<br />

Non-native Grassland<br />

Developed/Ornamental<br />

Ruderal/Disturbed<br />

Open Water/Waterway<br />

(Rev 09-22-11 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig2_<strong>Project</strong>_Effects.pdf<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

<strong>Project</strong> Effects<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 2B


Map Extent<br />

A<br />

B<br />

C<br />

FRUITVALE AV<br />

Emery Ditch<br />

WEAR ST<br />

Calloway Canal<br />

Emery Ditch<br />

MOHAWK ST<br />

LANDCO DR<br />

CASE ST<br />

GIBSON ST<br />

99<br />

Calloway Canal<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

PARKER LN<br />

Kern River<br />

Biological Study Area<br />

<strong>Project</strong> Impacts<br />

Grade Separation<br />

Species Location<br />

Kit Fox Observation<br />

Active Kit Fox Den<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Impacts.mxd<br />

Temporary Impacts<br />

Potential Kit Fox Den<br />

Vegetation Types and other Areas Kit Fox Sign<br />

Non-native Grassland<br />

Developed/Ornamental<br />

Ruderal/Disturbed<br />

Open Water/Waterway<br />

(Rev 09-22-11 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig2_<strong>Project</strong>_Effects.pdf<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

<strong>Project</strong> Effects<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 2C


Chapter 1 Introduction<br />

1.2.1. <strong>Project</strong> Phasing<br />

Construction is expected to be done in three phases. The first phase would be from<br />

Calloway Drive to SR 99. The second phase would be from Allen Road to Calloway<br />

Drive. Construction on the first two segments is expected to start in early 2014 and be<br />

completed in mid-2015. The grade separation at the San Joaquin Valley Railroad<br />

would be constructed as a final phase, with construction projected to start in 2025 and<br />

end in 2027. Construction for all phases is expected to be completed within this<br />

project’s 20-year horizon.<br />

The roadway would be open through all phases of construction. No detours are<br />

expected to be necessary. During construction of the grade-separation, a temporary<br />

route on the north side of the roadway would be provided during construction to allow<br />

traffic to continue to use SR-<strong>58</strong>. The temporary route would be located next to the<br />

roadway and would use property that would be bought as part of the project.<br />

Relocation/reconstruction of utilities and drainage facilities within the proposed ROW<br />

would include power poles, underground utilities, and storm drains. Utility relocations<br />

are expected to be accomplished without interrupting service. Drainage improvements<br />

would include installation of operational BMPs.<br />

1.2.2. Avoidance and Minimization Measures<br />

Standard Avoidance and Minimization Measures for the San Joaquin kit fox (such as<br />

pre-construction surveys, worker environmental awareness training, and construction<br />

monitoring) will be implemented. In addition to the standard Avoidance and<br />

Minimization Measures, the project proposes to incorporate structural design elements<br />

that are intended to facilitate safe kit fox crossing and to reduce the potential for<br />

unintentional vehicular strike. The structural design elements would include limited<br />

median height, low-level landscaping, avoidance of current movement corridors (i.e.,<br />

canals and railways), and warning signs. The proposed project would also avoid the<br />

use of fencing. These design elements will be addressed in more detail in<br />

Section 4.1.1.5. The specifics of these structural elements will be finalized during the<br />

project’s final design phase by the City of <strong>Bakersfield</strong> and Caltrans and submitted for<br />

review and approval by the USFWS.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 7


Chapter 1 Introduction<br />

1.3. Summary of Consultation to Date<br />

During preparation of the Implementation Plan (<strong>Bakersfield</strong> and Caltrans 2010),<br />

Stephanie Coppeto, Leo Edson, and the City of <strong>Bakersfield</strong> consulted with the<br />

USFWS and the CDFG; Caltrans; Dr. Brian Cypher with the California <strong>State</strong><br />

University, Stanislaus Endangered Species Recovery Program (ESRP); and other<br />

environmental consultants with knowledge of the status and distribution of the San<br />

Joaquin kit fox in <strong>Bakersfield</strong>.<br />

Stephanie Coppeto, Leo Edson, and the City of <strong>Bakersfield</strong> coordinated with the<br />

USFWS, CDFG, and Caltrans on the approach for San Joaquin kit fox field surveys,<br />

potential project-specific and program-level effects of the TRIP, and mitigation<br />

options for project-specific and program-level effects.<br />

Stephanie Coppeto and Leo Edson worked closely with Dr. Brian Cypher, kit fox<br />

specialist with ESRP, to gather supplemental information about kit fox distribution,<br />

abundance, and ecology in metropolitan <strong>Bakersfield</strong>, including: known kit fox<br />

locations, reported observations, habitat associations of kit fox in <strong>Bakersfield</strong>, suitable<br />

kit fox habitat areas, and potential movement corridors. Dr. Cypher provided guidance<br />

throughout the development of field surveys, synthesis and interpretation of kit fox<br />

data for project-specific surveys, appropriate project-specific and program-level<br />

mitigation measures, and preparation of kit fox technical reports.<br />

Stephanie Coppeto and Leo Edson also sought input from various environmental<br />

consultants in <strong>Bakersfield</strong> with knowledge of the local San Joaquin kit fox population.<br />

Marcia Wolfe of MH Wolfe and Associates provided a general assessment of the kit fox<br />

distribution in central and north-eastern <strong>Bakersfield</strong>. Steven Pruett of Paul Pruett and<br />

Associates conducted field surveys with Stephanie Coppeto and provided information on<br />

suitability of project-specific habitat, kit fox den evaluation, and historical accounts of kit<br />

fox movement in project-specific study areas and throughout metropolitan <strong>Bakersfield</strong>.<br />

In 2007, the City and Caltrans authorized Stephanie Coppeto and Leo Edson to<br />

develop a conceptual strategy for San Joaquin kit fox to determine the potential effects<br />

of implementing the TRIP projects on kit fox and to evaluate mitigation options for<br />

such effects. USFWS and CDFG concur that a conceptual strategy was needed.<br />

USFWS requested cumulative and project-specific analyses of potential effects on kit<br />

fox to comply with Section 7 consultation for each TRIP project evaluated.<br />

8 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 1 Introduction<br />

In 2008, USFWS and CDFG concurred on methods proposed by Stephanie Coppeto<br />

and Leo Edson to develop the kit fox conceptual strategy: diurnal surveys for kit fox<br />

dens and signs, collaboration with Dr. Brian Cypher, and a project specific and<br />

cumulative approach to evaluating potential impacts on kit fox and efforts to avoid,<br />

minimize, and compensate for potential effects. USFWS, CDFG, Caltrans, Stephanie<br />

Coppeto and Leo Edson, and the City agreed to meet throughout the development of<br />

the conceptual strategy to ensure that it complies with the FESA and California<br />

Endangered Species Act (CESA). In July, 2008, CDFG, Caltrans, Stephanie Coppeto<br />

and Leo Edson, the City, Steven Pruett, and Dr. Brian Cypher toured various TRIP<br />

projects in <strong>Bakersfield</strong>. In August, 2008, Stephanie Coppeto and Leo Edson presented<br />

preliminary results of kit fox surveys. USFWS identified habitat connectivity and the<br />

maintenance of corridors connecting kit fox populations as a major issue facing kit fox<br />

in <strong>Bakersfield</strong>. Potential compensatory mitigation options were discussed, including<br />

culverts, refugia, and artificial kit fox dens.<br />

In 2009, USFWS and CDFG approved the San Joaquin Kit Fox Life History, Effects<br />

Analysis, and Conceptual Mitigation Strategy (City of <strong>Bakersfield</strong> and Caltrans 2009)<br />

that describes program-level impacts and conceptual program-level mitigation.<br />

USFWS and CDFG concurred that Caltrans should begin to develop a mitigation<br />

implementation plan of the conceptual approach.<br />

In 2010, USFWS and CDFG approved the Implementation Plan (City of <strong>Bakersfield</strong><br />

and Caltrans 2010). CDFG recommended that Caltrans seek a 2080.1 Consistency<br />

Determination for projects requiring a state Incidental Take Permit. USFWS and<br />

CDFG approved the standard Avoidance and Minimization Measures that would be<br />

described for the San Joaquin kit fox in BAs. USFWS and CDFG agreed that the letter<br />

from the MBHCP Trust Group to the City (dated August 3, 2010) approving eligible<br />

TRIP projects to participate in the fee payment program was valid for projects that are<br />

ready to build prior to MBHCP expiration in 2014 but asked that the City clarify that<br />

fees can be paid at higher than 1:1 ratios as required by USFWS. USFWS and CDFG<br />

approved the concept of the Sump Habitat Program to compensate for program-level<br />

effects.<br />

In 2011, based on agency consultation and the release of the Draft Biological Opinion<br />

for the Morning Drive/<strong>State</strong> <strong>Route</strong> 178 Interchange <strong>Project</strong>, a 3:1 mitigation ratio is<br />

identified for all permanent impacts and a 1.1:1 ratio is identified for all temporary<br />

impacts. Caltrans is no longer seeking an Incidental Take Permit or a Consistency<br />

Determination under CESA as it is now assumed that take of San Joaquin kit fox, as<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 9


Chapter 1 Introduction<br />

defined under CESA, can be avoided. Caltrans and the City have identified the<br />

Wildlife Heritage Foundation (WHF), a non-profit land trust, to hold endowments<br />

necessary to fully fund the Sump Habitat Program and conservation easement<br />

oversight. The USFWS also released an updated Recommendations for Protection of<br />

the Endangered San Joaquin Kit Fox Prior to or During Ground Disturbance<br />

(USFWS 2011).<br />

1.4. Document Preparation History<br />

This document was prepared based on the Implementation Plan (<strong>Bakersfield</strong> and<br />

Caltrans 2010). Information on the BSA was obtained from the <strong>State</strong> <strong>Route</strong> <strong>58</strong><br />

<strong>Widening</strong> <strong>Project</strong> (Rosedale Highway) Final Natural Environment Study (NES)<br />

(Caltrans 2011).<br />

10 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 2.<br />

Study Methods<br />

2.1. Listed and Proposed Species Potentially in the<br />

Biological Study Area<br />

Fourteen federally listed species are included on the species list provided by the<br />

USFWS for the proposed project (Table 1). Of these species, the San Joaquin kit fox<br />

has potential to occur in the BSA. The remaining species are not expected to occur in<br />

the BSA due to the lack of suitable habitat, because they were not observed during<br />

surveys, or because they are not known to occur in the immediate project vicinity.<br />

Table 1<br />

Listed, Proposed Species, and Critical Habiat Potentially Occuring or<br />

Known to Occur in the <strong>Project</strong> Area<br />

Common<br />

Name<br />

California<br />

jewelflower<br />

Kern mallow<br />

San Joaquin<br />

woolly-threads<br />

<strong>Bakersfield</strong><br />

cactus<br />

vernal pool<br />

fairy shrimp<br />

valley<br />

elderberry<br />

longhorn<br />

beetle<br />

delta smelt<br />

Scientific Name<br />

Caulanthus<br />

californicus<br />

Eremalche parryi<br />

ssp. kernensis [E.<br />

kernensis]<br />

Monolopia<br />

[Lembertia]<br />

congdonii<br />

Opuntiabasilaris<br />

var. treleasei<br />

Branchinecta<br />

lynchi<br />

Desmocerus<br />

californicus<br />

dimorphus<br />

Hypomesus<br />

transpacificus<br />

Status<br />

FE, SE<br />

FE<br />

FE<br />

FE, SE<br />

FT<br />

FT<br />

FT,<br />

ST<br />

General Habitat<br />

Description<br />

Saltbush scrub;<br />

pinyon and juniper<br />

woodland; valley and<br />

foothill grassland<br />

(sandy).<br />

Saltbush scrub; valley<br />

and foothill grassland.<br />

Saltbush scrub; valley<br />

and foothill grassland<br />

(sandy).<br />

Saltbush scrub;<br />

cismontane woodland;<br />

valley and foothill<br />

grassland (sandy or<br />

gravelly).<br />

Ephemeral freshwater<br />

habitats, such as<br />

vernal pools and<br />

swales.<br />

Associated with blue<br />

elderberry.<br />

Sacramento-San<br />

Joaquin Delta.<br />

Habitat<br />

Present/<br />

Absent<br />

A<br />

A<br />

A<br />

A<br />

A<br />

A<br />

A<br />

Rationale<br />

Not observed during<br />

focused plant<br />

surveys.<br />

Not observed during<br />

focused plant<br />

surveys.<br />

Not observed during<br />

focused plant<br />

surveys.<br />

Not observed during<br />

focused plant<br />

surveys.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

Outside known<br />

range; not expected<br />

to occur.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 11


Chapter 2 Study Methods<br />

Table 1 (Continued)<br />

Listed, Proposed Species, and Critical Habiat Potentially Occuring or<br />

Known to Occur in the <strong>Project</strong> Area<br />

Common<br />

Name<br />

California redlegged<br />

frog<br />

blunt-nosed<br />

leopard lizard<br />

giant garter<br />

snake<br />

giant kangaroo<br />

rat<br />

Tipton<br />

kangaroo rat<br />

Buena Vista<br />

Lake shrew<br />

San Joaquin<br />

kit fox<br />

Scientific Name<br />

Rana [aurora]<br />

draytonii<br />

Gambelia sila<br />

Thamnophis gigas<br />

Dipodomys ingens<br />

Dipodomys<br />

nitratoides<br />

nitratoides<br />

Sorex ornatus<br />

relictus<br />

STATUS DESIGNATIONS<br />

A Absent<br />

P Present<br />

Vulpes macrotis<br />

mutica<br />

Status<br />

FT, SSC<br />

FE,<br />

SE/FP<br />

FT,<br />

ST<br />

FE,<br />

SE<br />

FE,<br />

SE<br />

FE, SSC<br />

FE,<br />

ST<br />

General Habitat<br />

Description<br />

Variety of aquatic<br />

habitats in forests,<br />

woodlands,<br />

grasslands, and<br />

streamsides with<br />

deep, still, or slowmoving<br />

water.<br />

Semiarid grasslands,<br />

alkali flats, and<br />

washes.<br />

Perennial fresh water<br />

with emergent wetland<br />

vegetation and<br />

basking sites.<br />

Slopes in grasslands<br />

and shrub<br />

communities.<br />

Alkali sink scrub and<br />

valley saltbush scrub<br />

with widely scattered<br />

shrubs.<br />

Wetlands with dense<br />

vegetation and an<br />

abundant layer of<br />

detritus.<br />

Valley sink scrub,<br />

saltbush scrub, upper<br />

Sonoran scrub,<br />

annual grasslands, oil<br />

fields, urban areas.<br />

Habitat<br />

Present/<br />

Absent<br />

A<br />

A<br />

A<br />

A<br />

A<br />

A<br />

P<br />

Rationale<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

Outside current<br />

known range; not<br />

expected to occur.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

No suitable habitat;<br />

not expected to<br />

occur.<br />

Observed during<br />

2008 focused<br />

surveys.<br />

Federal Designations<br />

FE Listed by the federal government as an endangered species<br />

FT Listed by the federal government as a threatened species<br />

<strong>State</strong> Designations<br />

SE Listed as endangered by the <strong>State</strong> of California<br />

ST Listed as threatened by the <strong>State</strong> of California<br />

SSC Species of Special Concern<br />

FP Fully Protected<br />

12 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 2 Study Methods<br />

2.2. Studies Required<br />

2.2.1. Literature Review<br />

The BSA includes the current SR-<strong>58</strong> ROW and areas located 500 feet north and south<br />

of its centerline.<br />

Prior to conducting field surveys, a list of special-status plant and animal species that<br />

have potential to occur within a ten-mile query radius of the BSA was established by<br />

conducting a literature review. Literature reviewed included the CNPS’ Inventory of<br />

Rare and Endangered Vascular Plants of California (CNPS 2008), the CDFG’s<br />

CNDDB (CDFG 2008), and the USFWS List of Proposed, Threatened, and<br />

Endangered Species (USFWS 2008) for the U.S. Geologic Survey (USGS) 7.5-minute<br />

quadrangles of Famoso, Lamont, North of Oildale, Oil Center, Oildale, Rosedale, Rio<br />

Bravo, Tupman, Stevens, Gosford, and Wasco. The database searches were updated<br />

(CNPS 2010, CDFG 2010) when the NES was updated in 2010. The USFWS list was<br />

updated in March 2011 (USFWS 2011). The Western Rosedale Specific Plan (Kern<br />

County 1994), the Metropolitan <strong>Bakersfield</strong> General Plan (MBGP) (<strong>Bakersfield</strong> and<br />

Kern County 2002), the MBHCP, support documents (Thomas Reid Associates 1994,<br />

1991, and 1990), and the USFWS’s Recovery Plan for Upland Species of the San<br />

Joaquin Valley, California (USFWS 1998) were also reviewed.<br />

Other documentation that included information on biological resources in the BSA and<br />

in the general project vicinity were reviewed including: the 7 th Standard Road<br />

<strong>Widening</strong> Environmental Assessment/Initial Study with Proposed Mitigated Negative<br />

Declaration (Caltrans 2006), the Tier 2 Environmental Assessment/Final<br />

Environmental Impact Report for Westside Parkway (<strong>Bakersfield</strong> et al. 2006), the<br />

Kern County Waste Facilities Habitat Conservation Plan (Kern County Waste<br />

Management Department 1997), and the Kern Water Bank Authority Habitat<br />

Conservation Plan (Kern Water Bank Authority 1997).<br />

2.2.2. Vegetation Mapping<br />

Vegetation mapping was conducted on March 21, 2007 by walking the BSA, to<br />

describe the vegetation present in the BSA. All plant species observed were recorded<br />

in field notes. A list of species observed is included in Appendix A.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 13


Chapter 2 Study Methods<br />

2.2.3. General Wildlife Surveys<br />

A general survey for wildlife species was conducted on March 21, 2007, to document<br />

wildlife habitat and evaluate the BSA’s potential to support special-status wildlife<br />

species that are known or expected to occur in the BSA. During the surveys, active<br />

searches for reptiles and amphibians were accomplished by systematically surveying<br />

appropriate habitat and included lifting, overturning, and carefully replacing rocks and<br />

debris. Birds were identified by visual and auditory recognition. Surveys for mammals<br />

were conducted during the day and included searching for and identifying diagnostic<br />

sign including scat, footprints, scratch-outs, dust bowls, burrows, and trails. Wildlife<br />

species that were observed were recorded in field notes. A list of species observed is<br />

located in Appendix A.<br />

2.2.4. Focused Surveys<br />

2.2.4.1. San Joaquin Kit Fox<br />

Existing data on the status and distribution of San Joaquin kit fox in the Metropolitan<br />

<strong>Bakersfield</strong> area were used to supplement field survey data and to evaluate the<br />

distribution of kit foxes in the TRIP kit fox study area. Existing kit fox data were<br />

compiled from CNDDB records; a report prepared by Bjurlin et al. (2005) on kit fox<br />

and urban roads; and the MBHCP’s San Joaquin kit fox database, which is maintained<br />

by the City of <strong>Bakersfield</strong> Planning Department. Data were compiled as described in<br />

Bjurlin et. al. (2005) to examine vehicular mortality locations from maps and activity<br />

areas from radio telemetry locations of collared foxes.<br />

Surveys for San Joaquin kit fox dens and sign were conducted in the BSA following a<br />

methodology established for the TRIP and approved by the USFWS and the CDFG as<br />

described in the Implementation Plan (Caltrans and City of <strong>Bakersfield</strong> 2010). The<br />

surveys for kit fox were conducted by wildlife biologists Stephanie Coppeto and Steve<br />

Pruett.<br />

The BSA was surveyed during two discrete survey sessions to maximize the potential<br />

for biologists to detect kit fox during both denning (session 1 – May 20, June 1 and<br />

17, July 7, 2008) and dispersal (session 2 – July 29 and 30, 2008) seasons. Surveys<br />

were conducted on all accessible parcels within the BSA where the property owner<br />

had granted access. In general, field surveys did not include residential property.<br />

14 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 2 Study Methods<br />

During surveys, biologists walked linear transects within the survey area; transects<br />

were separated by no more than 50 feet and included 100 percent visual coverage. At<br />

all times, biologists had maps that included locations of known kit fox dens, sightings,<br />

and activity areas as reported in the CNDDB, the MBHCP kit fox den database, and in<br />

Bjurlin et al.<br />

Kit fox data collected included potential dens, natal dens, sign, and kit fox<br />

observations. Kit fox dens were described as potential and natal according to<br />

descriptions provided in the USFWS Standardized Recommendations for Protection of<br />

the San Joaquin Kit Fox Prior to or During Ground Disturbance (USFWS 1999). All<br />

dens were further described in field notes by number of entrances, proximity to nearest<br />

road, potential for den to be located within the proposed new alignment, substrate, and<br />

surrounding habitat type. Kit fox data were recorded using a Global Positioning<br />

System (GPS) unit. Kit fox data categories are described below.<br />

Potential Den: A potential den is any subterranean hole that has entrances of<br />

appropriate dimensions for which available evidence is insufficient to conclude that it is<br />

being used or has been used by a kit fox (USFWS 1999). Dens were not described as<br />

having kit fox potential if there were signs of active use by squirrel (fresh scat, tracks)<br />

and/or if the biologist saw a squirrel using the den during the time of surveys. A<br />

potential den was further described as active if excavation appeared recent or recently<br />

maintained and/or included kit fox sign within approximately ten feet of the den.<br />

Natal Den: A natal den is any den used by kit foxes to whelp and/or rear their pups.<br />

Natal dens may be larger with more numerous entrances than dens occupied only by<br />

adults. These dens typically have more kit fox tracks, scat, and prey remains in the<br />

vicinity of the den, and may have a broader apron of matted dirt and/or vegetation at<br />

one or more entrances (USFWS 1999).<br />

Sign: Sign includes kit fox scat, track and prey remains.<br />

Observations: Observations are visual sightings of live or dead kit foxes within the<br />

BSA.<br />

2.3. Personnel and Survey Dates<br />

Botanist Pam De Vries conducted a general plant survey, a habitat assessment for<br />

special-status plant species, and vegetation mapping on March 21, 2007. Ecologist<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 15


Chapter 2 Study Methods<br />

Amber Oneal conducted a general wildlife survey and a habitat assessment for specialstatus<br />

wildlife species concurrently with vegetation mapping on March 21, 2007.<br />

Wildlife Biologists Stephanie Coppeto and Steve Pruett conducted kit fox den and<br />

sign surveys on May 20; June 1 and 17; and July 7, 29, and 30, 2008.<br />

2.4. Agency Coordination and Professional Contacts<br />

The following is a summary of consultation to date with USFWS and CDFG for the<br />

TRIP.<br />

November 20, 2007: The City and Caltrans agree to develop an<br />

Implementation Plan to determine the effects of the TRIP projects on the kit<br />

fox and to design avoidance, minimization, and mitigation measures for these<br />

effects. The USFWS and the CDFG concur that an Implementation Plan is<br />

needed. The USFWS requests cumulative and project specific analyses of<br />

potential effects on kit fox to comply with Section 7 consultation for each<br />

TRIP project evaluated.<br />

June 3, 2008: The USFWS and the CDFG concur on methods proposed to<br />

develop the Implementation Plan: diurnal surveys for kit fox dens and signs;<br />

collaboration with Dr. Brian Cypher; and a project-specific and cumulative<br />

approach to evaluating potential effects on kit fox and efforts to avoid,<br />

minimize, and mitigate for potential effects. The USFWS and the CDFG agree<br />

to meet throughout the development of the Implementation Plan to ensure that<br />

it complies with the FESA and the CESAand to participate in a visit to the<br />

various TRIP project sites in <strong>Bakersfield</strong>.<br />

July 8, 2008: The CDFG, Caltrans, Stephanie Coppeto, the City, Steve Pruett,<br />

and Dr. Brian Cypher tour various TRIP projects in <strong>Bakersfield</strong>.<br />

August 26, 2008: Stephanie Coppeto and Leo Edson present preliminary<br />

results of kit fox surveys. The USFWS identifies habitat connectivity and the<br />

maintenance of corridors connecting kit fox populations as a major issue facing<br />

kit fox in <strong>Bakersfield</strong>. Potential compensatory mitigation options are discussed,<br />

including culverts, refugia, and artificial kit fox dens.<br />

September 10, 2009: USFWS and CDFG approve the Draft TRIP San Joaquin<br />

Kit Fox Life History, Effects Analysis, and Conceptual Mitigation Strategy that<br />

16 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 2 Study Methods<br />

describes program-level impacts and conceptual program-level avoidance,<br />

minimization and mitigation measures. USFWS and CDFG concur that<br />

Caltrans will begin to develop a mitigation implementation plan of the<br />

conceptual approach.<br />

October 7, 2009: TRIP receives letter (81420-2008-TA-0368-29) from Peter<br />

Cross, Deputy Assistant Field Supervisor with USFWS, approving Draft TRIP<br />

San Joaquin Kit Fox Life History, Effects Analysis, and Conceptual Mitigation<br />

Strategy (<strong>Bakersfield</strong> and Caltrans 2009).<br />

March 11, 2010: USFWS and CDFG approve the Implementation Plan<br />

(<strong>Bakersfield</strong> and Caltrans 2010). CDFG recommends that Caltrans seek a<br />

2080.1 Consistency Determination for projects requiring a state Incidental<br />

Take Permit. USFWS and CDFG approve the Sump Habitat Program and<br />

request that the City, in coordination with Caltrans, establish long-term<br />

conservation assurances for the 19 sumps through conservation easements,<br />

endowment, and long-term management plan.<br />

May 5, 2010: Stephanie Coppeto and Leo Edson hold an informal<br />

teleconference with USFWS to discuss FESA compliance approach and<br />

schedule before the May 11, 2010 meeting in which Susan Jones and Jen<br />

Schofield will not attend. For compensatory mitigation, USFWS requests that<br />

the City submit a letter of commitment with each BA for the Sump Habitat<br />

Program.<br />

May 11, 2010: Caltrans will submit project BAs to USFWS and CDFG for<br />

concurrent review to expedite the CESA consultation process. The Sump<br />

Habitat Program would be discussed in the BAs but the requirements<br />

(easement application, management plan, and endowment) would not need to<br />

be met before construction of a road project. CDFG is willing to hold the<br />

conservation easement for the sumps, the City and Caltrans will identify an<br />

agency-approved endowment holder. The City and Caltrans consider<br />

identifying an alternative cumulative mitigation strategy in the event that the<br />

Sump Habitat Program is fiscally infeasible.<br />

July 14, 2010: Caltrans will submit the draft BA for SR-178/Morning Drive<br />

Interchange (another TRIP project) to CDFG for review and comment prior to<br />

submittal to USFWS to expedite the CESA process. USFWS and CDFG<br />

approve the standard Avoidance and Minimization Measures that would be<br />

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Chapter 2 Study Methods<br />

described for the San Joaquin kit fox in the BA. CDFG recommends that<br />

Caltrans and the City consider an alternative compensatory mitigation strategy<br />

to the MBHCP because of concerns about MBHCP expiration in 2014.<br />

USFWS and CDFG agreed that mitigation for cumulative effects (Sump<br />

Habitat Program) could be described generally in the BA to maintain flexibility<br />

while the program evolves, but that a chapter describing the cumulative<br />

mitigation framework that would later be finalized and included as chapter 3 in<br />

the Implementation Plan, be submitted as a separate, supporting document with<br />

the BA. CDFG requested that standard CESA requirements be included in the<br />

terms and conditions section of the Biological Opinion (BO) so that the BO<br />

complies with CESA.<br />

August 18, 2010: USFWS and CDFG agreed that the letter from the MBHCP<br />

Trust Group to the City (dated August 3, 2010) approving eligible TRIP projects<br />

to participate in the fee payment program was valid for projects that are ready to<br />

build prior to MBHCP expiration in 2014 but asked that the City clarify that fees<br />

can be paid at higher than 1:1 ratios as required by USFWS. The City suggests<br />

that long-term conservation assurances for the Sump Habitat Program<br />

(mitigation for cumulative effects) include National Fish and Wildlife<br />

Foundation (NFWF) as endowment holder, CDFG as conservation easement<br />

holder, and City as program manager. This arrangement will require review and<br />

approval by CDFG and USFWS as the Sump Habitat Program continues to be<br />

finalized. CDFG recommends that the Sump Habitat Program prioritize high<br />

and medium conservation priority sumps that are owned in fee by the City.<br />

January 2011: The USFWS released an updated Recommendations for<br />

Protection of the Endangered San Joaquin Kit Fox Prior to or During Ground<br />

Disturbance.<br />

May 11, 2011: Based on agency consultation and the release of the Draft<br />

Biological Opinion for the Morning Drive/<strong>State</strong> <strong>Route</strong> 178 Interchange<br />

<strong>Project</strong>, a 3:1 mitigation ratio is identified for all permanent impacts and a<br />

1.1:1 ratio is identified for all temporary impacts. Caltrans is no longer seeking<br />

an Incidental Take Permit (ITP) or a Consistency Determination under CESA<br />

as it is now assumed that take of San Joaquin kit fox, as defined under CESA,<br />

can be avoided. Caltrans and the City have identified the Wildlife Heritage<br />

Foundation (WHF), a non-profit land trust, to hold endowments necessary to<br />

fully fund the Sump Habitat Program and conservation easement oversight.<br />

18 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 2 Study Methods<br />

2.5. Limitations That May Influence Results<br />

Much of the open space adjacent to SR-<strong>58</strong> is private property or property belonging to<br />

other agencies; therefore, permission was required to conduct surveys on those<br />

properties. Access was granted for most areas with potential to support San Joaquin kit<br />

fox. Private property for which access was not granted was surveyed from the<br />

boundary of the property. In general, field surveys did not include residential property.<br />

The access limitations are not expected to affect the conclusions presented herein.<br />

Surveys for the San Joaquin kit fox did not follow the USFWS protocol for the<br />

species; however, the methodology used was coordinated with and approved by the<br />

USFWS and the CDFG. Surveys were conducted during both denning and dispersal<br />

seasons to maximize the potential for kit fox detection.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 19


Chapter 2 Study Methods<br />

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20 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 3.<br />

Results: Environmental<br />

Setting<br />

3.1. Description of Existing Biological and Physical<br />

Conditions<br />

3.1.1. Study Area<br />

The BSA is located along SR-<strong>58</strong> in the City of <strong>Bakersfield</strong>, in Kern County,<br />

California. The BSA includes the current highway pavement and shoulders, ROW,<br />

and a buffer zone extending 500 feet north and south of it (Figures 3A–3C). The BSA<br />

is located in the western portion of the MBHCP on the USGS’s 7.5-minute Rosedale<br />

and Oildale quadrangles (Figure 4).<br />

Several watercourses are located within, or in proximity to, the BSA. The Kern River<br />

is located southeast of the BSA boundary, the Friant-Kern Canal crosses the BSA just<br />

east of Coffee Road, the Calloway Canal crosses the BSA at multiple locations in the<br />

eastern portion of the BSA, and Emery Ditch occurs north of SR-<strong>58</strong> just east of the<br />

Calloway Canal.<br />

Land uses in the BSA include commercial, industrial, and residential development as<br />

well as some undeveloped lots interspersed with the developed areas.<br />

3.1.2. Physical Conditions<br />

The BSA is located in the southern San Joaquin Valley, which is in the southernmost<br />

basin of the Great Central Valley of California. Topography in the BSA is generally<br />

flat with elevation ranges from approximately 365 to 400 feet above mean sea level.<br />

The SJVR crosses SR-<strong>58</strong> west of SR-99 at Landco Drive and again east of Allen<br />

Road.<br />

The following soil types are located within the BSA: Cajon loamy sand, Cajon sandy<br />

loam and Wasco sandy loam. None of these soils are considered to be hydric<br />

(Reed 1988).<br />

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Chapter 3 Results: Environmental Setting<br />

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22 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


ALLEN RD<br />

OLD FARM RD<br />

JEWETTA AV<br />

VERDUGO LN<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

W JEWETTA AV<br />

Map Extent<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Bio_Study_Area.mxd<br />

Biological Study Area<br />

(Rev 12-20-10 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig3_Bio_Study_Area.pdf<br />

A<br />

B<br />

C<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

Biological Study Area<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 3A


Calloway Canal<br />

CALLOWAY DR<br />

MAIN PLAZA DR<br />

COFFEE RD<br />

Friant-Kern Canal<br />

HENRY LN<br />

PATTON WY<br />

WEAR ST<br />

FRUITVALE AV<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

WEDDING LN<br />

Calloway Canal<br />

Map Extent<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Bio_Study_Area.mxd<br />

Biological Study Area<br />

(Rev 12-20-10 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig3_Bio_Study_Area.pdf<br />

A<br />

B<br />

C<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

Biological Study Area<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 3B


Emery Ditch<br />

Calloway Canal<br />

Emery Ditch<br />

MOHAWK ST<br />

LANDCO DR<br />

CASE ST<br />

GIBSON ST<br />

99<br />

<strong>58</strong><br />

ROSEDALE HWY<br />

PARKER LN<br />

Kern River<br />

Map Extent<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_Bio_Study_Area.mxd<br />

Biological Study Area<br />

(Rev 12-20-10 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig3_Bio_Study_Area.pdf<br />

A<br />

B<br />

C<br />

800 400 0 800<br />

Feet<br />

Aerials flown 2006<br />

Biological Study Area<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 3C


Rosedale<br />

Stevens<br />

Oildale<br />

Gosford<br />

D:\<strong>Project</strong>s\HNTB\J006\MXD\Ex_LV_BA.mxd<br />

Biological Study Area<br />

Quad Boundary<br />

(Rev 092211 JFG) R:\<strong>Project</strong>s\HNTB\J006\Graphics\2010\BA\Fig4_LV_Quad.pdf<br />

2,000 1,000 0 2,000<br />

Feet<br />

USGS 7.5-minute quadrangles:<br />

Rosedale, Oildale, Stevens, Gosford<br />

Local Vicinity<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> (Rosedale Highway) <strong>Widening</strong> <strong>Project</strong><br />

PM 46.1 to PM 51.7<br />

D6-KER-<strong>58</strong><br />

EA 06-0F360<br />

Figure 4


Chapter 3 Results: Environmental Setting<br />

3.1.3. Biological Conditions in the BSA<br />

3.1.3.1. Vegetation Types<br />

The following vegetation types occur in the BSA: non-native grassland, ruderal or<br />

disturbed, open water or waterways, and developed or ornamental (Table 2,<br />

Figures 2A–2C). This section describes each of the vegetation types and other areas<br />

observed in the BSA.<br />

Table 2<br />

Vegetation Types and Other Areas Within the BSA<br />

Vegetation Types and Other Areas<br />

Existing in<br />

BSA (Acres)<br />

Non-native Grassland 64.83<br />

Ruderal/Disturbed 54.91<br />

Open Water/Waterway* 9.29<br />

Developed/Ornamental 603.59<br />

Total 732.62<br />

* Open water/waterway is the mapping unit to describe areas<br />

potentially within the jurisdiction of the U.S. Army Corps of<br />

Engineers (USACE), the CDFG, and the Regional Water Quality<br />

Control Board (RWQCB), primarily the canals within the BSA.<br />

These areas are vegetated with non-native grassland vegetation.<br />

Non-native Grassland<br />

Non-native grassland is dominated by non-native annual grasses and both native and<br />

non-native herbs, including red brome (Bromus madritensis ssp. rubens), foxtail<br />

barley (Hordeum murinum), telegraph weed (Heterotheca grandiflora), red-stemmed<br />

filaree (Erodium cicutarium), and rancher’s fiddleneck (Amsinckia menziesii).<br />

Non-native grassland areas occur primarily in undeveloped lots interspersed with<br />

developed areas along SR-<strong>58</strong>. These areas match Holland’s (1986) description of<br />

non-native grassland.<br />

Ruderal/Disturbed<br />

Ruderal/disturbed areas consist of graded and regularly maintained areas such as dirt<br />

roads, active oil fields, and cleared roadsides. These areas are generally without<br />

vegetation or have a sparse cover of ornamental or weedy annual species.<br />

Open Water/Waterways<br />

Open water is present in the Friant-Kern Canal, a concrete-lined channel that bisects<br />

SR-<strong>58</strong> just east of Coffee Road. No vegetation was observed within the open water or<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 25


Chapter 3 Results: Environmental Setting<br />

the sides of the Friant-Kern Canal. The Friant-Kern Canal is potentially under the<br />

jurisdiction of the USACE, the CDFG and the RWQCB.<br />

Calloway Canal and Emery Ditch are waterways within the BSA that contain<br />

non-native grassland species similar to those described above for non-native<br />

grassland. No open water was observed in these waterways at the time of the survey.<br />

However, these areas have features, such as a discernable bed, bank or channel and an<br />

ordinary high water mark, that indicate they are potentially under the jurisdiction of<br />

the USACE, the CDFG and the RWQCB.<br />

Developed/Ornamental<br />

Developed/ornamental areas consist of residential and commercial developments,<br />

paved roadways, compacted road shoulders, railroad tracks, and ornamental plantings<br />

including maintained turf grass. Common plant species observed in these areas<br />

include oleander (Nerium oleander), American sweet gum (Liquidambar styraciflua),<br />

olive (Olea europaea), and Mexican fan palm (Washingtonia robusta).<br />

3.1.3.2. Common Animal Species<br />

Amphibians<br />

No amphibian species were observed during surveys. Amphibian species expected to<br />

occur in the BSA in the vicinity of the watercourses include the western toad (Bufo<br />

boreas), California treefrog (Pseudacris [Hyla] cadaverina), and Pacific treefrog<br />

(Pseudacris [Hyla] regilla).<br />

Reptiles<br />

The only reptile species observed in the BSA during the field surveys was the<br />

side-blotched lizard (Uta stansburiana). Other reptile species expected to occur in the<br />

BSA include western fence lizard (Sceloporus occidentalis), western whiptail<br />

(Aspidoscelis [Cnemidophorus] tigris), southern alligator lizard (Elgaria<br />

multicarinata), California whipsnake (Masticophis lateralis), and gopher snake<br />

(Pituophis catenifer).<br />

Birds<br />

Several resident bird species are expected to occur in the BSA, using the habitats<br />

throughout the year. Other species are present only during certain seasons. For<br />

example, the white-crowned sparrow (Zonotrichia leucophrys) is expected to occur in<br />

the BSA during the winter season and migrate north in the spring to breed during the<br />

summer.<br />

26 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 3 Results: Environmental Setting<br />

Resident bird species observed in the BSA during surveys include killdeer<br />

(Charadrius vociferous), rock pigeon (Columba livia), mourning dove (Zenaida<br />

macroura), Anna’s hummingbird (Calypte anna), western scrub-jay (Aphelocoma<br />

californica), American crow (Corvus brachyrhynchos), northern mockingbird (Mimus<br />

polyglottos), European starling (Sturnus vulgaris), house finch (Carpodacus<br />

mexicanus), and house sparrow (Passer domesticus).<br />

Migrant bird species observed in the BSA during surveys include Say’s phoebe<br />

(Sayornis saya), western kingbird (Tyrannus verticalis), northern rough-winged<br />

swallow (Stelgidopteryx serripennis), cliff swallow (Petrochelidon pyrrhonota), barn<br />

swallow (Hirundo rustica), yellow-rumped warbler (Dendroica coronata), and<br />

white-crowned sparrow.<br />

Raptor species observed in the BSA include red-tailed hawk (Buteo jamaicensis),<br />

American kestrel (Falco sparverius), great horned owl (Bubo virginianus), and<br />

burrowing owl (Athene cunicularia). These species forage in the BSA and may nest<br />

in the BSA.<br />

Mammals<br />

Mammals observed in the BSA include desert cottontail (Sylvilagus audubonii),<br />

black-tailed jackrabbit (Lepus californicus), California ground squirrel (Spermophilus<br />

beecheyi), striped skunk (Mephitis mephitis), coyote (Canis latrans), San Joaquin kit<br />

fox, and red fox (Vulpes vulpes). Rodents that may occur in the BSA include house<br />

mouse (Mus musculus) and Botta’s pocket gopher (Thomomys bottae). Medium- to<br />

large-sized mammals expected to occur in the BSA include Virginia opossum<br />

(Didelphis virginiana), common raccoon (Procyon lotor), and American badger<br />

(Taxidea taxus).<br />

Bats occur throughout most of Southern California and may use some areas of the<br />

BSA as foraging habitat, however, no bats or sign of bats were observed during<br />

surveys. Most of the bats that could potentially occur in the BSA are inactive during<br />

the winter and either hibernate or migrate, depending on the species. Cavities in trees<br />

and man-made structures (such as bridges and culverts) provide potential roosting<br />

opportunities for bat species. Common bat species that may occur in the BSA include<br />

big brown bat (Eptesicus fuscus), California myotis (Myotis californicus), Brazilian<br />

free-tailed bat (Tadarida brasiliensis), and western pipistrelle (Pipistrellus hesperus).<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 27


Chapter 3 Results: Environmental Setting<br />

Wildlife Movement<br />

The majority of the BSA consists of developed areas with only a few areas of open<br />

space such as non-native grassland and ruderal/disturbed areas interspersed.<br />

Development consists of high-density commercial and residential land uses, and is<br />

therefore expected to support very limited wildlife movement. Wildlife may disperse<br />

along the canals, railroad tracks, and along the road edges.<br />

28 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 4.<br />

Results: Biological<br />

Resources, Discussion of<br />

Impacts and Mitigation<br />

One federally listed species has potential to occur in the BSA: the San Joaquin kit<br />

fox. The following analysis covers background information on this species, the<br />

presence of this species in the BSA, Avoidance and Minimization Measures, project<br />

effects on the kit fox, compensatory mitigation, and cumulative effects of the TRIP<br />

projects.<br />

4.1. Federally Listed or Proposed Animal Species<br />

Occurrences<br />

4.1.1. Discussion of San Joaquin Kit Fox (Vulpes macrotis mutica)<br />

The San Joaquin kit fox is a federally listed endangered species and a <strong>State</strong>-listed<br />

threatened species. Kit foxes are primarily nocturnal, but can also be crepuscular or at<br />

times diurnal. Typically, they emerge at sunset to hunt prey such as kangaroo rats<br />

(Dipodomys sp.), black-tailed jackrabbits, desert cottontails, and California ground<br />

squirrels (Thomas Reid Associates 1994). San Joaquin kit foxes prefer open habitats<br />

such as grasslands and open scrubland (USFWS 1998). In the southernmost portion<br />

of their range, the kit fox is commonly associated with valley sink scrub, valley<br />

saltbush scrub, upper Sonoran subshrub scrub, and annual grassland (USFWS 1998).<br />

The species also inhabits grazed grasslands, petroleum fields, urban areas, and land<br />

adjacent to tilled or fallow fields (USFWS 1998). Kit foxes may also occasionally<br />

utilize agricultural lands, including croplands and orchards (Warrick et al. 2007),<br />

although areas that are routinely disturbed by agricultural practices have a limited<br />

capacity to support them.<br />

Kit foxes use dens throughout the year to rear pups, to avoid water loss and heat<br />

stress in summer, to minimize metabolic costs in winter, and to escape predation<br />

(USFWS 1998). While kit foxes prefer loose-textured soils for denning, they are<br />

found on virtually every soil type (<strong>Bakersfield</strong> and Caltrans 2010).<br />

The San Joaquin kit fox has historically occurred throughout most of the San Joaquin<br />

Valley from San Joaquin County in the north to Kern County in the south (USFWS<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 29


Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

1998). The largest extant populations of kit foxes are in western Kern County in the<br />

vicinity of the Elk Hills and Buena Vista Valley and in the Carrizo Plain Natural Area<br />

in San Luis Obispo County (USFWS 1998).<br />

In <strong>Bakersfield</strong>, San Joaquin kit foxes have adapted to urban conditions and use<br />

anthropogenic habitats in which natural ecological processes are nonexistent or<br />

substantially altered (<strong>Bakersfield</strong> and Caltrans 2010). Kit fox populations in<br />

<strong>Bakersfield</strong> supplement their diet with anthropogenic foods such as refuse, pet food,<br />

and handouts; however, natural prey is an important part of their diet, especially for<br />

the pups (<strong>Bakersfield</strong> and Caltrans 2010). They appear to be relatively undisturbed by<br />

noise from traffic and human activity, as well as nighttime light typical of urban<br />

environments (<strong>Bakersfield</strong> and Caltrans 2010). Dens are found in a variety of urban<br />

areas, but are most commonly found in relatively open areas with low anthropogenic<br />

disturbance (<strong>Bakersfield</strong> and Caltrans 2010).<br />

Despite their apparent adaptations to urban environments, kit foxes in <strong>Bakersfield</strong> are<br />

concentrated around low-density industrial areas (e.g., oil fields, airport grounds,<br />

manufacturing facilities, shipping yards), undeveloped lands (e.g., vacant lots, fallow<br />

fields); storm water drainage basins (i.e., sumps), manicured open spaces (e.g., golf<br />

courses, parks, school campuses); and some larger commercial areas (e.g., office and<br />

retail facilities) (<strong>Bakersfield</strong> and Caltrans 2010). Kit foxes rarely use dense residential<br />

areas of <strong>Bakersfield</strong> where disturbance is frequent, since walls may inhibit<br />

movement, domestic dogs pose a survival threat, and few denning opportunities exist.<br />

A major effect on the kit fox in <strong>Bakersfield</strong> is the increase in barriers to movement as<br />

a result of development, which affects habitat connectivity and the maintenance of<br />

corridors connecting kit fox populations (<strong>Bakersfield</strong> and Caltrans 2010). Kit foxes<br />

have been found to move along, and also den in, linear habitat features like canals,<br />

railroad corridors, power line ROW, and the shoulders of some roads (<strong>Bakersfield</strong><br />

and Caltrans 2010).<br />

This species is known to occur within the City limits of <strong>Bakersfield</strong> and has been<br />

reported from multiple locations within one mile of the BSA (CDFG 2008, 2010).<br />

Existing information on kit fox distribution indicates that they have been found<br />

primarily in the central and eastern portions of SR-<strong>58</strong> between Rudd Avenue and<br />

SR-99 (<strong>Bakersfield</strong> and Caltrans 2010). Records from the CNDDB show kit foxes in<br />

the western portion of the BSA, between Renfro Road and Jewetta Avenue and in the<br />

low-density industrial lands in the eastern portion of the BSA between Coffee Road<br />

30 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

and Landco Drive (CDFG 2008). Vehicle-related mortality of kit foxes has occurred<br />

on Coffee Road approximately 1,000 feet south of SR-<strong>58</strong> (<strong>Bakersfield</strong> and Caltrans<br />

2010). Kit foxes have been found throughout the low-density industrial lands between<br />

Coffee Road and SR-99 and have been seen crossing SR-<strong>58</strong> between these areas<br />

(Wolfe 2008).<br />

4.1.1.1. Survey Results<br />

Suitable foraging and denning habitat for this species is present in the BSA. This<br />

habitat includes non-native grassland, ruderal/disturbed areas, and open<br />

water/waterways 2 .<br />

The habitat with the highest potential to be suitable for denning and movement by<br />

San Joaquin kit fox includes the non-native grasslands and ruderal/disturbed areas<br />

associated with low-density industrial development and vacant lots; landscaped<br />

vegetation and open space under portable units associated with elementary school and<br />

low-density commercial areas; the SJVR and the Friant-Kern and Calloway canals<br />

that cross under SR-<strong>58</strong>.<br />

During focused surveys conducted in the spring/summer of 2008 one kit fox was<br />

observed immediately south of the BSA at Rosedale Middle School on the south side<br />

of SR-<strong>58</strong>, east of Allen Road and west of Old Farm Road.<br />

During focused surveys of the BSA for sign of kit fox, four potential San Joaquin kit<br />

fox dens and four instances of scat were observed in the BSA. One potential kit fox<br />

den and one instance of fresh kit fox scat were observed on the north side of SR-<strong>58</strong><br />

north of Rosedale Middle School. The second potential kit fox den was observed<br />

south of SR-<strong>58</strong> and west of Jewetta Avenue. Potential dens three and four and three<br />

locations with kit fox scat were observed in the eastern portion of the alignment just<br />

west of Mohawk Street.<br />

Kit foxes appear to be concentrated in the low-density industrial lands at the eastern<br />

portion of the BSA and dispersed throughout the vacant lots and Rosedale Middle<br />

School in the western portion of the BSA.<br />

2<br />

Open water/waterway is the mapping unit to describe areas potentially within the jurisdiction of<br />

the USACE, the CDFG, and the RWQCB, primarily the canals within the BSA. These areas are<br />

vegetated with non-native grassland vegetation.<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

4.1.1.2. Critical Habitat<br />

No Critical Habitat has been proposed or designated by the USFWS for the San<br />

Joaquin kit fox.<br />

4.1.1.3. Avoidance and Minimization Efforts<br />

Standard Avoidance and Minimization Measures<br />

This section describes standard Avoidance and Minimization Measures that will be<br />

implemented as part of the SR-<strong>58</strong> <strong>Widening</strong> <strong>Project</strong> to reduce potential adverse<br />

effects of project construction on the San Joaquin kit fox. The measures have been<br />

developed from standard recommendations described in the USFWS Standardized<br />

Recommendations for Protection of the Endangered San Joaquin Kit Fox Prior to or<br />

During Ground Disturbance (USFWS 2011). Caltrans, in coordination with the City<br />

of <strong>Bakersfield</strong>, will be responsible for implementation of these measures.<br />

• SJKF – 1 USFWS Standardized Construction and Operational Requirements<br />

Construction activities will adhere to the standard construction and operational<br />

requirements as described in the USFWS Standardized Recommendations for<br />

Protection of the Endangered San Joaquin Kit Fox Prior to or During Ground<br />

Disturbance (USFWS 2011).<br />

• SJKF – 2 Pre-activity Surveys<br />

Approximately 60 days before road construction, a USFWS- approved biologist will<br />

conduct a survey for kit fox dens within 200 feet of the construction footprint,<br />

including utility relocations. A letter report and map of known and potential kit fox<br />

dens will be submitted to USFWS.<br />

Pre-activity clearance surveys for kit fox will be repeated approximately two weeks<br />

(no sooner than 14 days and no longer than 30 days) before construction or after any<br />

delays in construction of over two weeks. Any new kit fox dens identified since<br />

completing the 60-day survey will be reported to USFWS in a letter report and map.<br />

If no new kit fox dens are identified, an internal record will be maintained that<br />

includes the survey date, designated biologist conducting the survey, and general<br />

survey findings. The records can be submitted to USFWS upon request.<br />

• SJKF – 3 Den Monitoring, Excavation, and Exclusion<br />

If dens or potential dens are detected within the project footprint during 60-day and/or<br />

two-week pre-activity clearance surveys, agency permission will be requested to<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

monitor and excavate dens that would be affected by the project. The biologist will<br />

monitor potential dens for three consecutive nights and submit monitoring results in a<br />

letter report to USFWS. The biologist will oversee the excavation of dens following<br />

approval by USFWS. Dens found within 200 feet of project construction but not<br />

affected by construction activities will be monitored and buffered from construction<br />

by an exclusion zone. The biologist will place flagged stakes in a 50-foot radius<br />

buffer around any potential or atypical den and will place a fence (e.g., untreated<br />

wood particle board, silt fencing, orange construction fencing, or other fencing<br />

approved by the USFWS as long as it has openings for ingress/egress of kit fox and<br />

keeps humans and equipment out) 100 feet from a known den; USFWS will be<br />

contacted if a natal den is found. The biologist will submit results of den excavation<br />

and exclusion in a letter report to USFWS.<br />

• SJKF – 4 Employee Education Program<br />

The biologist will conduct an employee education program for all construction crews<br />

before ground disturbing activities. The purpose of this training is to inform<br />

construction crew members of permit terms and conditions and the potential for kit<br />

fox to occur at a site and be affected by construction activities. The training will be<br />

repeated to all new crew members and annually to all crew members working in kit<br />

fox habitat. Following the training, crew members will sign an attendance sheet<br />

stating that they attended the training and understand the protection measures and<br />

construction restrictions. Training materials and records of attendees will be<br />

submitted to USFWS.<br />

• SJKF – 5 Construction Monitoring<br />

The biologist will monitor road construction activities once daily. The biologist will<br />

verify that construction complies with permit terms and conditions and construction<br />

and operation requirements described in USFWS Standardized Recommendations for<br />

the Protection of the Endangered San Joaquin Kit Fox Prior to or During Ground<br />

Disturbance (USFWS 2011). The biologist will maintain a log of daily monitoring<br />

notes that can be summarized and transmitted to USFWS at their request.<br />

4.1.1.4. <strong>Project</strong> Impacts<br />

The effects of the proposed project on San Joaquin kit fox are described as direct and<br />

indirect effects. As defined under ESA, direct effects are those caused by the<br />

proposed project and occur at the time of the project, and indirect effects are those<br />

that are caused by the proposed project and are later in time, but still are reasonably<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

certain to occur. <strong>Project</strong> direct effects are further differentiated by permanent and<br />

temporary effects. Temporary effects are not expected to extend beyond the period of<br />

project construction, and occur where the area that is affected will be restored to preproject<br />

conditions following project construction. Permanent effects include those<br />

that occur at the time of construction and remain following project completion, and<br />

occur when the area is permanently converted from one cover/habitat type to another.<br />

Direct Effects<br />

The proposed project could result in the direct permanent loss of approximately<br />

1.21 acre (0.18 acre non-native grassland, 1.00 acre ruderal/disturbed, and 0.03 acre<br />

open water/waterway) of kit fox habitat, which represent both potential foraging and<br />

denning habitat for this species, and temporary effects to approximately 6.61 acres<br />

(3.25 acres of non-native grassland, 3.30 acres of ruderal/disturbed areas, and<br />

0.06 acre of open water/waterway) of kit fox habitat. Direct, permanent effects<br />

include the removal of non-native grassland, ruderal/disturbed, and open<br />

water/waterways to accommodate the new roadbed, intersection improvements, and<br />

proposed new ROW limits. Direct temporary effects include disturbance during<br />

construction of the project to provide access and staging areas of the proposed<br />

project. Kit fox could forage and den in this habitat and the permanent loss and<br />

temporary disturbance of habitat could cause kit fox to move elsewhere in search of<br />

foraging and denning opportunities (Table 3).<br />

Of the dens identified in the BSA during 2008 surveys, one den is located within the<br />

project footprint and could be directly permanently eliminated during project<br />

construction. This estimate of den loss is based on those dens identified within the<br />

project footprints during 2008 surveys and could change if kit fox create additional<br />

dens or abandon dens in the project footprint, or if the footprint limits are extended or<br />

reduced. Loss of dens could result in kit fox displacement.<br />

Disturbances associated with the construction of the proposed project may also<br />

temporarily affect the San Joaquin kit fox. Kit foxes could be struck by construction<br />

equipment or other vehicles or become entrapped in dens during ground disturbing<br />

activities. Noise and light pollution during construction are considered direct effects<br />

as they may prevent kit foxes from foraging, mating, or rearing their young.<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

Vegetation Types<br />

Table 3<br />

Habitat a for San Joaquin Kit Fox That Would be Affected<br />

by the Proposed <strong>Project</strong><br />

Total<br />

Existing in<br />

the BSA<br />

(acres)<br />

Permanent<br />

Effect<br />

At-grade<br />

<strong>Widening</strong><br />

(acres)<br />

Permanent<br />

Effect<br />

Grade<br />

Separation at<br />

Landco Drive<br />

(acres)<br />

Temporary<br />

Effect Atgrade<br />

<strong>Widening</strong><br />

(acres)<br />

Temporary<br />

Effect<br />

Grade<br />

Separation at<br />

Landco Drive<br />

(acres)<br />

Total <strong>Project</strong><br />

Effect<br />

(acres)<br />

Non-native Grassland 64.83 0.16 0.02 3.17 0.08 3.43<br />

Ruderal/Disturbed 54.91 0.53 0.47 2.78 0.52 4.30<br />

Open Water/Waterways a, b 9.29 0.03 0.00 0.06 0.00 0.09<br />

a<br />

b<br />

c<br />

Total c 129.03 0.72 0.49 6.01 0.60 7.82<br />

This effect includes the widened portion of the bridge over Calloway Canal.<br />

Open water/waterway is the mapping unit to describe areas potentially within the jurisdiction of the USACE, the CDFG, and the RWQCB, primarily the<br />

canals within the BSA. These areas are vegetated with non-native grassland vegetation.<br />

Developed/ornamental areas that are surrounded by open space also present potential habitat opportunities for the San Joaquin kit fox; however, this<br />

habitat type has not been included in the table because the overall Developed/Ornamental vegetation type as mapped is characterized as primarily<br />

developed.<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

Indirect Effects<br />

Following project completion, there could be an unintentional increase in kit fox<br />

vehicle strike in the action area. Vehicular strike is the primary source of mortality<br />

among kit foxes in <strong>Bakersfield</strong> (Cypher 2000, Bjurlin et al. 2005) and has been found<br />

to occur most frequently where kit foxes are abundant, on major arterial roads with<br />

relatively high traffic volumes, and at intersections (Bjurlin et al. 2005). Currently,<br />

the San Joaquin kit fox is exposed to the traffic along SR-<strong>58</strong>. Crossing additional<br />

lanes may result in an increase in road kill mortality.<br />

The construction of the proposed project could result in the displacement of kit foxes<br />

and altered space use patterns, such as a change in habitat use or daily movement<br />

patterns, both of which could result in disrupted social ecology, reduced fertility,<br />

pregnancy rates, prenatal survival, mortality, and reduced carrying capacity in the<br />

vicinity of the BSA.<br />

Effects Determination<br />

Based on the analysis of the potential direct and indirect effects, it can be concluded<br />

that the proposed project ‘may affect, likely to adversely affect’ the San Joaquin kit<br />

fox.<br />

To reduce the potential for adverse effects on San Joaquin kit fox that could occur<br />

during ground disturbing activities, Caltrans is proposing to implement standard<br />

Avoidance and Minimization Measures that were described previously in<br />

Section 4.1.1.3. These measures include standard construction and operational<br />

requirements, pre-activity surveys, den monitoring, worker environmental awareness<br />

training, and construction monitoring that are in accordance with USFWS<br />

Standardized Recommendations for Protection of the Endangered San Joaquin Kit<br />

Fox Prior to or During Ground Disturbance (USFWS 2011) and are expected to<br />

avoid or substantially reduce the potential for adverse effects on kit fox such as den<br />

loss and disturbance during construction activities.<br />

Caltrans is also proposing to implement additional conservation measures beyond<br />

those described for the standard Avoidance and Minimization Measures that would<br />

further offset the potential adverse effects and also compensate for effects to habitat<br />

that would result from the proposed project. As described in the following section<br />

(4.1.1.5., see Onsite Mitigation through <strong>Project</strong> Design Modifications), Caltrans is<br />

proposing to incorporate elements into the road design that are intended to facilitate<br />

safe movement by kit foxes and substantially reduce adverse direct effects associated<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

with habitat fragmentation and reduced landscape connectivity and indirect effects<br />

associated with potential for vehicle strike. Caltrans is also proposing to compensate<br />

for habitat permanently lost and temporarily disturbed during ground disturbing<br />

activities by paying fees per requirements in the MBHCP. Compensation according to<br />

the MBHCP requirements would serve to enhance comparable kit fox foraging and<br />

denning habitat within the local MBHCP Plan area and at ratios requested by the<br />

USFWS and greater than those required by the MBHCP. Compensatory mitigation<br />

for habitat loss and disturbance is described below in Section 4.1.1.5. (see Offsite<br />

Mitigation for <strong>Project</strong>-specific Habitat Loss).<br />

Together, the standard construction-related Avoidance and Minimization Measures<br />

and additional conservation measures are expected to substantially reduce the<br />

potential for take and compensate for residual impacts. However, although the<br />

Avoidance and Minimization Measures would reduce potential for direct mortality of<br />

kit foxes related to construction, the proposed project would result in a small loss of<br />

occupied suitable habitat. Therefore, it is concluded that the proposed project ‘may<br />

affect, likely to adversely affect’ the San Joaquin kit fox.<br />

4.1.1.5. Modifications to the <strong>Project</strong> to Mitigate Effects<br />

Standard Avoidance and Minimization Measures will be in place during construction<br />

to avoid and minimize potential adverse effects on kit fox during project construction.<br />

In addition to these measures, mitigation will be implemented to compensate for postconstruction<br />

project-specific and program-level effects on kit fox and habitat loss.<br />

Onsite mitigation for project effects includes implementing project design<br />

modifications that are intended to reduce adverse effects on kit fox movement and<br />

potential for vehicle strike. Offsite mitigation for project effects involves<br />

compensating for the permanent and temporary loss of known kit fox habitat by<br />

participating in the MBHCP fee payment program. Offsite mitigation for programlevel<br />

effects resulting from construction of the six TRIP road improvement projects<br />

involves implementing the Sump Habitat Program, a long-term habitat conservation<br />

program for the urban kit fox population. Caltrans, in coordination with the City of<br />

<strong>Bakersfield</strong>, will be responsible for implementation of these measures.<br />

Onsite Mitigation through <strong>Project</strong> Design Modifications<br />

The following project design modifications are expected, when implemented<br />

together, to reduce the potential for adverse effects on kit fox. Stephanie Coppeto and<br />

Leo Edson met on two occasions in 2009 with project engineers, City of <strong>Bakersfield</strong>,<br />

and Caltrans to identify project design modifications that could be incorporated into<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

the design plans for SR-<strong>58</strong> <strong>Widening</strong>. Final project design modifications intended to<br />

reduce potential adverse effects on kit fox will be approved by USFWS during the<br />

final design phase.<br />

The primary objective of the project design modifications is to maintain opportunities<br />

for kit foxes to cross over the road surface while reducing the potential for an increase<br />

in vehicle strike. Limited research indicates that kit foxes infrequently use culverts to<br />

cross under a roadway, even when a culvert is present nearby; foxes tend to continue<br />

to cross over the roadway surface opportunistically (Cypher 2009). Therefore, project<br />

design modifications do not emphasize the creation of new culverts, especially when<br />

the project is not anticipated to disrupt a known movement corridor (e.g., canal and/or<br />

railway corridor). However, some use of culverts has been documented by ESRP, and<br />

use has increased with increasing culvert size (Cypher 2000). Because there are<br />

culverts in the project BSA and no data to suggest whether or not kit fox use these<br />

features, project design modifications recommend retaining existing culverts in the<br />

BSA to the extent feasible in the event that these passageways are used, or may be<br />

used in the future, by kit fox in the project area.<br />

• SJKF – 6 Fencing<br />

Fencing is not proposed for any portion of SR <strong>58</strong> <strong>Widening</strong> project ROW. If fencing<br />

is required during a later planning stage, permeable fencing will be installed. One or a<br />

combination of the following three design options may be adopted to provide kit fox<br />

with movement opportunities: elevating the bottom of the fence 5 inches above<br />

ground to allow unobstructed movement by kit foxes under the fence; installing<br />

ground-level 8-x-8-inch-wide gaps no more than 100 feet apart for the length of the<br />

fence, which would allow kit fox movement at regular intervals along the ROW; and<br />

installing fencing with a minimum mesh size of 3½ x 7 inches, preferably<br />

5 x 12 inches, which would allow unlimited movement by kit fox through the fence.<br />

Permeable fence design is expected to reduce the potential to disrupt north-south kit<br />

fox movement and habitat fragmentation in the project area, when implemented in<br />

conjunction with all project design modifications, by allowing unlimited kit fox<br />

movement.<br />

• SJKF – 7 Curbed Medians and Median Barriers<br />

Curbed medians are proposed as part of project design. The height of curbed medians<br />

will be no greater than 10 inches. Ten-inch curbed medians will remain un-vegetated<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

to prevent obstructing the visual field of kit foxes near the roadway. Curbed medians<br />

less than 10 inches in height and requiring landscaping will be planted with low level<br />

vegetation (i.e., less than 6 inches) and will not require mowing (see measure<br />

SJKF – 9).<br />

No median barriers are currently proposed; however, if taller median barriers are<br />

required in a later planning stage and for public safety, Caltrans-designed modified<br />

median barrier type 60/S will be used. Caltrans type 60/S design has been approved<br />

by USFWS (BO# 81420-2009-F-0752; USFWS 2009) and includes 9-inch radius<br />

openings (9 inch high x 18 inch wide half circle openings) spaced every 150 feet to<br />

allow passage by kit fox.<br />

Low-height curbed medians or gapped median barriers are expected to reduce the<br />

potential to disrupt north-south kit fox movement in the project area and reduce the<br />

potential for vehicle strike, when implemented in conjunction with all project design<br />

modifications, by allowing unlimited kit fox movement and providing kit fox with an<br />

unobstructed line of sight.<br />

• SJKF – 8 Maintain Open Movement Corridors<br />

Existing kit fox movement corridors along all canals and railroad would be preserved<br />

through the use of existing bridges. The toe-of-road fill and bridge support walls<br />

should be maintained and new walls designed, no less than 20 feet from the centerline<br />

of canal access roads and the centerline of railroads.<br />

• SJKF – 9 Landscaping<br />

<strong>Project</strong> landscaping will be designed to allow unobstructed visibility to kit fox and to<br />

provide opportunities for movement across the roadway. Curbed median and roadside<br />

landscaping will be planted in one of three alternative strategies: selecting plants that<br />

do not exceed 6 inches tall at maturity, maintaining vegetation height so that it does<br />

not exceed 6 inches and does not require mowing, and/or creating gaps no less than<br />

4 feet wide every 12 feet in areas landscaped with trees and shrubs.<br />

Low-height or gapped landscaping is expected to reduce the potential for vehicle<br />

strike, when implemented in conjunction with all project design modifications, by<br />

providing kit fox with an unobstructed line of sight.<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

• SJKF – 10 Warning Signs<br />

Warning signs alerting east- and west-bound drivers to potential kit fox presence are<br />

proposed on Rosedale Highway at several locations. Intersections under consideration<br />

include Rosedale Highway and Calloway Drive, Coffee Road, and Landco Drive. The<br />

need for and number of appropriate signage at intersections will continue to be<br />

evaluated as the project design advances. Signage proposed would follow FHWA<br />

(2003) guidelines or other guidelines recommended by Caltrans.<br />

Installation of a sign warning drivers of the potential for crossing kit foxes is expected<br />

to reduce the potential for vehicle strike.<br />

Offsite Mitigation for <strong>Project</strong>-Specific Habitat Loss<br />

Permanent and temporary loss of San Joaquin kit fox habitat resulting from<br />

construction of the proposed project will be mitigated by participating in the MBHCP<br />

fee payment program. Suitable kit fox habitat that will be affected by SR-<strong>58</strong><br />

<strong>Widening</strong> construction and mitigated through the MBHCP is comprised of non-native<br />

grassland, ruderal/disturbed, and open water/waterway. In accordance with prior<br />

direction from Peter Cross, Susan Jones, and Ellen McBride (USFWS) to Caltrans for<br />

habitat mitigation for Mohawk Street Extension (USFWS 2008), a TRIP project<br />

currently under construction in <strong>Bakersfield</strong> and mitigated through the MBHCP. Fees<br />

will be paid to the MBHCP Trust Group at a ratio of 3:1 for permanent impacts and<br />

1.1:1 for temporary impacts to all suitable San Joaquin kit fox habitat types. These<br />

ratios are based on recent agency consultation and the release of the Draft Biological<br />

Opinion for the Morning Drive/<strong>State</strong> <strong>Route</strong> 178 Interchange <strong>Project</strong>.<br />

• SJKF – 11 MBHCP Fee Payment<br />

The permanent loss of 1.21 acre of non-native grassland, ruderal/disturbed, and open<br />

water/waterway and the temporary disturbance of 6.61 acres of non-native grassland,<br />

ruderal/disturbed, and open water/waterway will be mitigated by participating in the<br />

MBHCP at agency-approved ratios. Sufficient funding would be paid to allow the<br />

MBHCP Trust Group to purchase of 10.90 acres of habitat (Table 4).<br />

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At-grade<br />

<strong>Widening</strong><br />

Grade<br />

Separation<br />

at Landco<br />

Drive<br />

Table 4<br />

San Joaquin Kit Fox Habitat Compensatory Mitigation Ratios,<br />

Anticipated Acreage of Effect, and Mitigation Acreage<br />

Habitat Type<br />

Affected<br />

Non-native<br />

grassland;<br />

Ruderal/Disturbed;<br />

Open wash/<br />

waterway a<br />

Non-native<br />

grassland;<br />

Ruderal/Disturbed;<br />

Open wash/<br />

waterway a<br />

Proposed<br />

Compensatory<br />

Mitigation Ratios<br />

Permanent:<br />

acquisition of<br />

habitat of similar or<br />

greater value at 3:1<br />

ratio. Temporary:<br />

acquisition of<br />

habitat of similar or<br />

greater value at<br />

1.1:1 ratio.<br />

Permanent:<br />

acquisition of<br />

habitat of similar or<br />

greater value at 3:1<br />

ratio. Temporary:<br />

acquisition of<br />

habitat of similar or<br />

greater value at<br />

1.1:1 ratio.<br />

Permanent<br />

<strong>Project</strong><br />

Effects<br />

(acres)<br />

Temporary<br />

<strong>Project</strong><br />

Effects<br />

(acres)<br />

Mitigation<br />

Required<br />

(acres)<br />

0.72 6.01 8.77<br />

0.49 0.60 2.13<br />

Total 1.21 6.61 10.90<br />

Source: USFWS 2008 (See Table 7 of Appendix A); Vegetation types have been changed to correspond to those<br />

mapped for the proposed project.<br />

a<br />

Open water/waterway is the mapping unit to describe areas potentially within the jurisdiction of the USACE, the<br />

CDFG, and the RWQCB, primarily the canals within the BSA. These areas are vegetated with non-native<br />

grassland vegetation.<br />

• SJKF – 12 Delineating Impact Acreages<br />

Prior to construction, the limits of permanent and temporary effects would be verified<br />

and mapped by habitat type within those limits. The map would be submitted for<br />

approval by USFWS before submittal to the City of <strong>Bakersfield</strong> Planning Department<br />

for fee payment.<br />

Mitigation for Program-Level Effects<br />

Caltrans, in coordination with the City of <strong>Bakersfield</strong>, is proposing to mitigate for<br />

program-level effects of construction of the six TRIP road improvement projects by<br />

implementing the Sump Habitat Program, which is intended to provide long-term<br />

habitat conservation for the urban kit fox population. The conservation goals of the<br />

program would be achieved by installing artificial dens in selected sumps, enhancing<br />

kit fox habitat by controlling vegetation in and around dens, increasing kit fox<br />

accessibility to sumps through fence/gate gaps, and reducing the potential for effects<br />

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Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

to kit foxes associated with regular maintenance activities. The program is currently<br />

being developed with USFWS and CDFG. The conceptual framework for the<br />

program is described in Draft Thomas Roads Improvement Program Mitigation for<br />

Cumulative Effects to San Joaquin Kit Fox, a working version of the third chapter of<br />

the Implementation Plan (City of <strong>Bakersfield</strong> and Caltrans 2010). The program will<br />

continue to be refined through an ongoing collaborative, consultation process among<br />

Caltrans, City, USFWS, and CDFG. Caltrans and the City have taken necessary<br />

actions to begin developing the program by participating in four meetings with<br />

USFWS and CDFG on March 11, 2010, May 11, 2010, July 14, 2010, and August 18,<br />

2010 and the City has begun evaluating ownership of sumps with potential to be<br />

conserved as part of the program, calculated a preliminary estimate of anticipated<br />

program costs, and collected information from the resource agencies that would be<br />

required in a long-term management plan. Caltrans and the City have identified the<br />

Wildlife Heritage Foundation, a non-profit land trust, to hold endowments necessary<br />

to fully fund the Sump Habitat Program and conservation easement oversight.<br />

• SJKF – 13 Implement the Sump Habitat Program<br />

The final approved version of the Sump Habitat Program will be implemented within<br />

one year of the approval of the Final Environmental Document (FED) for the last of<br />

the six TRIP projects.<br />

4.1.1.6. Cumulative Effects (FESA)<br />

The action area for the cumulative effects analysis is the TRIP program area analyzed<br />

in the Implementation Plan (City and Caltrans 2010), which includes the BSAs for the<br />

six proposed TRIP projects.<br />

The proposed project is one of the ten TRIP projects. The cumulative effects of all ten<br />

TRIP projects include loss of kit fox habitat and kit fox dens, habitat fragmentation,<br />

and degradation, change in habitat use patterns, geographic isolation, change of<br />

movement patterns, and an increase in mortality associated with an unintentional<br />

increase in vehicle strike. Roadway expansion could bisect safe movement corridors,<br />

reducing the probability that kit foxes could safely move from one area of suitable<br />

habitat to another in search of denning and foraging habitat. Patches of undeveloped<br />

kit fox habitat, which are already highly fragmented in <strong>Bakersfield</strong>, could be<br />

sufficiently degraded by construction of new and expanded roadways that they would<br />

no longer function as suitable habitat. Habitat fragmentation and degradation could<br />

force kit foxes to use different areas for movement, denning and foraging, which<br />

42 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 4 Results: Biological Resources, Discussion of Impacts and Mitigation<br />

could result in greater exposure to potential predators and risk of collisions with<br />

vehicles and contribute to disrupted social ecology, reduced fertility, pregnancy rates,<br />

prenatal survival, mortality, and reduced carrying capacity in the BSA.<br />

Implementing the TRIP projects in combination with other future development could<br />

substantially impair north-south movement by kit foxes because most of the TRIP<br />

project alignments cross the study area in an east-west direction isolating kit fox<br />

populations on small parcels of land, some of which may be too small to support<br />

current population numbers, resulting in geographic isolation of populations in the<br />

north from populations in the south.<br />

Implementation of all ten of the TRIP projects could permanently or temporarily<br />

affect up to 24 potential and 8 presumed active kit fox dens, including 1 natal den.<br />

The direct removal of 7.82 acres of occupied suitable habitat and loss of one kit fox<br />

den would contribute to the cumulative loss of habitat/dens within the action area.<br />

While existing kit foxes would be expected to move to adjacent areas for foraging and<br />

denning, they would be moving into areas already occupied by kit fox individuals,<br />

thereby increasing the competition for foraging and denning habitat. Reproducing<br />

individuals would compete for dens and food resources and may not be able to<br />

produce as many offspring in areas of competition. Long-term, this could be expected<br />

to decrease the carrying capacity and overall abundance of kit foxes within the action<br />

area. Additionally, the proposed project could increase unintentional vehicle strikes,<br />

and loss of individuals could result in the loss of genetic diversity in the population.<br />

The maintenance of canal and railway corridors would maintain the movement<br />

corridors currently being used in the BSA, and would allow the exchange of<br />

individuals, and therefore, genetic exchange with other individuals in the action area.<br />

Therefore, the proposed project’s contribution to habitat fragmentation is expected to<br />

be limited. The purchase of 10.90 acres of occupied suitable habitat for contribution<br />

to the MBHCP Reserve, in combination with participation in the Sump Mitigation<br />

Program, would compensate for the proposed project’s contribution to the cumulative<br />

loss of habitat resulting from the TRIP program.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 43


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44 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 5.<br />

Conclusions and<br />

Determination<br />

5.1. Conclusions<br />

The construction of the proposed project will result in the permanent loss of<br />

1.21 acres and the temporary loss of 6.61 acres of potential San Joaquin kit fox<br />

habitat. One potential kit fox den may be directly affected by project development.<br />

Direct mortality resulting from contact with construction equipment or other vehicles<br />

or entrapment within dens, pipes, or trenches may occur. Noise and light pollution<br />

may directly affect the kit fox.<br />

Indirect effects include the potential for unintentional increased vehicle strikes,<br />

habitat fragmentation, disruption in movement patterns, displacement of kit foxes and<br />

altered space use patterns that could result in disrupted social ecology, reduced<br />

fertility, pregnancy rates, prenatal survival, mortality, and reduced carrying capacity<br />

in the vicinity of the BSA.<br />

5.2. Determination<br />

Together the standard construction-related Avoidance and Minimization Measures<br />

and additional conservation measures are expected to substantially reduce the<br />

potential for take and compensate for residual effects. However, although Avoidance<br />

and Minimization Measures would reduce the potential for direct mortality of kit fox<br />

related to construction, the proposed project would result in a small loss of occupied<br />

suitable habitat. Therefore, the proposed project ‘may affect, likely to adversely affect’<br />

the San Joaquin kit fox.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 45


Chapter 5 Conclusions and Determination<br />

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46 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 6.<br />

References<br />

<strong>Bakersfield</strong>, City of. 2008. MBHCP Kit Fox Den Database (GIS Database).<br />

<strong>Bakersfield</strong>, CA: the City.<br />

<strong>Bakersfield</strong>, City of and California Department of Transportation (<strong>Bakersfield</strong> and<br />

Caltrans) 2010. Thomas Roads Improvement Program: San Joaquin Kit Fox<br />

Life History, Effects Analysis, Mitigation Strategy, and Implementation Plan.<br />

(Implementation Plan) <strong>Bakersfield</strong> and Fresno, CA: the City and Caltrans,<br />

respectively.<br />

———. 2009. Thomas Roads Improvement Program: San Joaquin Kit Fox Life<br />

History, Effects Analysis, and Conceptual Mitigation Strategy. <strong>Bakersfield</strong> and<br />

Fresno, CA: the City and Caltrans, respectively.<br />

———. 2007 (November). Westside Parkway San Joaquin Kit Fox Study Final<br />

Report. <strong>Bakersfield</strong>, CA: the City.<br />

<strong>Bakersfield</strong>, City of, California Department of Transportation (Caltrans), and County<br />

of Kern (<strong>Bakersfield</strong> et al.). 2006. Tier II Environmental Assessment/Final<br />

Environmental Impact Report: Westside Parkway. <strong>Bakersfield</strong>, CA: the City,<br />

Caltrans, and the County of Kern.<br />

<strong>Bakersfield</strong>, City of and County of Kern. 2002 (December). Metropolitan <strong>Bakersfield</strong><br />

General Plan. <strong>Bakersfield</strong>, CA: the City.<br />

Bjurlin, C.D., B.L. Cypher, C.M. Wingert, and C.L. Van Horn Job. 2005 (July 10).<br />

Urban Roads and the Endangered San Joaquin Kit Fox (Prepared for<br />

California Department of Transportation). Fresno, CA: California <strong>State</strong><br />

University Stanislaus Endangered Species Recovery Program.<br />

California Department of Fish and Game (CDFG). 2010. California Natural Diversity<br />

Database. Records of Occurrence for U.S. Geologic Survey Gosford, Stevens,<br />

Tupman, Oildale, Rosedale, Rio Bravo, North of Oildale, Famoso, Wasco,<br />

Lamont, and Oil Center 7.5-minute quandrangles. Sacramento, CA: CDFG,<br />

Natural Heritage Division.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 47


Chapter 6 References<br />

———. 2008. California Natural Diversity Database. Records of Occurrence for U.S.<br />

Geologic Survey Famoso, Lamont, North of Oildale, Oil Center, Oildale,<br />

Rosedale, Rio Bravo, Tupman, Stevens, Gosford, and Wasco. 7.5-minute<br />

topographical quandrangles. Sacramento, CA: CDFG, Natural Heritage<br />

Division.<br />

California Department of Transportation (Caltrans). 2010. Rosedale Highway<br />

<strong>Widening</strong> <strong>Project</strong> Final Natural Environment Study (prepared by BonTerra<br />

Consulting). Fresno, CA: the Department, District 6.<br />

———. 2006 (February). 7 th Standard Road <strong>Widening</strong> <strong>Project</strong> Environmental<br />

Assessment/Initial Study with Proposed Mitigated Negative Declaration.<br />

Fresno, CA: California Department of Transportation, District 6.<br />

———. 1998 (December). Final Natural Environment Study Tier I EIS for <strong>Route</strong><br />

Adoption On <strong>Route</strong> <strong>58</strong>, I 5 to SR 99. Fresno, CA: the Department, District 6.<br />

California Native Plant Society (CNPS). 2010. Electronic Inventory of Rare and<br />

Endangered Vascular Plants of California. Records of Occurrence for U.S.<br />

Geologic Survey Gosford, Stevens, Tupman, Oildale, Rosedale, Rio Bravo,<br />

North of Oildale, Famoso, Wasco, Lamont, and Oil Center 7.5-minute<br />

quadrangles. Sacramento, CA: CNPS. http://www.cnps.org/inventory.<br />

———. 2008. Electronic Inventory of Rare and Endangered Vascular Plants of<br />

California. Records of Occurrence for U.S. Geologic Survey Rio Bravo,<br />

Rosedale, Oildale, Tupman, Stevens, and Gosford 7.5-minute topographical<br />

quadrangles. Sacramento, CA: CNPS. http://www.cnps.org/inventory.<br />

Cypher, B.L. 2009. Personal communication regarding kit fox concentration areas,<br />

movement corridors, and potential mitigation for the conceptual strategy<br />

between Brian Cypher and Stephanie Coppeto (AECOM).<br />

Holland, R.F. 1986. Preliminary Descriptions of the Terrestrial Natural Communities<br />

of California. Sacramento, CA: CDFG, Non-game Heritage Program.<br />

Kern, County of. 1994. Western Rosedale Specific Plan. <strong>Bakersfield</strong>, CA: Kern<br />

County.<br />

Kern County Waste Management Department. 1997 (October). Kern County Waste<br />

Facilities Habitat Conservation Plan. <strong>Bakersfield</strong>, CA: Kern County Waste<br />

Management Department.<br />

48 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Chapter 6 References<br />

Kern Water Bank Authority. 1997. Kern Water Bank Authority Habitat Conservation<br />

Plan. <strong>Bakersfield</strong>, CA: Kern Water Bank Authority.<br />

Reed, P.B., Jr. 1988. National List of Plant Species That Occur In Wetlands: National<br />

Summary (Biological Report 88 [24]). Washington, D.C.: USFWS.<br />

Sawyer, J.O. and T. Keeler-Wolf. 1995. A Manual of California Vegetation.<br />

Sacramento, CA: CNPS.<br />

Thomas Reid Associates. 1994 (August 29). Metropolitan <strong>Bakersfield</strong> Habitat<br />

Conservation Plan and Final Environmental Impact Report (Chapter 4:<br />

Biological Resources). Palo Alto, CA: Thomas Reid Associates.<br />

———. 1991 (July). Metropolitan <strong>Bakersfield</strong> Habitat Conservation Plan<br />

Endangered Species Inventory in Support of the Conservation Plan. Palo Alto,<br />

CA: Thomas Reid Associates.<br />

———. 1990 (September). MBHCP Field Documentation for the Endangered Species<br />

Inventory in Support of the Habitat Conservation Plan. Palo Alto, CA:<br />

Thomas Reid Associates.<br />

United <strong>State</strong>s Fish and Wildlife Service (USFWS). 2008 (March 12). Species List for<br />

Rosedale Highway <strong>Widening</strong> <strong>Project</strong>. Sacramento, CA: U.S. Fish and Wildlife<br />

Service.<br />

———. 2011 (January). Standardized Recommendations for Protection of the<br />

Endangered San Joaquin Kit Fox Prior to or During Ground Disturbance.<br />

Sacramento, CA: USFWS.<br />

———. 1999 (June). Standardized Recommendations for Protection of the San<br />

Joaquin Kit Fox Prior to or During Ground Disturbance. Sacramento, CA:<br />

USFWS.<br />

———. 1998. Recovery Plan for Upland Species of the San Joaquin Valley,<br />

California. Portland, OR: USFWS, Region 1.<br />

Warrick, G.D., H.O. Clark, Jr., P.A. Kelly, D.F. Williams, and B.L. Cypher. 2007. Use<br />

of Agricultural Lands by San Joaquin Kit Foxes. Western North American<br />

Naturalist 67(2): 270-277.<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment 49


Chapter 6 References<br />

Wolfe, M. 2008. Personal communication regarding general kit fox occurrence on<br />

East Rosedale Highway in the area of the Big West property between Marcia<br />

Wolfe (MH Wolfe and Associates) and Stephanie Coppeto (AECOM).<br />

50 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Appendix A Wildlife Species Observed in<br />

the BSA


Appendix A Wildlife Species Observed in the BSA<br />

WILDLIFE SPECIES OBSERVED<br />

IN THE BIOLOGICAL STUDY AREA<br />

Species<br />

Reptiles<br />

PHRYNOSOMATIDAE - ZEBRA-TAILED, FRINGE-TOED,<br />

SPINY, TREE, SIDE-BLOTCHED, AND HORNED LIZARDS<br />

Uta stansburiana<br />

side-blotched lizard<br />

Buteo jamaicensis<br />

red-tailed hawk<br />

Falco sparverius<br />

American kestrel<br />

Charadrius vociferus<br />

killdeer<br />

Pavo cristatus<br />

common peafowl *<br />

Gallus gallus<br />

domestic chicken *<br />

Columba livia<br />

rock pigeon *<br />

Zenaida macroura<br />

mourning dove<br />

Patagioenas fasciata<br />

band-tailed pigeon<br />

Bubo virginianus<br />

great horned owl<br />

Athene cunicularia<br />

burrowing owl<br />

Birds<br />

ACCIPITRIDAE - HAWKS<br />

FALCONIDAE - FALCONS<br />

CHARADRIIDAE - PLOVERS<br />

PHASIANIDAE - UPLAND FOWL<br />

COLUMBIDAE - PIGEONS & DOVES<br />

Calypte anna<br />

Anna's hummingbird<br />

STRIGIDAE - TRUE OWLS<br />

TROCHILIDAE - HUMMINGBIRDS<br />

TYRANNIDAE - TYRANT FLYCATCHERS<br />

Sayornis nigricans<br />

black phoebe<br />

Sayornis saya<br />

Say's phoebe<br />

Tyrannus verticalis<br />

western kingbird<br />

Lanius ludovicianus<br />

loggerhead shrike<br />

* introduced species<br />

LANIIDAE - SHRIKES<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment A-1


Appendix A Wildlife Species Observed in the BSA<br />

WILDLIFE SPECIES OBSERVED<br />

IN THE BIOLOGICAL STUDY AREA<br />

(Continued)<br />

Species<br />

CORVIDAE - JAYS & CROWS<br />

Aphelocoma californica<br />

western scrub-jay<br />

Corvus brachyrhynchos<br />

American crow<br />

Eremophila alpestris<br />

horned lark<br />

ALAUDIDAE - LARKS<br />

HIRUNDINIDAE - SWALLOWS<br />

Stelgidopteryx serripennis<br />

northern rough-winged swallow<br />

Petrochelidon pyrrhonota<br />

cliff swallow<br />

Hirundo rustica<br />

barn swallow<br />

Turdus migratorius<br />

American robin<br />

TURDIDAE - THRUSHES & ROBINS<br />

Mimus polyglottos<br />

northern mockingbird<br />

Sturnus vulgaris<br />

European starling *<br />

Bombycilla cedrorum<br />

cedar waxwing<br />

Dendroica petechia<br />

yellow warbler<br />

Agelaius phoeniceus<br />

red-winged blackbird<br />

Sturnella neglecta<br />

western meadowlark<br />

Euphagus cyanocephalus<br />

Brewer’s blackbird<br />

Carpodacus mexicanus<br />

house finch<br />

MIMIDAE - THRASHERS<br />

STURNIDAE - STARLINGS<br />

BOMBYCILLIDAE - WAXWINGS<br />

PARULIDAE - WARBLERS<br />

ICTERIDAE - BLACKBIRDS<br />

FRINGILLIDAE - FINCHES<br />

PASSERIDAE - OLD WORLD SPARROWS<br />

Passer domesticus<br />

house sparrow *<br />

* introduced species<br />

A-2 <strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment


Appendix A Wildlife Species Observed in the BSA<br />

WILDLIFE SPECIES OBSERVED<br />

IN THE BIOLOGICAL STUDY AREA<br />

(Continued)<br />

Species<br />

Mammals<br />

LEPORIDAE - HARES & RABBITS<br />

Sylvilagus audubonii<br />

desert cottontail<br />

Lepus californicus<br />

black-tailed jackrabbit<br />

Spermophilus beecheyi<br />

California ground squirrel<br />

Vulpes macrotis mutica<br />

San Joaquin kit fox<br />

Canis lupus familiaris<br />

domestic dog<br />

Mephitis mephitis<br />

striped skunk<br />

Felis catus<br />

domestic cat<br />

* introduced species<br />

SCIURIDAE - SQUIRRELS<br />

CANIDAE - WOLVES & FOXES<br />

FELIDAE - CATS<br />

<strong>State</strong> <strong>Route</strong> <strong>58</strong> <strong>Widening</strong> <strong>Project</strong> Biological Assessment A-3

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