Thousand Oaks City Council
June 9, 2026

Biological crusts are likely located within the Study Area along with multiple pollinator species.

However, impacts are not anticipated since the Project site’s existing access roads, pedestrian pathways, and utility facilities are already developed and disturbed. Therefore, impacts to sensitive biological crusts and pollinator species are not likely to occur. ƒ CO-26: Isolation and fragmentation of natural open space areas should be prevented wherever possible.

Natural open space areas are located throughout the Study Area. However, isolation and fragmentation of natural open space will not occur since the Project will take place within existing access roads, pedestrian pathways, and utility facilities that are already developed and disturbed.
ƒ CO-27: Since natural streams often serve as important movement corridors for wildlife, they should be preserved wherever it is feasible to do so.

Natural streams are located throughout the Study Area. However, the Project will take place within existing access roads, pedestrian pathways, and utility facilities that are already developed and disturbed within and adjacent to the natural streams. Therefore, natural streams will be preserved.

City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
40 CO-29: Continue to protect oak and landmark trees and their habitat in recognition of their historic, aesthetic and environmental value to the citizens of Thousand Oaks; in particular, Valley Oak habitat.

Oak and landmark trees and their habitat are located throughout the Study Area. However, since the Project site is comprised of existing access roads, pedestrian access pathways, and utility facilities, removal of protected trees is not required. Some minor trimming of branches to city protected trees may be necessary for the Project; however, trimming would be limited to branches that are two inches in diameter or smaller and would be in compliance with the associated ordinances. Therefore, the Project would continue to protect oak and landmark trees and their habitat.
ƒ CO-30: Preserve wetlands and associated wetland buffers as open space and maintain these areas in a natural state to protect the community's water quality, biodiversity and aesthetic value.

Two seeps are located within the Study Area. However, the Project footprint will not expand into the seeps; therefore, they will be preserved.
ƒ CO-32: The City shall encourage and promote the conservation and protection of all rare, threatened, endangered or sensitive species listed by State and Federal agencies (USFWS and CDFW), the CNPS, the County of Ventura, and the City of Thousand Oaks.

Threatened, endangered, rare, and special status wildlife species are known to occur or have the potential to occur within the Study Area. However, with the incorporation of the Project-specific BMPs and AMMs, impacts to these species will be avoided or minimized; they will therefore be protected and/or conserved.

Avoidance and Minimization Measures
Jurisdictional Delineation and Habitat Assessment 41
6 Avoidance and Minimization Measures
The AMMs below should be incorporated into the Project design to avoid or minimize impacts to special-status species and other sensitive biological resources.

BIO-1 Pre-construction Surveys
Preconstruction surveys will be conducted by a qualified biologist within CDFW jurisdictional streambed no greater than seven days prior to the initiation of vegetation trimming or ground disturbance activities. Woodrat middens, American badger burrows, and any other regulated biological resource will be flagged for avoidance and work activities at that location will be avoided until a qualified biologist confirms that the sensitive biological resource(s) will not be directly or indirectly impacted by the construction activities.

BIO-2 Burrowing Owl
A burrowing owl habitat assessment will be conducted by a qualified biologist within 500 feet of the Project’s work area (survey area) prior to initiation of the Project. If suitable burrowing owl habitat is documented within CDFW jurisdiction, focused burrowing owl surveys will be conducted to determine the presence or absence of the species within the survey area. Surveys will be conducted in accordance with CDFW’s Staff Report on Burrowing Owl Mitigation (CDFW 2012). If burrowing owl is located, CDFW will be notified and occupied burrows will not be disturbed during the nesting season (February 1 through August 31) unless a qualified biologist approved by CDFW verifies through non-invasive methods that either the birds have not begun egg-laying and incubation or that juveniles from the occupied burrows are foraging independently and are capable of independent survival. Limits of construction to avoid an active nest shall be established in the field with flagging, fencing, or other appropriate barriers, and construction personnel shall be instructed on the sensitivity of nest areas. The biologist shall serve as a construction monitor during those periods when construction activities will occur near active nest areas to ensure that no inadvertent impacts to these nests occur. Results of the surveys shall be provided to CDFW in the annual mitigation status report. If the burrowing owl is detected in the Project Area but nesting is not occurring, construction work can proceed after any owls have been evacuated from the site using CDFW-approved burrow closure procedures and after alternative nest sites have been provided in accordance with the CDFW Staff Report on Burrowing Owl Mitigation (2012).

BIO-3 Rare Plants
Focused rare plant surveys will be conducted prior to Project initiation to verify the presence or absence, estimate the abundance, and map the extent of the special-status plant species that are present or have a high or moderate potential to occur within 50 feet of the Project site. The results of the survey will be used to determine if the Project has the potential to impact these special-status plant species. The surveys should be conducted within the plants’ most distinct phenology period to correctly identify the species and in accordance with guidelines published by the CDFW (2018) and CNPS (2001).

If special-status plant species are detected within the Project’s work area(s), the limits of their distribution shall be flagged. Flagging shall extend to the furthest extent within the Project Area, but City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
42 outside any private property. Results of the surveys shall be provided to CDFW in the annual mitigation status report. Special-status plant species shall be monitored for avoidance to the maximum extent feasible. Take of ESA and CESA listed; candidate, and proposed species or State Rare species will not occur as a result of the Project.

BIO-4 Crotch’s Bumble Bee
If Crotch’s bumble bee is still considered a CESA candidate species or has been listed as threatened or endangered under CESA at the time vegetation clearance or ground disturbance commences, PWD or its contractor(s) shall implement the following avoidance, minimization, and compensation measures for this species:
ƒ Prior to construction activities or vegetation disturbance, a qualified biologist shall conduct a habitat assessment for Crotch’s bumble bee within 50 feet of the Project’s work area (survey area). The habitat assessment shall identify potential foraging, nesting, and/or overwintering resources. If suitable habitat is present, those areas shall be avoided to the extent feasible. ƒ If suitable habitat is unavoidable, prior to the start of initial ground-disturbing activities (including, but not limited to, site preparation, staging and mobilization, vegetation clearance/mowing/trimming, grading, and excavation), a qualified biologist shall conduct a protocol-level presence/absence survey for Crotch’s bumble bee in areas of suitable habitat during the peak active period for Crotch’s bumble bee (highest detection probability). The peak active period for Crotch’s bumble bee in the Project Area is anticipated to be April through June given the expected desiccation of Crotch’s bumble bee floral resources within the project area by mid-summer, though this timing could depend on annual climatic factors. Survey methodology shall be based on Section 4.1.1 of CDFW’s 2023 Survey Considerations for CESA Candidate Bumble Bee Species, or the most current CDFW guidance in effect at the time. ƒ If Crotch’s bumble bee is present, the qualified biologist shall identify the location of nests in the survey area, to the extent feasible. If nests are identified, the qualified biologist shall determine the need to establish a no-disturbance buffer around the nest, where feasible, to reduce the risk of disturbance or accidental take. The buffer shall provide at least 50 feet (15 meters) of clearance around active nest entrances. If project component activities may result in disturbance or potential take, the qualified biologist, in coordination with CDFW, shall expand the buffer zone as necessary to prevent disturbance or take. If establishment of a no disturbance buffer is feasible, construction activities shall not occur within the buffer until a qualified biologist determines the colony is no longer active (i.e., no Crotch’s bumble bees are seen flying in or out of the nest for three consecutive days, indicating the colony has completed its nesting season and the next season’s queens have dispersed from the colony). Once the nest has been determined to be inactive, construction activities within the no-disturbance buffer(s) shall be allowed to resume. Otherwise, the no-disturbance buffer shall be maintained for the duration of Project component construction activities in each work area and shall be removed only after the conclusion of all grading, clearing, and construction activities at each construction site.
ƒ If Crotch’s bumble bee is determined to be present on the project site, floral resources associated with the species that will be removed or damaged by project construction activities in the areas of the project site where Crotch’s bumble bee is detected and documented, shall be replaced at a minimum 1:1 ratio.

Avoidance and Minimization Measures
Jurisdictional Delineation and Habitat Assessment 43
BIO-5 Pre-construction Nesting Bird Surveys
To avoid disturbance of nesting birds, including special-status species and birds protected by the MBTA and CFGC Section 3503, Project activities should occur outside of the breeding season for nesting birds (February 1 through August 31), if feasible.

If vegetation trimming or soil disturbing activities occur during the breeding season, a preconstruction nesting bird survey should be conducted no more than seven days prior to the initiation of Project activities. The nesting bird survey shall be conducted on foot inside the Project Area and include a 500-foot buffer for raptors and special-status species a 100-foot buffer for all other species. The survey shall be conducted by a biologist familiar with avian species known to inhabit Southern California. If nests are found, an avoidance buffer of up to 500 feet for raptors and special-status species and up to 100 feet for non-raptors (dependent upon the species, the proposed work activity, and existing disturbances associated with land use outside of the workspace) shall be determined and demarcated by the biologist with construction fencing, flagging, or other means to mark the boundary. Intrusion into the buffer may be conducted if it is determined by the biologist that there is no risk of harm to the nest and work is monitored by the biologist. If the risk of nest abandonment is observed, all construction activities within the buffer shall cease until the nest is no longer active as determined by the biologist.

BIO-6 Worker Environmental Awareness Training
Prior to the initiation of maintenance activities each year, an approved biologist shall present a Worker Environmental Awareness Training (WEAT) to all on-site personnel. The WEAT will educate the personnel on the identification of special-status species and regulated biological resources that are present or have the potential to occur within the Project Area and will cover the applicable regulatory policies and provisions regarding their protection and provide an overview of the Project’s AMMs. Furthermore, on-site personnel will be briefed on the reporting process if an inadvertent injury or mortality should occur to a special-status species during construction.

BIO-7 Biological Monitoring
A qualified biologist should monitor all creek crossing maintenance, temporary fill crossing installation and decommissioning, and HCTP to D Structure washed out access road temporary rebuild installation and decommissioning. The biological monitor will conduct clearance sweeps immediately prior to the initiation of construction activities and will monitor for the presence of special-status species in areas where there is a moderate or high potential for presence. Daily monitoring reports will be prepared for each monitoring day. The biological monitor will have authority to halt any action that may result in direct impacts on special-status species or any other sensitive biological resources. If special-status wildlife are observed in work areas and do not readily leave on their own volition, work activities will be temporarily suspended until the animal moves out of harm’s way.

City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
44 7 Limitations
This BRA has been conducted in accordance with professionally accepted biological investigation practices conducted at this time and in this geographic area. The biological investigation is limited by the scope of work performed. Reconnaissance biological surveys for certain taxa may have been conducted as part of this assessment but were not performed during a particular blooming period, nesting period, or particular portion of the season when positive identification would be expected if present, and therefore, cannot be considered definitive. The biological surveys are limited also by the environmental conditions present at the time of the surveys. In addition, general biological (or protocol) surveys do not guarantee that the organisms are not present and will not be discovered in the future within the site. In particular, mobile wildlife species could occupy the site on a transient basis or re-establish populations in the future. Our field studies were based on current industry practices, which change over time and may not be applicable in the future. No other guarantees or warranties, expressed or implied, are provided. The findings and opinions conveyed in this report are based on findings derived from site reconnaissance, jurisdictional areas, review of CNDDB RareFind5, and specified historical and literature sources (CDFW 2025). Standard data sources relied upon during the completion of this report, such as the CNDDB, may vary with regard to accuracy and completeness. In particular, the CNDDB is compiled from research and observations reported to CDFW that may or may not have been the result of comprehensive or site-specific field surveys.

Although Rincon believes the data sources are reasonably reliable, Rincon cannot and does not guarantee the authenticity or reliability of the data sources it has used. Additionally, pursuant to our contract, the data sources reviewed included only those that are practically reviewable without the need for extraordinary research and analysis.

References
Jurisdictional Delineation and Habitat Assessment 45
8 References
Baldwin , B.G. (Ed.), D.H. Goldman (Ed.), D. J. Keil (Ed.), R. Patterson (Ed.), T. J. Rosatti (Ed.), D. H.

Wilken (Ed.). 2012. The Jepson Manual: Vascular Plants of California, Second Edition, Thoroughly Revised and Expanded. University of California Press. Berkeley, California.

Calflora. 2025. Information on California plants for education, research and conservation. Available at: https://www.calflora.org/ Accessed: January 2025.

California Department of Fish and Wildlife (CDFW). 2012. Staff Report on Burrowing Owl Mitigation.

Natural Resources Agency, Dept. of Fish and Wildlife, Sacramento, CA. _____. 2018. Protocols for Surveying and Evaluating Impacts to Special Status Native Plant Populations and Natural Communities. Available at:
https://nrm.dfg.ca.gov/FileHandler.ashx?DocumentID=18959&inline. Accessed August 2025.
_____. 2022. Final Lake or Streambed Alteration Agreement, EPIMS Notification No. VEN-26963 – Unit W Wastewater Interceptor Condition Assessment Project. _____. 2025. California Natural Diversity Database (CNDDB) using RareFind. Electronic database managed by the Biogeographic Data Branch, California Department of Fish and Wildlife.

Sacramento, California. Available at:
https://apps.wildlife.ca.gov/rarefind/view/RareFind.aspx. Accessed January 2025.

California Native Plant Society (CNPS). 2001. Botanical Survey Guidelines. Available at:
http://www.cnps.org/cnps/rareplants/pdf/cnps_survey_guidelines.pdf. Accessed August 2025.
_____. 2025a. Inventory of Rare and Endangered Plants, Online Edition. California Native Plant Society, Sacramento, CA. Available at: http://www.rareplants.cnps.org. Accessed January 2025.
_____. 2025b. A Manual of California Vegetation, Online Edition. California Native Plant Society, Sacramento, CA. Available at: http://www.cnps.org/cnps/vegetation/. Accessed January 2025.

California Water Board (Water Boards). 2020. Implementation Guidance for the State Wetland Definition and Procedures for Discharges of Dredged or Fill Material to Waters of the State.

Available at: https://www.waterboards.ca.gov/water_issues/programs/cwa401/docs/ dredge_fill/ revised_guidance.pdf. Accessed 2022.

City of Thousand Oaks. 2013. City of Thousand Oaks General Plan, Conservation Element. Available at: http://www.toaks.org/home/showdocument?id=332.
_____. 2018. Road Design and Construction Standards and Standard Land Development Specifications. City of Thousand Oaks Public Works Department. May 2018.

Conejo Open Space Conservation Agency. 2025. Arroyo Conejo. Online. Thousand Oaks, CA. https://conejo-openspace.org/openspace/arroyo-conejo/ Accessed January 2025.

Consortium of California Herbaria (CCH). 2025. Consortium of California Herbaria. Available at:
https://ucjeps.berkeley.edu/consortium. Accessed January 2025.

City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
46 eBird. 2025. eBird: An online database of bird distribution and abundance [web application]. eBird, Ithaca, New York. Available at: http://www.ebird.org. Accessed January 2025.

Elbroch, M., M. Kresky, and J. Evans. 2012. Field Guide to Animal Tracks and Scat of California.

Berkeley: University of California Press.

Griffith, G.E., Omernik, J.M., Smith, D.W., Cook, T.D., Tallyn, E., Moseley, K., and Johnson, C.B., 2016, Ecoregions of California (poster): U.S. Geological Survey Open-File Report 2016–1021, with map, scale 1:1,100,000.
iNaturalist 2025. Web application. California Academy of Sciences, National Geographic Society.

Available at: www.inaturalist.org. Accessed January 2025.

Jepson Flora Project (eds.) 2025. Jepson eFlora. Available at: https://ucjeps.berkeley.edu/eflora/.

Accessed January 2025.

Natural Resources Conservation Service (NRCS). 2025a. Web Soil Service. U.S. Department of Agriculture. Available at: https://websoilsurvey.sc.egov.usda.gov/App/HomePage.htm Accessed January 2025.
_____. 2025b. Soil Data Access Hydric Soils List. U.S. Available at: https://www.nrcs.usda.gov/ Internet/FSE_DOCUMENTS/nrcseprd1316620.html Accessed January 2025.

NatureServe. 2025. Definitions of NatureServe Conservation Status Ranks. Available at:
https://help.natureserve.org/biotics/content/record_management/Element_Files/Element_T rackin g/ETRACK_Definitions_of_Heritage_Conservation_Status_Ranks.htm. Accessed:

January 2025.

Padre Associates, Inc. (Padre). 2022. Unit w Wastewater Interceptor Condition Assessment Biological Resources Study.

PRISM Climate Group, Oregon State University, https://prism.oregonstate.edu. Accessed January 2025.

Reid, F. 2006. Peterson Field Guide to Mammals of North America. 4th ed. Boston, Massachusetts:

Houghton Mifflin.

Sibley, D.A. 2016. Sibley Birds West: Field Guide to Birds of Western North America. New York, New York: Knopf.

Stebbins, R.C., and S.M. McGinnis. 2018. Peterson Field Guide to Western Reptiles and Amphibians. 4th ed. New York, New York: Houghton Mifflin.

SWCA Environmental Consultants. 2022a. Biological Resources Assessment Report for Unit W and Y. _____. 2022b. Jurisdictional Delineation Report for the Unit W and Unit Y.

U.S. Army Corps of Engineers (USACE). 1987. Corps of Engineers Wetlands Delineation Manual.

Technical Report Y-87-1. Vicksburg, Mississippi: U.S. Army Engineers Waterways Experiment Station.
_____. 2008a. Regional Supplement to the Corps of Engineers Wetlands Delineation Manual: Arid West (Version 2.0), U.S. Army Engineer Research and Development Center. ERDC/EL TR-08-

28. References
Jurisdictional Delineation and Habitat Assessment 47
_____. 2008b. A Field Guide to the Identification of the Ordinary High Water Mark (OHWM) in the Arid West Region of the United States. Edited by R.W. Lichvar and S. M. McColley.

ERDC/CRREL TR-08-12. Hanover, New Hampshire: U.S. Army Engineer Research and Development Center.
_____. 2008c. Clean Water Act Jurisdiction following the U.S. Supreme Court’s decision in Rapanos v.

United States & Carbell v. United States. Available at: https://www.epa.gov/sites/default/ files/2016-02/documents/cwa_jurisdiction_following _rapanos120208.pdf. _____. 2016. Map and Drawing Standards for the South Pacific Division Regulatory Program, February 10, 2016.
_____. 2022. National Wetland Plant List. Version 3.4. Hanover, New Hampshire: U.S. Army Corps of Engineers Research and Development Center, Cold Regions Research and Engineering Laboratory. Available at: https://wetland-plants.sec.usace.army.mil/nwpl_static/v34/home/ home.html. Accessed January 2025.

U.S. Fish and Wildlife Service (USFWS). 2025a. Information for Planning and Consultation (IPaC).

Available at: http://ecos.fws.gov/ipac/. Accessed January 2025. _____. 2025b. U.S. Fish and Wildlife Service Critical Habitat Mapper. Available at:
https://fws.maps.arcgis.com/home/webmap/viewer.html?webmap=9d8de5e265ad4fe09893 cf75b 8dbfb77 Accessed January 2025.
_____. 2025c. National Wetlands Inventory (NWI). Available at: https://www.fws.gov/wetlands/.

Accessed January 2025.

U.S. Geological Survey (USGS). 2025. USGS National Watershed Boundary Dataset. Available at:
https://apps.nationalmap.gov/viewer/. Accessed January 2025.

Werner Biological Consulting (Werner). 2022. Least Bell’s Vireo Protocol Survey for the Conejo Canyon’s Bridge at Hill Canyon Project.

Appendix A
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^Z/ĂŶĚŝƚƐůŝĐĞŶƐŽƌƐΞϮϬϮϱ͘ĚĚŝƚŝŽŶĂůĚĂƚĂƉƌŽǀŝĚĞĚďLJE,͕ϮϬϮϱ͘ m Ϭ ϮϬϬ ϭϬϬ &ĞĞƚ
WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚhƚŝůŝƚLJ&ĂĐŝůŝƚLJWĞĚĞƐƚƌŝĂŶWĂƚŚ
E,&ůŽǁůŝŶĞ
^ƚƌĞĂŵͬZŝǀĞƌ
ϮϰͲϭϲϱϭϮ/K
&ŝŐϮWƌŽũĞĐƚ>ŽĐĂƟŽŶ
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ϲ ϳ
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ŽŽƌĚŝŶĂƚĞ^LJƐƚĞŵ͗Eϭϵϴϯ^ƚĂƚĞWůĂŶĞĂůŝĨŽƌŶŝĂs WƌŽũĞĐƟŽŶ͗>ĂŵďĞƌƚŽŶĨŽƌŵĂůŽŶŝĐ ĂƚƵŵ͗EŽƌƚŚŵĞƌŝĐĂŶϭϵϴϯϭŝŶĐŚсϮϬϬĨĞĞƚƌĞĂƚĞĚŽŶdŚƵƌƐĚĂLJ͕ƵŐƵƐƚϮϭ͕ϮϬϮϱ DĂƉƌĞĂƚĞĚďLJ͗ZŝŶĐŽŶŽŶƐƵůƚĂŶƚƐ͕/ŶĐ͘ hŶŝƚzĐĐĞƐƐZŽĂĚ
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1RUWK )RUN $UUR\R &RQHMR
/ŵĂŐĞƌLJƉƌŽǀŝĚĞĚďLJ
^Z/ĂŶĚŝƚƐůŝĐĞŶƐŽƌƐΞϮϬϮϱ͘ĚĚŝƚŝŽŶĂůĚĂƚĂƉƌŽǀŝĚĞĚďLJE,͕ϮϬϮϱ͘ m Ϭ ϮϬϬ ϭϬϬ &ĞĞƚ
WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚWĞĚĞƐƚƌŝĂŶWĂƚŚ
E,&ůŽǁůŝŶĞ
^ƚƌĞĂŵͬZŝǀĞƌ
ϮϰͲϭϲϱϭϮ/K
&ŝŐϮWƌŽũĞĐƚ>ŽĐĂƟŽŶ
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ŽŽƌĚŝŶĂƚĞ^LJƐƚĞŵ͗Eϭϵϴϯ^ƚĂƚĞWůĂŶĞĂůŝĨŽƌŶŝĂs WƌŽũĞĐƟŽŶ͗>ĂŵďĞƌƚŽŶĨŽƌŵĂůŽŶŝĐ ĂƚƵŵ͗EŽƌƚŚŵĞƌŝĐĂŶϭϵϴϯϭŝŶĐŚсϮϬϬĨĞĞƚƌĞĂƚĞĚŽŶdŚƵƌƐĚĂLJ͕ƵŐƵƐƚϮϭ͕ϮϬϮϱ DĂƉƌĞĂƚĞĚďLJ͗ZŝŶĐŽŶŽŶƐƵůƚĂŶƚƐ͕/ŶĐ͘ D^Ͳ,dW
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^Z/ĂŶĚŝƚƐůŝĐĞŶƐŽƌƐΞϮϬϮϱ͘ĚĚŝƚŝŽŶĂůĚĂƚĂƉƌŽǀŝĚĞĚďLJE,͕ϮϬϮϱ͘ m Ϭ ϮϬϬ ϭϬϬ &ĞĞƚ
WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚ
E,&ůŽǁůŝŶĞ
^ƚƌĞĂŵͬZŝǀĞƌ
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dƌĞĂƚŵĞŶƚ
WůĂŶƚ
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WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚhƚŝůŝƚLJ&ĂĐŝůŝƚLJƌĞĞŬƌŽƐƐŝŶŐ
E,&ůŽǁůŝŶĞ
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WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
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E,&ůŽǁůŝŶĞ
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E,&ůŽǁůŝŶĞ
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Site Photographs
Site Photographs
Habitat Assessment and Jurisdictional Delineation 1
Photo 1. Overview of the Coast Live Oak Woodland & Forest present on- site (facing northeast).

Photo 2. Overview of the California Sagebrush – (Purple Sage) Scrub present on-site (facing north).

City of Thousand Oaks
Arroyo Conejo Maintenance Project
2 Photo 3. Overview of the California Sycamore - Coast Live Oak Riparian Woodlands present on-site (facing south, taken in February so sycamore leaves are absent).

Photo 4. Overview of the Goodding's Willow - Red Willow Riparian Woodland & Forest present on-site (facing south).

Site Photographs
Habitat Assessment and Jurisdictional Delineation 3
Photo 5. Overview of the Coast Live Oak Woodland & Forest present on-site (facing south).

Photo 6. Overview of the Coast Live Oak Woodland & Forest in the foreground with Scrub Oak Chaparral in the background present on-site.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
4 Photo 7. Overview of the Coast prickly pear scrub vegetaƟon community present on-site.

Photo 8. Overview of the Upland Mustards or Star-Thistle Fields vegetaƟon community present on-site.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 5
Photo 9. Overview of the California Walnut Groves present on-site.

Photo 10. Overview of the Scrub Oak Chaparral vegetaƟon community present on-site.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
6 Photo 11. Overview of Wild Oats & Annual Brome Grasslands vegetaƟon community present on-site.

Photo 12. Overview of Survey Area near confluence of two drainages. Area consists of Upland Mustards or Star-thistle Fields. Photo facing east- southeast.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 7
Photo 13. Site condiƟons located in east end of Project Area. Photo facing west-southwest.

Photo 14. Overview of drainage near the east end of the Project Area. Photo facing north.

Site supports a Coast Live Oak Woodland & Forest at this location.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
8 Photo 15. Perennial flow in drainage. Photo facing southeast.

Photo 16. Overview of NFAC. Photo facing south-southeast looking towards Paradise Falls waterfall. Photo captured near the central porƟon of the Project Area.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 9
Photo 17. Bridge supporƟng access across a perennial feature in the Survey Area. Photo facing southeast.

Photo 18. Example of Mulefat Thickets in Survey Area. Photo facing northwest.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
10 Photo 19. Example of Coast Prickly Pear Scrub on-site. Photo facing east- northeast.

Photo 20. Example of California Sycamore - Coast Live Oak Riparian Woodlands on site.

Photo facing northeast.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 11
Photo 21. Cleanout #3. Photo facing northwest.

Photo 22. Cleanout #4. Photo facing east.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
12 Photo 23. Cleanout #5. Photo facing northeast.

Photo 24. Cleanout #5. Photo facing southwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 13
Photo 25. Manhole Y-1 and Manhole A37-1. Photo facing south, downslope towards F18.

Photo 26. Manhole A37-A at white post. Photo facing southwest.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
14 Photo 27. Manhole A37-A at white post on right side of the access road. Photo facing eastsoutheast.

Photo 28. Manhole Y-2 adjacent to F18’ steep top of bank. Photo facing west- northwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 15
Photo 29. Photo directly adjacent to Manhole Y-2 looking down into F18. Photo facing west.

Photo 30. Manhole Y-3 at white post. Photo facing east towards F18.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
16 Photo 31. Photo looking towards plaƞorm supporƟng Manhole Y-10. Photo facing southeast.

Photo 32. Manhole Y-10 plaƞorm. Photo facing southeast.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 17
Photo 33. Photo looking up at plaƞorm supporƟng Manhole Y-10. Photo facing northnorthwest.

Photo 34. Y Structure. Photo facing east.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
18 Photo 35. Y Structure. Photo facing west.

Photo 36. Creek Crossing A at NFAC. Photo facing south-southwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 19
Photo 37. Creek Crossing A at NFAC. Photo facing north.

Photo 38. Creek Crossing B at NFAC. Photo facing southeast.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
20 Photo 39. Creek Crossing B at NFAC. Photo facing west.

Photo 40. Creek Crossing C at NFAC. Photo facing northwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 21
Photo 41. Creek Crossing C at NFAC. Photo facing southeast.

Photo 42. Creek Crossing D at NFAC. Photo facing north.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
22 Photo 43. Creek Crossing D at NFAC. Photo facing south.

Photo 44. Creek Crossing F at NFAC. Photo facing south-southeast.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 23
Photo 45. Photo facing west from Creek Crossing F at NFAC.

Photo 46. OHWM limits of F01 at MSC-HTP crossing to be abandoned.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
24 Photo 47. Overview of Wetland DeterminaƟon Sampling Pit (SP01) at shovel locaƟon, facing southeast. Photo taken January 25, 2022.

Photo 48. Overview of Wetland DeterminaƟon Sampling Pit (SP02) at shovel locaƟon, facing north. Photo taken January 25, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 25
Photo 49. Overview of MSC-HTP access road across F01, facing southwest. Photo taken January 25, 2021.

Photo 50. Overview of HCTP to D Structure across F01, facing southeast. Photo taken January 25, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
26 Photo 51. HCTP to D Structure across F01, facing north. Photo taken January 25, 2022.

Photo 52. HCTP to D Structure across F01, facing southeast. Photo taken January 25, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 27
Photo 53. Overview of HCTP to D Structure across F01, facing southwest. Photo taken February 2, 2022.

Photo 54. Overview of Wetland DeterminaƟon Sampling Pit (SP09), facing southeast. Photo taken February 02, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
28 Photo 55. Overview of HCTP to D Structure across F01, facing north. Photo taken January 25, 2022.

Photo 56. Overview of W/F Structure and A Structure, facing northeast. Photo taken January 25, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 29
Photo 57. Overview of W/F Structure and A Structure, facing east southeast. Photo taken February 2, 2022.

Photo 58. Overview of W/F Structure and A Structure, facing northeast. Photo taken January 25, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
30 Photo 59. Secondary channel of F01 overlapping with W/F Structure and A Structure, facing west (downstream). Photo taken January 25, 2022.

Photo 60. Secondary drainage of F01 overlaps with HCTP to D access road, facing southwest (downstream). Photo taken June 10, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 31
Photo 61. Overview of HCTP to D Structure across F01, facing northeast. Photo taken February 1, 2022.

Photo 62. HCTP to D Structure across F01, facing east. Photo taken February 1, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
32 Photo 63. HCTP to D Structure across F01, facing north northeast. Photo taken February 1, 2022.

Photo 64. Wetland DeterminaƟon Sampling Pit (SP06), facing east. SP06 examined approximately at red circle. Photo taken February 1, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 33
Photo 65. Overview of HCTP to D Structure across F01, facing southeast. Photo taken January 25, 2022
Photo 66. HCTP to D Structure across F01, facing southeast. Photo taken June 10, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
34 Photo 67. Overview of HCTP to D Structure across F01, facing northwest. Photo taken January 25, 2022.

Photo 68. Wetland DeterminaƟon Sampling Pit (SP07), facing south SP06 examined at shovel locaƟon. Photo taken February 1, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 35
Photo 69. Wetland DeterminaƟon Sampling Pit (SP10), view facing east. Photo taken February 2, 2022.

Photo 70. Overview of Shappell Lateral Valves, view facing north. Photo taken January 26, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
36 Photo 71. Overview of Shappell Lateral Valves, facing northeast. Photo taken January 26, 2022.

Photo 72. Wetland DeterminaƟon Sampling Plot (SP03), view facing north. Photo taken January 25, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 37
Photo 73. Overview of HCTP to D Structure across F01, view facing northeast. Photo taken January 26, 2022.

Photo 74. Overview of HCTP to D Structure across F01, facing northwest. Photo taken February 2, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
38 Photo 75. Wetland DeterminaƟon Sampling Plot (SP08), view facing southeast. Photo taken February 1, 2022.

Photo 76. Overview of Rancho Conejo access road across F01 overlapping secondary channel, view facing south. Photo taken February 2, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 39
Photo 77. Rancho Conejo access road across F01, view facing southeast. Photo taken January 26, 2022.

Photo 78. Rancho Conejo access road across F01, view facing southwest. Photo taken January 26, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
40 Photo 79. Rancho Conejo access road across F01, view facing northwest. Photo taken January 26, 2022.

Photo 80. Wetland DeterminaƟon Sampling Plot (SP05), view facing north. Photo taken January 26, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 41
Photo 81. Overview of the D Structure, facing southwest. Photo taken January 26, 2022.

Photo 82. D Structure view facing southeast. Photo taken January 26, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
42 Photo 83. D Structure, view facing northwest. Photo taken January 26, 2022.

Photo 84. D Structure, view facing southeast. Photo taken January 26, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 43
Photo 85. D Structure, view facing southeast. Photo taken January 26, 2022.

Photo 86. Calle Salto Lateral, view facing west. Photo taken January 26, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
44 Photo 87. Calle Salto Lateral, view facing southeast. Photo taken January 26, 2022.

Photo 88. Wetland DeterminaƟon Sampling Plot (SP04), view facing northeast. Photo taken January 26, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 45
Photo 89. Overview of Rancho Conejo Lateral, facing southeast. Photo taken February 8, 2022.

Photo 90. Rancho Conejo Lateral, view facing east. Photo taken February 8, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
46 Photo 91. Rancho Conejo Lateral, view facing east. Photo taken February 8, 2022.

Photo 92. Overview of concrete drain in Rancho Conejo Lateral, facing north. Photo taken February 8, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 47
Photo 93. Overview of J structure, facing south. Photo taken February 4, 2022.

Photo 94. Overview of J Structure, facing west-southwest. Photo taken February 4, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
48 Photo 95. Box Canyon access road across F01, view facing west. Photo taken February 4, 2022.

Photo 96. Box Canyon access road across F01, view facing east. Photo taken February 4, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 49
Photo 97. F07, view facing west. Photo taken June 3, 2022.

Photo 98. Wetland DeterminaƟon Sampling Plot (SP14), view facing southwest. Photo taken February 4, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
50 Photo 99. Overview of F02, a tributary to F01 that originates from an energy dissipator outlet located near MSC-HTP, view facing north. Photo taken June 9, 2022.

Photo 100. Overview of F03, an ephemeral tributary to F01 that originates from erosional flow from MSC-HTP, facing east. Photo taken June 9, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 51
Photo 101. Overview of F05, an ephemeral stream, located parallel to Rancho Conejo, facing southwest. Photo taken January 26, 2022.

Photo 102. Overview of F05, an ephemeral stream as it drains into F01, located parallel to Rancho Conejo, facing southwest. Photo taken January 26, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
52 Photo 103. Overview of F05, an ephemeral stream that crosses under Rancho Conejo via a funcƟonal culvert, facing north. Photo taken June 16, 2022.

Photo 104. No hydrological indicators on Rancho Conejo at the locaƟon where F05 crosses under access road via culvert, view facing northeast. Photo taken June 16, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 53
Photo 105. Bed and development of F06 from accumulaƟon of erosional flow from Rancho Conejo, view facing northwest. Photo taken June 16, 2022.

Photo 106. F08, an ephemeral tributary to F01 that parallels Box Canyon, view facing northwest. Photo taken June 3, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
54 Photo 107. View of F08 that parallels Box Canyon, facing west. Photo taken June 3, 2022.

Photo 108. F08 parallels Box Canyon, view facing west. Photo taken June 3, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 55
Photo 109. Wetland DeterminaƟon Sampling Plot (SP21), view facing southwest. Photo taken June 3, 2022.

Photo 110. FuncƟonal culvert inlet of F10 under Box Canyon, view facing west (downstream). Photo taken June 3, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
56 Photo 111. FuncƟonal culvert outlet of F10 under Box Canyon draining to F8, view facing west (upstream). Photo taken June 3, 2022.

Photo 112. F11 conveys sheet flow across along Box Canyon to F8, view facing northwest (downstream). Photo taken June 3, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 57
Photo 113. Upslope porƟon of F11 is obscured by vegetaƟon. The red lines indicate approximate OHWM boundary of the feature; view facing east (upstream). Photo taken June 3, 2022.

Photo 114. Wetland DeterminaƟon Sampling Plot (SP20) located in the of F01, view facing west. Photo taken June 3, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
58 Photo 115. F15 conveying flow northeast to F01 via a concrete culvert under CitaƟon Way.

Bed facing north. Photo taken June 1, 2022.

Photo 116. F15 conveying flow northeast to F01 via a concrete culvert under CitaƟon Way.

Bed facing southeast. Photo taken June 1, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 59
Photo 117. F14, an ephemeral stream that crosses under CitaƟon Way via a culvert, view facing southeast (downstream). Photo taken June 2, 2022.

Photo 118. Overview of CitaƟon Way access road across F01, facing northeast. Photo taken June 2, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
60 Photo 119. Wetland DeterminaƟon Sampling Plot (SP17), view facing northeast. Photo taken June 2, 2022.

Photo 120. CitaƟon Way access road crossing at F01, view facing northeast. Photo taken June 2, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 61
Photo 121. Overview of F13, an ephemeral tributary to F01 crossing CitaƟon Way as undefinable sheet flow, view facing southwest. Photo taken June 1, 2022.

Photo 122. Overview of F13, crossing CitaƟon Way as undefinable sheet flow, facing southwest. Photo taken June 1, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
62 Photo 123. CitaƟon Way access road across F01, view facing northeast. Photo taken June 1, 2022.

Photo 124. CitaƟon Way access road across F01, view facing northeast. Photo taken June 1, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 63
Photo 125. Overview of CitaƟon Way Road across South Branch Arroyo Conejo (S12), view facing southwest. Photo taken June 1, 2022.

Photo 126. Wetland DeterminaƟon Sampling Plot (SP18) located on a terrace below the OHWM of F12, view facing north. Photo taken June 2, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
64 Photo 127. Wetland DeterminaƟon Sampling Plot (SP19), view facing west. Photo taken June 2, 2022.

Photo 128. Calle Brusca access pathway parallels F01, view facing west. Photo taken May 31, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 65
Photo 129. Calle Brusca access pathway parallels F01, view facing northeast. Photo taken May 31, 2022.

Photo 130. Tunnel access road parallels F01, view facing north. Photo taken May 31, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
66 Photo 131. View of F01 from Tunnel access road, view facing east (upstream). Photo taken May 31, 2022.

Photo 132. View of F01 from Tunnel access road, view facing south (upstream). Photo taken May 31, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 67
Photo 133. View of F01 from Tunnel access road, view facing southeast (upstream). Photo taken May 31, 2022.

Photo 134. View of F01 from Tunnel access road, facing northeast (upstream). Photo taken May 31, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
68 Photo 135. OHWM limits of F01 within the Calle Brusca access road boundary, view facing southwest. Photo taken May 31, 2022.

Photo 136. Riparian vegetaƟon associated with F1 adjacent to Calle Brusca access road, view facing southwest. Photo taken May 31, 2022.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 69
Photo 137. Example of upland habitat adjacent to Calle Brusca access road, view facing southwest. Photo taken May 31, 2022.

Photo 138. Example of upland habitat adjacent to Calle Brusca access road, view facing south. Photo taken May 31, 2022.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
70 Photo 139. Overview of F17 near the east end of the Project Area. Photo facing north. F17, conveys flow west of the pictured access road. F17 supports an oak woodland at this locaƟon.

Photo 140. Perennial flow at F17, approximately 200 feet from the F17-F18 confluence.

Photo facing southeast.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 71
Photo 141. Overview of F17. Photo facing south-southeast looking towards Paradise Falls waterfall. Photo captured near the central porƟon of the Project Area.

Photo 142. Bridge supporƟng access across F18. Photo facing southeast.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
72 Photo 143. Flow at F18. Photo taken from bridge facing south- southeast.

Photo 144. F19 facing upstream (north-northeast). F19 is deeply incised and showcases a shared OHWM/top of bank.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 73
Photo 145. Culvert inlet facilitaƟng F19 flow across exisƟng access road.

Photo 146. Culvert outlet facilitaƟng F19 flow to F17. Photo facing south- southwest.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
74 Photo 147. F20 riparian vegetaƟon abuƫng exisƟng access road. No hydrologic connecƟvity across the road was idenƟfied. Photo facing northwest.

Photo 148. Overview of F20 upslope of access road. Photo facing northwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 75
Photo 149. Overview of F20 downslope of access road. Dense vegetaƟon obscures hydrology indicators. Photo facing east-northeast.

Photo 150. Start of F21 directly downslope of exisƟng access road. Photo facing west.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
76 Photo 151. North of exisƟng access road, upslope of F21. No hydrology indicators. Area was idenƟfied as a non-jurisdicƟonal swale. Photo facing northeast.

Photo 152. F23 culvert inlet providing flow across exisƟng access road. Culvert conveys flow from exisƟng drainage and roadside erosional gully. Photo facing north.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 77
Photo 153. Culvert outlet facilitaƟng F23 flow across exisƟng access road. Photo facing downstream (south).

Photo 154. F23 just before conveying flow onto an exisƟng access road. Photo facing upstream (north).

City of Thousand Oaks
Arroyo Conejo Maintenance Project
78 Photo 155. Water shoot conveying F23 flow away from exisƟng access road and towards F17. Photo facing south-southeast.

Photo 156. Culverts concentraƟng flow from various sources onto F24, a concrete v-ditch.

Photo facing south.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 79
Photo 157. Foot bridge over F24. Photo facing south.

Photo 158. Culvert inlet on east side of access road facilitaƟng F24 flow across the exisƟng access road. Drainage is not concreted downslope of access road. Photo facing north.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
80 Photo 159. F24 culvert outlet approximate locaƟon. Dense vegetaƟon and liƩer obscure culvert outlet. Photo facing northwest.

Photo 160. F25 facing downstream (southeast).

Site Photographs
Habitat Assessment and Jurisdictional Delineation 81
Photo 161. Cleanout #1. Photo facing north-northeast.

Photo 162. SP22 located at shovel locaƟon, examined adjacent to F17 OHWM. Photo facing west-southwest.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
82 Photo 163. SP22 located at shovel locaƟon, examined adjacent to F17 OHWM. Photo facing west-southwest.

Photo 164. SP23 (paired pit associated with SP22) located on elevated terrace just beyond the F17 OHWM. Photo facing northwest.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 83
Photo 165. SP23 (paired pit associated with SP22) at shovel locaƟon examined on elevated terrace just beyond the F17 OHWM. Photo facing northwest.

Photo 166. SP24 examined on terrace adjacent to F17. Photo facing southwest.

City of Thousand Oaks
Arroyo Conejo Maintenance Project
84 Photo 167. SP25 adjacent to F18 OHWM. Photo facing north.

Photo 168. SP26 (paired pit to SP25) examined at orange pole locaƟon within F18. Photo facing east.

Site Photographs
Habitat Assessment and Jurisdictional Delineation 85
Photo 169. SP26 (paired pit to SP25) examined at orange pole locaƟon within F18. Photo facing east.

Appendix C
Species Compendium
Species Compendium
Jurisdictional Delineation and Habitat Assessment C-1
Plant Species Detected in the Study Area
Scientific Name Common Name Lifeform Native Status
Angiosperms (eudicots)
Amaranthaceae Amaranth family
Amaranthus sp. Amaranth Annual herb N/a
Anacardiaceae Sumac family
Malosma laurina Laurel sumac Tree, shrub Native
Rhus integrifolia Lemonade berry Shrub Native
Rhus ovata Sugar bush Shrub Native
Schinus molle Peruvian pepper tree Tree Invasive
Toxicodendron diversilobum Poison oak Vine, shrub Native Apiaceae Umberllifer family
Apium graveolens Celery Annual, biennial herb Non-native Conium maculatum Poison hemlock Perennial herb Invasive Foeniculum vulgare Fennel Perennial herb Invasive
Sanicula sp. Sanicle Perennial herb Native
Apocynaceae Dogbane family
Asclepias fascicularis Narrow leaf milkweed Perennial herb Native Nerium oleander Oleander Tree Invasive
Araliaceae Ivy family
Hedera helix English ivy Vine, shrub Invasive
Asteraceae Sunflower family
Achyrachaena mollis Blow wives Annual herb Native
Acourtia microcephala Sacapellote Perennial herb Native Anthemis cotula Dog fennel Annual herb Invasive
Artemisia californica Coastal sage brush Shrub Native
Artemisia douglasiana California mugwort Perennial herb Native Baccharis pilularis Coyote brush Shrub Native
Baccharis salicifolia Mule fat Shrub Native
Baccharis sarothroides Broom baccharis Shrub Native
Brickellia californica California brickellia Perennial herb Native Carduus pycnocephalus ssp.
pycnocephalus
Italian thistle Annual herb Invasive
Centaurea melitensis Tocalote Annual herb Invasive
Corethrogyne filaginifolia Common sandaster Perennial herb Native Cotula australis Brass buttons Annual herb Non-native
Cotula coronopifolia Brass buttons Perennial herb Invasive Deinandra fasciculata Clustered tarweed Annual herb Native Dimorphotheca fruticosa Trailing african daisy Perennial herb Non-native Encelia californica Bush sunflower Shrub Native
Erigeron canadensis Canadian horseweed Annual herb Native City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
C-2
Scientific Name Common Name Lifeform Native Status
Eriophyllum confertiflorum var.
cofertiflorum
Golden yarrow Shrub Native
Hedypnois rhagadioloides Crete weed Annual herb Non-native Helminthotheca echioides Bristly ox-tongue Annual, perennial herb Invasive Heterotheca grandiflora Telegraph weed Annual, perennial herb Native Isocoma menziesii var. menziesii Menzies’ goldenbush Shrub Native Lactuca serriola Prickly lettuce Annual herb Invasive
Matricaria discoidea Pineapple weed Annual herb Native
Pseudognaphalium biolettii Two-colored rabbit-tobacco Perennial herb Native Pseudognaphalium californicum Ladies’ tobacco Annual, perennial herb Native Pseudognaphalium microcephalum Wright’s cudweed Perennial herb Native Silybum marianum Milk thistle Annual, perennial herb Invasive Solidago velutina ssp. californica Oreja de liebre Perennial herb Native Soncus oleraceus Sow thistle Annual herb Non-native
Streptanomeria sp. Wirelettuce Annual, perennial herb Native Uropappus lindleyi Silver puffs Annual herb Native
Xanthium strumarium Cocklebur Annual herb Native
Betulaceae Birch family
Alnus rhombifolia White alder Tree Native
Boraginaceae Borage family
Amsinckia intermedia Common fiddleneck Annual herb Native Cryptantha sp. Cryptantha Annual herb Native
Pectocarya linearis ssp. ferocula Slender comb seed Annual herb Native Phacelia cicutaria Caterpillar phacelia Annual herb Native Phacelia ramosissima Branching phacelia Perennial herb Native Phacelia viscida Sticky phacelia Annual herb Native
Brassicaeae Mustard family
Capsella bursa-pastoris Shepherd’s purse Annual herb Non-native Hirschfeldia incana Mustard Perennial herb Invasive
Nasturium officinale Watercress Perennial herb (aquatic) Native Raphanus sativus Jointed charlock Annual, biennial herb Invasive Sisymbrium orientale Indian hedge mustard Annual, perennial herb Non-native Cactaceae Cactus family
Cylindropuntia prolifera Coastal cholla Shrub (stem succulent) Native Opuntia littoralis Prickly pear Shrub (stem succulent) Native Opuntia oricola Chaparral pricklypear Shrub (stem succulent) Native Caprifoliaceae Honeysuckle family
Lonicera subspicata var. denudata Johnston’s honeysuckle Shrub Native Symphoricarpos mollis Snowberry Shrub Native
Species Compendium
Jurisdictional Delineation and Habitat Assessment C-3
Scientific Name Common Name Lifeform Native Status
Caryophyllaceae Carnation family
Herniaria hirsuta Herniaria Annual herb Non-native
Polycarpon tetraphylum var. tetraphyllum Four leaved allseed Annual herb Non-native Stellaria media Chickweed Annual herb Non-native
Chenopodiaceae Chenopod family
Atriplex semibaccata Australian saltbush Perennial herb Invasive Salsola tragus Russian thistle Annual herb Invasive
Convolvulaceae Bindweed family
Calystegia macrostegia Island morning glory Perennial herb, vine Native Convolvulus arvensis Field bindweed Perennial herb, vine Invasive Crassulaceae Stonecrop family
Dudleya lanceolata Southern California dudleya Perennial herb Native Dudleya pulverulenta Chalk dudleya Perennial herb Native Curcubitaceae Gourd family
Marah macrocarpa Chilicothe Perennial herb, vine Native Euphorbiaceae Euphorbia family
Euphorbia dendroides Tree spurge Shrub Non-native
Euphorbia lathyris Gopher plant Annual, perennial herb Invasive Euphorbia peplus Petty spurge Annual herb Non-native
Euphorbia spp. Spurge Annual herb Native
Ricinus communis Castor bean Shrub Invasive
Fabaceae Legume family
Acmispon glaber Deerweed Perennial herb Native
Acmispon maritimus Coastal lotus Annual herb Native
Lotus corniculatus Bird’s foot trefoil Perennial herb Invasive Lotus tenuis Narrow-leaf bird’s-foot trefoil Perennial herb Non-native Melilotus albus White sweetclover Annual, biennial herb Invasive Fagaceae Beech family
Quercus agrifolia Coast live oak Tree Native
Quercus berberidifolia Inland scrub oak Tree Native
Quercus lobata Valley oak Tree Native
Geraniaeceae Geranium family
Erodium cicutarium Coastal heron's bill Annual herb Invasive Grossulariaceae Currant family
Ribes speciosum Fuchsia flowered gooseberry Shrub Native Juglandaceae Walnut family
Juglans californica Southern California black walnut Perennial deciduous tree Native (CRPR 4.2) City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
C-4
Scientific Name Common Name Lifeform Native Status
Lamiaceae Mint family
Lamium amplexicaule Henbit Annual herb Non-native
Marrubium vulgare White horehound Perennial herb Invasive Salvia leucophylla Purple sage Shrub Native
Salvia mellifera Black sage Shrub Native
Stachys albens Cobwebby hedge nettle Perennial herb Native Malvaceae Mallow family
Fremontodendron californicum California fremontia Shrub Native Malacothamnus fasciculatus var.
fasciculatus
Chaparral bush mallow Shrub Native
Malva parviflora Cheeseweed Annual herb Non-native
Montiaceae Pussypaw family
Claytonia parviflora ssp. parviflora Miner’s lettuce Annual herb Native Claytonia perfoliata Miner’s lettuce Annual herb Native Myrsinaceae Myrsine family
Lysimachia arvensis Scarlet pimpernel Annual herb Non-native Myrtaceae Myrtle family
Eucalyptus camaldulensis Red gum Tree Invasive
Eucalyptus sp. Gum tree Tree Non-native
Melaleuca viminalis Weeping bottlebrush Tree Non-native Nyctaginaceae Four o’clock Family
Bougainvillea spectabilis Great bougainvillea Shrub Non-native Mirabilis laevis var. crassifolia California four o’clock Perennial herb Native Oleaceae Olive family
Fraxinus americana American ash Tree Non-native
Fraxinus dipetala Two petaled ash Tree, shrub Native
Fraxinus velutina Arizona ash Tree Native
Olea europaea Olive Tree, shrub Invasive
Onagraceae Evening primrose family
Clarkia bottae Punch bowl godetia Annual herb Native
Clarkia unguiculata Woodland clarkia Annual herb Native Epilobium canum ssp. canum California fuchsia Perennial herb Native Epilobium ciliatum ssp. ciliatum Willow herb Perennial herb Native Oenothera elata ssp. hirsutissima Evening primrose Perennial herb Native Oxalidaceae Woodsorrel family
Oxalis pes-caprae Bermuda buttercup Perennial herb Invasive Paeoniaceae Peony family
Paeonia californica California peony Perennial herb Native Papaveraceae Poppy family
Eschscholzia californica California poppy Annual, perennial herb Native Species Compendium
Jurisdictional Delineation and Habitat Assessment C-5
Scientific Name Common Name Lifeform Native Status
Phyrmaceae Lopseed family
Diplacus australis Southern monkeyflower Shrub Native
Erythranthe guttata Yellow monkeyflower Annual, perennial herb (rhizomatous)
Native
Plantaginaceae Plantain family
Keckiella cordifolia Heart leaved keckiella Shrub Native Plantago major Common plantain Perennial herb Non-native Veronica anagallis-aquatica Water speedwell Perennial herb Non-native Platanaceae Plane-tree family
Platanus racemosa California sycamore Tree Native
Polygonaceae Buckwheat family
Eriogonum cinereum Coastal buckwheat Shrub Native
Eriogonum elongatum Longstern buckwheat Perennial herb Native Eriogonum fasciculatum California buckwheat Shrub Native Persicaria sp. Smartweed Annual herb N/a
Polygonum aviculare ssp. depressum Prostrate knotweed Annual, perennial herb Non-native Rumex conglomeratus Green dock Perennial herb Non-native Rumex obtusifolius Broadleaf dock Perennial herb Non-native Rumex sp. Dock Perennial herb N/a
Ranunculaceae Buttercup family
Clematis lasiantha Pipestem Perennial herb, vine Native Clematis ligusticifolia Creek clematis Perennial herb, vine Native Delphinium sp. Spreading larkspur Perennial herb Native Rhamnaceae Buckthorn family
Ceanothus megacarpus var. megacarpus Big pod ceanothus Shrub Native Rhamnus crocea Redberry Shrub Native
Rhamnus ilicifolia Evergreen buckthorn Shrub Native
Rosaceae Rose family
Adenostoma fasciculatum Chamise Tree, shrub Native
Cerocarpus betuloides Mountain-mahogany Perennial evergreen shrub
Native
Eriobotrya japonica Loquat Tree Non-native
Heteromeles arbutifolia Toyon Shrub Native
Prunus ilicifolia Holly leaf cherry Tree, shrub Native
Rosa californica California wild rose Shrub Native
Rubus ursinus California blackberry Vine, shrub Native
Rubiaceae Bedstraw family
Galium aparine Cleavers Annual herb Native
City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
C-6
Scientific Name Common Name Lifeform Native Status
Salicaceae Willow family
Populus fremontii ssp. fremontii Cottonwood Tree Native Populus trichocarpa Black cottonwood Tree Native
Salix exigua Narrowleaf willow Tree, shrub Native
Salix laevigata Polished willow Tree Native
Salix lasiolepis Arroyo willow Tree, shrub Native
Sapindaceae Soapberry family
Acer negundo Boxelder Tree Native
Koelreuteria bipinnata Goldenrain tree Tree Non-native
Scrophulariaceae Figwort family
Myoporum parvifolium Slender myoporum Tree, shrub Non-native Solanaceae Nightshade family
Datura wrightii Jimsonweed Perennial herb Native
Nicotiana glauca Tree tobacco Tree, shrub Invasive
Solanum xanti Nightshade Perennial herb, shrub Native
Ulmaceae Elm family
Ulmus parvifolia Siberian elm Tree Non-native
Utricaceae Nettle family
Hesperocnide tenella Western stinging nettle Annual herb Native Urtica dioica Stinging nettle Perennial herb Native
Urtica urens Annual stinging nettle Annual herb Non-native Viburnaceae Elder family
Sambucus mexicana Blue elderberry Shrub Native
Vitaceae Grape family
Parthenocissus inserta Woodbine Vine, shrub Non-native
Vitis californica California wild grape Vine, shrub Native Angiosperms (magnoliids)
Lauraceae Laurel family
Umellularia californica California bay Tree Native
Saururaceae Lizard’s tail family
Anemopsis californica Yerba mansa Perennial herb Native Angiosperms (monocots)
Agavaceae Agave family
Agave americana American century plant Perennial herb, shrub Non-native Chlorogalum pomeridianum var.
pomeridianum
Common soaproot Perennial herb Native
Hersperoyucca whipplei Chaparral yucca Shrub Native
Araceae Arum family
Lemna minuta Least duckweed Perennial herb Native
Arecaceae Palm family
Washingtonia robusta Mexican fan palm Tree Invasive
Species Compendium
Jurisdictional Delineation and Habitat Assessment C-7
Scientific Name Common Name Lifeform Native Status
Cyperaceae Sedge family
Bolboschoenus maritimus ssp. paludosus Saltmarsh bulrush Perennial grasslike herb Native Cyperus alternifolius ssp. flabelliformis Umbrella papyrus Perennial grasslike herb Non-native Cyperus eragrostis Tall cyperus Perennial grasslike herb Native Eleocharis macrostachya Spike rush Perennial grasslike herb Native Eleocharis sp. Spikerush Perennial grasslike herb Native Schoenoplectus acutus var. occidentalis Tule Perennial grasslike herb Native Schoenoplectus americanus Chairmaker’s bulrush Perennial grasslike herb Native Juncaceae Rushes
Juncus balticus Wire rush Perennial grasslike herb Native Juncus xiphioides Iris leaved rush Perennial grasslike herb Native Liliaceae Lily family
Calchortus clavatus var. clavatus Club-haired mariposa lily Perennial bulbiferous herb
Native (CRPR 4.3)
Poaceae Grass family
Arundo donax Giant reed Perennial grasslike herb Invasive Avena fatua Wildoats Annual grass Invasive
Bromus diandrus Ripgut brome Annual grass Invasive
Bromus hordeaceus Soft chess Annual grass Invasive
Bromus rubens Red brome Annual grass Non-native
Elymus condensatus Giant wild rye Perennial grass Native Festuca perennis Iitalian rye grass Annual, perennial grass Invasive Hordeum murinum Foxtail barley Annual grass Invasive
Leptochola fusca Sprangletop Annual grass Native
Melica imperfecta Coast range melic Perennial grass Native Pennisetum setaceum Fountaingrass Perennial grass Invasive Polypogon monspeliensis Annual beard grass Annual grass Invasive Polypogon viridis Water beard grass Perennial grass Non-native Stipa miliacea var. miliacea Smilo grass Perennial grass Invasive Stipa pulchra Purple needle grass Perennial grass Native Themidaceae Brodiaea family
Dipterostemon capitatus Blue dicks Perennial herb Native Typhaceae Cattail family
Typha domingensis Cattail Perennial herb Native
Bryophytes (Liverworts)
Lunulariaceae
Lunularia cruciate Crescent-cup liverwort Liverwort Non-native Ferns
Nephrolepidaceae Sword fern family
Nephrolepis cordifolia Fishbone fern Fern Non-native
City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
C-8
Wildlife Species Detected in the Study Area
Scientific Name Common Name Native Status
Class Amphibia (Amphibians)
Hylidae Tree Frogs and Allies
Pseudacris hypochondriaca Baja California tree frog Native Ranidae Typical frogs
Lithobates catesbeianus American bullfrog Non-native
Class Aves (Birds)
Accipitridae Hawks, Eagles, and Kites
Buteo jamaicensis Red-tailed hawk Native
Alcedinidae Kingfishers
Megaceryle alcyon Belted kingfisher Native
Anatidae Ducks, Geese, and Swans
Aix sponsa Wood duck Native
Anas platyrhynchos Mallard Native
Bucephala albeola Bufflehead Native
Apodidae Swifts
Aeronautes saxatalis White-throated swift Native
Ardeidae Herons, Egrets, and Bitters
Ardea herodias Great blue heron Native
Cardinalidae Cardinals and Allies
Pheucticus melanocephalus Black-headed grosbeak Native
Cathartidae New world vultures
Cathartes aura Turkey vulture Native
Columbidae Pigeons and Doves
Zenaida macroura Mourning dove Native
Corvidae Crows, Jays, and Magpies
Aphelocoma californica California scrub-jay Native
Corvus branchyrhynchos American crow Native
Corvus corax Common raven Native
Fringillidae Finches, Euphonias, and Allies
Haemorphous mexicanus House finch Native
Spinus psaltria Lesser goldfinch Native
Spinus tristis American goldfinch Native
Hirundinidae Swallows and Martins
Stelgidopteryx serripennis Northern rough-winged swallow Native Odontophoridae New world quails
Callipepla californica California quail Native
Mimidae Mimic Thrushes or Mimids
Mimus polyglottos Northern mockingbird
Paridae Tits, Chickadees, and Titmice
Baeolophus inornatus Oak titmouse Native
Species Compendium
Jurisdictional Delineation and Habitat Assessment C-9
Scientific Name Common Name Native Status
Parulidae New world warblers
Geothlypis trichas Common yellowthroat Native
Leiothlypis celata Orange-crowned warbler Native
Setophaga coronata Yellow-rumped warbler Native
Passerellidae New world sparrows
Junco hyernalis Dark-eyed junco Native
Melospiza melodia Song sparrow Native
Melozone crissalis California towhee Native
Pipilo maculatus Spotted towhee Native
Phalacrocoracidae Typical Cormorants and Shags
Phalacrocorax auritus Double-crested cormorant Native
Picidae Woodpeckers
Colaptes auratus Northern flicker Native
Dryobates nuttallii Nuttall's woodpecker Native
Melanerpes formicivorus Acorn woodpecker Native
Sphyrapicus sp. Sapsucker Native
Polioptilidae Gnatcatchers and Gnatwrens
Polioptila caerulea Blue-grey gnatcatcher Native
Rallidae Rails, Gallinules, and Coots
Fulica americana American coot Native
Regulidae Kinglets
Regulus calendula Ruby-crowned kinglet Native
Sittidae Nuthatches
Sitta carolinensis White-breasted nuthatch Native
Sylviidae Sylviid Warblers and Parrotbills
Chamaea fasciata Wrentit Native
Trochilidae Hummingbirds
Selasphorus sasin Allen’s hummingbird Native
Troglodytidae Wrens
Catherpes mexicanus Canyon wren Native
Thryomanes bewickii Bewick's wren Native
Troglodytes aedon House wren
Tyrannidae Flycatchers
Empidonax difficilis Pacific-slope flycatcher Native
Myiarchus cinerascens Ash-throated flycatcher Native
Sayornis nigricans Black phoebe Native
Sayornis saya Say’s phoebe Native
City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project
C-10
Scientific Name Common Name Native Status
Class Insecta (Insects)
Apidae Honey Bees, Bumble Bees, and Allies
Apis mellifera Western honey bee Non-native
Bombus vosnesenskii Yellow-faced bumble bee Native
Chrysomelidae Leaf beetles
Chrysomelidae sp. Leaf beetle N/a
Coccinellinae Lady beetles
Coccinella septempunctata Seven-spotted lady beetle Non-native Coenagrionidae Narrow-winged Damselflies
Coenagrionidae sp. Narrow-winged damselfly N/a
Cynipidae Gall wasps
Cynips douglasii Spined turban gall wasp Native
Geometridae Geometer moths
Nemoria leptalea Emerald moth Native
Hesperiidae Skippers
Erynnis tristis Mournful duskywing Native
Lygaeidae Seed bugs
Oncopeltus fasciatus Large milkweed bug Native
Papilionidae Swallowtails and Parnassians
Papilio rutulus Western tiger swallowtail Native
Pentatomidae Stink bugs
Asopinae sp. Predatory stink bug N/a
Pieridae Whites, Yellows, and Sulfurs
Colias sp. Clouded yellow N/a
Syrphidae Hover flies
Copestylum violaceum Purple bromeliad fly Native
Tenebrionidae Darkling beetles
Coelocnemis dilaticollis California broad-necked darkling beetle Native Class Malacostracans
Cambaridae Cambarid crayfishes
Camparidae sp. Crawfish N/a
Class Mammalia (Mammals)
Canidae Canids
Canis latrans Coyote Native
Urocyon cinereoargenteus Gray fox Native
Cervidae Deers
Odocoileus hernionus Mule deer Native
Cricetidae New World Mice and Rats
Neotoma sp.* Pack rat Native
Leporidae Rabbits and Hares
Sylvilagus audubonii Desert cottontail Native
Species Compendium
Jurisdictional Delineation and Habitat Assessment C-11
Scientific Name Common Name Native Status
Sciuridae Squirrels
Otospermophilus beecheyi California ground squirrel Native Class Reptilia (Reptiles)
Emydidae Pond and Box Turtles
Trachemys scripta ssp. elegans Red-eared slider Non-native Phrynosomatidae Phrynosomatid lizards
Sceloporus occidentalis Western fence lizard Native
Uta stansburiana Common side-blotched lizard Native
Teiidae Whiptails and Tegus
Aspidoscelis tigris stejnegeri Coastal whiptail Native
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Appendix D
Regulatory Setting
Regulatory Setting
Jurisdictional Delineation and Habitat Assessment D-1
Regulatory Setting
The following is a brief summary of the regulatory context under which biological resources are managed at the federal, state, and local levels. A number of federal and state statutes provide a regulatory structure that guides the protection of biological resources. Agencies with the responsibility for protection of biological resources within the Study Area include:
ƒ U.S. Army Corps of Engineers (wetlands and other waters of the United States); ƒ U.S. Fish and Wildlife Service (federally listed species and migratory birds); ƒ Colorado River Regional Water Quality Control Board (waters of the State); ƒ California Department of Fish and Wildlife (riparian areas, streambeds, and lakes; state-listed species; nesting birds, marine resources); and
ƒ The City of Coachella
United States Army Corps of Engineers Jurisdiction
The United States Army Corps of Engineers (USACE) is responsible for administering several federal programs related to ensuring the quality and navigability of the nation’s waters.

Clean Water Act Section 404
Congress enacted the Clean Water Act (CWA) “to restore and maintain the chemical, physical, and biological integrity of the Nation’s waters.” Section 404 of the CWA authorizes the Secretary of the Army, acting through the USACE, to issue permits regulating the discharge of dredged or fill materials into the “navigable waters at specified disposal sites.” Section 502 of the CWA further defines “navigable waters” as “waters of the United States, including the territorial seas.” “Waters of the United States” are broadly defined at 33 CFR Part 328.3 to include navigable, tidal, and interstate waters and certain impoundments, tributaries, and wetlands. The agencies’ most recent regulatory definition of the term was promulgated in January 2023, following failed attempts in prior years that had been frustrated by legal challenges. However, in May 2023 the U.S. Supreme Court issued its ruling in Sackett v. Environmental Protection Agency, which invalidated portions of the updated regulations. To address this ruling, in September 2023 the agencies issued a “conforming rule” (88 FR 61964-61969) modifying their definition of “waters of the United States” to comport with the Court’s ruling. This definition is described in detail below.

Waters of the U.S.

Current USACE and USEPA regulations, reflecting of the January 2023 definition as modified by the September 2023 Conforming Rule, define “waters of the United States” as follows (33 CFR 328.3; see also 88 FR 61964-61969):
(1) Waters which are:
(i) Currently used, or were used in the past, or may be susceptible to use in interstate or foreign commerce, including all waters which are subject to the ebb and flow of the tide; City of Thousand Oaks
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(ii) The territorial seas; or
(iii) Interstate waters;
(2) Impoundments of waters otherwise defined as waters of the United States under this definition, other than impoundments of waters identified under paragraph (a)(5) of this section; (3) Tributaries of waters identified in paragraph (a)(1) or (2) of this section that are relatively permanent, standing or continuously flowing bodies of water; (4) Wetlands adjacent to the following waters:
(I) Waters identified in paragraph (a)(1) of this section; or (ii) Relatively permanent, standing or continuously flowing bodies of water identified in paragraph (a)(2) or (a)(3) of this section and with a continuous surface connection to those waters;
(5) Intrastate lakes and ponds, not identified in paragraphs (a)(1) through (4) of this section that are relatively permanent, standing or continuously flowing bodies of water with a continuous surface connection to the waters identified in paragraph (a)(1) or (a)(3) of this section.

The definition specifies that the following features are not “waters of the United States” even where they otherwise meet the terms of provisions (2) through (5) above:
(1) Waste treatment systems, including treatment ponds or lagoons, designed to meet the requirements of the Clean Water Act;
(2) Prior converted cropland designated by the Secretary of Agriculture. The exclusion would cease upon a change of use, which means that the area is no longer available for the production of agricultural commodities. Notwithstanding the determination of an area’s status as prior converted cropland by any other Federal agency, for the purposes of the Clean Water Act, the final authority regarding Clean Water Act jurisdiction remains with EPA; (3) Ditches (including roadside ditches) excavated wholly in and draining only dry land and that do not carry a relatively permanent flow of water;
(4) Artificially irrigated areas that would revert to dry land if the irrigation ceased; (5) Artificial lakes or ponds created by excavating or diking dry land to collect and retain water and which are used exclusively for such purposes as stock watering, irrigation, settling basins, or rice growing;
(6) Artificial reflecting or swimming pools or other small ornamental bodies of water created by excavating or diking dry land to retain water for primarily aesthetic reasons; (7) Waterfilled depressions created in dry land incidental to construction activity and pits excavated in dry land for the purpose of obtaining fill, sand, or gravel unless and until the construction or excavation operation is abandoned and the resulting body of water meets the definition of waters of the United States; and
(8) Swales and erosional features (e.g., gullies, small washes) characterized by low volume, infrequent, or short duration flow.

The lateral limits of USACE jurisdiction in non-tidal waters is defined by the “ordinary high-water mark” (OHWM) unless adjacent wetlands are present. The OHWM is a line on the shore or edge of a channel established by the fluctuations of water and indicated by physical characteristics such as a clear, natural line impressed upon the bank, shelving, changes in the character of soil, destruction of vegetation, or the presence of debris (33 CFR 328.3(c)(1)). As such, waters are recognized in the Regulatory Setting
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field by the presence of a defined watercourse with appropriate physical and topographic features.

If wetlands occur within, or adjacent to, waters of the United States, the lateral limits of USACE jurisdiction extend beyond the OHWM to the outer edge of the wetlands (33 CFR 328.4 (c)). The upstream limit of jurisdiction in the absence of adjacent wetlands is the point beyond which the OHWM is no longer perceptible (33 CFR 328.4; see also 51 FR 41217).

Wetlands
The USACE defines wetlands as “those areas that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions” (33 CFR 328.3(c)(1)). The USACE’s delineation procedures identify wetlands in the field based on indicators of three wetland parameters: hydrophytic vegetation, hydric soils, and wetland hydrology. The following is a discussion of each of these parameters.

Hydrophytic Vegetation
Hydrophytic vegetation dominates areas where frequency and duration of inundation or soil saturation exerts a controlling influence on the plant species present. Plant species are assigned wetland indicator status according to the probability of their occurring in wetlands. More than 50 percent of the dominant plant species must have a wetland indicator status to meet the hydrophytic vegetation criterion. The USACE published the National Wetland Plant List (USACE 2018), which separates vascular plants into the following four basic categories based on plant species frequency of occurrence in wetlands:
ƒ Obligate Wetland (OBL). Almost always occur in wetlands ƒ Facultative Wetland (FACW). Usually occur in wetlands, but occasionally found in non-wetlands ƒ Facultative (FAC). Occur in wetlands or non-wetlands
ƒ Facultative Upland (FACU). Usually occur in non-wetlands, but may occur in wetlands ƒ Obligate Upland (UPL). Almost never occur in wetlands The USACE considers OBL, FACW and FAC species to be indicators of wetlands. An area is considered to have hydrophytic vegetation when greater than 50 percent of the dominant species in each vegetative stratum (tree, shrub, and herb) fall within these categories. Any species not appearing on the United States Fish and Wildlife Service’s list is assumed to be an upland species, almost never occurring in wetlands. In addition, an area needs to contain at least five percent vegetative cover to be considered as a vegetated wetland.

Hydric Soils
Hydric soils are saturated or inundated for a sufficient duration during the growing season to develop anaerobic or reducing conditions that favor the growth and regeneration of hydrophytic vegetation. Field indicators of wetland soils include observations of ponding, inundation, saturation, dark (low chroma) soil colors, bright mottles (concentrations of oxidized minerals such as iron), gleying (indicates reducing conditions by a blue-grey color), or accumulation of organic material.

Additional supporting information includes documentation of soil as hydric or reference to wet conditions in the local soils survey, both of which must be verified in the field.

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Wetland Hydrology
Wetland hydrology is inundation or soil saturation with a frequency and duration long enough to cause the development of hydric soils and plant communities dominated by hydrophytic vegetation.

If direct observation of wetland hydrology is not possible (as in seasonal wetlands), or records of wetland hydrology are not available (such as stream gauges), assessment of wetland hydrology is frequently supported by field indicators, such as water marks, drift lines, sediment deposits, or stream patterns in wetlands.

Limitations on Jurisdiction based on Sackett v. USEPA Supreme Court On May 25, 2023, the Supreme Court issued its decision on the petition from the Sacketts, a family in Idaho that was subject to a compliance order from the USEPA for backfilling their lot near Priest Lake, which the USEPA claimed contained federally regulated wetlands. The wetlands in question were adjacent to a ditch that fed a creek that ultimately drained into Priest Lake, a navigable water body. The USEPA asserted that the Sacketts had violated the law by filling the wetlands on their property without a permit. The Court’s decision addressed controversy over whether, and under what conditions, the CWA reaches navigable waters’ tributaries or adjacent wetlands. The Supreme Court’s decision in Sackett provides definitive guidance to the agencies in determining the limits of their Clean Water Act authority. Major tenets of the decision have been incorporated into the agencies’ current regulations through the September 2023 Conforming Rule.

The Court decided:
ƒ “Adjacent wetlands” are WOTUS only if there is a continuous surface connection between the wetland and a navigable or relatively permanent water body, such that it is difficult to determine the boundary between the wetland and the water body. The opinion notes that “temporary interruptions to surface connection may sometimes occur because of phenomena like low tides or dry spells.” The agencies addressed this element by defining the term “adjacent” to mean “having a continuous surface connection” in the Conforming Rule. ƒ The Significant Nexus Standard, introduced by the Court in prior decisions, is not mentioned in the Clean Water Act and should not be used. The Court determined that the standard applies ecological factors whose use in determining jurisdiction is not supported by the statute. The Conforming Rule removed significant nexus considerations from the definition. ƒ Although jurisdiction over tributaries was not addressed by the Court, the decision stated that “…the [Clean Water Act’s] use of “waters” encompasses only those relatively permanent, standing or continuously flowing bodies of water forming geographical features that are described in ordinary parlance as streams, oceans, rivers, and lakes.” The Conforming Rule makes clear that only relatively permanent tributaries qualify as “waters of the United States.” Rivers and Harbors Act Section 10
Section 10 of the Rivers and Harbors Act of 1899 requires authorization from the USACE for the construction of any structure in or over any navigable water of the United States. Structures or work outside the limits defined for navigable waters of the United States require a Section 10 permit if the structure or work affects the course, location, or condition of the water body. The law applies to any dredging or disposal of dredged materials, excavation, filling, re-channelization, or any other modification of a navigable water of the United States and applies to all structures and work. It further includes, without limitation, any wharf, dolphin, weir, boom breakwater, jetty, groin, bank protection (e.g. riprap, revetment, bulkhead), mooring structures such as pilings, aerial or Regulatory Setting
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subaqueous power transmission lines, intake or outfall pipes, permanently moored floating vessel, tunnel, artificial canal, boat ramp, aids to navigation, and any other permanent, or semi-permanent obstacle or obstruction. It is important to note that Section 10 applies only to navigable waters, and thus does not apply to work in non-navigable wetlands or tributaries. In some cases, Section 10 authorization is issued by the USACE concurrently with CWA Section 404 authorization, such as when certain Nationwide Permits are used.

Regional Water Quality Control Board
The State Water Resources Control Board (SWRCB) and nine Regional Water Quality Control Boards (RWQCBs) have jurisdiction over “waters of the State,” which are defined as any surface water or groundwater, including saline waters, within the boundaries of the state (California Water Code sec. 13050(e)). These agencies also have responsibilities for administering portions of the CWA.

Clean Water Act Section 401
Section 401 of the CWA requires an applicant requesting a federal license or permit for an activity that may result in any discharge into navigable waters (such as a Section 404 Permit) to provide state certification that the proposed activity will not violate state and federal water quality standards. In California, CWA Section 401 Water Quality Certification (Section 401 Certification) is issued by the RWQCBs and by the SWRCB for multi-region projects. The process begins when an applicant requests a pre-application meeting with the RWQCB, waits no less than 30 days, and then submits an application to the RWQCB and informs the USACE (or the applicable agency from which a license or permit was requested) that an application has been submitted. The USACE will then determine a “reasonable period of time” for the RWQCB to act on the application; this is typically 60 days for routine projects and longer for complex projects but may not exceed one year. Under current regulations, once initiated, the reasonable period of time cannot be stopped or paused.

When the period has elapsed, if the RWQCB has not either issued or denied the application for Section 401 Certification, the USACE may determine that Certification has been waived and issue the requested permit. If a Section 401 Certification is issued it may include binding conditions, imposed either through the Certification itself or through the requested federal license or permit.

Porter-Cologne Water Quality Control Act
The Porter-Cologne Water Quality Control Act (Porter-Cologne Act) is the principal law governing water quality regulation in California. It establishes a comprehensive program to protect water quality and the beneficial uses of water. The Porter-Cologne Act applies to surface waters, wetlands, and ground water and to both point and nonpoint sources of pollution. Pursuant to the PorterCologne Act (California Water Code section 13000 et seq.), the policy of the State is as follows:
ƒ The quality of all the waters of the State shall be protected ƒ All activities and factors affecting the quality of water shall be regulated to attain the highest water quality within reason
ƒ The State must be prepared to exercise its full power and jurisdiction to protect the quality of water in the State from degradation
The State Water Resources Control Board (SWRCB) works in coordination with nine Regional Water Quality Control Boards (RWQCBs) to preserve, protect, enhance, and restore water quality throughout the state. Each RWQCB makes decisions related to water quality for its region, and may City of Thousand Oaks
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approve, with or without conditions, or deny projects that could affect waters of the State. Their authority to regulate activities that could result in a discharge of dredged or fill material comes from the CWA and the Porter-Cologne Water Quality Act.

The Porter-Cologne Water Quality Act broadly defines waters of the State as “any surface water or groundwater, including saline waters, within the boundaries of the state” (SWRCB 2023). Because the act applies to any water, whereas the CWA applies only to certain waters, California’s jurisdictional reach overlaps and may exceed the boundaries of waters of the United States. For example, Water Quality Order No. 2004-0004-DWQ states that “shallow” waters of the State include headwaters, wetlands, and riparian areas. In practice, the RWQCBs may claim jurisdiction over riparian areas. Where riparian habitat is not present, such as may be the case at headwaters and urbanized areas, jurisdiction is taken to the top of bank. Within the region of the project site, the SWRCB and the local Santa Ana RWQCB have jurisdiction over waters of the State, with federal authority under CWA Section 401 and State authority under the Porter-Cologne Water Quality Act.

The SWRCB adopted a State Wetland Definition and Procedures for Discharges of Dredged or Fill Material to waters of the State, for inclusion in the forthcoming Water Quality Control Plan for Inland Surface Waters and Enclosed Bays and Estuaries and Ocean Waters of California. The Procedures consist of four major elements: a wetland definition; a framework for determining if a feature that meets the wetland definition is a water of the State; wetland delineation procedures; and procedures for the submittal, review and approval of applications for Water Quality Certifications and Waste Discharge Requirements for dredge or fill activities (SWRCB 2019).

Pursuant to Section 401 of the CWA, projects regulated by USACE must obtain a Water Quality Certification from the RWQCB. This certification ensures the proposed project will uphold State water quality standards. Because California’s jurisdiction to regulate its water resources is much broader than that of the federal government, proposed impacts on waters of the State require Water Quality Certification even if the area occurs outside of USACE jurisdiction.

Non-Wetland Waters of the State
The SWRCB and RWQCBs have not established regulations for field determinations of waters of the state except for wetlands currently. In many cases the RWQCBs interpret the limits of waters of the State to be bounded by the OHWM unless isolated conditions or ephemeral waters are present.

However, in the absence of statewide guidance each RWQCB may interpret jurisdictional boundaries within their region and the SWRCB has encouraged applicants to confirm jurisdictional limits with their RWQCB before submitting applications. As determined by the Colorado River RWQCB, the lateral limits of waters of the State is consistent with the OHWM, similar to the USACE.

Wetland Waters of the State
Procedures for defining wetland waters of the State pursuant to the SWRCB’s State Wetland Definition and Procedures for Discharges of Dredged or Fill Material to Waters of the State went into effect May 28, 2020. The SWRCB defines an area as wetland if, under normal circumstances:

1. the area has continuous or recurrent saturation of the upper substrate caused by groundwater, or shallow surface water, or both;

2. the duration of such saturation is sufficient to cause anaerobic conditions in the upper substrate; and

3. the area’s vegetation is dominated by hydrophytes or the area lacks vegetation.

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The SWRCB’s Implementation Guidance for the Wetland Definition and Procedures for Discharges of Dredge and Fill Material to Waters of the State (2020), states that waters of the U.S. and waters of the State should be delineated using the standard USACE delineation procedures, taking into consideration that the methods shall be modified only to allow for the fact that a lack of vegetation does not preclude an area from meeting the definition of a wetland.

United States Fish and Wildlife Service
The United States Fish and Wildlife Service (USFWS) implements several laws protecting the Nation’s fish and wildlife resources, including the Endangered Species Act (ESA; 16 United States Code [USC] Sections 153 et seq.), the Migratory Bird Treaty Act (MBTA; 16 USC Sections 703-711) and the Bald and Golden Eagle Protection Act (16 USC Section 668).

Endangered Species Act
The USFWS and National Marine Fisheries Service (NMFS) share responsibility for implementing the ESA. Generally, the USFWS implements the ESA for terrestrial and freshwater species, while the NMFS implements the ESA for marine and anadromous species. Projects that would result in “take” of any threatened or endangered animal species, or a threatened or endangered plant species if occurring on federal land, are required to obtain permits from the USFWS or NMFS through either Section 7 (interagency consultation with a federal nexus) or Section 10 (Habitat Conservation Plan) of the ESA, depending on the involvement by the federal government in funding, authorizing, or carrying out the Project. The permitting process is used to determine if a Project would jeopardize the continued existence of a listed species and what measures would be required to avoid jeopardizing the species. “Take” under federal definition means to harass, harm (which includes habitat modification), pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in any such conduct. Proposed or candidate species do not have the full protection of the ESA; however, the USFWS and NMFS advise Project applicants that they could be elevated to listed status at any time.

Migratory Bird Treaty Act
The MBTA of 1918 implements four international conservation treaties that the U.S. entered into with Canada in 1916, Mexico in 1936, Japan in 1972, and Russia in 1976. It is intended to ensure the sustainability of populations of all protected migratory bird species. The law has been amended with the signing of each treaty, as well as when any of the treaties were amended, such as with Mexico in 1976 and Canada in 1995. The MBTA prohibits the take (including killing, capturing, selling, trading, and transport) of protected migratory bird species without prior authorization by the USFWS.

The list of migratory bird species protected by the law, in regulations at 50 CFR Part 10.13, is primarily based on bird families and species included in the four international treaties. A migratory bird species is included on the list if it meets one or more of the following criteria:
ƒ It occurs in the United States or U.S. territories as the result of natural biological or ecological processes and is currently, or was previously listed as, a species or part of a family protected by one of the four international treaties or their amendments; ƒ Revised taxonomy results in it being newly split from a species that was previously on the list, and the new species occurs in the United States or U.S. territories as the result of natural biological or ecological processes; or
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ƒ New evidence exists for its natural occurrence in the United States or U.S. territories resulting from natural distributional changes and the species occurs in a protected family.

In 2004, the Migratory Bird Treaty Reform Act limited the scope of the MBTA by stating the MBTA applies only to migratory bird species that are native to the United States or U.S. territories, and that a native migratory bird species is one that is present as a result of natural biological or ecological processes. The MBTRA requires the USFWS to publish a list of all non-native, humanintroduced bird species to which the MBTA does not apply, and an updated list was published in 2020. The 2020 update identifies species belonging to biological families referred to in treaties the MBTA implements but are not protected because their presence in the United States or U.S. territories is solely the result of intentional or unintentional human-assisted introductions.

Bald and Golden Eagle Protection Act
The Bald and Golden Eagle Protection Act prohibits anyone, without a permit issued by the USFWS, from “taking” bald or golden eagles, including their parts (including feathers), nests, or eggs. The Act provides criminal penalties for persons who “take, possess, sell, purchase, barter, offer to sell, purchase or barter, transport, export or import, at any time or any manner, any bald eagle ... [or any golden eagle], alive or dead, or any part, nest, or egg thereof.” The Act defines “take” as “pursue, shoot, shoot at, poison, wound, kill, capture, trap, collect, molest or disturb.” “Disturb” means “to agitate or bother a bald or golden eagle to a degree that causes, or is likely to cause, based on the best scientific information available, 1) injury to an eagle, 2) a decrease in its productivity, by substantially interfering with normal breeding, feeding, or sheltering behavior, or 3) nest abandonment, by substantially interfering with normal breeding, feeding, or sheltering behavior.”
In addition to immediate impacts, this definition also covers impacts that result from humaninduced alterations initiated around a previously used nest site during a time when eagles are not present, if, upon the eagle’s return, such alterations agitate or bother an eagle to a degree that interferes with or interrupts normal breeding, feeding, or sheltering habits, and causes injury, death or nest abandonment.

California Department of Fish and Wildlife
The California Department of Fish and Wildlife (CDFW) derives its authority from the Fish and Game Code of California and administers several State laws protecting fish and wildlife resources and the habitats upon which they depend.

California Endangered Species Act
The California Endangered Species Act (CESA) (Fish and Game Code Section 2050 et. seq.) prohibits take of state listed threatened or endangered. Take under CESA is defined as “Hunt, pursue, catch, capture, or kill, or attempt to hunt, pursue, catch, capture, or kill” (Fish and Game Code sec. 86).

This definition does not prohibit indirect harm by way of habitat modification, except where such harm is the proximate cause of death of a listed species. Where incidental take would occur during construction or other lawful activities, CESA allows the CDFW to issue an Incidental Take Permit upon finding, among other requirements, that impacts to the species have been minimized and fully mitigated. Unlike the federal ESA, CESA’s protections extend to candidate species during the period Regulatory Setting
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(typically one year) while the California Fish and Game Commission decides whether the species warrants CESA listing.

Native Plant Protection Act
The CDFW also has authority to administer the Native Plant Protection Act (NPPA) (Fish and Game Code Section 1900 et seq.). The NPPA requires the CDFW to establish criteria for determining if a species, subspecies, or variety of native plant is endangered or rare, and prohibits the take of listed plant species. Effective in 2015, CDFW promulgated regulations (14 CCR 786.9) under the authority of the NPPA, establishing that the CESA’s permitting procedures would be applied to plants listed under the NPPA as “Rare.” With this change, there is little practical difference for the regulated public between plants listed under CESA and those listed under the NPPA.

Fully Protected Species Laws
The CDFW enforces Sections 3511, 4700, 5050, and 5515 of the Fish and Game Code, which prohibit take of species designated as Fully Protected. The CDFW is not allowed to issue an Incidental Take Permit for Fully Protected species; therefore, impacts to these species must be avoided. The exception is situations where a Natural Community Conservation Plan (NCCP) is in place that authorizes take of the fully protected species.

Avian Protection Laws
California Fish and Game Code sections 3503, 3503.5, and 3513 describe unlawful take, possession, or destruction of native birds, nests, and eggs. Section 3503.5 of the Code protects all birds-of-prey and their eggs and nests against take, possession, or destruction of nests or eggs. Section 3513 makes it a state-level offense to take any bird in violation of the federal Migratory Bird Treaty Act.

Protection of Lakes and Streambeds
California Fish and Game Code section 1602 states that it is unlawful for any person to “substantially divert or obstruct the natural flow of, or substantially change or use any material from the bed, channel, or bank of, any river, stream, or lake” without first notifying the CDFW of that activity.

Thereafter, if CDFW determines and informs the entity that the activity will not substantially adversely affect any existing fish or wildlife resources, the entity may commence the activity. If, however, CDFG determines that the activity may substantially adversely affect an existing fish or wildlife resource, the entity may be required to obtain from CDFW a Streambed Alteration Agreement (SAA), which will include reasonable measures necessary to protect the affected resource(s), before the entity may conduct the activity described in the notification. Upon receiving a complete Notification of Lake/Streambed Alteration, CDFW has 60 days to present the entity with a Draft SAA. Upon review of the Draft SAA by the applicant, any problematic terms are negotiated with CDFW and a final SAA is executed.

The CDFW has not defined the term “stream” for the purposes of implementing its regulatory program under Section 1602, and the agency has not promulgated regulations directing how jurisdictional streambeds may be identified, or how their limits should be delineated. However, four relevant sources of information offer insight as to the appropriate limits of CDFW jurisdiction as discussed below:

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ƒ The plain language of Section 1602 of CFGC establishes the following general concepts:
▫ References “river,” “stream,” and “lake”
▫ References “natural flow”
ƒ References “bed,” “bank,” and “channel”
ƒ Applicable court decisions, in particular Rutherford v. State of California (188 Cal App. 3d 1276); 1987), which interpreted Section 1602’s use of “stream” to be as defined in common law. The Court indicated that a “stream” is commonly understood to:
▫ Have a source and a terminus
▫ Have banks and a channel
▫ Convey flow at least periodically, but need not flow continuously and may at times appear outwardly dry
▫ Represent the depression between the banks worn by the regular and usual flow of the water
▫ Include the area between the opposing banks measured from the foot of the banks from the top of the water at its ordinary stage, including intervening sand bars ▫ Include the land that is covered by the water in its ordinary low stage ▫ Include lands below the OHWM
ƒ CDFW regulations defining “stream” for other purposes, including sport fishing (14 CCR 1.72) and streambed alterations associated with cannabis production (14 CCR 722(c)(21)), which indicate that a stream:
▫ Flows at least periodically or intermittently
▫ Flows through a bed or channel having banks
▫ Supports fish or aquatic life
▫ Can be dry for a period of time
▫ Includes watercourses where surface or subsurface flow supports or has supported riparian vegetation
ƒ Guidance documents, including A Field Guide to Lake and Streambed Alteration Agreements (CDFG 1994) and Methods to Describe and Delineate Episodic Stream Processes on Arid Landscapes for Permitting Utility-Scale Solar Power Plants (Brady and Vyverberg 2013), which suggest the following:
▫ A stream may flow perennially or episodically
▫ A stream is defined by the course in which water currently flows, or has flowed during the historic hydrologic course regime (approximately the last 200 years) ▫ Width of a stream course can reasonably be identified by physical or biological indicators ▫ A stream may have one or more channels (single thread vs. compound form) ▫ Features such as braided channels, low-flow channels, active channels, banks associated with secondary channels, floodplains, islands, and stream-associated vegetation, are interconnected parts of the watercourse
▫ Canals, aqueducts, irrigation ditches, and other means of water conveyance can be considered streams if they support aquatic life, riparian vegetation, or stream-dependent terrestrial wildlife
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▫ Biologic components of a stream may include aquatic and riparian vegetation, all aquatic animals including fish, amphibians, reptiles, invertebrates, and terrestrial species which derive benefits from the stream system
▫ The lateral extent of a stream can be measured in different ways depending on the particular situation and the type of fish or wildlife resource at risk The tenets listed above, among others, are applied to establish the boundaries of streambeds in various environments. Importance of each factor may be weighted based on site-specific considerations and the applicability of the indicators to the streambed at hand.

Local Policies and Ordinances
City of Thousand Oaks General Plan
The Conservation Element of the Thousand Oaks General Plan (City of Thousand Oaks 2013) helps identify human activities that affect natural resources both directly and indirectly and define various policies and implementation measures by which these natural resources can be conserved within the Planning Area. The following are local policies that may be considered as part of the proposed project review:
ƒ CO-10: Streams and creeks should be protected as open space and maintained in as natural a state as possible, and appropriate measures taken to manage urban runoff, in order to protect the City's and other downstream communities' water quality, wildlife diversity, native vegetation, and aesthetic value. This will contribute to the regional effort to improve the quality of Calleguas Creek, Malibu Creek and Mugu Lagoon.
ƒ CO-13: Use of concrete for flood control improvements in natural stream courses should occur only when no reasonable alternatives can be found that would maintain natural hydrological and ecological functions.
ƒ CO-15: Every effort shall be made to design and construct stormwater retention and debris basins to minimize any potentially adverse impacts to significant landform features, aquatic resources, and associated native plant and animal communities. ƒ CO-21: The City shall encourage the proper management, conservation and protection of native plant communities throughout the City's Planning Area, including developed areas and undeveloped open space lands.
ƒ CO-23: Critical wildlife habitat resources such as movement corridors, surface water impoundments, streams and springs should be given special consideration for protection, restoration or enhancement, in order to maintain biodiversity, biological productivity and ecological integrity of natural open space areas.
ƒ CO-25: The City should foster an holistic approach to conservation of wildlife resources including consideration of biological crusts and pollinator species in recognition of the many important functions they perform in a healthy ecosystem.
ƒ CO-26: Isolation and fragmentation of natural open space areas should be prevented wherever possible.
ƒ CO-27: Since natural stream streams often serve as important movement corridors for wildlife, they should be preserved wherever it is feasible to do so.

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ƒ CO-28: Urban land uses adjoining natural open space areas should be designed in a manner that is sensitive to the needs of wildlife and avoids or minimizes any potentially adverse impacts to movement corridors.
ƒ CO-29: Continue to protect oak and landmark trees and their habitat in recognition of their historic, aesthetic and environmental value to the citizens of Thousand Oaks, in particular Valley Oak habitat.
ƒ CO-30: Preserve wetlands and associated wetland buffers as open space and maintain these areas in a natural state to protect the community's water quality, biodiversity and aesthetic value.
ƒ CO-31: Encourage the restoration and enhancement of degraded wetland and riparian habitats in order to conserve and protect native plant and animal species, increase biological diversity and productivity, and maintain permanent access for wildlife to surrounding open space. ƒ CO-32: The City shall encourage and promote the conservation and protection of all rare, threatened, endangered or sensitive species listed by State and Federal agencies (United States Fish and Wildlife Service and California Department of Fish and Wildlife), the California Native Plant Society (CNPS), the County of Ventura and the City of Thousand Oaks.

City of Thousand Oaks Oak Tree Preservation and Protection Title 9, Chapter 4, Article 42, Sec.9-4.4200 of The City of Thousand Oaks municipal code contains the Oak Tree Preservation and Protection policy of the City, which requires the preservation of all healthy oak trees. Any oak tree of the genus Quercus that exceeds 2 inches in diameter when measured at a point 4.5 feet above the tree's natural grade is protected and requires permitting for removal, cutting, pruning and/or encroachment into the protected zone of the oak tree (5 feet outside of the dripline and extending inwards to the trunk of the tree, but not less than 15 feet from the trunk of an oak tree).

City of Thousand Oaks Landmark Tree Preservation and Protection Title 9, Chapter 4, Article 43, Sec.9-4.4300 of The City of Thousand Oaks municipal code contains the Landmark Tree Preservation and Protection policy of the City to require the preservation of all landmark trees. Landmark trees are protected and require a permit for removal, cutting, pruning, and/or encroachment into the protected zone (5 feet outside of the dripline and extending inwards to the trunk of the tree, but not less than 15 feet from the trunk of a tree) if the diameter measured at 4.5 feet above the natural grade at the base of a tree exceeds 12 inches for Platanus racemosa, (California sycamore), or 8 inches for Umbellularia californica (California bay laurel), Juglans californica (California black walnut), and Heteromeles arbutifolia (toyon). Trees with multiple trunks shall be deemed to have reached maturity if the sum of the diameters of the multiple trunks exceed the required diameter plus 2 inches of a single trunked tree. Landmark trees also include all designated historic trees. Likewise, landmark trees also include any tree(s), of any type, designated as landmark trees by the Planning Commission or City Council during review of any land use entitlement request and which trees are required to be preserved as a condition of that City approved entitlement, land division, or tract map. This designation shall continue whether or not the use for which the entitlement is issued is inaugurated or the land division or tract map is recorded.

Appendix E
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Appendix F
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^Z/ĂŶĚŝƚƐůŝĐĞŶƐŽƌƐΞϮϬϮϱ͘ĚĚŝƚŝŽŶĂůĚĂƚĂƉƌŽǀŝĚĞĚďLJE,͕ϮϬϮϱ m Ϭ ϮϬϬ ϭϬϬ &ĞĞƚ
WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚhƚŝůŝƚLJ&ĂĐŝůŝƚLJWĞĚĞƐƚƌŝĂŶWĂƚŚ
E,&ůŽǁůŝŶĞ
^ƚƌĞĂŵͬZŝǀĞƌ
sĞŐĞƚĂƚŝŽŶŽŵŵƵŶŝƚŝĞƐ
ĂůŝĨŽƌŶŝĂ^ĂŐĞďƌƵƐŚͲ;WƵƌƉůĞ^ĂŐĞͿ^ĐƌƵď;ϯϴ͘ϭϵĂĐͿĂůŝĨŽƌŶŝĂ^LJĐĂŵŽƌĞͲŽĂƐƚ>ŝǀĞKĂŬZŝƉĂƌŝĂŶtŽŽĚůĂŶĚƐ;ϰϬ͘ϱϲĂĐͿŽĂƐƚ>ŝǀĞKĂŬtŽŽĚůĂŶĚΘ&ŽƌĞƐƚ;ϯϴ͘ϵϰĂĐͿŽĂƐƚWƌŝĐŬůLJWĞĂƌ^ĐƌƵď;Ϯ͘ϬϮĂĐͿ&ƌĞŵŽŶƚŽƚƚŽŶǁŽŽĚ&ŽƌĞƐƚΘtŽŽĚůĂŶĚ;Ϭ͘ϳϮĂĐͿ^ĐƌƵďKĂŬŚĂƉĂƌƌĂů;ϮϮ͘ϳϰĂĐͿhƉůĂŶĚDƵƐƚĂƌĚƐŽƌ^ƚĂƌdŚŝƐƚůĞ&ŝĞůĚƐ;ϯ͘ϲϭĂĐͿ >ĂŶĚŽǀĞƌ
ĞǀĞůŽƉĞĚͬŝƐƚƵƌďĞĚ;Ϯϱ͘ϲϭĂĐͿKƌŶĂŵĞŶƚĂů>ĂŶĚƐĐĂƉŝŶŐ;Ϯ͘ϳϴĂĐͿ WƌŽũŽŵƉͺWŽŝŶƚ
ϮϰͲϭϲϱϭϮ/K
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ŽŽƌĚŝŶĂƚĞ^LJƐƚĞŵ͗Eϭϵϴϯ^ƚĂƚĞWůĂŶĞĂůŝĨŽƌŶŝĂs WƌŽũĞĐƟŽŶ͗>ĂŵďĞƌƚŽŶĨŽƌŵĂůŽŶŝĐ ĂƚƵŵ͗EŽƌƚŚŵĞƌŝĐĂŶϭϵϴϯϭŝŶĐŚсϮϬϬĨĞĞƚƌĞĂƚĞĚŽŶdŚƵƌƐĚĂLJ͕ƵŐƵƐƚϮϭ͕ϮϬϮϱ DĂƉƌĞĂƚĞĚďLJ͗ZŝŶĐŽŶŽŶƐƵůƚĂŶƚƐ͕/ŶĐ͘ 
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ĞǀĞůŽƉĞĚͬŝƐƚƵƌďĞĚ;Ϯϱ͘ϲϭĂĐͿ
WƌŽũŽŵƉͺWŽŝŶƚ
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ŝŐƉŽĚĞĂŶŽƚŚƵƐŚĂƉĂƌƌĂů;ϭ͘ϱϯĂĐͿĂůŝĨŽƌŶŝĂ^ĂŐĞďƌƵƐŚͲ;WƵƌƉůĞ^ĂŐĞͿ^ĐƌƵď;ϯϴ͘ϭϵĂĐͿĂůŝĨŽƌŶŝĂ^LJĐĂŵŽƌĞͲŽĂƐƚ>ŝǀĞKĂŬZŝƉĂƌŝĂŶtŽŽĚůĂŶĚƐ;ϰϬ͘ϱϲĂĐͿĂůŝĨŽƌŶŝĂtĂůŶƵƚ'ƌŽǀĞƐ;ϱ͘ϰϱĂĐͿŽĂƐƚ>ŝǀĞKĂŬtŽŽĚůĂŶĚΘ&ŽƌĞƐƚ;ϯϴ͘ϵϰĂĐͿ&ƌĞŵŽŶƚŽƚƚŽŶǁŽŽĚ&ŽƌĞƐƚΘtŽŽĚůĂŶĚ;Ϭ͘ϳϮĂĐͿhƉůĂŶĚDƵƐƚĂƌĚƐŽƌ^ƚĂƌdŚŝƐƚůĞ&ŝĞůĚƐ;ϯ͘ϲϭĂĐͿ >ĂŶĚŽǀĞƌ
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Appendix G
Special-Status Species Potential to Occur
Special-Status Species Potential to Occur
Jurisdictional Delineation and Habitat Assessment G-1
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations Plants and Lichens
Braunton's milk-vetch Astragalus brauntonii
FE/None G2/S21B.1
Perennial herb. Chaparral, coastal scrub, valley and foothill grassland. Recent burns or disturbed areas; usually on sandstone with carbonate layers. Soil specialist; requires shallow soils to defeat pocket gophers and open areas, preferably on hilltops, saddles or bowls between hills. Elevations: 15-2100ft. (4-640m.) Blooms Jan-Aug.

Low Virtually all occurrences east of HWY 23 or when not, they are south of 101.

Coulter's saltbush Atriplex coulteri
None/None G3/S21B.2
Perennial herb. Coastal bluff scrub, coastal dunes, coastal scrub, valley and foothill grassland. Alkaline (sometimes), clay (sometimes). Elevations: 10-1510ft. (3-460m.) Blooms Mar-Oct.

None No coastal dunes or bluff habitat within the Study Area.

Malibu baccharis Baccharis malibuensis
None/None G1/S11B.1
Perennial deciduous shrub. Chaparral, cismontane woodland, coastal scrub, riparian woodland. In Conejo volcanic substrates, often on exposed roadcuts. Sometimes occupies oak woodland habitat. Elevations: 490-1000ft. (150-305m.) Blooms Aug.

Low Nearest occurrence a 2008 CNDDB site 5.3mi east of Study Area in similar sandy loam, nfacing slope, part shade, chaparral habitat. Most occurrences around the Santa Monica National Rec Area. Documented in the watershed adjacent to the Study Area in 2004. slender mariposa-lily Calochortus clavatus var. gracilis None/None G4T2T3/S2S3 1B.2
Perennial bulbiferous herb. Chaparral, coastal scrub, valley and foothill grassland. Shaded foothill canyons; often on grassy slopes within other habitat. Elevations: 1050-3280ft. (320-1000m.) Blooms Mar-Jun(Nov).

None Project site is below the known elevational range of the species. southern tarplant Centromadia parryi ssp. australis
None/None G3T2/S21B.1
Annual herb. Marshes and swamps, valley and foothill grassland, vernal pools. Often in disturbed sites near the coast at marsh edges; also in alkaline soils sometimes with saltgrass. Sometimes on vernal pool margins. Elevations: 0-1575ft. (0-480m.) Blooms May-Nov.

Low Nearest occurrence a 2003 CNDDB record 1.5mi west of Study Area in clay loam, full sun, annual grassland. Could occur on similar grassland/chaparral areas within Study Area. Although, most occurrences in Isla Vista and LA/Huntington Beach areas.

Orcutt's pincushion Chaenactis glabriuscula var. orcuttiana None/None G5T1/S11B.1
Annual herb. Coastal bluff scrub, coastal dunes. Sandy sites. Elevations: 0-330ft. (0-100m.) Blooms Jan-Aug. None No coastal dunes or bluff habitat within the Study Area. salt marsh bird's-beak Chloropyron maritimum ssp. maritimum FE/SE G4?T1/S11B.2
Annual herb (hemiparasitic). Coastal dunes, marshes and swamps. Limited to the higher zones of salt marsh habitat. Elevations: 0-100ft. (0-30m.) Blooms May-Oct(Nov).

None Study Area is above the known elevational range of the species.

Parry's spineflower Chorizanthe parryi var. parryi
None/None G3T2/S21B.1
Annual herb. Chaparral, cismontane woodland, coastal scrub, valley and foothill grassland. Openings, Rocky (sometimes), sandy (sometimes). Elevations: 900-4005ft. (275-1220m.) Blooms Apr-Jun.

None Study Area is below the known elevational range of the species.

Santa Susana tarplant Deinandra minthornii
None/SR G2/S21B.2
Perennial deciduous shrub. Chaparral, coastal scrub. On sandstone outcrops and crevices, in shrubland. Elevations: 920-2495ft. (280-760m.) Blooms Jul-Nov.

None Study Area is below the known elevational range of the species. dune larkspur Delphinium parryi ssp. blochmaniae
None/None G4T2/S21B.2
Perennial herb. Chaparral, coastal dunes. On rocky areas and dunes. Elevations: 0-655ft. (0-200m.) Blooms AprJun. Low Vast majority of occurrences from San Luis Obispo and Santa Barbara counties. Ventura occurrences in CCH from 60s/70s Blochman's dudleya Dudleya blochmaniae ssp. blochmaniae None/None G3T2/S21B.1
Perennial herb. Chaparral, coastal bluff scrub, coastal scrub, valley and foothill grassland. Open, rocky slopes; often in shallow clays over serpentine or in rocky areas with little soil. Elevations: 15-1475ft. (5-450m.) Blooms Apr-Jun.

Moderate Most occurrences tend to be closer in proximity to coast, although a 2016 CNDDB occurrence is only 0.62mi from Study Area. Species in same genus found in the Study Area, D. lanceolata and D. pulverulenta. Potentially suitable habitat located in scrub and Optunia patches within Study Area. nearby occurrence notes steep rocky area with Artemisia californica, Opuntia littoralis, Eriogonum fasciculatum. this is similar to onsite conditions.

Agoura Hills dudleya Dudleya cymosa ssp. agourensis
FT/None G5T1/S11B.2
Perennial herb. Chaparral, cismontane woodland. Rocky, volcanic breccia. Elevations: 655-1640ft. (200-500m.) Blooms May-Jun.

Low Study Area generally lacks volcanic outcrops that are common in the vicinity of the site, thus very marginal suitable habitat despite species in same genus found in the Study Area. Virtually all occurrence in Agoura Hills area. marcescent dudleya Dudleya cymosa ssp. marcescens
FT/SR G5T2/S21B.2
Perennial herb. Chaparral. On sheer rock surfaces and rocky volcanic cliffs. Elevations: 490-1705ft. (150-520m.) Blooms Apr-Jul.

Low Virtually all occurrences found in Santa Monica Mountains in a discrete geologically separated population south of the Study Area.

Santa Monica dudleya Dudleya cymosa ssp. ovatifolia
FT/None G5T1/S11B.1
Perennial herb. Chaparral, coastal scrub. In canyons on volcanic or sedimentary substrates; primarily on northfacing slopes. Elevations: 490-5495ft. (150-1675m.) Blooms Mar-Jun. Low Virtually all occurrences found in Santa Monica Mountains in a discrete geologically separated population south of the Study Area. 1980 occurrence found 2mi west, but CCH notes indicate close to subspecies cuymosa.

City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project G-2
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations Conejo dudleya Dudleya parva
FT/None G1/S11B.2
Perennial herb. Coastal scrub, valley and foothill grassland. In clay or volcanic soils on rocky slopes and grassy hillsides. Elevations: 195-1475ft. (60-450m.) Blooms May-Jun.

Moderate Northern portion of Study Area is in the middle of the small species range, with the range shaped in an arch from Mountclef Ridge to Conejo Mountain, with the Study Area in the center. The Study Area generally lacks the open volcanic rocky habitat this species is found in, but clay/gravelly microhabitats exist where species in same genus flourish, D. lanceolata & D. pulverulenta. General coastal scrub and grassland is present.

Verity's dudleya Dudleya verityi
FT/None G1/S11B.1
Perennial herb. Chaparral, cismontane woodland, coastal scrub. On volcanic rock outcrops in the Santa Monica Mountains. Elevations: 195-395ft. (60-120m.) Blooms May-Jun.

Low Virtually all occurrences found east of Conejo Mountain, which is ~2.5mi west of survey area. Project site generally lacks the volcanic microhabitat D. verityi is found in. conejo buckwheat Eriogonum crocatum
None/SR G1/S11B.2
Perennial herb. Chaparral, coastal scrub, valley and foothill grassland. Conejo volcanic outcrops; rocky sites. Elevations: 165-1905ft. (50-580m.) Blooms Apr-Jul.

Moderate Northern portion of Study Area is in the middle of the small species range, with the range shaped in an arch from Mountclef Ridge to Conejo Mountain, with the Study Area in the center. 2012 CNDDB occurrence notes it is found in similar habitat to the project area: riparian vegetation with coastal sage scrub further upland. associated with Dudleya pulverulenta, D. lanceolata. mesa horkelia Horkelia cuneata var. puberula
None/None G4T1/S11B.1
Perennial herb. Chaparral, cismontane woodland, coastal scrub. Sandy or gravelly sites. Elevations: 230-2660ft. (70-810m.) Blooms Feb-Jul(Sep).

Low No occurrences within 7+ miles. Nearest population north of Simi Valley.

Coulter's goldfields Lasthenia glabrata ssp. coulteri
None/None G4T2/S21B.1
Annual herb. Marshes and swamps, playas, vernal pools. Usually found on alkaline soils in playas, sinks, and grasslands. 1-. Elevations: 5-4005ft. (1-1220m.) Blooms Feb-Jun.

None No saline places or vernal pools within the Study Area. Species does not occur in the Jepson geographic range Study Area is located within.

Payne's bush lupine Lupinus paynei
None/None G1Q/S11B.1
Perennial shrub. Coastal scrub, riparian scrub, valley and foothill grassland. Sandy. Elevations: 720-1380ft. (220- 420m.) Blooms Mar-Apr(May-Jul).

Low All CCH occurrences are north of Las Posas Hills.
white-veined monardella Monardella hypoleuca ssp. hypoleuca None/None G4T3/S31B.3
Perennial herb. Chaparral, cismontane woodland. Dry slopes. Elevations: 165-5005ft. (50-1525m.) Blooms (Apr)May-Aug(Sep-Dec).

Low Species distributed in distinct clusters. Most occur in Simi Hills and Santa Monica Mountains/Boney Mountain. Study Area separated from those populations by city development/infrastructure.

Gerry's curly-leaved monardella Monardella sinuata ssp. gerryi None/None G3T1/S11B.1
Annual herb. Coastal scrub. Sandy openings. Elevations: 490-805ft. (150-245m.) Blooms Apr-Jun. Low Although the Study Area is within the Jepson geographic subdivision range (Western Transverse Ranges District, CA floristic province) for the species, there are no recordings of the species south of the Santa Rosa Valley which the Study Area is below, separated geographically by Mountclef Ridge, except a low quality Calflora checklist entry which is quad- wide.

Ojai navarretia Navarretia ojaiensis
None/None G2/S21B.1
Annual herb. Chaparral, coastal scrub, valley and foothill grassland. Openings in shrublands or grasslands.

Elevations: 900-2035ft. (275-620m.) Blooms May-Jul.

Moderate Although the Study Area is below the elevational range of the species listed by CNPS, there is a 2014 CNDDB population at 650ft, only 0.6mi southwest of the Study Area which is in coastal scrub and grassland habitats in open Eriogonum fasciculatum, Artemisia californica, or Eriogonum cinereum scrub, which all occur/similar habitat within the Study Area. chaparral nolina Nolina cismontana
None/None G3/S31B.2
Perennial evergreen shrub. Chaparral, coastal scrub. Primarily on sandstone and shale substrates; also known from gabbro. Elevations: 460-4185ft. (140-1275m.) Blooms (Mar)May-Jul.

Low The cluster of occurrences nearest the Study Area are all east of The City of Thousand Oaks.

California Orcutt grass Orcuttia californica
FE/SE G1/S11B.1
Annual herb. Vernal pools. Elevations: 50-2165ft. (15-660m.) Blooms Apr-Aug. None No vernal pool habitat on-site.

Sonoran maiden fernPelazoneuron puberulum var. sonorense None/None G5T4/S22B.2
Meadows and seeps (seeps, streams). Along streams, seepage areas. 50-610m. Blooms Jan-Sep. Moderate Seeps and stream sides present within the Study Area. Multiple occurrences within 9 quad search area.

Lyon's pentachaeta Pentachaeta lyonii
FE/SE G1/S11B.1
Annual herb. Chaparral, coastal scrub, valley and foothill grassland. Edges of clearings in chaparral, usually at the ecotone between grassland and chaparral or edges of firebreaks. Elevations: 100-2265ft. (30-690m.) Blooms (Feb)Mar-Aug.

High There are several overlapping 1996 and 1997 occurrence overlapping with the Study Area located in Northern portion of the Project. Suitable habitat including openings in grassland and understory of scrub within are located in this portion of the Study Area. Additionally Critical habitat for Lyon's pentachaeta overlaps with the Study Area.

Special-Status Species Potential to Occur
Jurisdictional Delineation and Habitat Assessment G-3
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations white rabbit-tobacco Pseudognaphalium leucocephalum
None/None G4/S22B.2
Perennial herb. Chaparral, cismontane woodland, coastal scrub, riparian woodland. Sandy, gravelly sites. Elevations: 0-6890ft. (0-2100m.) Blooms (Jul)Aug-Nov(Dec).

Low Records in Ventura Co. are north of the Santa Susana Mountains or older (<1959).

Nuttall's scrub oak Quercus dumosa
None/None G3/S31B.1
Perennial evergreen shrub. Chaparral, closed-cone coniferous forest, coastal scrub. Generally on sandy soils near the coast; sometimes on clay loam. Elevations: 50-1310ft. (15-400m.) Blooms Feb-Apr(May-Aug).

Low Species tends to occur at lower elevations. Nearest occurrence is from 1938 with low location quality (~1.5mi west of Study Area).

Santa Catalina Island currant Ribes viburnifolium
1B.2 Perennial evergreen shrub found in chaparral, cismontane woodland. 100- 1150 ft. Blooming Period: Feb-Apr Low SWCA recorded a possible individual of this species within the Study Area; however, the Study Area is outside of this species documented range (Jepson 2025), no records have been recorded within the 9-quad search area, and the identification has not been confirmed. chaparral ragwort Senecio aphanactis
None/None G3/S22B.2
Annual herb. Chaparral, cismontane woodland, coastal scrub. Drying alkaline flats. Elevations: 50-2625ft. (15-800m.) Blooms Jan-Apr(May).

High A 2016 CNDDB population occurrence overlaps with the Study Area located in Northern portion of the Project. Suitable habitat was observed in this portion of the Study Area. broadleaf pondweed Stuckenia striata
None/None G3G4Q/S2S32B.3
Marshes and swamps. Lakes, ponds, rivers, and stream canals. - -70-2135m. Blooms (Jun)Jul-Aug. Low Some marginal riverine and stream habitat is present within the Study Area and one record is located within the Santa Clara River; however, preferred pond/lake habitat is absent within the Study Area and this species documented geographic range is located outside of the Study Area (Jepson2025). estuary seablite Suaeda esteroa
None/None G3/S21B.2
Perennial herb. Marshes and swamps. Coastal salt marshes in clay, silt, and sand substrates. Elevations: 0-15ft. (0-5m.) Blooms (Jan-May)Jul-Oct.

None Study Area is above the known elevational range of the species.

California screw moss Tortula californica
None/None G2G3/S2?1B.2
Moss. Chenopod scrub, valley and foothill grassland. Moss growing on sandy soil. Elevations: 35-4790ft. (10-1460m.) Low No Calflora or CNDDB records in Ventura Co
Invertebrates
Crotch bumble bee Bombus crotchii
None/SCE G2/S2
Coastal California east to the Sierra-Cascade crest and south into Mexico. Food plant genera include Antirrhinum, Phacelia, Clarkia, Dendromecon, Eschscholzia, and Eriogonum.

Moderate Upland areas in the Study Area provide suitable habitat for the species and several of the required food plant genera were detected during the field survey. CNDDB shows a 2020 occurrence approximately 4 miles southwest of the project. monarch - California overwintering populationDanaus plexippus plexippus pop. 1 FPT/None G4T1T2Q/S2
Winter roost sites extend along the coast from northern Mendocino to Baja California, Mexico. Roosts located in wind-protected tree groves (eucalyptus, Monterey pine, cypress), with nectar and water sources nearby.

Moderate (migrating)
Overwintering groves are absent from the Study Area. However, migrating individuals from nearby overwintering groves could stop within the Study Area to oviposit and feed on the milkweed documented within the Study Area. quino checkerspot butterfly Euphydryas editha quino
FE/None G4G5T1T2/S1S2
Sunny openings within chaparral and coastal sage shrublands in parts of Riverside and San Diego counties. Hills and mesas near the coast. Need high densities of food plants Plantago erecta, P. insularis, and Orthocarpus purpurescens.

None There is suitable habitat within the project area, however there are no known records in Ventura County and the nearest CNDDB records in Los Angeles County are considered extirpated.

Riverside fairy shrimp Streptocephalus woottoni
FE/None G1G2/S2
Endemic to Western Riverside, Orange, and San Diego counties in areas of tectonic swales/earth slump basins in grassland and coastal sage scrub. Inhabit seasonally astatic pools filled by winter/spring rains. Hatch in warm water later in the season.

None The project area lacks the habitat to support the species Fish
Santa Ana sucker Catostomus santaanae
FT/None G1/S1SSC
Endemic to Los Angeles Basin south coastal streams. Habitat generalists, but prefer sand-rubble-boulder bottoms, cool, clear water, and algae.

None The watershed the project area is located in is out of the known range of the species. tidewater goby Eucyclogobius newberryi
FE/None G3/S3SSC
Brackish water habitats along the California coast from Agua Hedionda Lagoon, San Diego County to the mouth of the Smith River. Found in shallow lagoons and lower stream reaches, they need fairly still but not stagnant water and high oxygen levels.

None The project area lacks the habitat to support the species. unarmored threespine stickleback Gasterosteus aculeatus williamsoni FE/SE G5T1/S1FP
Weedy pools, backwaters, and among emergent vegetation at the stream edge in small Southern California streams. Cool (<24 C), clear water with abundant vegetation.

None The watershed the project area is located in is out of the known range of the species.

City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project G-4
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations arroyo chub Gila orcuttii
None/None G1/S2SSC
Native to streams from Malibu Creek to San Luis Rey River basin. Introduced into streams in Santa Clara, Ventura, Santa Ynez, Mojave and San Diego river basins. Slow water stream sections with mud or sand bottoms. Feeds heavily on aquatic vegetation and associated invertebrates.

High Arroyo Conejo is known to support the species. CNDDB show a 2000 occurrence overlapping with the project and indicates the population is a transplant outside of its native range. Arroyo chub are considered somewhat common within this watershed. steelhead - southern California DPS Oncorhynchus mykiss irideus pop. 10 FE/SCE G5T1Q/S1
Federal listing refers to populations from Santa Maria River south to southern extent of range (San Mateo Creek in San Diego County). Southern steelhead likely have greater physiological tolerances to warmer water and more variable conditions.

Low The project area could potentially support the species. CNDDB shows a 2013 occurrence approximately 3.8 miles west in Conejo Creek which Arroyo Conejo becomes after merging with Arroyo Santa Rosa. While the watershed has historically not supported the species, it is possible for the species to travel upstream into Arroyo Conejo to locate spawning sites.

Amphibians
western spadefoot Spea hammondii
FPT/None G2G3/S3S4SSC
Occurs primarily in grassland habitats but can be found in valley-foothill hardwood woodlands. Vernal pools are essential for breeding and egg-laying.

Low Upland areas in the project area could potentially support the species however no suitable breeding habitat such as vernal pools were observed. CNDDB shows several 2008 – 2013 occurrences approximately 8 miles northeast of the Study Area Reptiles
southwestern pond turtle Actinemys pallida
FPT/None G2G3/SNRSSC
A thoroughly aquatic turtle of ponds, marshes, rivers, streams and irrigation ditches, usually with aquatic vegetation, below 6000 ft elevation. Needs basking sites and suitable (sandy banks or grassy open fields) upland habitat up to 0.5 km from water for egg-laying. Occurs in southern California from Monterey County south to Los Angeles, Riverside, and San Diego Counties into northern Baja California, Mexico.

High The species was observed basking in the Arroyo Conejo during surveys conducted by Bowland & Associates on July 17 and 18, 2012. The species was not observed during the 2022 surveys.

Southern California legless lizard Anniella stebbinsi
None/None G3/S3SSC
Generally south of the Transverse Range, extending to northwestern Baja California. Occurs in sandy or loose loamy soils under sparse vegetation. Disjunct populations in the Tehachapi and Piute Mountains in Kern County. Variety of habitats; generally in moist, loose soil. They prefer soils with a high moisture content.

High Suitable sandy and loamy soils were found in the Study Area. As of 2013, There is taxonomic uncertainty regarding which species of California legless lizard. Occurs withinthe project vicinity. CNDDB shows several occurrences of California legless lizard and Southern California legless lizard within the vicinity of the Project California glossy snake Arizona elegans occidentalis
None/None G5T2/S2SSC
Patchily distributed from the eastern portion of San Francisco Bay, southern San Joaquin Valley, and the Coast, Transverse, and Peninsular ranges, south to Baja California. Generalist reported from a range of scrub and grassland habitats, often with loose or sandy soils.

Low There is suitable habitat in the Study Area to support the species, however the species is rarely seen and there are few records in Ventura County. CNDDB shows a 1995 occurrence located approximately 7.5 miles north of the Study Area. coastal whiptail Aspidoscelis tigris stejnegeri
None/None G5T5/S3SSC
Found in deserts and semi-arid areas with sparse vegetation and open areas. Also found in woodland and riparian areas. Ground may be firm soil, sandy, or rocky.

Present Several individuals were observed in the Study Area. coast horned lizard Phrynosoma blainvillii
None/None G4/S4SSC
Frequents a wide variety of habitats, most common in lowlands along sandy washes with scattered low bushes. Open areas for sunning, bushes for cover, patches of loose soil for burial, and abundant supply of ants and other insects.

High There is suitable habitat in the upland areas of Study Area. CNDDB shows a 2007 occurrence located approximately 2.5 miles north of the Study Area. two-striped gartersnake Thamnophis hammondii
None/None G4/S3S4SSC
Coastal California from vicinity of Salinas to northwest Baja California. From sea to about 7,000 ft elevation. Highly aquatic, found in or near permanent fresh water. Often along streams with rocky beds and riparian growth.

High There is suitable habitat in the Study Area near Arroyo Conejo and its intermittent and perennial tributaries. CNDDB shows a 1995 occurrence located approximately 3.5miles west of the Study Area. south coast gartersnake Thamnophis sirtalis pop. 1
None/None G5T1T2/S1S2 SSC
Southern California coastal plain from Ventura County to San Diego County, and from sea level to about 850 m. Marsh and upland habitats near permanent water with good strips of riparian vegetation.

Low There is suitable habitat in the Study Area near Arroyo Conejo and its intermittent and perennial tributaries, however occurrences in Ventura County are uncommon. CNDDB shows a 2008 occurrence located approximately 12 miles northwest of the Study Area.

Birds
tricolored blackbird Agelaius tricolor
None/ST G1G2/S2SSC
Highly colonial species, most numerous in Central Valley and vicinity. Largely endemic to California. Requires open water, protected nesting substrate, and foraging area with insect prey within a few km of the colony.

None The project area lacks the appropriate nesting habitat to support the species. May occur on-site for foraging. CNDDB shows an occurrences from 1995 located approximately 3.5 miles southeast near Lake Sherwood
golden eagle Aquila chrysaetos
None/None G5/S3FPWL
Rolling foothills, mountain areas, sage-juniper flats, and desert. Cliff-walled canyons provide nesting habitat in most parts of range; also, large trees in open areas.

Low The project area lacks the appropriate nesting habitat to support the species. Species may be observed as a flyover and has a low potential to forage on-site. CNDDB shows several 1989 occurrences approximately 4.5 – 6 miles south and southwest all generally considered inactive nest sites
burrowing owl Athene cunicularia
None/SCE G4/S2SSC
Open, dry annual or perennial grasslands, deserts, and scrublands characterized by low-growing vegetation. Subterranean nester, dependent upon burrowing mammals, most notably, the California ground squirrel.

High Suitable grassland habitat is located within the upland portions of the Y Study Area.

There is an eBird observation located within this area (eBird 2025).

Special-Status Species Potential to Occur
Jurisdictional Delineation and Habitat Assessment G-5
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations Western snowy plover Charadrius nivosus nivosus
FT/None G3T3/S3SSC
Sandy beaches, salt pond levees and shores of large alkali lakes. Needs sandy, gravelly or friable soils for nesting.

None The Study Area lacks the appropriate nesting habitat to support the species western yellow-billed cuckoo Coccyzus americanus occidentalis FT/SE G5T2T3/S1
Riparian forest nester, along the broad, lower flood-bottoms of larger river systems. Nests in riparian jungles of willow, often mixed with cottonwoods, with lower story of blackberry, nettles, or wild grape.

Low The riparian forest habitat along Arroyo Conejo provides marginally suitable habitat for nesting. CNDDB shows the nearest confirmed nesting occurrence, from 2018, is located along the Santa Clara River approximately 11 miles northwest of the Study Area. white-tailed kite Elanus leucurus
None/None G5/S3S4FP
Rolling foothills and valley margins with scattered oaks and river bottomlands or marshes next to deciduous woodland. Open grasslands, meadows, or marshes for foraging close to isolated, dense-topped trees for nesting and perching.

Moderate Suitable habitat is present within the Study Area and multiple eBird observations have been made within Wildwood Park (eBird 2025).
southwestern willow flycatcher Empidonax traillii extimus FE/SE G5T2/S3
Riparian woodlands in Southern California. . Low The riparian forest habitat along Arroyo Conejo provides suitable habitat for nesting, however the species has never been observed nesting in the vicinity. CNDDB shows the nearest confirmed nesting occurrence, from 2009, is located along the Santa Clara River approximately 11 miles northwest of the Study Area.

Belding's Savannah Sparrow Passerculus sandwichensis beldingi None/SE G5T3/S3
Inhabits coastal salt marshes, from Santa Barbara south through San Diego County. Nests in Salicornia on and about margins of tidal flats.

None The Study Area lacks the appropriate nesting habitat to support the species coastal California gnatcatcher Polioptila californica californica FT/None G4G5T3Q/S2SSC
Obligate, permanent resident of coastal sage scrub below 2500 ft in Southern California. Low, coastal sage scrub in arid washes, on mesas and slopes. Not all areas classified as coastal sage scrub are occupied.

High The upland portions of the Study Area provide suitable coastal scrub habitat to support the species. CNDDB shows a 2016 occurrence approximately 280 feet west from the western limits of the Study Area. An additional 2019 occurrence is located approximately 0.5 miles south of the Study Area light-footed Ridgway's rail Rallus obsoletus levipes
FE/SE G3T1T2/S1FP
Found in salt marshes traversed by tidal sloughs, where cordgrass and pickleweed are the dominant vegetation. Requires dense growth of either pickleweed or cordgrass for nesting or escape cover; feeds on molluscs and crustaceans.

None The Study Area lacks the appropriate nesting habitat to support the species Bank swallow Riparia riparia
None/ST G5/S3
Colonial nester; nests primarily in riparian and other lowland habitats west of the desert. Requires vertical banks/cliffs with fine-textured/sandy soils near streams, rivers, lakes, ocean to dig nesting hole.

None The Study Area lacks the appropriate nesting habitat to support the species. Generally considered extirpated in this area (CDFW 2025).
yellow warbler Setophaga petechia
None/None G5/S3SSC
Riparian plant associations in close proximity to water. Also nests in montane shrubbery in open conifer forests in Cascades and Sierra Nevada. Frequently found nesting and foraging in willow shrubs and thickets, and in other riparian plants including cottonwoods, sycamores, ash, and alders.

High The riparian habitat associated with Arroyo Conejo provides suitable nesting and foraging habitat.

California Least tern Sternula antillarum browni
FE/SE G4T2T3Q/S2FP
Nests along the coast from San Francisco Bay south to northern Baja California. Colonial breeder on bare or sparsely vegetated, flat substrates: sand beaches, alkali flats, landfills, or paved areas.

None The Study Area lacks the appropriate nesting habitat to support the species least Bell's vireo Vireo bellii pusillus
FE/SE G5T2/S3
Summer resident of Southern California in low riparian in vicinity of water or in dry river bottoms; below 2000 ft. Nests placed along margins of bushes or on twigs projecting into pathways, usually willow, Baccharis, mesquite.

Present The riparian habitat found associated with Arroyo Conejo provides suitable nesting and foraging habitat. CNDDB shows a 2008 occurrence approximately 1.3 miles north of the Study Area along Arroyo Santa Rosa. An additional occurrence, from 2017 is located approximately 2.7 miles from the Study Area along Conejo Creek. Focused surveys were conducted by Werner in 2022 and identified one individual male (Werner 2022).

Mammals
pallid bat Antrozous pallidus
None/None G4/S3SSC
Found in a variety of habitats including deserts, grasslands, shrublands, woodlands, and forests. Most common in open, dry habitats with rocky areas for roosting. Roosts in crevices of rock outcrops, caves, mine tunnels, buildings, bridges, and hollows of live and dead trees which must protect bats from high temperatures. Very sensitive to disturbance of roosting sites.

Low Cliff side faces observed along Arroyo Conejo may provide suitable roosting sites The species would also utilize the Study Area for foraging. CNDDB shows a 2004 occurrence approximately 7.6 miles east of the Study Area. western mastiff bat Eumops perotis californicus
None/None G4G5T4/S3S4 SSC
Occurs in open, semi-arid to arid habitats, including coniferous and deciduous woodlands, coastal scrub, grasslands, and chaparral. Roosts in crevices in cliff faces and caves, and buildings. Roosts typically occur high above ground.

Low Cliff side faces observed along Arroyo Conejo may provide suitable roosting sites The species would also utilize the site for foraging. CNDDB shows a 2004 occurrence approximately 7.6 miles east of the Study Area western red bat Lasiurus blossevillii
None/None G4/S3SSC
Roosts primarily in trees, 2-40 ft above ground, from sea level up through mixed conifer forests. Prefers habitat edges and mosaics with trees that are protected from above and open below with open areas for foraging.

Moderate Several oaks may provide suitable roosting sites. The species would also utilize the Study Area for foraging. CNDDB shows a 2004 occurrence approximately 8.5 miles southeast of the Study Area
City of Thousand Oaks
Arroyo Conejo Utility and Road Maintenance Project G-6
Common Name Scientific Name Status Habitat Requirements Potential to Occur in Study Area Habitat Suitability/Observations Southern coast marsh vole Microtus californicus
None/None G5T2T3/S2SSC
Occurs in tidal marshes of Orange, Los Angeles, and Ventura Counties. None The Study Area lacks the habitat to support the species.

San Diego desert woodrat Neotoma lepida intermedia
None/None G5T3T4/S3S4 SSC
Occurs in scrub habitats of southern California from San Luis Obispo County to San Diego County. Moderate Rocky areas and hillslopes within the Study Area would provide suitable habitat for the species. Additionally, several middens were found during the survey, however species identification cannot be established without small mammal trapping CNDDB shows a 2016 occurrence located approximately 3 miles southwest of the Study Area.

Southern California saltmarsh shrew Sorex ornatus salicornicus None/None G5T1?/S1SSC
Coastal marshes in Los Angeles, Orange and Ventura counties. Requires dense vegetation and woody debris for cover.

None The Study Area lacks the habitat to support the species.

American badger Taxidea taxus
None/None G5/S3SSC
Most abundant in drier open stages of most shrub, forest, and herbaceous habitats, with friable soils. Needs sufficient food, friable soils and open, uncultivated ground. Preys on burrowing rodents. Digs burrows.

Moderate Upland areas in the Study Area provide suitable habitat for the species. The species is infrequently observed but has a wide distribution. CNDDB shows a 2013 occurrence located 4.8 miles west of the Study Area ft. = feet; meter = m. Regional Vicinity refers to within a 9-quad search radius of site. Status (Federal/State) CRPR (CNPS California Rare Plant Rank) FE = Federal Endangered 1A = Presumed extirpated in California, and rare or extinct elsewhere FT = Federal Threatened 1B = Rare, Threatened, or Endangered in California and elsewhere FPE = Federal Proposed Endangered 2A = Presumed extirpated in California, but common elsewhere FPT = Federal Proposed Threatened 2B= Rare, Threatened, or Endangered in California, but more common elsewhere FD = Federal Delisted FC = Federal Candidate SE = State Endangered CRPR Threat Code ExtensionST = State Threatened .1 = Seriously endangered in California (>80% of occurrences threatened/high degree and immediacy of threat) SCE = State Candidate Endangered .2 = Moderately threatened in California (20-80% of occurrences threatened/moderate degree and immediacy of threat) SCT = State Candidate Threatened .3 = Not very endangered in California (<20% of occurrences threatened/low degree and immediacy of threat) SR = State Rare SD = State Delisted SSC = CDFW Species of Special Concern FP = CDFW Fully Protected WL = CDFW Watch List Other StatusesG1 or S1 Critically Imperiled Globally or Subnationally (state) G2 or S2 Imperiled Globally or Subnationally (state) G3 or S3 Vulnerable to extirpation or extinction Globally or Subnationally (state) G4/5 or S4/5 Apparently secure, common and abundant GH or SH Possibly Extirpated – missing; known from only historical occurrences but still some hope of rediscovery LR Locally Rare (Santa Barbara Botanical Gardens 2018) Additional notations may be provided as follows T – Intraspecific Taxon (subspecies, varieties, and other designations below the level of species) Q – Questionable taxonomy that may reduce conservation priority ? – Inexact numeric rank
Appendix H
Jurisdictional Delineation Map Book
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WƌŽũĞĐƚŽŵƉŽŶĞŶƚƐ
^ƚƵĚLJƌĞĂĐĐĞƐƐZŽĂĚWĞĚĞƐƚƌŝĂŶWĂƚŚ
E,&ůŽǁůŝŶĞ
^ƚƌĞĂŵͬZŝǀĞƌ
:ƵƌŝƐĚŝĐƚŝŽŶĂů&ĞĂƚƵƌĞƐ
&t^ƚƌĞĂŵďĞĚEŽŶͲtĞƚůĂŶĚtĂƚĞƌƐŽĨƚŚĞh͘^͘EŽŶͲtĞƚůĂŶĚtĂƚĞƌƐŽĨƚŚĞ^ƚĂƚĞ ϮϰͲϭϲϱϭϮ/K
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:ƵƌŝƐĚŝĐƚŝŽŶĂů&ĞĂƚƵƌĞƐ
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Representative Photographs
Photo 3: Erosional feature observed where F09 (Western Channel) drainage was mapped by Rincon. Photo 4: Another view of erosional feature where F09 (Western Channel) drainage was mapped by Rincon.

Photo 1: Representative photo of eastern portion of drainage F08. Photo 2: Representative photo of western portion of drainage F08.

Representative Photographs
Photo 5: F09 (Large Central Channel) drainage showing mostly upland vegetation. Photo 6: Additional riparian vegetation (red willow) associated with eastern F09 (Eastern Channel) Photo 7: Riparian vegetation (red willow and coast live oak) in drainage F08 overhanging access road. 



 




 



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City of Thousand Oaks
2100 Thousand Oaks Boulevard
Thousand Oaks, CA 91362
Attn: Patrick McCulloch, Utilities Maintenance Supervisor Jon Turner, PE, Principal Civil Engineer
4165 E Thousand Oaks Blvd,
Suite #290
Westlake Village, CA 91362
Authors:

Wayne Bishoff, Ph.D.

Rowan Barton,M.S.
(818) 879-4700
PREPARED FOR: PREPARED BY:

Public Works Department
Cultural Resources Phase I Assessment
Negative Findings Letter Report
Box Canyon Manhole &
Road Improvements Project
City of Thousand Oaks, California
NOVEMBER 2025
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Box Canyon in the Early 20th Century

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 4&5
Figure 4: 1900 Triunfo Pass 1:62,500 USGS Map, showing no development on the project site and surrounding region.

Figure 5: 1938 Aerial Image, showing no development on the project site and surrounding region (UCSB Aerial Photograph Database).

Box Canyon in the Mid 20th Century

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 6&7
Figure 6: 1950 Newbury Park 1:24,000 USGS Map, again showing no development.

Figure 7: 1965 Aerial Image, showing an access road on the project site and residential construction for the first time in the surrounding area (UCSB Aerial Photograph Database).
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Box Canyon in the Late 20th Century to Present

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 8&9
Figure 8: 1977 Aerial Image, showing the project site aera and surrounding residential development (UCSB Aerial Photograph Database).

Figure 9: 2025 Satellite Image, showing current conditions (Google Earth Pro).

Project Site Overview

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 10&11
Figure 10: Project site overview, showing the graded access road (facing east).

Figure 11: Project site overview, showing the stream downhill from the road (facing west).

Vegetation and Ground Visibility

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 12&13
Figure 12: Image showing the excellent visibility along the graded road and moderate visibility along the stream (facing west).

Figure 13: Exposed bedrock and sparce vegetation; no evidence of prehistoric quarrying of toolstone was observed (facing north).

Natural Site Disturbance

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 14&15
Figure 14: Erosion of bedrock on the project site (facing north).

Figure 15: Water cut channels in the graded road (facing west).

Human Site Disturbance

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 16&17
Figure 16: Powerline installed on the project site (facing east).

Figure 17: Wastewater main and manhole installed on the project site (facing south). )/ '
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Project Site Geology

BOX CANYON MANHOLE AND ROAD IMPROVEMENTS PROJECT - CULTURAL PHASE I FIGURES 19&20
Figure 19: Lower Topanga Formation clay shale (Ttlc) observed in the project area.

Figure 20: Lower Topanga Formation sandstone (Ttls) observed in the project area. )/ '
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October 9, 2025
Native American Heritage Commission
1550 Harbor Boulevard, Room 100
West Sacramento, CA 95691
Subj: Project to Provide a Cultural Resource Phase I for Box Canyon, Thousand Oaks, Ventura County, California (Envicom Project #2025-112-01)
To Whom It May Concern,
Envicom Corporation (Envicom) is requesting a record review of the Native American Heritage Commission (NAHC) records of cultural resources for the Project site, plus a 0.25-mile study area. We also request a list of Tribal Group representatives for the area in the event we need to contact their offices.

The Project site is located at:

United States Geological Survey 7.5’ Quadrangle: Newbury Park, 2021 County: Ventura County
Envicom appreciates the NAHC’s help with this request. For correspondence or questions regarding this Project, please contact Dr. Wayne Bischoff at 818-879-4700 ext. 229 ([email protected]).

Sincerely,
Rowan Barton
Staff Archaeologist

Sacred Lands File & Native American Contacts List Request Native American Heritage Commission
1550 Harbor Blvd, Suite 100
West Sacramento, CA 95691
916-373-3710
916-373-5471 – Fax
[email protected]
Information Below is Required for a Sacred Lands File Search Project: ______________________________________________________________________ County:______________________________________________________________________ USGS Quadrangle Name:_______________________________________________________ Township:__________ Range:__________ Section(s):__________ Company/Firm/Agency:_________________________________________________________ Street Address:________________________________________________________________ City:______________________________________________ Zip:______________________ Phone:_____________________________________________
Fax:_______________________________________________
Email:_____________________________________________
Project Description:

Newbury Park
 
Envicom Corporation
4165 E Thousand Oaks Blvd #290, Thousand Oaks, CA
Thousand Oaks, CA 91362
(818) 879-4700
[email protected]
Ventura
Box Canyon Project, Thousand Oaks, Ventura County (Envicom Project #2025-112-01) Project to provide a cultural resource Phase I for the Box Canyon Project in Thousand Oaks, Ventura County, CA
(Envicom Project # 2025-112-010)
October 9, 2025
Natural History Museum of Los Angeles
900 Exposition Blvd.

Los Angeles, CA 90007
Subj: Project to Provide a Cultural Resource Phase I for Box Canyon, Thousand Oaks, Ventura County, California (Envicom Project #2025-112-01)
To Whom It May Concern,
Envicom Corporation (Envicom) is requesting a record search of the Natural History Museum of Los Angeles County (NHMLAC) database for paleontological resources/sensitivity for the Project site and surrounding area (within 0.25 mile of the Project site), as well as a map/listing of all paleontological resources previously identified within the attached Project site, plus the 0.25-mile study area. The Project site is located at:

United States Geological Survey 7.5’ Quadrangle: Newbury Park, 2021 County: Ventura County
Envicom appreciates the NHMLAC’s help with this request. For correspondence or questions regarding this Project, please contact Dr. Wayne Bischoff at 818-879-4700 ext. 229 ([email protected]).

Sincerely,
Rowan Barton
Staff Archaeologist
Attachment:

Project vicinity map on 1:24,000 topographic map
STATE OF CALIFORNIA Gavin Newsom, Governor

NATIVE AMERICAN HERITAGE COMMISSION

October 10, 2025
Wayne Bischoff
Envicom Corporation
Via Email to: [email protected]
Re: Box Canyon, Thousand Oaks, Ventura County (Envicom #2025-112-01) Project, Ventura County
To Whom It May Concern:

As requested, a search of the Native American Heritage Commission (NAHC) Sacred Lands File (SLF) was completed based on information submitted for the above referenced project. The results were negative. Be aware that tribes do not always record their sacred sites in the SLF, nor are they required to do so. As such, an SLF search is not a substitute for consultation with all tribes that are traditionally and culturally affiliated with a project’s geographic area.

Attached is a list of Native American tribes that are traditionally and culturally affiliated with the project’s geographic area. Please contact all of the listed tribes as they may have information about sacred sites within the project area that is not listed with the NAHC.

If within two weeks of notification, a response has not been received, the Commission requests that you follow up with a telephone call or email to ensure that the project information was received.

If you receive notification of a change of address or phone number from a tribe, please inform the NAHC so that we can assure that our lists contain current information.

In addition to engaging in tribal consultation, you should consult the appropriate regional California Historical Research Information System (CHRIS) information center to determine whether it has information regarding the presence of recorded archaeological sites within the project area.

If you have any questions or need additional information, please contact me at [email protected].

Sincerely,
Mathew Lin, MPP
Cultural Resources Analyst
Attachment

CHAIRPERSON
Reginald Pagaling
Chumash

VICE-CHAIRPERSON
Buffy McQuillen
Yokayo Pomo, Yuki,
Nomlaki

SECRETARY
Isaac Bojorquez
Ohlone-Costanoan

PARLIAMENTARIAN
Wayne Nelson
Luiseño

COMMISSIONER
Sara Dutschke
Miwok

COMMISSIONER
Stanley Rodriguez
Kumeyaay

COMMISSIONER
Bennae Calac
Pauma-Yuima Band of
Luiseño Indians

COMMISSIONER
Vacant

COMMISSIONER
Vacant

ACTING EXECUTIVE

SECRETARY
Michelle Carr

NAHC HEADQUARTERS
1550 Harbor Boulevard
Suite 100
West Sacramento,
California 95691
(916) 373-3710
[email protected]
County Tribe Name Fed (F) Non-Fed (N) Contact Person Contact Address Phone # Fax # Email Address Cultural Affiliation Barbareño/Ventureño Band of Mission Indians N Cultural Resource Committee P.O. Box 364 Ojai, CA, 93024 (805) 746-6685 [email protected] ChumashCoastal Band of the Chumash Nation N Michael Khuz-Zarate, CBCN Vice Chairman 5151 W Vartikian Ave. Fresno, CA, 93722 (559) 761-9827 [email protected] ChumashCoastal Band of the Chumash Nation N Janet Hall, CBCN Cultural Resources Manager 1529 West Lemon Ave. Lompoc, CA, 93436 (805) 451-8757 [email protected] ChumashCoastal Band of the Chumash Nation N Mati Waiya, Tribal Chair 16500 S Mountain Drive Santa Paula, CA, 93060 (805) 794-1248 [email protected] ChumashNorthern Chumash Tribal Council N Violet Walker, Chairperson P.O. Box 6533 Los Osos, CA, 93412 (760) 549-3532 [email protected] ChumashSanta Ynez Band of Chumash Indians F General CRM Consultation Account 100 Via Juana Road Santa Ynez, CA, 93460 [email protected] v ChumashSanta Ynez Band of Chumash Indians F Nakia Zavalla, Tribal Historic Preservation Officer 100 Via Juana Road Santa Ynez, CA, 93460 [email protected] ChumashSanta Ynez Band of Chumash Indians F Wendy Teeter, Cultural Resources Archaeologist 100 Via Juana Road Santa Ynez, CA, 93460 (805) 325-8630 [email protected] ChumashSanta Ynez Band of Chumash Indians F Sam Cohen, Government & Legal Affairs Director 100 Via Juana Road Santa Ynez, CA, 93460 [email protected] Chumash Native American Heritage Commission
Native American Contact List
Ventura County
10/10/2025
Counties Last Updated
Ventura Kern, Los Angeles, San Luis
Obispo, Santa Barbara, Ventura
6/19/2023
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 5/14/2025
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 5/14/2025
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 5/14/2025
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 6/5/2023
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 4/28/2025
This list is current only as of the date of this document. Distribution of this list does not relieve any person of statutory responsibility as defined in Section 7050.5 of the Health and Safety Code, Section 5097.94 of the Public Resources Code and Section 5097.98 of the Public Resources Code.

This list is only applicable for contacting local Native Americans with regard to cultural resources assessment for the proposed Box Canyon, Thousand Oaks, Ventura County (Envicom #2025-112-01) Project, Ventura County
Record: PROJ-2025-005659
Report Type: List of Tribes
Counties: Ventura
NAHC Group: All
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 7/6/2023
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 7/6/2023
Kern, Los Angeles, San Luis Obispo, Santa Barbara, Ventura 7/6/2023
10/10/2025 10:07 AM
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