TERRESTRIAL AND AQUATIC WILDLIFE BIOLOGICAL EVALUATION

USDA Forest Service, Eldorado National Forest, Pacific Ranger District

PROJECT NAME: Sunset Campground Rehabilitation Project

DATE: 12 Sept 2017 REPORTER: Janelle Nolan, Principal Terrestrial Ecologist

NEPA DOCUMENT: FERC and USFS Final Environmental Impact Statement for

Hydropower License, UARP and Chili Bar Hydroelectric Project. March 2008.

LEGAL SUBDIVISION: T12N R14E S22

IMPLEMENTATION START DATE: Spring 2018

COMPLETION DATE: December 2019

EFFECTS DETERMINATIONS:

The proposed Sunset Campground Rehabilitation Project is not likely to result in a trend toward federal listing or loss of viability of any of the sensitive species identified for the project.

Species Status Determination Sierra Nevada yellow-legged FE, FSS, CT, CDFW Watchlist No effect frog Sierra Nevada yellow-legged No effect – project is not located frog Designated Critical Habitat in critical habitat Bald eagle BCC, FSS, CE, CFP May affect, but is not likely to result in a trend toward federal listing Pallid bat FSS, CSC May affect, but is not likely to result in a trend toward federal listing Townsend’s big-eared bat FSS, CSC May affect, but is not likely to result in a trend toward federal listing Fringed myotis FSS May affect, but is not likely to result in a trend toward federal listing Pacific marten FSS No effect BCC = Birds of Conservation Concern, CDFW Watchlist = California Department of Fish and Wildlife Watchlist, CE = California Endangered, CFP = California Fully Protected, CSC = California Species of Special Concern, CT = California Threatened, FE = Federal Endangered, FSS = Forest Service Sensitive Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

1 Introduction The Biological Evaluation (BE) was prepared to evaluate the effects of the Sacramento Municipal Utility District (SMUD) Sunset Campground Rehabilitation Project (project or proposed project) on federally listed threatened, endangered, candidate, and proposed species, as well as Forest Service Sensitive (FSS) or Watchlist species. Some of these species are also state-listed threatened, endangered, and proposed species.

The purpose of the BE is to document activities in sufficient detail to determine how the project may affect threatened, endangered, proposed, or sensitive species and their habitats (U.S. Forest Service Manual [USFSM] 2670.5). USFSM 2672.4 directs the U.S. Forest Service (USFS or Forest Service) to complete a BE for all Forest Service– planned, funded, executed, or permitted programs and activities to evaluate possible effects on threatened, endangered, candidate, proposed, and FSS species. The BE assists in determining whether a proposed project or any of the alternatives will result in a trend toward the sensitive species becoming federally listed.

The project is required under the license terms and conditions for the Upper American River Project (UARP), Federal Energy Regulatory Commission (FERC) Project No. 2101, which was issued by FERC on July 23, 2014. Specifically, USFS 4(e) Condition No. 45 (j) – Specific Recreation Measures requires that SMUD redesign and reconstruct Sunset Campground by December 31, 2019. USFS 4(e) Condition No. 38 – Wildlife and Plant Protection Measures requires that SMUD prepare a BE before commencing any new construction or maintenance (including, but not limited to, proposed recreation developments) authorized by the license on USFS lands (Appendix A). This BE was developed to comply with components of these conditions that are relevant to the project.

The UARP was constructed from 1959 to 1985 on USFS lands and consists of 7 developments within the Rubicon River, Silver Creek, and South Fork American River drainages. It consists of 8 hydroelectric power plants operating from 11 reservoirs, with a combined installed capacity of 637 megawatts (MW). In all, the UARP has 11 reservoirs, 8 powerhouses, 11 transmission lines with a combined length of 180 miles, 28 miles of power tunnels or penstocks, 1 canal, and 700 developed public- use campsites in 47 recreation areas, including Sunset Campground. The location of the UARP, including the proposed project, is shown in Figure 1.

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Figure 1. Upper American River Project and Sunset Campground Rehabilitation Project Location.

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1.1 Special-status Species Addressed in this Biological Evaluation For the purposes of this document, special-status species are defined as any species granted status by the U.S. Fish and Wildlife Service (USFWS) as threatened (FT), endangered (FE), candidate (FC), or delisted (FD), or species that have been designated by USFS as FSS. Some of these species may also be granted status by California Department of Fish and Wildlife (CDFW) as California Endangered (CE), California Threatened (CT), California Species of Special Concern (CSC), California Fully Protected (CFP), or by CDFW as Watchlist.

Table 1 provides a list of special-status species that have potential to occur in the project area as identified in the USFWS Species List (USFWS 2016a), California Natural Diversity Database (CNDDB; 2016), and Regional Forester’s List of Sensitive Animal Species for Region 5 (USFS 2013a). Table 1 also provides the potential for each of these species to occur within the project area.

Special-status species that are known to occur or have potential to occur in the project area are listed in Section 1.1.1 below. Special-status species that are shown in Table 1 as unlikely to occur are not addressed further in this document.

This document includes analysis of the potential effects of the proposed project on the federally endangered Sierra Nevada yellow-legged frog (Rana sierrae; SNYLF) (FE and FSS). The project is not located within critical habitat for this species. The closest critical habitat unit (Subunit 2E: Crystal Range) is located 6 miles northeast of the project area (Figure 2).

FERC, in its Order Issuing New License for Project No. 2101, acknowledged that the SNYLF was federally listed on April 29, 2014, with proposed critical habitat designated on April 25, 2013. The UARP is located in designated critical habitat for the SNYLF. However, in the Order, FERC noted the historical absence of SNYLF within the UARP reservoirs and affected reaches, further noting that the license measures will actually increase potential habitat for the SNYLF, as described in the Final Environmental Impact Statement (FEIS) for the relicensing of the UARP (USFS and FERC 2008; Sections 3-91–92; 3-193–194; 3-208–228; 5–18). FERC also acknowledged that the Order requires SMUD to monitor for the presence of SNYLF over the life of the license.

As the lead federal action agency for the UARP, FERC concluded with the determination that the continued operation of the UARP, “will not affect this federally listed frog” and “would not destroy or adversely modify proposed Critical Habitat” (FEIS paragraphs 90–94:21–22).1 Lastly, FERC stated that “if the frog is found during

1 It should be noted that although critical habitat was identified as “proposed” in the 2014 FERC license for the UARP, in 2016, USFWS designated final critical habitat. However, in the case of the UARP, the extent of the “proposed” critical habitat did not change within the UARP sub-unit when it became “designated.” As such, the determination made by FERC still applies.

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monitoring, ESA [Endangered Species Act] consultation with USFWS may be needed in the future.”

This BE, which describes design criteria to avoid impacts to this species, is an environmental measure prescribed by the FEIS for the UARP License. It provides additional site-specific analysis to support the “no effect” determination by FERC.

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Figure 2. Nearest Known Occurrence and Critical Habitat for Sierra Nevada Yellow-Legged Frog.

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1.1.1 Federal and State-listed Species The project area is within the geographic range and includes potential habitat for 8 FSS wildlife species:

• SNYLF – FE, FSS, CT, CDFW Watchlist

• Bald eagle (Haliaeetus leucocephalus) – Birds of Conservation Concern (BCC), FSS, CE, CFP

• Pallid bat (Antrozous pallidus) – FSS, CSC

• Townsend’s big-eared bat (Corynorhinus townsendii) – FSS, CSC

• Fringed myotis (Myotis thysanodes) – FSS

• Pacific marten (Martes caurina) – FSS Refer to Table 1 and Figure 3 for species-specific habitat requirements and documented occurrences of each species within the project vicinity.

1.2 Project Location The project is located on the east shoreline of Union Valley Reservoir within the Eldorado National Forest (ENF), approximately 38 miles from Placerville, California, and 55 miles from South Lake Tahoe, California (Figure 1). Sunset Campground is located on a peninsula, which is accessible via Fashoda Way from Ice House Road. The area is generally accessible from May 1 to November 1 or as snow conditions allow.

1.3 Project Description and Project Proponent Sunset Campground is a 131-unit campground that opened in 1966 with 51 campsites. In 1969, the campground was expanded with 80 additional campsites. The campground is well maintained; however, the design of the campsites, restrooms, and associated amenities does not reflect current USFS design standards and does not meet accessibility objectives.

Sunset Campground was constructed at a time when accessibility needs were not widely recognized and/or incorporated into management objectives and design standards. Since that time, design objectives and construction standards for recreation facilities have changed significantly, most notably regarding the provision of accessible facilities for persons with disabilities.

The purpose of the project is to rehabilitate Sunset Campground to meet the needs of current and future users at Union Valley Reservoir. SMUD will rehabilitate Sunset Campground as specified in USFS 4(e) Condition No. 45 (j) to meet current USFS

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The project proponent, SMUD, may be contacted at:

Ethan Koenigs, Environmental Management Specialist Environmental Management Sacramento Municipal Utility District 7540 Highway 50, Pollock Pines, CA 95726 P.O. Box 1500, Pollock Pines, CA 95726 (530) 647-5094 [email protected]

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Figure 3. Special-Status Wildlife Known to Occur in the Vicinity of the Project.

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2 Current Regulatory Management This section summarizes current regulatory management as it pertains to the management of special-status species listed under the ESA, as well as species considered sensitive by the USFS.

2.1 Endangered Species Act Pursuant to the federal ESA, the USFWS and National Oceanic and Atmospheric Administration – Fisheries Division (NOAA Fisheries) must be consulted with regard to proposed actions that may affect the continued existence of a federally listed species. Species are defined as either threatened or endangered by the USFWS if they are listed in Title 50 of the Code of Federal Regulations (50 CFR §§17.11 or 17.12). Section 9 of the ESA and federal regulations prohibit the “take” of federally listed species. “Take” is defined under the ESA, in part, as killing, harming, or harassment of such species. Under federal regulations, “take” is further defined to include either habitat modification or degradation where it actually results in either death or injury to wildlife by significantly impairing essential behavioral patterns, including breeding, feeding, and/or sheltering. An incidental take permit under Section 10(a), or federal consultation under Section 7, is required if the proposed action might affect a federally listed species.

As part of the UARP relicensing process, compliance with Section 7 of the ESA was completed by FERC, the federal lead agency. This consultation included analysis of the potential effects of implementation of USFS 4(e) Condition No. 45 (j), including the Sunset Campground Rehabilitation Project, on federally listed plant and wildlife species. On September 28, 2009, USFWS issued a Biological Opinion for issuance of the new UARP License. USFWS determined that the UARP, including the Sunset Campground Rehabilitation Project, would not likely jeopardize the continued existence of the Pine Hill ceanothus (Ceanothus roderickii), Pine Hill flannelbush (Fremontodendron decumbens), Layne’s butterweed (Senecio layneae), or the valley elderberry longhorn beetle (Desmocerus californicus dimorphus). Following issuance of the Biological Opinion, the SNYLF was federally listed as endangered on April 29, 2014, and critical habitat was designated on August 26, 2016. FERC, as the federal lead agency, determined that continued operation and maintenance of the UARP would not affect SNYLF (FERC 2014). Refer to FERC’s FEIS for the UARP for analysis to support this determination (USFS and FERC 2008).

2.2 National Forest Management Act The National Forest Management Act (NFMA) of 1976 reorganized, expanded, and otherwise amended the Forest and Rangeland Renewable Resources Planning Act of 1974, which called for the management of renewable resources on national forest lands. The NFMA is the primary statute governing the administration of national forests. It requires the Secretary of Agriculture to develop and implement resource management plans for each unit of the National Forest System. The secretary must specify procedures to ensure management plans are in accordance with the National Environmental Policy Act and (1) ensure consideration of both economic and environmental factors; (2) provide for wildlife and fish; (3) provide for the diversity of plant and animal communities; (4)

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ensure timber harvesting will occur only where water quality and fish habitat are adequately protected from serious detriment; and (5) ensure clearcutting and other harvesting will occur only where they may be done in a manner consistent with the protection of soil, watersheds, fish, wildlife, recreation, aesthetic resources, and regeneration of the timber resource. Plans must be updated every 15 years.

2.3 Eldorado National Forest Land and Resource Management Plan The ENF Land and Resource Management Plan (LRMP) was developed by the USFS to direct the management of the ENF. The goal of this plan is to provide a management program that reflects a variety of activities, allows use and protection of forest resources, and fulfills legislative requirements while addressing local, regional, and national issues. The LRMP describes the desired future state of the ENF, forestwide management direction, and prescriptions for individual management areas, management standards and guidelines, location maps, schedules of proposed and possible outputs and activities, monitoring and evaluation requirements, and how issues were resolved. The LRMP applies to all national forest land administered by the ENF. The LRMP states that the USFS will manage sensitive species to avoid future listings of those species as either threatened or endangered and will ensure maintenance of genetic and geographic diversity and viable populations for sensitive species. The LRMP recognizes hydropower and recreation as two very important beneficial uses of the ENF.

2.4 Final Environmental Impact Statement and Record of Decision, Sierra Nevada Forest Plan Amendment The Sierra Nevada Forest Plan Amendment (SNFPA or Framework) is an amendment to the Pacific Southwest Regional Guide, the Intermountain Regional Guide, and LRMPs for national forests in the Sierra Nevada and Modoc Plateau, including the ENF (USFS 2004). The Framework addresses five problem areas, including old forest ecosystems and associated species and aquatic, riparian, and meadow ecosystems and associated species, which were considered by the USFS to need urgent attention at the Sierra range-wide scale. Management recommendations in the Framework strive to protect, increase, and perpetuate desired conditions of old forest ecosystems and conserve their associated species (e.g., California spotted owl and Pacific marten) and to protect and restore desired conditions of aquatic, riparian, and meadow ecosystems. The Framework addresses the stated needs of: (1) sustaining desired conditions of old forest ecosystems; (2) protecting and restoring riparian, aquatic, and meadow ecosystems; (3) combating noxious weeds; (4) improving fire and fuels management; and (5) sustaining desired conditions of lower west side hardwood ecosystems in the affected national forests. The Record of Decision for the Framework was submitted with the FEIS and provides the rationale for the decision to select the specified alternative. The preferred alternative applies a cautious approach for vegetation and fuels management in habitats for sensitive wildlife species, particularly those associated with old forest ecosystems, while recognizing the need to reduce fire threat to human communities.

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The goal of the Forest Sensitive Plant Program is to maintain viable populations of sensitive plant species and, under Standards and Guidelines for Management Practice 49, “provide for protection and habitat needs of sensitive plants so that Forest activities will not jeopardize the continued existence of such species" (USFS 1989).

Current policy as stated in the USFSM (2670.32) states the following related to sensitive species:

1. Assist states in achieving their goals for conservation of endemic species. 2. Review programs and activities as part of the National Environmental Policy Act of 1969 process through a BE, to determine their potential effect on sensitive species. 3. Avoid or minimize impacts to species whose viability has been identified as a concern. 4. Analyze, if impacts cannot be avoided, the significance of potential adverse effects on a species’ population or its habitat within the area of concern and on the species as a whole. (The line officer, with project approval authority, makes the decision to allow or disallow impact, but the decision must not result in loss of species viability or create significant trends toward federal listing.) 5. Establish management objectives in cooperation with the states when projects on National Forest System lands may have a significant effect on sensitive species population numbers or distributions. Establish objectives for federal candidate species, in cooperation with the USFWS or NOAA Fisheries and the states.

USFSM 2900, Invasive Species Management, sets forth National Forest System policy, responsibilities, and direction for the prevention, detection, control, and restoration of effects from aquatic and terrestrial invasive species (including vertebrates, invertebrates, plants, and pathogens).

The SNFPA (USFS 2004) provides standards and guidelines for managing noxious weeds, including the following:

1. As part of project planning, conduct a noxious weed risk assessment to determine risks for weed spread (high, moderate, or low) associated with different types of proposed management activities. Refer to weed prevention practices in the Regional Noxious Weed Management Strategy to develop mitigation measures for high and moderate risk activities. 2. When recommended in project-level noxious weed risk assessments, consider requiring off-road equipment and vehicles (both USFS and contracted) used for project implementation to be weed free. 3. Minimize weed spread by incorporating weed prevention and control measures into ongoing management or maintenance activities that involve ground disturbance or the possibility of spreading weeds.

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4. Conduct follow-up inspections of ground-disturbing activities to ensure adherence to the Regional Noxious Weed Management Strategy. 5. As outlined in the Regional Noxious Weed Management Strategy, when new, small weed infestations are detected, emphasize eradication of these infestations while providing for the safety of field personnel.

2.5 USFS Species-specific Land Allocations, Desired Conditions, and Standards and Guidelines The SNFPA (USFS 2004) relies on a network of land allocations and has an associated set of desired conditions, management intents, and management objectives. These three elements provide direction to land managers for designing and developing fuels and vegetation management projects. Species-specific land allocations, desired conditions, and standards and guidelines are included in the SNFPA for northern goshawk and California spotted owl. Each of these is discussed below.

2.5.1 Northern Goshawk

Land Allocations The USFS is directed to establish and maintain 200-acre Protected Activity Centers (PACs) around all known and newly discovered breeding territories of northern goshawks on national forest lands within the Sierra Nevada (USFS 2004). PACs are intended to contain the best available nesting habitat in the largest contiguous blocks possible, based on aerial imagery. In patchy habitats, PACs are to consist of multiple patches greater than 30 acres within 0.5 mile of the nest site. Best available forest stands for PACs on the west side of the Sierra Nevada have the following characteristics: (1) trees in the dominant and co-dominant crown classes average 24 inches diameter at breast height (DBH) or greater, and (2) stands have at least 70 percent tree canopy cover. Non-forest vegetation types (e.g., brush and meadows) are not counted as part of the 200 acres.

As additional nest location and habitat data become available, the USFS is directed to adjust PAC boundaries as necessary to better include the best available 200 acres. PACs are to be maintained regardless of occupancy status, unless the habitat is rendered unsuitable by a catastrophic stand-replacing event (e.g., fire) and there are no opportunities to remap the PAC in proximity to the affected PAC (USFS 2004).

Desired Conditions The desired conditions for stands in each PAC include: (1) at least two tree canopy layers; (2) dominant and co-dominant trees with average diameters of at least 24 inches DBH; (3) at least 60 to 70 percent canopy cover; (4) some very large snags (greater than 45 inches DBH); and (5) snag and down woody material levels that are higher than average.

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Standards and Guidelines Standards and guidelines for northern goshawk require maintenance of a limited operating period (LOP), prohibiting vegetation treatments within approximately 0.25 mile of the nest site during the breeding season (February 15 through September 15) unless surveys confirm that northern goshawks are not nesting. If the nest stand within a PAC is unknown, either the LOP is applied to a 0.25-mile area surrounding the PAC or a survey is conducted to determine the nest stand location.

The LOP may be waived for vegetation treatments of limited scope and duration when a BE determines that such projects are unlikely to result in breeding disturbance considering their intensity, duration, timing, and specific location. Where a BE concludes that a nest site will be shielded from planned activities by topographic features that will minimize disturbance, the LOP buffer distance may be modified.

Mechanical treatments may be conducted in no more than 5 percent per year and 10 percent per decade of the acres in northern goshawk PACs in the 11 Sierra Nevada national forests.

Impacts must be mitigated where there is documented evidence of disturbance to the nest site from existing recreation, off-highway vehicle (OHV) use, and trail and road uses (including road maintenance). Proposals for new roads, trails, OHV routes, and recreational and other developments must be evaluated for their potential to disturb nest sites.

2.5.2 California Spotted Owl

Land Allocations California spotted owl PACs have been delineated on national forest lands since 1986. Current management direction (USFS 2004) requires 300-acre PACs around all known and newly discovered territories of California spotted owls in Sierra Nevada forests. PACs are intended to contain the best available habitat in as compact a unit as possible. Best available habitat in general includes: (1) two or more canopy layers; (2) dominant and co-dominant trees in the canopy averaging at least 24 inches DBH; and (3) at least 70 percent total canopy cover. As additional nest location and habitat data become available, the USFS is directed to adjust PAC boundaries as necessary to better include the best available 300 acres. PACs are to be maintained regardless of occupancy status, unless the habitat is rendered unsuitable by a catastrophic stand- replacing event (e.g., fire) and there are no opportunities to remap the PAC within a 1.5-mile radius of the affected PAC (USFS 2004).

Desired Conditions The desired conditions for stands in each PAC include: (1) at least two tree canopy layers; (2) dominant and co-dominant trees with average diameters of at least 24 inches DBH; (3) at least 60 to 70 percent canopy cover; (4) some very large snags (greater

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than 45 inches DBH); and (5) snag and down woody material levels that are higher than average.

Standards and Guidelines Standards and guidelines for California spotted owl require maintenance of an LOP, prohibiting vegetation treatments within approximately 0.25 mile of the activity center during the breeding season (March 1 through August 15), unless surveys confirm that California spotted owls are not nesting (as per Guidance on Limited Operating Periods for the California Spotted Owl, dated April 6, 2015).

Prior to implementing activities either within or adjacent to a California spotted owl PAC where the location of the nest site or activity center is uncertain, surveys must be conducted to either establish or confirm the location of the nest or activity center.

The LOP may be waived for vegetation treatments of limited scope and duration when a BE determines that such projects are unlikely to result in breeding disturbance considering their intensity, duration, timing, and specific location. Where a BE concludes that a nest site will be shielded from planned activities by topographic features that will minimize disturbance, the LOP buffer distance may be modified.

Vegetation treatments may be conducted in no more than 5 percent per year and 10 percent per decade of the acres in California spotted owl PACs in the 11 Sierra Nevada national forests. The number of PACs treated should be monitored at a bioregional scale.

Impacts must be mitigated where there is documented evidence of disturbance to the nest site from existing recreation, OHV use, and trail and road uses (including road maintenance). Proposals for new roads, trails, OHV routes, and recreational and other developments must be evaluated for their potential to disturb nest sites.

2.6 Resource Protection Measures The following measures and best management practices (BMPs) are proposed to minimize potential project impacts on botanical resources. Any additional measures included in the project permits and approvals will also be implemented as part of the project. Refer to Appendix B for a complete list of design criteria that includes measures for protection of environmental resources.

2.7 General Construction Measures • GEN 1 – SMUD will comply with the Fire Prevention and Response Plan during implementation of the project. This includes compliance with the SMUD Hot Work Standard.

• GEN 2 – Construction activities will be limited to the project site. The construction site will be clearly identified on the construction drawings and will be staked and flagged where necessary prior to initiation of construction activities.

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• GEN 3 – SMUD will not place construction equipment on USFS lands prior to actual use or allow equipment to remain on USFS lands subsequent to actual use, except for a reasonable mobilization and demobilization period agreed to by the USFS.

• GEN 4 – Tarps will be used for laydown of materials, equipment, and tools, and for secondary containments.

• GEN 5 – All waste and construction debris will be collected and disposed of at an authorized landfill or other legal disposal area.

• GEN 6 – Where present, existing paved and unpaved roads will be used to access the work area. Vehicles and equipment will be parked on pavement, existing roads, and previously disturbed areas to the extent practicable.

• GEN 7 – Trash dumping, firearms, open fires (such as barbecues), hunting, and pets will be prohibited at the project site.

• GEN 8 – After completion of construction activities, contractors will remove any temporary fill and construction debris and, where feasible, restore disturbed areas to pre-project conditions.

• GEN 9 – Vehicle speeds on unpaved roads will be limited to 15 miles per hour (mph) or less.

2.8 Water Quality Measures • WQ 1 – Prior to construction, SMUD will file an Erosion Control Measures Plan with the USFS for approval. The plan will include measures to control erosion, stream sedimentation, dust, and soil mass movement attributable to the project. Following approval, the plan will be submitted to FERC.

• WQ 2 – During construction, no equipment maintenance will be conducted within 100 feet of Union Valley Reservoir.

• WQ 3 – All stockpiled soil will be covered to minimize soil erosion when not actively being used, prior to forecast rain, and during rain events.

• WQ 4 – Soil stabilization and erosion control BMPs will be implemented to minimize soil erosion on newly graded or exposed soil areas resulting from construction.

• WQ 5 – SMUD will not use tightly woven fiber netting, plastic mono-filament netting, or similar material for erosion control or other purposes to minimize the chances for wildlife to be trapped, injured, or killed.

• WQ 6 – The contractor will implement BMPs per the Caltrans Stormwater Quality Handbooks for Construction Sites to ensure erosion and sediment control. BMPs may include, but are not limited to, SS-1 (Scheduling), SS-2 (Preservation of

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Existing Vegetation), WE-1 (Wind Erosion Control; Note, chemical dust palliatives are prohibited by contract documents), TC-1 (Stabilized Construction Entrance), WM-3 (Stockpile Management), WM-4 (Spill Prevention and Control), WM-6 (Hazardous Waste Management), NS-3 (Paving and Grinding Operations), NS-9 (Vehicle and Equipment Fueling), and NS-10 (Vehicle and Equipment Maintenance), per the Caltrans Stormwater Quality Handbooks for Construction Sites.

• WQ 7 – Stormwater Pollution Prevention Plan (SWPPP). SMUD will obtain coverage from the State Water Board under the General Permit for Discharges of Storm Water Associated with Construction Activity. A SWPPP will be developed and implemented as part of the project. At a minimum, fiber rolls, gravel check dams, and fencing will be utilized to control site erosion.

2.9 Hazardous Material Measures • HAZ 1 – SMUD will comply with the UARP Hazardous Substances Plan during implementation of the project.

• HAZ 2 – Prior to any hazardous materials being brought onsite, the contractor shall provide Safety Data Sheets to the SMUD Construction Management Inspector (CMI) for approval.

• HAZ 3 – All hazardous materials will be stored in labeled and chemical-compatible containers in accordance with federal, state, and local regulations. All hazardous waste containers shall be stored in secondary containment.

• HAZ 4 – When either a fuel-driven compressor or a generator is used, it will be placed in an industry-standard secondary containment that will capture any fuel or oil drips and be located a minimum of 100 feet from surface waters.

• HAZ 5 – All fuel and oil will be stored in upland staging areas in watertight containers with appropriate, industry-standard secondary containment to prevent any spillage or leakage from delivering to receiving water.

2.10 Biological Resource Measures • BIO 1 – Environmental Training:

o Contractors working on SMUD projects will receive environmental awareness training prior to beginning work activities. The training will include review of environmental laws and guidelines that must be followed by all personnel to either reduce or avoid effects on special- status species during construction. In addition, locations of any project- specific sensitive habitats or species will be discussed.

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• BIO 2 – Inadvertent Discovery:

o If occurrences of USFS, USFWS, or CDFW sensitive species are detected prior to or during construction of the project, SMUD will immediately notify the USFS, USFWS, and CDFW. If the USFS, USFWS, or CDFW determine that project-related activities are adversely affecting sensitive species, SMUD will, in consultation with the USFS, USFWS, and CDFW, develop and implement appropriate protection measures.

• BIO 3 – Upland Swale:

o SMUD will comply with the SNFPA Standards and Guidelines for Riparian Conservation Areas as defined in the Sunset Campground Rehabilitation Project Riparian Conservation Objectives Consistency Report (SMUD 2016).

• BIO 4 – Retention of Trees:

o Project design and engineering will retain overstory and mature, large trees within the project area to the extent possible.

o The project has been designed to minimize removal of trees greater than 10 inches DBH. During construction, SMUD will further avoid removal of trees identified in Figure 4, to the extent possible, based on site-specific conditions.

• BIO 5 – Preconstruction Raptor Surveys:

o A qualified biologist will search within 0.25 mile of the site for raptor nests in conjunction with annual bald eagle monitoring completed as part of the UARP.

o Biologists will conduct a visual and aural search of the survey area on foot using binoculars to scan tree tops for the presence of raptor nests.

o Consistent with the USFWS Bald Eagle Management Guidelines, a 660- foot no-activity buffer will be established around active bald eagle nests during the breeding season or until the young have fledged the nest, as determined by a qualified biologist. This protective buffer may be modified through consultation with resource agencies (USFWS, USFS, and CDFW) considering the location of the nest and proposed construction measures.

o If any active nests are identified, a species-appropriate buffer for the nest will be developed in consultation with appropriate resources agencies (USFS, CDFW, and/or USFWS). The site-specific buffers will

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be developed considering the species, the location of the nest, and the nature of the construction activities to be implemented.

o If no active nests are detected during these surveys, no additional mitigation is required.

• BIO 6 – Bald Eagle Roost Protection

o Project design will be modified to prevent the loss of any bald eagle roost trees identified through ongoing monitoring activities.

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Figure 4. Sunset Campground Rehabilitation Project, Trees To Be Removed.

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3 Methods

3.1 Vegetation Communities/Wildlife Habitats Information on vegetation communities within the project area was obtained from the Vegetation Mapping Technical Report conducted for relicensing of the UARP (SMUD 2004a). Vegetation classification followed the CalVeg system described by Matyas and Parker (1980) and the USFS (USFS 2000) and was cross-referenced with the California Wildlife Habitat Relationship (CWHR) System (CWHR 2016).

3.2 Special-status Wildlife Species Information on the special-status wildlife species described in this section is based on a review of existing literature and biological surveys completed as part of relicensing of the UARP. This includes:

• CDFW CNDDB (2016)

• ENF, Geographic Information System (GIS) Wildlife Data Files obtained in 2017

• Regional Forester’s List of Sensitive Animal Species for Region 5 (USFS 2013a)

• USFWS Species List (USFWS 2016a)

• Amphibians and Aquatic Reptiles Technical Report, Upper American River Project (FERC No. 2101) (SMUD 2005)

• Bald Eagle and Osprey Technical Report, Upper American River Project (FERC No. 2101) (SMUD 2004b)

• Bats Technical Report, Upper American River Project (FERC No. 2101) (SMUD 2004c)

• Willow Flycatcher Nesting Habitat Technical Report, Upper American River Project (SMUD 2004d)

• Final Rule for the Designation of Critical Habitat for the Sierra Nevada Yellow- Legged Frog, the Northern Distinct Population Segment of the Mountain Yellow- Legged Frog, and the Yosemite Toad (Federal Register [FR] Vol. 81, No. 166, Pages 59046–59119), August 26, 2016

• Final Rule for Endangered Species Status for Sierra Nevada Yellow-Legged Frog and Northern Distinct Population Segment of the Mountain Yellow-Legged Frog, and Threatened Species Status for Yosemite Toad (FR, Vol. 79, No. 82, Pages 24256– 24310), April 29, 2014

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The results of the literature review and field surveys are discussed in the following subsections. Figure 3 shows the locations of special-status wildlife species known to occur in the vicinity of the project area.

4 Results The following section describes the vegetation communities/wildlife habitats and special-status wildlife species that occur or may potentially occur in the project area. Refer to Figure 3 for species locations.

4.1 Vegetation Communities/Wildlife Habitats The project area is located at an elevation of 4,870 to 4,975 feet above mean sea level. It consists of barren/developed areas and an upland swale surrounded by mixed conifer–fir forest. The project area is located directly adjacent to Union Valley Reservoir, which is considered open water habitat (Figure 5). Table 2 provides the CWHR classification for each vegetation community. These vegetation communities/wildlife habitats and the adjacent open water habitat are described below.

Table 2. Wildlife Habitats Present in the Project Area

CWHR Wildlife Habitat1 CalVeg Vegetation Alliance2 Montane Hardwood-Conifer Mixed Conifer-Fir Barren Barren/Developed Fresh Emergent Wetland - Lacustrine Open Water 1 Source: CWHR 2016. 2 Source: USFS 2014. Source: SMUD 2016.

4.1.1 Barren/Developed The “barren” classification is used to map lands supporting little or no vegetation, including drawdown zones around reservoirs. Sunset Campground supports developed areas, including campsites, shower facilities, restrooms, water system, and access and interior roads. In addition, the drawdown zone around Union Valley Reservoir does not support vegetation and is considered barren.

4.1.2 Mixed Conifer–Fir The mixed conifer–fir community is the high-elevation counterpart of the mixed conifer– pine community and occurs from approximately 3,700 to 8,800 feet in elevation. Three major species define the mixed conifer–fir community: white fir (Abies concolor), Jeffrey pine (Pinus jeffreyi), and lodgepole pine (Pinus contorta). As elevation increases, lodgepole pine (Pinus contorta) and red fir (Abies magnifica) become more prominent. Other associates include sugar pine (Pinus lambertiana) and incense cedar (Calocedrus decurrens). The understory habitats are usually a function of canopy closure—open areas support greenleaf manzanita (Arctostaphylos patula), mountain whitethorn (Ceanothus cordulatus), and bitter cherry (Prunus emarginata), while closed canopies

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support Sierra gooseberry (Ribes roezlii) and prince’s pine (Chimaphila umbellata). Canopy closure within the project area is primarily dense (60–100 percent canopy closure) with small patches of open cover (0–39 percent canopy closure) and moderate (40–59 percent canopy closure) (Figure 6; CWHR 2016).

4.1.3 Open Water Union Valley Reservoir is an open water habitat with a shoreline area that contains a mixture of bedrock, sand, and bare soils incapable of supporting riparian vegetation. No riparian habitat is present along the shoreline of Union Valley Reservoir adjacent to the project area. The vegetation surrounding the reservoir is composed of mixed conifer–fir forest.

4.1.4 Upland Swale An upland swale was identified within the project area. The upland swale is located at a culvert inlet 70 feet from campsite #87 within Sunset Loop (Figure 5). The swale is a topographical depression area that is approximately 0.11 acre in size and supports hydrophytic vegetation. Plant species within this area include species of sedge (Carex sp.), rose meadowsweet or dense-flowered spiraea (Spiraea splendens), Klamath rush (Juncus exiguus), and serviceberry (Amelanchier alnifolia). This upland swale is not considered to be a jurisdictional water of the U.S. or state and is not hydrologically connected to Union Valley Reservoir or any other jurisdictional waters.

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Figure 5. Vegetation Communities Known to Occur in the Project Vicinity.

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Figure 6. Canopy Closure within the Project Area

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4.2 Special-status Wildlife This section discusses special-status wildlife species that are known to occur or may potentially occur in the project area. Based on literature, survey data, and an evaluation of the location and elevation of the proposed project and wildlife habitats present, 8 special-status wildlife species are known to occur or could potentially occur in the project area (Table 1). Refer to Figure 3 for locations of documented wildlife occurrences in relation to the project area.

4.2.1 Special-status Amphibians SNYLF (Rana sierrae) FE, FSS, CT, CDFW Watchlist. USFWS listed SNYLF as endangered on April 29, 2014 (FR, Vol. 79, No. 82, Pages 24256–24310) and issued a final ruling on critical habitat on August 26, 2016 (FR, Vol. 81, No. 166, Pages 59046– 59119). USFWS describes habitat for SNYLF as “lakes, ponds, marshes, meadows, and streams at elevations typically ranging from 1,370 to 3,550 meters (4,500 to 12,000 feet (ft.))” (FR, Vol. 79, No. 82, Page 24259). SNYLF are a highly aquatic species and are generally not found more than 3 feet from water. Both tadpoles and adults typically use open shorelines that gently slope up to shallow waters of only 2 to 3 inches deep. SNYLF are typically absent from aquatic habitats that support predatory fish (FR, Vol. 79, No. 82, Pages 24259–24260). The nearest known occurrence of SNYLF is 4.5 miles northeast of the project area on Bassi Fork Creek (Figure 2).

Suitable Habitat USFS Region 5 recently completed ESA Section 7 consultation with the USFWS on the effects of ongoing implementation of programs within nine national forests in the Sierra Nevada on recently listed special-status amphibians, including SNYLF (USFWS 2014). As part of consultation, the USFS and USFWS developed GIS layers showing the location of suitable habitat for SNYLF within Region 5 forests, including the ENF. Suitable habitat for SNYLF was defined as follows:

• Typically occurs above 4,500 feet in elevation, but in some areas (including west side of Plumas National Forest), it may occur as low as 3,500 feet.

• Includes either permanent water bodies or those hydrologically connected with permanent water, such as wet meadows, lakes, streams, rivers, tarns, perennial creeks, permanent plunge pools within intermittent creeks, and pools, such as a body of impounded water contained above a natural dam.

• Includes adjacent areas up to a distance of 82 feet.

• When water bodies occur within 984 feet of one another (as is typical of some high mountain lake habitat), suitable habitat for dispersal and movement includes the overland areas between lake shorelines.

• In mesic areas, such as lake/meadow systems, either the entire contiguous or proximate areas are suitable habitat for dispersal and foraging.

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Within the project area, Union Valley Reservoir meets the USFWS/USFS definition of suitable habitat.

Although the project area is located at an elevation between 4,870 and 4,975 feet, it should be noted that in the vicinity of the proposed project, SNYLF are typically found at much higher elevations, above 6,000 feet in Highland, Leland, McConnell, Gertrude, and Twin Lakes (CDFW 2012; CNDDB 2016). The nearest known occurrence is at Bassi Fork Creek located at an elevation of 6,000 feet. Extensive surveys have not been conducted for this species around the project area.

Special-status Birds Bald eagle (Haliaeetus leucocephalus) FSS, CE, CFP, BCC. Bald eagles nest in either mature, old-growth trees or snags near large aquatic ecosystems (lakes, reservoirs, or free-flowing rivers) that support an adequate food supply. The project area and surrounding areas represent foraging and nesting habitat for bald eagles. Bald eagles have historically and are currently known to forage, roost, and nest in trees along Union Valley Reservoir. Bald eagle surveys were conducted in 2016 for the UARP. These surveys encompassed the project area and Union Valley Reservoir. Based on these surveys, there is a documented bald eagle nest, winter roost, and foraging perch in the project area (Figure 3; SMUD 2017). The location of each of these is summarized below.

• The bald eagle nest is located in a large, mature tree adjacent to campsite #19 in Shady Loop in 2016. Two chicks fledged from this nest location (SMUD 2017).

• The bald eagle winter roost is present in Shady Loop of Sunset Campground (SMUD 2017).

• The foraging perch is located in Shady Loop of Sunset Campground (SMUD 2017).

Historically, bald eagles have been nesting and roosting near Union Valley Reservoir since 1986 (SMUD 2004b). Historical nests and roosts have been documented at the following locations in the vicinity of the project. These historical locations are not depicted on Figure 3.

• Historical nests:

o Wench Creek (1986–1988 and 1990–1991)

o West Point (1989)

o Granlees Point (1992–2004) • Historical night roosts:

o Night roosts were documented in 2003 in the vicinity of the project at Granlees Point and occasionally on the Sunset/Fashoda Peninsula.

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Special-status Bats Pallid bat (Antrozous pallidus) FSS, CSC. A year-round resident in California, the pallid bat is found in arid desert areas, grasslands and oak savanna, coastal forested areas, and coniferous forests of the mountain regions of California. The active period for the species is April through October. Maternal colonies are active during this period and are often very large. Rock outcroppings, caves, hollow trees, buildings, and bridges are used for maternal roost sites. The hibernation period for the species is October through March. While not fully migratory, this species may migrate to suitable hibernation sites during these months.

During technical studies conducted for the UARP, Union Valley Reservoir and Sunset Campground were surveyed for the presence of bats (SMUD 2004c). No pallid bats were captured, and no evidence of bats was observed either in the project area or surrounding areas (SMUD 2004c). The project area represents appropriate foraging and roosting habitat for pallid bat.

Townsend’s big-eared bat (Corynorhinus townsendii) FSS, CSC. Townsend’s big-eared bat is a year-round resident in California, occurring from low desert to mid-elevation montane habitats. They are found primarily in rural settings, from inland deserts to coastal redwoods, oak woodland of the inner Coast Ranges and Sierra Nevada foothills, and low- to mid-elevation mixed coniferous-deciduous forests. Townsend’s big-eared bats are non-migratory, year-round residents that are active April through September and hibernate October through March. They typically roost during the day in caves and mines, but can roost in buildings that offer suitable conditions (Kunz 1982). Night roosts are in more open settings and include bridges. This species uses caves, tunnels, mines, and buildings for maternity roosts. Hibernation occurs from October through April for prolonged periods in colder areas and intermittently in non-freezing areas.

During technical studies conducted for the UARP, Union Valley Reservoir and Sunset Campground were surveyed for the presence of bats (SMUD 2004c). No Townsend’s big-eared bats were captured, and no evidence of bats was observed in either the project area or surrounding areas (SMUD 2004c). The project area represents appropriate foraging and roosting habitat for Townsend’s big-eared bat.

Fringed myotis (Myotis thysanodes) FSS. Little is known about the migratory patterns of fringed myotis bats; however, it is likely that they are either non-migratory or only migrate short distances (Keinath 2004). Fringed myotis bats use a broad range of habitats and are most frequently found in either oak or conifer habitats at middle elevations, as well as grasslands. This species uses caves and rock crevices, mines, and buildings for roosting sites, and they may also roost in the hollows of tree snags. The active period for this species is generally April through September. During this period, maternal colonies (up to 200 individuals) form in caves, mines, buildings, and crevices. The hibernation period is generally from October through March.

During technical studies conducted for the UARP, Union Valley Reservoir and Sunset Campground were surveyed for the presence of bats (SMUD 2004c). No fringed myotis

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bats were captured, and no evidence of bats was observed in either the project area or surrounding areas (SMUD 2004c). The project area represents appropriate foraging and roosting habitat for fringed myotis.

Special-status Mesocarnivores Pacific marten (Martes caurina) FSS. The Pacific marten forages in coniferous forests with large diameter trees and snags, large down logs, moderate-to-high canopy closure, and an interspersion of riparian areas and meadows. Their optimal habitats are various mixed evergreen forests with more than 40 percent crown closure and large trees and snags for den sites.

There are no documented Pacific marten dens in the project area. Forested areas surrounding the project area represent potential foraging habitat (generally, mature, dense forest stands with snags and greater than 40 percent canopy cover). However, due to the high degree of human activity during the recreation season at the campground, Pacific marten are unlikely to occur within the project area.

5 Effects of Proposed Project Implementation of the proposed project could either directly or indirectly affect special- status wildlife. Direct effects are caused by the proposed activity and are immediate in nature (e.g., loss of individuals during project activities, loss of habitat, harassment, disrupted reproduction, or noise disturbance). Indirect effects are caused by the proposed activity but either occur later in time or are farther removed in distance, but are reasonably certain to occur. Provided below is a discussion of potential direct and indirect impacts to special-status wildlife as a result of the proposed project.

5.1 Special-Status Amphibians

5.1.1 Sierra Nevada Yellow-Legged Frog The proposed project will have no effect on critical habitat for SNYLF.

The closest critical habitat unit (Subunit 2E, Crystal Range) is 6 miles northeast of the project area (refer to Figure 2). The project area is not located in critical habitat for SNYLF. Therefore, the proposed project will have no direct or indirect effects on, and will not result in, adverse modification of SNYLF critical habitat.

The proposed project will have no effect on suitable habitat for SNYLF.

The proposed project will have no effect on suitable habitat for SNYLF for several reasons described below.

While Union Valley Reservoir (in the project area) meets the USFS/USFWS definition of suitable habitat for SNYLF, the project area has never been known to support SNYLF populations. USFWS (USFWS 2016b) has stated that SNYLF are not generally found in large reservoirs, such as Union Valley Reservoir, for several reasons:

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• Construction of dams and associated infrastructure, as well as flooding from the resulting impoundment, results in the degradation and removal of riparian habitat.

• Dams alter the natural flow regime, temperature, and sediment loads of the waterways they impound.

• Reservoirs provide habitat for introduced predators, including fish, bullfrogs, and crayfish.

In the Final Rule for the listing of SNYLF, USFWS stated that they considered dams and diversions a “moderate, prevalent threat to the persistence and recovery of the species.” This assessment was downgraded to “a minor, localized threat” in the Final Rule based on the fact that “large water and power projects generally do not overlap with the current accepted distribution of SNYLF in the Sierra Nevada” (USFWS 2016b).

Union Valley Reservoir is routinely stocked and supports a large trout population, and there is a strong negative correlation between introduced trout and SNYLF. The presence and abundance of the species is dramatically reduced in stocked reservoirs (USFWS 2016b). There are also other SNYLF predators within Union Valley Reservoir including smallmouth bass and bullfrogs. Therefore, the presence of trout and other predatory species likely precludes establishment of SNYLF populations in the reservoir.

Union Valley Reservoir lake levels also fluctuate throughout the year, causing the main body of the reservoir to be unsuitable habitat for SNYLF. Therefore, SNYLF are unlikely to occur in Union Valley Reservoir.

Additionally, all project work and staging areas are limited to upland areas within the existing campground footprint, and no work within aquatic habitat will occur. Recreation use (e.g., camping; cycling; and water sports including the use of boats, wave-runners, and ski-doos) and maintenance, and associated site disturbance has been ongoing at Sunset Campground since it was developed in 1966.

Finally, SMUD will implement the design criteria described in Section 2 to protect water quality in Union Valley Reservoir during implementation of construction activities. This includes general construction measures that limit project activities to a designated work area (GEN 2), BMPs and measures to protect water quality from erosion and sedimentation (WQ 1–6), and hazardous materials measures to prevent contamination of aquatic habitats (HAZ 1–5). In addition, a General Construction National Pollutant Discharge Elimination System (NPDES) permit will be obtained from the State Water Board and SMUD will develop and implement a SWPPP (WQ 7).

Considering that Union Valley Reservoir supports predatory fish, that this species has never been documented and is highly unlikely to be utilizing habitat in Project area, that all project activities are limited to upland areas that have existing and ongoing disturbance related to recreation and maintenance activities; and with incorporation design criteria to protect water quality during implementation of the project, the project will have no effect on suitable habitat for SNYLF.

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The proposed project will have no effect on SNYLF individuals.

Focused surveys for SNYLF were not completed as part of the project. However, based on review of existing data, there are no recorded occurrences of SNYLF in the project area. Known populations of SNYLF are mainly concentrated at elevations of 6,000 feet above mean sea level or higher in the ENF. The project area is located between 4,870 and 4,975 feet in elevation. The nearest known occurrence is located 4.5 miles northeast of the project area in Bassi Fork Creek (6,000-foot elevation) (Figure 2). There were two reports for this location in 1992, each of a single adult SNYLF. SNYLF move primarily within stream systems and are documented to move at distances of up to 2 miles in or along streams, typically to disperse to better lentic breeding habitat. Overland movements of SNYLF have been recorded at approximately 215 feet to 0.26 mile (FR, Vol. 79, No. 82, Page 24260). Based on this information, Union Valley Reservoir is located outside the overland dispersal range of known SNYLF populations, and outside the aquatic dispersal distance from the Bassi Fork Creek occurrence (4.5 miles). Union Valley Reservoir also supports numerous predatory fish species including rainbow trout, lake trout, brown trout, Kokanee, green sunfish, and smallmouth bass. The presence of predatory fish makes it highly unlikely that a breeding SNYLF population could be sustained in the reservoir (USFWS 2016b). Union Valley Reservoir lake levels also fluctuate throughout the year, causing the main body of the reservoir to be unsuitable habitat for SNYLF. Therefore, SNYLF are unlikely to occur in Union Valley Reservoir.

In addition, SNYLF are highly aquatic and, on average, are not found more than 3.0 feet from water (USFWS 2016b). Therefore, because the work activities are restricted to upland areas 50 feet from Union Valley Reservoir, in the unlikely event that individuals are in the reservoir, project activities will not result in direct effects to SNYLF.

Finally, the design criteria in Section 2 state that SMUD will not use tightly woven fiber netting or similar material for erosion control or other purposes where construction activities are implemented within suitable habitat (as defined by USFWS and USFS), to ensure that special-status amphibians and wildlife are not trapped, injured, or killed (WQ 5). In addition, plastic mono-filament netting or similar material will not be used because individuals may become entangled or trapped in it.

Because SNYLF are not likely to occur in the project area, the project will only be implemented in upland areas that have existing and ongoing disturbance related to recreation and maintenance activities, the project is short term and temporary, and design criteria will be incorporated, the project will have no direct or indirect effects on SNYLF individuals.

5.2 Special-status Birds

5.2.1 Bald Eagle The proposed project may affect bald eagles.

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The proposed project will be implemented during the breeding season for bald eagles (February through August). Bald eagles have recently (2016 and 2017) nested in Sunset Campground near campsite #19 (2016) and are known to forage and nest in the vicinity of Union Valley Reservoir. Therefore, construction activities could potentially result in disturbance of either foraging or nesting bald eagles.

The USFWS has developed the National Bald Eagle Management Guidelines (USFWS 2007), which recommend that activities be restricted within 660 feet of bald eagle nests and provide general guidelines to modify activities in the vicinity of bald eagle roosts.

To protect active bald eagle nests, SMUD will implement BIO 5. This includes monitoring of existing nests and identification of any new nests during the annual bald eagle monitoring completed at Union Valley Reservoir as part of the UARP. If a new nest is documented, no construction activities will be initiated within the no-activity buffer (660 feet for bald eagles) until the fledglings have left the nest, unless appropriate alternative measures have been developed and approved through consultation with resource agencies. Implementation of BIO 5 will reduce any potential effects to existing and new or previously undocumented nests.

The proposed project includes removal of several trees. The trees are located within a developed campground in a dense mixed conifer–fir forest. All trees that will be removed are located within disturbed areas in campsites and directly adjacent to campsites and loop roads. The project has been designed to retain overstory and mature, large trees to the extent possible, and many large-diameter dominant trees will remain. To further reduce tree removal, SMUD will implement BIO 4, which allows for avoidance of trees that have been identified for removal based on site-specific conditions identified during construction. SMUD will implement preconstruction bird surveys, per BIO 5. If a new nest is documented, no construction activities will be initiated within the no-activity buffer until the fledglings have left the nest, unless appropriate alternative measures have been developed and approved through consultation with resource agencies. Implementation of design criteria will reduce effects on bald eagle nesting and foraging habitat. SMUD will also implement BIO 6, which protects all bald eagle roost trees, identified through ongoing monitoring activities, from removal as part of the project. Therefore, any impacts to bald eagle will be minimal.

With implementation of BIO 4, 5, and 6 impacts to bald eagles would be minimized. The project may affect bald eagles, but is not likely to result in a trend toward federal listing.

5.3 Special-status Bats

5.3.1 Pallid Bat, Townsend’s Big-Eared Bat, and Fringed Myotis Bat The proposed project may affect pallid bats, Townsend’s big-eared bats, or fringed myotis bats.

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The proposed project may potentially overlap with the active (breeding) season and the hibernation season for pallid bats, Townsend’s big-eared bats, and fringed myotis bats. Hollow trees, buildings, caves, mines, and crevices represent potential roosting habitat for these species.

During technical studies conducted for the UARP, Union Valley Reservoir and Sunset Campground were surveyed for the presence of bats (SMUD 2004c). No special-status bats were captured in the project area or surrounding areas, and no bat evidence (e.g., guano, staining, etc.) was observed in project facilities or recreation facilities in Sunset Campground (SMUD 2004c).

Implementation of the project could potentially affect roosting special-status bat species. The project includes replacement of 15 single-seat or two-seat vault toilets with Forest Service-approved pre-fabricated restrooms. No evidence of bat use was observed in the existing toilet structures during technical studies conducted for the UARP or during reconnaissance surveys.

Two special-status bat species roost in cavities and may use hollow trees or snags. The project includes removal of 520 trees. The majority of these trees are small, young trees with a DBH of 10 to 24 inches (416, which is over 80 percent) that do not represent roosting habitat. The remaining trees (89 trees with 25–35 inches DBH and 15 trees with DBH greater than 35 inches) are mature trees that are greater than 25 inches DBH. None of the trees to be removed are snags. Snags and hollow trees are removed as part of the annual campground hazard tree abatement program. Although the project will result in removal of 104 trees that may potentially represent roosting habitat for special-status bats, the project area is located within a dense conifer–fir forest that provides ample roosting opportunities. The project has been designed to retain overstory and large, mature trees to the extent possible.

Noise, vibration, and human activity may cause disturbance to roosting or foraging special-status bats. However, the project area is an existing campground that has extensive human disturbance from ongoing recreation and routine maintenance of the existing facilities. The potential disturbance would be minimal because the construction activities are short term and temporary, will be restricted to designated work areas, and will be limited to daylight hours (GEN 2).

Implementation of the proposed project may affect special-status bats, but is not likely to result in a trend toward federal listing.

5.4 Special-status Mesocarnivores

5.4.1 Pacific Marten The proposed project will not affect Pacific marten.

The proposed project will not affect Pacific marten for several reasons. While the forests surrounding Sunset Campground represent potential foraging habitat, due to the

Sacramento Municipal Utility District Upper American River Project 32 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017 high degree of human activity during the recreation season at the campground, this species is unlikely to occur within the project area. Construction will be limited in scope and short term. SMUD will implement design criteria (refer to Section 2) that restrict all project activities to defined work areas and limit construction to daylight hours. With implementation of design criteria, the proposed project will not affect Pacific marten.

The proposed project will not indirectly affect Pacific marten.

Pacific marten tend to avoid areas with high human activity and are, therefore, unlikely to occur in the project area. Consequently, the project will not result in indirect effects on Pacific marten.

6 Cumulative Effects The FEIS for the issuance of the new 50-year FERC License for the UARP discusses cumulative impacts as a result of implementing all of the UARP under the new license, including all proposed recreation projects (USFS and FERC 2008).

7 Conclusions This section describes how potential effects are defined and summarizes potential impacts of implementing the proposed project on wildlife species.

7.1 U.S. Forest Service Effects Definitions • No effect – Is the appropriate conclusion for an FSS species when the effects of the action will not affect the species.

• May affect individuals, but is not likely to result in a trend toward federal listing – Is the appropriate conclusion for an FSS species when the effects of an action will not lead to federal listing or loss of species viability.

• May affect individuals and is likely to result in a trend toward federal listing – Is the appropriate conclusion for an FSS species when the effects of an action will lead to federal listing or loss of species viability.

7.2 U.S. Forest Service Effects Determinations It is our determination that the proposed project will not affect:

• SNYLF – FE, FSS, CT, CSC

• Pacific marten – FSS

It is our determination that the proposed project may affect, but is not likely to result in a trend toward federal listing of:

• Bald eagle – FSS, CE, CFP

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• Pallid bat – FSS, CSC

• Fringed myotis – FSS

• Townsend’s big-eared bat – FSS, CSC

REVIEWED BY: XX, Biologist, El Dorado National Forest DATE: XX, XX, 2017

8 References California Department of Fish and Wildlife (CDFW). 2012. Aquatic Biodiversity Management Plan for the Desolation Wilderness. December 12.

California Herps. 2017. Northern Western Pond Turtle-Actinemys marmorata. http://www.californiaherps.com/turtles/pages/a.marmorata.html. Accessed March 2017.

California Natural Diversity Database (CNDDB). 2016. Rare Find 5.0. California Department of Fish and Wildlife, Biogeographic Data Branch. Electronic Database. Accessed January 2016.

California Wildlife Habitat Relationship System (CWHR). 2016. California Department of Fish and Wildlife, Biogeographic Data Branch. V9. Database. Accessed December.

Eldorado National Forest (ENF). 2017. GIS spotted owl data layers. Received February 2017.

Federal Energy Regulatory Commission (FERC). 2014. Order Issuing New License, UARP. July 23.

Holland, D.C. 1994. The western pond turtle: habitat and natural history. Unpublished final report, U.S. Department of Energy. Portland, Oregon.

Jennings. 1994. Amphibian and reptile species of special concern in California. California Department of Fish and Game, Inland Fisheries Division, Final report, Rancho Cordova, California.

Keinath, D.A. 2004. Fringed Myotis (Myotis thysanodes): a technical conservation assessment. USDA Forest Service, Rocky Mountain Region. October 29.

Kunz, T.H. 1982. Roosting ecology of bats. Pp. 1-55 in: T.H. Kunz (editor), Ecology of Bats. Plenum Press, New York. 425 pp.

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Matyas, W.J., and I. Parker. 1980. CalVeg – Mosaic of Existing Vegetation of California. U.S. Forest Service Regional Ecology Group, San Francisco, California.

Sacramento Municipal Utility District (SMUD). 2004a. Vegetation Mapping Technical Report, Upper American River Project FERC No. 2101. July.

SMUD. 2004b. Bald Eagle and Osprey Technical Report, Upper American River Project FERC No. 2101. October.

SMUD. 2004c. Bats Technical Report, Upper American River Project FERC No. 2101. July.

SMUD. 2004d. Willow Flycatcher Nesting Habitat Technical Report, Upper American River Project FERC No. 2101. July.

SMUD. 2005. Amphibians and Aquatic Reptiles Technical Report, Upper American River Project FERC No. 2101. April.

SMUD. 2016. Riparian Conservation Objectives Consistency Report. December.

SMUD. 2017. Bald Eagle Monitoring Report. Hydro License Implementation for the Upper American River Project (FERC Project No. 2101). March 2017.

Schweitzer, D.F., N.A. Capuano, B.E. Young, and S.R. Colla. 2012. Conservation and management of North American bumble bees. NatureServe, Arlington, Virginia, and USDA Forest Service, Washington, DC.

U.S. Forest Service (USFS). 1989. Land and Resource Management Plan, Eldorado National Forest, Pacific Southwest Region.

USFS. 2000. Remote Sensing Lab CalVeg Geobook: Existing Vegetation, V1. Pacific Southwest Experiment Station, Sacramento, California.

USFS. 2004. Sierra Nevada Forest Plan Amendment, Final Environmental Impact Statement, Record of Decision. January.

USFS and FERC. 2008. Final Environmental Impact Statement for Hydropower License. Upper American River Hydroelectric Project No. 2101-084, California, and Chili Bar Hydroelectric Project FERC Project No. 2155-024, California. March 2008.

USFS. 2013a. Regional Forester’s List of Sensitive Animal Species for Region 5.

USFS. 2013b. Biological evaluation template for western bumble bee Bombus occidentalis (Greene 1858). Updated May 2013. Provided by EN2 Resources – unpublished.

Sacramento Municipal Utility District Upper American River Project 35 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

USFS. 2014. CALVEG Geographic Information Systems (GIS) data and vegetation descriptions. North Coast and Montane Ecological Province. Accessed 2016.

U.S. Fish and Wildlife Service (USFWS). 2007. National Bald Eagle Management Guidelines. May.

USFWS. 2014. Endangered Species Status for Sierra Nevada Yellow-Legged Frog and Northern Distinct Population Segment of the Mountain Yellow-Legged Frog, and Threatened Species Status for Yosemite Toad; Final Rule (Federal Register, Vol. 79, No. 82, Pages 24256–24310), April 29.

USFWS. 2016a. Species List, Information for Planning and Conservation (IPaC). Electronic Database. Accessed December 2016.

USFWS. 2016b. Designation of Critical Habitat for the Sierra Nevada Yellow-Legged Frog, the Northern Distinct Population Segment of the Mountain Yellow-Legged Frog, and the Yosemite Toad; Final Rule (FR, Vol. 81, No. 166, Pages 59046– 59119), August 26.

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Tables

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Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence

Insect

Bombus The historical range of the western bumble bee includes most of western North America. This species occidentalis Unlikely to occur. No appropriate habitat is — FSS — is dependent on continuous access to meadows with present within the project area. Western bumble floral resources from spring through late summer within bee 0.3-0.5 miles of burrowing nests (USFS 2013b). Desmocerus californicus Occurs only in the Central Valley of California below None. Project area is not within the dimorphus FT — — 3,000 feet in elevation, in association with elderberry geographic and/or elevation range of this Valley elderberry shrubs (Sambucus mexicana). species. longhorn beetle

Amphibian

Montane meadows and forest borders; breeds in None. Project area is not within the Anaxyrus canorus FT shallow pools, at lake margins, or in pools of quiet FSS CSC geographic and/or elevation range of this (6/30/14) streams at elevations ranging from 6,400 to 11,300 Yosemite toad species. feet. Perennial rocky (pebble or cobble) streams with cool, Rana boylii clear water in a variety of habitats from valley and Unlikely to occur. No appropriate habitat is — FSS CSC foothill oak woodland, riparian forest, ponderosa pine, Foothill yellow- present within the project area. legged frog mixed conifer, coastal scrub, and mixed chaparral at elevations ranging from 0 to 6,370 feet. Breeds in quiet streams and permanent, deep, cool ponds with overhanging and emergent vegetation None. No appropriate habitat is present below 5,000-foot elevation. Known to occur adjacent Rana draytonii within the project area. Nearest known to breeding habitats in riparian areas and heavily FT CSC occurrence is approximately 13 miles California red- vegetated streamside shorelines, and non-native southwest of the project area in Spivey legged frog grasslands. Sierran streams historically supported Pond (southwest of Pollock Pines). populations of red-legged frog; however, these populations have been eliminated.

Sacramento Municipal Utility District Upper American River Project 38 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence

Unlikely to occur. USFWS have identified potential habitat in the project area; however, these aquatic habitats support predatory fish populations, and there hasn’t been a documented occurrence of the Rana sierrae Streams, lakes, and ponds in montane riparian, animal in the Project area. lodgepole pine, subalpine conifer, and wet meadow Sierra Nevada FE FSS CT, W habitats. Breeds in shallow water in low-gradient The nearest known occurrence is yellow-legged frog perennial streams and lakes. Elevations range from approximately 4.5 miles to the northeast of (SNYLF) 4,500 to 12,000 feet. the project area on Bassi Fork Creek.

None. The closest critical habitat unit (Subunit 2E: Crystal Range) is located 6 miles northeast of the project area.

Reptile

Perennial wetlands and slow-moving creeks and Unlikely to occur. No individuals were ponds, from sea level to 6,000 feet in elevation, with observed during relicensing studies (SMUD Actinemys overhanging vegetation and suitable basking sites 2005). There are no known occurrences marmorata — FSS CSC such as logs and rocks above the waterline. While this within 10 miles of the project area. This species is noted at elevations up to 5,900 feet Western pond turtle species is uncommon at elevations above elevation, they are uncommon anywhere above 4,900 4,900 feet elevation. feet (Holland 1994).

Birds

Unlikely to occur. Although the project area Middle to high elevation, mature, dense conifer forests supports appropriate habitat (CWHR Tree for foraging and nesting. Casual in foothills during Canopy Closure M, D), northern goshawk is Accipiter gentilis CSC — FSS winter, northern deserts in pinyon-juniper woodland, unlikely to occur in the project area given (nesting) Northern goshawk and low-elevation riparian habitats. Elevations range the extensive human activity, disturbed from 5,500 to 10,000 feet. understory, and the fact that the project area is currently within a bald eagle territory.

Sacramento Municipal Utility District Upper American River Project 39 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence

Breeding habitat includes shrub-steppe areas with Unlikely to occur. No appropriate nesting or Buteo swainsoni CT scattered trees (juniper-sage flats and oak woodlands), BCC — foraging habitat is present in the project (nesting) large shrubs, and riparian woodlands. Grasslands and Swainson’s hawk area. agricultural areas are used for foraging. Coccyzus americanus Breeds in riparian habitat along low-gradient (surface BCC, FT CE slope less than 3%) rivers and streams, and in open None. No appropriate habitat is present occidentalis FSS (nesting) (nesting) riverine valleys that provide wide floodplain conditions within the project area. Western yellow- (greater than 325 feet [100 meters]). billed cuckoo

Wet meadow and montane riparian habitats at Empidonax traillii CE elevations ranging from 2,000 to 8,000 feet. Most often None. No appropriate habitat present within BCC FSS Willow flycatcher (nesting) occurs in broad, open river valleys or large mountain the project area. meadows with lush growth of shrubby willows.

Known to occur in the project area. • An active nest is located in a large, mature tree adjacent to campsite #19 in Shady Loop in 2016. Two chicks fledged from this nest location (SMUD 2017). • A winter roost is present in the Year-round resident in ice-free regions of California. Shady Loop of Sunset Haliaeetus FD Foraging areas include regulated and unregulated Campground (SMUD 2017). Bald rivers, reservoirs, lakes, estuaries, and coastal marine leucocephalus FSS CE, CFP • Eagle ecosystems. Most bald eagles in California breed near A foraging perch is located in the Bald eagle Act, BCC reservoirs, and nests are usually located within 1 mile Shady Loop of Sunset of foraging habitat. Campground (SMUD 2017). Historical nests in the project vicinity: • Bald eagles have been nesting near Union Valley Reservoir since 1986. • Historical nests have been documented at the following locations in the vicinity of the

Sacramento Municipal Utility District Upper American River Project 40 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence project (not depicted on Figure 3): o Wench Creek (1986–1988 and 1990–1991)1 1 o West Point (1989) 1 o Granlees Point (1992–2004) Historical night roosts in the project vicinity (Not depicted on Figure 3): • Night roosts were documented in 2003 in the vicinity of the project at Granlees Point and occasionally on the Sunset/Fashoda Peninsula.1

Nests in old-growth coniferous forests and forages in Strix nebulosa CE montane meadows. Distribution includes high Unlikely to occur. No appropriate habitat is — FSS Great gray owl (nesting) elevations of the Sierra Nevada and Cascade ranges, present within the project area. from 4,500 to 7,500 feet in elevation.

Unlikely to occur. Although the project area supports appropriate habitat (CWHR Tree Canopy Closure M, D), this species is unlikely to occur in the project area given the extensive human activity, disturbed Strix occidentalis Dense, old-growth, multi-layered mixed conifer, understory, and the fact that the project area is currently within a bald eagle territory. California spotted BCC FSS CSC redwood, Douglas-fir, and oak woodland habitats, from owl sea level to elevations of approximately 7,600 feet. • The nearest known Home Range Core Area is located 277 feet southeast outside of the project area.2 • The nearest known Protected Activity Center is located 1,520 feet south outside of the project area.2

Sacramento Municipal Utility District Upper American River Project 41 FERC Project No. 2101 Sunset Campground Rehabilitation Project Biological Evaluation - Terrestrial September 2017

Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence

Mammals-Bats

Inhabits a variety of habitats, including coniferous forests. Rock outcroppings, caves, buildings, and Antrozous pallidus May potentially forage or roost in the project — FSS CSC bridges are used for roost sites. Pallid bats are year- area. Pallid bat round residents that hibernate during the winter months. Found in all but alpine and subalpine habitats; most Corynorhinus abundant in mesic habitats. Year-round residents that townsendii hibernate from October through April. Requires caves, May potentially forage or roost in the project — FSS CSC Townsend’s big- mines, or human-made structures for roosting. This area. eared bat species is extremely sensitive to disturbance and may abandon a roost if disturbed. Optimal habitats are pinyon-juniper, valley foothill hardwood, and hardwood-conifer, generally at 4,000 to 7,000 feet. Roosts in caves, mines, buildings, and Myotis thysanodes crevices. Separate day and night roosts may be used. May potentially forage or roost in the project — FSS — Fringed myotis Uses open habitats, early successional stages, area. streams, lakes, and ponds as foraging areas. This species is migratory, making relatively short, local movements to suitable hibernacula.

Mammals-Mesocarnivores

Mixed conifer, red fir, and lodgepole habitats, and probably sub-alpine conifer, alpine dwarf shrub, wet Unlikely to occur in the project area. This Gulo luscus meadow, and montane riparian habitats. Occurs in the species typically occurs above 8,000-foot Sierra Nevada from 4,300 to 10,800 feet. Majority of elevation. Additionally, this species typically FC FSS CT, CFP North American recorded sightings are found above 8,000-foot avoids areas with extensive human activity wolverine elevation. Denning habitat consists of caves, cliffs, and will not likely occur within a developed hollow logs, and other cavities located in rocky areas campground. free of human disturbance.

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Table 1. Special-Status Wildlife Species Potential for Occurrence in the Sunset Campground Rehabilitation Project Area

Forest Scientific/ Federal Service State Common Name Status Status Status Habitat Potential for Occurrence

Optimal habitats are various mixed evergreen forests Martes caurina with more than 40% crown closure and large trees and May potentially forage in the project area. — FSS — snags for den sites. Most commonly found in red fir Unlikely to den in the project area due to Pacific marten and lodgepole pine forests between 4,000 and 10,600- extensive human activity. foot elevation. Large areas of mature and dense forest red fir, Pekania pennanti Unlikely to occur in the project area. lodgepole pine, ponderosa pine, mixed conifer, and Extirpated from the region with isolated Fisher - West Coast — FSS CSC Jeffrey pine forests with snags and greater than 40% populations existing in southern Sierra and Distinct Population canopy closure. Known from elevations of 4,000 to to the north. Segment 8,000 feet.

Occurs throughout the Sierra Nevada at elevations Vulpes necator Unlikely to occur in the project area. Project above 7,000 feet in forests interspersed with meadows FC FSS CT area is not within the geographic and/or Sierra Nevada red or alpine forests. Open areas are used for hunting, and elevation range of this species. fox forested habitats for cover and reproduction.

Federal Status BCC = Birds of Conservation Concern FC = Federal Candidate Species FD = Federal Delisted FE = Federal Endangered FT = Federal Threatened

State Status CE = California Endangered CFP = California Fully Protected CSC = California Species of Special Concern CT = California Threatened W = CDFW Watchlist

Forest Service Status FSS = Forest Service Sensitive

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CWHR Tree Canopy Closure Classes M = 40 to 59% Canopy Closure D = 60 to 100% Canopy Closure

Sources: CNDDB 2016b; CWHR 2016; USFS 2013a; USFS 2013 b; USFWS 2016a. 1 Source: SMUD 2004b. 2 Source: Eldorado National Forest 2017.

Sacramento Municipal Utility District Upper American River Project 44 FERC Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

Appendix A Upper American River Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

Sacramento Municipal Utility District Upper American River Project 1 FERC Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

UPPER AMERICAN RIVER PROJECT NO. 2101

Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

Condition No. 38 - Wildlife and Plant Protection Measures (1) To protect wildlife from the hazards of open canals and other project facilities, the licensee for the term of a new license for the project shall maintain and operate in working condition all devices and measures for wildlife along project canals that are deemed necessary by USFS, FWS, and CDFG. The licensee shall provide USFS, FWS, and CDFG by April 1 of each year an annual report describing the date, location, and species information (deer or other wildlife) found in project canals. Should annual wildlife mortality (deer) during any 3- year period be more than three individuals, the licensee shall develop a Wildlife Exclusion Plan that is approved by USFS, FWS, and CDFG. The licensee shall implement the Wildlife Exclusion Plan upon approval. The amount, kind, and location of any future fencing or other protective measures shall be decided upon at the annual meeting described in Condition No. 40.

(2) Before commencing any new construction or maintenance (including but not limited to proposed recreation developments) authorized by the license on National Forest System lands that may affect a USFS, FWS, or CDFG sensitive plant or wildlife species or its habitat, the licensee shall ensure that a biological evaluation (including necessary surveys) is completed that evaluates the potential effects of the action on the species or its habitat and follows the recommendations in the biological evaluation determined necessary by USFS. The biological evaluation must be approved by USFS. In consultation with FERC, USFS, FWS, or CDFG may require mitigation measures for the protection of sensitive species.

Before commencing any activities to construct (including, but not limited to, proposed recreation developments), operate, or maintain the project that may affect a species proposed for listing or listed under the federal Endangered Species Act, or that may affect that species’ critical habitat, the licensee shall ensure that a Biological Assessment that evaluates the potential effects of the action on the species or its critical habitat is prepared for the relevant Service agency (United States Fish and Wildlife Service or National Marine Fisheries Service) for consultation or conference in accordance with the Endangered Species Act.

(3) If occurrences of USFS, FWS, or CDFG sensitive plant or wildlife species are detected prior to or during ongoing construction, operation, or maintenance of the project or during project operations, the licensee shall immediately notify USFS, CDFG, and FWS. If USFS, FWS, or CDFG determine that the project- related activities are adversely affecting the sensitive species, the licensee shall, in consultation with USFS, CDFG, and FWS, develop and implement appropriate protection measures.

Sacramento Municipal Utility District Upper American River Project 1 FERC Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

(4) The licensee shall, beginning the first full calendar year after license issuance, in consultation with USFS, FWS, and CDFG annually review the current list of special status plant and wildlife species (species that are Federal Endangered or Threatened, USFS Sensitive, or Eldorado National Forest Watch Lists) that might occur on National Forest System lands in the project area directly affected by project operations. When a species is added to one or more of the lists, USFS, FWS, and CDFG, in consultation with the licensee shall determine if the species or un-surveyed suitable habitat for the species is likely to occur on such National Forest System lands. For such newly added species, if USFS, FWS, or CDFG determine that the species is likely to occur on such National Forest System lands, the licensee shall develop and implement a study plan in consultation with USFS, FWS, and CDFG to reasonably assess the effects of the project on the species. The licensee shall prepare a report on the study including objectives, methods, results, recommended resource measures where appropriate, and a schedule of implementation, and shall provide a draft of the final report to USFS, FWS, and CDFG for review and approval. The licensee shall file the report, including evidence of consultation, with FERC and shall implement those resource management measures required by FERC.

(5) The Bird-Powerline Associations Technical Report (Devine Tarbell & Associates 2004c), identifies the following problem designs based on the design and sighting standards developed by the Avian Power Line Interaction Committee (APLIC) for avoidance or minimization of bird electrocutions and collisions (APLIC 1996 and APLIC 1994):

a. Eleven type-H five-pole dead end structures used on the Jones Fork- Union Valley 69 kV line, with less than 36 inches of clearance between energized jumper wires and grounded cross-arms.

b. Exposed energized hardware and inadequate phase-to-phase and phase to ground spacing along the 1.2-mile-long Brush Creek 12 kV tap line.

c. Overhead ground wires existing throughout most of the higher elevation segments of the transmission line from Loon Lake Powerhouse to just west of Camino Powerhouse, including the Jones Fork-Union Valley transmission line segment, and an isolated segment of approximately 3.0 miles near White Rock Powerhouse.

Within 1 year of license issuance, the licensee shall develop an Avian Protection Plan, as described above that is approved by the FWS that addresses retrofitting transmission lines to meet the design and sighting standards established by APLIC for minimization of bird electrocutions and collisions.

Sacramento Municipal Utility District Upper American River Project 2 FERC Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

Condition No. 45 – Specific Recreation Measures

j. Sunset Campground By December 31 of 2019, the licensee shall redesign and reconstruct the 131 unit campground, retaining existing family unit capacity on existing footprint, to meet the current USU design standards and requirements of the Americans with Disabilities Act (ADA), and add a Group Site. The following describes the specific elements of this condition.

• Replace all 15 two-unit vault toilets with a combination of vault and flush toilets (where septic system is feasible). Relocate some toilets to reduce the distance between them and to avoid the steeper sections of the roads that have grades over 10 percent. Construct paved turnouts in front of each toilet, and provide a paved access route to the toilet entrances.

• Construct one eight-stall shower facility with toilet (including septic system).

• Construct potable water filling station for recreational vehicles.

• Engineer and reconstruct water storage and distribution system, sized to accommodate new flush toilets, recreational vehicle filling station and shower units.

• Replace any non-accessible faucet units with new units of ADA- approved design. Provide a level and compacted surface on the sides and in front of each faucet unit.

• Construct a campground entrance station with building to serve the Sunset peninsula facilities.

• Pave access and all interior campground roads.

• Where feasible, reconstruct and pave all spurs to 16-foot minimum widths and 25- or 50- foot lengths, with slopes and cross slopes at 2 percent or less. Set barrier rocks 4 feet apart for access from spur to unit.

• Replace all tables with accessible ones, level surfaces, and provide 36 inches of clearance around tables.

• Sunset Campground Design Narrative - Draft October 2016.

• Sacramento Municipal Utility District Upper American River Project, FERC Project No. 2101

• Replace all grills that have exceeded their service life, and reset newer grills to accessible cooking surface height of 30 to 36 inches. Provide 36 inches of clear level area around pedestal grills.

Sacramento Municipal Utility District Upper American River Project 3 FERC Project No. 2101 Revised U.S. Forest Service Section 4(e) Conditions Sunset Campground Measures

• Where feasible, level and regrade tent pads to provide 1,200 square feet each, with a maximum cross-slope of 3 percent in all directions. Where feasible, construct raised tent pads for accessibility (27 potential campsites have been identified).

• Regrade pathways between camp units and spurs/roadways.

• Formalize access routes to the shoreline from the Campground, and consider erosion (wave action) control measures along shoreline.

• Replace control valve at the sanitary dump station to a lever-type valve of accessible design.

• Add a group site (30 persons-at-one-time) on the south side of the access road near Loop 2.

• Construct trash bin pads with paved approaches, and purchase or retrofit refuse containers for accessibility and bear resistance.

• Install bear-proof food lockers at all camp units.

• Provide vegetative screening, and use natural materials to restrict indiscriminate pedestrian and bicycle traffic within and between campsites and use area.

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Appendix B Sunset Campground Rehabilitation Project Project Description

Sacramento Municipal Utility District Upper American River Project 1 FERC Project No. 2101

Sunset Campground Rehabilitation Project Project Description

Sacramento Municipal Utility District

FERC Project No. 2101

May 2017

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Sunset Campground Rehabilitation Project Project Description

Table of Contents

1.0 Introduction ...... 1 2.0 Location ...... 1 3.0 Background ...... 1 4.0 Current Conditions / Existing Facilities ...... 2 5.0 Purpose ...... 2 6.0 Description of Proposed Project ...... 3 6.1 Single, Double, Triple, and Host Campsites ...... 3 6.2 Group Campsite ...... 4 6.3 Shower Facility ...... 4 6.4 Restrooms ...... 4 6.5 Water System ...... 5 6.6 Access and Interior Roads ...... 5 6.7 Lakeside Access ...... 6 6.8 Restoration and Revegetation ...... 6 6.9 Recreational Vehicle Service Station ...... 6 6.10 Entry Kiosk ...... 6 6.11 Signage and Information Boards ...... 6 6.12 Site Access and Staging Areas ...... 7 6.13 Public Access and Signage During Construction ...... 7 6.14 Equipment and Labor Force ...... 7 7.0 Project Schedule ...... 7 8.0 Permit Compliance ...... 7 9.0 Design Criteria ...... 9 General Construction Measures: ...... 9 Water Quality Measures: ...... 10 Hazardous Material Measures: ...... 10 Biological Resource Measures: ...... 11 Cultural Resources Measures: ...... 11 Vegetation and Invasive Weeds Measures: ...... 11

i Sunset Campground Rehabilitation Project Project Description

Tables Table 1. Existing and Proposed Amenities Table 2. Summary of Existing and Proposed Amenities Table 3. Construction Vehicles and Equipment

Figures Figure 1. Sunset Campground Project Location. Figure 2. Sunset Campground Location of Existing Facilities. (5 sheets) Figure 3. Sunset Campground Location of Proposed Facilities. (5 sheets)

Appendix Appendix A. Upper American River Project (FERC Project No. 2101) USDA-FS 4(e) Condition No. 45 – Sunset Campground Enhancements

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Sunset Campground Rehabilitation Project Project Description

1.0 Introduction

Sacramento Municipal Utility District (SMUD) has prepared this Project Description for the Sunset Campground Rehabilitation Project (SCRP or project) to define the proposed redesign and reconstruction of the Sunset Campground. When completed, the project will enhance the overall recreation experience at the existing Sunset Campground by bringing the site up to current U.S. Department of Agriculture – Forest Service (USDA- FS or FS) standards; improving accessibility throughout the site; providing additional site amenities; and ensuring continued functionality for future recreation use.

The project is required under the license terms and conditions for the Upper American River Project (UARP), which was issued by the Federal Energy Regulatory Commission (FERC) on July 23, 2014 (FERC Project No. 2101). Specifically, USDA-FS Section 4(e) Condition No. 45 requires that SMUD implement the project by December 31, 2019. Appendix A contains the project measures specified in Condition No. 45 for Sunset Campground. USDA-FS 4(e) Condition No. 41 requires SMUD to develop a Recreation Implementation Plan in coordination with FS. The Recreation Implementation Plan is intended to guide SMUD and FS staff in design and construction of recreation facilities identified in USDA-FS 4(e) Condition No. 45.

The UARP was constructed from 1959 to 1985 on FS lands and consists of seven developments within the Rubicon River, Silver Creek, and South Fork American River drainages. It consists of 8 hydroelectric power plants operating from 11 reservoirs, which have a total authorized installed capacity of 637 megawatts (MWs). In all, the UARP has 11 reservoirs, 8 powerhouses, 11 transmission lines with a combined length of 180 miles, 28 miles of power tunnels or penstocks, 1 canal, and 700 developed public-use campsites in 47 recreation areas. The project location is shown in Figure 1.

2.0 Location

The SCRP is located on the east shoreline of Union Valley Reservoir within the Eldorado National Forest (ENF), approximately 38 miles from Placerville, California, and 55 miles from South Lake Tahoe, California (Figure 1). Sunset Campground is located on a peninsula which is accessible via Fashoda Way from Ice House Road. The area is generally accessible from May 1 to November 1,or as snow conditions allow.

3.0 Background

Sunset Campground is a 131-unit campground that opened in 1966 with 51 campsites. In 1969 the campground was expanded and 80 additional campsites were added. The campground is well maintained; however, the design of the campsites, restrooms, and associated amenities does not reflect current FS design standards and does not meet accessibility objectives. Field observations from Forest Service and concessionaire staff report that trends in group size within developed overnight recreation facilities are evolving to larger family and friends groups, rather than the small family groups

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Sunset Campground Rehabilitation Project Project Description

observed in the past. An increased number of double and triple sites were included in the design to accommodate this trend.

4.0 Current Conditions / Existing Facilities

Sunset Campground is organized into three loops: Shady Loop, Meadow Loop, and Sunset Loop (Figure 2). The current conditions and existing facilities are summarized below:

 Shady Loop has a total of 36 campsites with bear boxes, three of which are double sites (#4, #26, and #32 – also known as ‘family sites’), and four two-seat vault toilets.  Meadow Loop has a total of 44 campsites, seven of which are double sites (#40, #51, #56, #64, #66, #76, and #77), and six two-seat vault toilets.  Sunset Loop has a total of 51 campsites and five two-seat vault toilets.

All campsites include a fire-ring, grill, and picnic table. There are no bear boxes on Meadow or Sunset loops, but bear boxes are located on Shady Loop. All campsites within Sunset Campground are on native soil with varying slopes.

All the toilet buildings are wood-sided with minimal grading around each site. There are numerous user-developed pathways from the campground loop road (typically starting near the toilet buildings) to the shoreline of Union Valley Reservoir.

Access roads within the loops and spurs are paved and heavily worn with broken pavement, and occasional steep offsets between the spurs and the campsites.

The site drains by naturally contoured swales. Where the swales intersect with roads, culverts have been installed to route water beneath the road. Some of these culverts are currently non-functional.

A recreational vehicle (RV) dump station is located on the south side of Fashoda Road prior to reaching the campground loops. In general, this facility is in good condition. A water tank that services the campground is located on a hill to the north of Shady Loop.

5.0 Purpose

Implementation of the project is required to comply with FS 4(e) Condition No. 45 (j) included in the UARP License Order (Appendix A).

Sunset Campground was constructed at a time when accessibility needs were not widely recognized and/or incorporated into management objectives and design standards. Since that time, design objectives and construction standards for recreation

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Sunset Campground Rehabilitation Project Project Description

facilities have changed significantly, most notably regarding the provision of accessible facilities for persons with disabilities.

The purpose of the project is to rehabilitate Sunset Campground to meet the needs of current and future users at Union Valley Reservoir. SMUD will rehabilitate Sunset Campground as specified in FS 4(e) Condition No. 45 to meet current FS standards, including design, accessibility, and environmental and safety standards.

6.0 Description of Proposed Project

This section describes the proposed reconstruction of Sunset Campground to meet the requirements of FS 4(e) Condition No. 45 as discussed in the FS-approved Design Narrative. The proposed improvements are shown in Figure 3 and are listed in Table 1.

6.1 Single, Double, Triple, and Host Campsites

For all campground loops, the following will be implemented:

 Existing person-at-one-time (PAOT) capacity will be maintained at each loop.  Single campsites are designed to be approximately 1,200 square feet at a 2 to 3 percent grade.  Double campsite are designed to be approximately 2,200 square feet at a 2 to 3 percent grade.  Triple campsites are designed to be approximately 3,600 square feet at a 2 to 3 percent grade.  Host sites will be located near the front entrance of each loop and will be larger to accommodate increasing RV/trailer sizes. In addition, each host site will have a septic tank.  All campsites are designed to incorporate site-specific contours. Fill drop-offs and taper down on the cuts and fill are limited to 3:1.  Compacted native soil will be used for the campsite surfaces.  Living spaces are designed to accommodate, as best possible, a “working triangle” between the accessible table, accessible grill, and bear-proof food locker (bear box). Grills will be set to a cooking surface height of 30 inches. A clear level area (60 inches) will be established around tables and pedestal grills.  Parking spurs will be 25 to 50 feet in length with a 10 percent maximum parking spur driveway slope and a 2 percent maximum parking area slope. Returns and transitions may exceed 10 percent as long as the center of the spur is 10 percent or less. Where possible, existing parking spur locations will be used. Parking spur angles will range from 35 to 70 degrees depending upon the location.

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Sunset Campground Rehabilitation Project Project Description

Where site-specific constraints (e.g., extensive tree removal or topographical considerations) do not allow specifications to be met for single, double, or triple campsites, the living space size may be reduced.

Table 2 provides a summary of existing and proposed amenities within each loop. Following implementation of the project, each loop will consist of the following:

 Shady Loop will have a total of 31 campsites, three of which will be double sites (#4, #26, and #32) and one of which will be a host site (#3). Three two-seat vault toilets will also be installed.  Meadow Loop will have a total of 45 campsites, of which eight will be double sites (#40, #44, #51, #56, #64, #66, # 68, and #77), one will be a triple site (#76), and one will be a host site (#61). Seven two-seat vault toilets will also be installed.  Sunset Loop will have a total of 46 campsites, of which eight will be double sites (#83, #93, #98, #104, #109, #116, #124, and #128) and one will be a host site. Five two-seat vault toilets will also be installed.

6.2 Group Campsite

A group campsite will be constructed on the south side of Fashoda Way between the Meadow and Sunset loop entrances. This area was historically used to deck logs and slash from logging. The site will be gated and have 11 parking spaces (1 accessible and 1 RV space in addition to 9 standard parking spaces), living space, a single large fire- ring, 2 pedestal grills, 4 bear boxes, a food preparation table, and 4 tables to accommodate 30 PAOT capacity. Large parking spaces for two RVs will also be at the group campsite. Additionally, a two-seat vault toilet and drinking water (single faucet) will be installed at the site.

6.3 Shower Facility

An eight-stall shower facility will be constructed approximately 100 feet west of the Meadow Loop entrance on the north side of Fashoda Way. A septic system will be installed to handle wastewater discharge from the shower facility. The system will consist of a septic tank and leach field sized for the proposed facility capacity. A single two-seat flush toilet will also be installed at this location. A parking area with 8 standard parking spaces, 1 accessible parking space and 1 RV space will be constructed to accommodate vehicular access to the showers.

6.4 Restrooms

The 15 existing single two-seat vault toilets will be replaced with FS-approved pre- fabricated restrooms (Single two-seat vault toilets). In addition, one flush toilet facility (with two seats)will be included in the shower building located adjacent to Meadow Loop

4

Sunset Campground Rehabilitation Project Project Description

(refer to Section 6.3 above). The flush toilets will tie into the shower facility septic system. Each vault toilet restroom will have a snow cap with screen over the vent, trash bin, water faucet, roadside turnout, and paved access route to the toilet entrance. Additionally, a 2’x4’ information board will also be installed at each bathroom. No additional roadside turnout will be constructed for the flush toilets as they will be co- located with the shower building and associated parking area. Refer to Table 2 for the number of vault and flush toilets to be installed by loop.

6.5 Water System

The existing water storage and distribution system will be rehabilitated to accommodate the existing campground capacity, new group campsite (30 PAOT), new flush toilet, RV filling station, and shower units. The existing distribution system will be abandoned in place and new lines will be installed to service all amenities. The new distribution system will be installed along existing roads. The existing water storage tank will be replaced with a new above-ground steel storage tank (capacity approximately 30,000 gallons).

Existing non-accessible faucets will be replaced with Architectual Barriers Act (ABA) compliant faucets. The faucet stand will be designed to match the original wooden design, with a wood cover over the pipe. The pipe will run inside the wood with the shutoff valve a few feet behind each faucet pad. Sloping aprons for faucets will be constructed to allow for a flat faucet pad.

6.6 Access and Interior Roads

Existing roads will be rehabilitated to meet the following criteria:  One-way roads (loop-roads) will be rehabilitated to be 10 feet wide with 1 foot of aggregate shoulder on each side. One-way roads will also be widened on tight curves as necessary to accommodate the turning radius of an RV and passenger vehicles with trailers.  Two-way roads will be rehabilitated to be 20 feet wide with 1 foot of aggregate on each side.

All roads will be paved and designed for sheet flow drainage; no curbs will be constructed. Barriers will be installed on the insides of curves and in problem areas to minimize the potential for vehicle contact. Barriers will consist of rocks, logs, and existing trees from within the campground. Speed control measures (4 to 5 speed bumps) will also be added on Fashoda Way before the entry kiosk and between the boat ramp access and Sunset Loop to minimize traffic speed. Speed bumps will also be added in each campground loop near entrance and exit areas.

5

Sunset Campground Rehabilitation Project Project Description

Where necessary, culverts will be replaced with new 24-inch-diameter culverts. This includes replacement of three culverts in Shady Loop, three culverts in Meadow Loop, and five culverts in Sunset Loop.

6.7 Lakeside Access

Existing user-created footpaths to the shoreline of Union Valley Reservoir are located behind the bathrooms between sites #70 and #72 in Meadow Loop and sites #117 and #119 in Sunset Loop. Rock and Log Barriers will be placed to discourage use of the existing footpaths and to promote passive growth of native vegetation. The beach access sign between sites 3 and 4 will be replaced with a new beach access sign.

Three developed trails will be constructed to facilitate access to the shoreline. The trail in Meadow Loop will be 130 feet long and the two trails in Sunset Loop will be 170 feet and 250 feet long. Each trail will be constructed with a compacted native surface that will transition to native stone steps or a stone slope at the high water mark.

6.8 Restoration and Revegetation

Barriers will be placed along user-developed trails within each campground loop and other areas lacking vegetation to promote passive growth of native vegetation. With time, this native vegetation will create a natural barrier and/or privacy screen for the campsites and deter human activity. As discussed above, barriers will consist of rocks, logs, and trees from within the campground.

6.9 Recreational Vehicle Service Station

At the dump site, new concrete will be poured and a new faucet will be installed at the existing RV dump station. The existing valve and tank will remain in place. A new fill station will be constructed an acceptable distance from the dump site to provide potable water for RV vehicles.

6.10 Entry Kiosk

A campground entry kiosk will be installed on Fashoda Way near the east end of the Sunset Boat Ramp parking lot (Figure 3a). Fashoda Way will be realigned (split into two single lanes) with room to accommodate installation of the kiosk between the lanes (Figure 3e). There will be a clear line-of-sight before and after the kiosk. The location of the kiosk was selected to reduce traffic to the Sunset Boat Ramp, Fashoda Campground, and Sunset Campground.

6.11 Signage and Information Boards

All of the existing fee station signage, message boards, and information boards will be replaced as part of the project. Three new bulletin boards will be installed at the entrance to each loop. All signs will be developed to meet FS and SMUD criteria.

6

Sunset Campground Rehabilitation Project Project Description

Additional signs to be installed include speed limit signs, stop signs, one-way signs, trail access signs, and accessible parking signs.

6.12 Site Access and Staging Areas

The Sunset Campground is accessed via Ice House Road and Fashoda Way. The entry kiosk, RV dump station, and all three campsite loops are accessible from Fashoda Way (Figure 1).

Staging areas will be located at the group campsite and adjacent to the shower building and parking area. Additional staging will be located in barren or disturbed areas within each campground loop.

6.13 Public Access and Signage During Construction

Sunset Campground will be closed to the public for 2 years during construction. However, Fashoda Way will remain open to provide access to the Fashoda Campground, the RV dump station, and Sunset Boat Ramp. During construction activities on Fashoda Way (e.g., realignment for entry kiosk, installation of speed bumps, asphalt overlay) and construction of the entry kiosk, there will be temporary lane closures on Fashoda Way. Activities occurring along Fashoda Way will occur after Labor Day to minimize impacts to Fashoda Campground and Sunset boat ramp users.

6.14 Equipment and Labor Force

Refer to Table 3 for a list of the type and number of construction vehicles and other equipment to be used during project implementation.

All materials and equipment will be staged at designated staging areas described in Section 6.12. All vehicle fueling areas will be within upland staging areas, at least 100 feet from Union Valley Reservoir.

7.0 Project Schedule

Construction will begin in the spring of 2018, as soon as snow melts, and will be completed by December 31, 2019.

8.0 Permit Compliance

As stated above, implementation of the SCRP is a requirement of the UARP license. Prior to issuance of the UARP license, FERC completed a National Environmental Policy Act (NEPA) evaluation and SMUD completed a California Environmental Quality Act (CEQA) evaluation that included analysis of the potential effects from implementation of the project.

7

Sunset Campground Rehabilitation Project Project Description

The State Water Resources Control Board (State Water Board) relied on SMUD’s Final CEQA Supplement for issuance of the Clean Water Act Section 401 Water Quality Certification for the new license (October 2013).

In addition, as part of the UARP relicensing process, compliance with Section 106 of the National Historic Preservation Act (NHPA) and Section 7 of the Endangered Species Act (ESA) consultation and compliance were completed. This included analysis of the potential effects of implementation of USDA-FS 4(e) Condition No. 45, including the SCRP (Appendix A). SMUD has prepared a Historic Properties Management Plan (HPMP) to comply with Section 106 of the NHPA, which governs how SMUD will address impacts to historic properties. SMUD’s HPMP coordinator has reviewed the maps of historic resources within the UARP and determined that there are no known resources within or adjacent to the proposed project. A memorandum will be prepared and reviewed by the FS for the project record.

The following project-specific permits and environmental documents will be prepared and obtained prior to project implementation:  SMUD is currently in the process of preparing two biological evaluations (BEs) to analyze the potential effects of the project on FS sensitive plant and wildlife species. Upon completion, these BEs will be submitted to FS for review and approval. All avoidance, protection, and mitigation measures included in the BEs and any additional measures identified by the FS will be implemented as part of the project.  SMUD will prepare a Visual Resource Protection Plan (VRPP) for the project. Upon completion, the VRPP will be provided to FS for review and approval. All measures included in the VRPP to ensure that the recreation facility is in compliance with ENF visual quality objectives and design standards, and any additional measures identified by the FS, will be implemented as part of the project.  SMUD will obtain coverage from the State Water Board under the General Permit for Discharges of Storm Water Associated with Construction Activity. A Stormwater Pollution Prevention Plan (SWPPP) will be developed and implemented as part of the project. At a minimum, fiber rolls, gravel check dams, and fencing will be utilized to control site erosion.  SMUD will obtain the necessary permits from El Dorado County – Environmental Management Division for the installation of a sanitary/septic system at the shower facility and for improvements to the water system (water tank and distribution system). As currently designed, the project will not result in impacts to jurisdictional waters of the United States or State; therefore, a U.S. Army Corps of Engineers (USACE) Clean Water Act Section 404 permit or a California Department of Fish and Wildlife (CDFW) Streambed Alteration Agreement will not be required.

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Sunset Campground Rehabilitation Project Project Description

9.0 Design Criteria

All construction-related activities performed, and materials used, will comply with the UARP Order Issuing New License (July 23, 2014) and terms and conditions contained in project permits and approvals issued by agencies. SMUD’s Environmental Management Specialist will work with a SMUD Construction Management Inspector (CMI) and the contractor to ensure that work is completed in accordance with the contract specifications, permits, and local, state, and federal laws. The CMI will be onsite during all construction activities. The following design criteria include measures that are proposed to minimize project impacts. Any additional measures included in project permits and approvals will also be implemented as part of the project.

General Construction Measures:  SMUD will comply with the Fire Prevention and Response Plan during implementation of the project. This includes compliance with the SMUD Hot Work Standard.  Construction activities will be limited to the project site. The construction site will be clearly identified on the construction drawings and will be staked and flagged where necessary prior to initiation of construction activities.  SMUD will not place construction equipment on FS lands prior to actual use or allow equipment to remain on FS lands subsequent to actual use, except for a reasonable mobilization and demobilization period agreed to by the FS.  Tarps will be used for laydown of materials, equipment, and tools, and for secondary containments.  All waste and construction debris will be collected and disposed of at an authorized landfill or other legal disposal area.  Where present, existing paved and unpaved roads will be used to access the work area. Vehicles and equipment will be parked on pavement, existing roads, and previously disturbed areas to the extent practicable.  Trash dumping, firearms, open fires (such as barbecues), hunting, and pets will be prohibited at the project site.  After completion of construction activities, contractors will remove any temporary fill and construction debris and, wherever feasible, restore disturbed areas to pre- project conditions.  Vehicle speeds on unpaved roads will be limited to 15 miles per hour (mph) or less.  Project activities will be limited to Monday thru Friday between the hours of 7:30am and 6:00pm to minimize disturbance to Fashoda Campground and Sunset Boat ramp users. In addition, project activities will be prohibited during the the Memorial Day, 4th of July, and Labor Day weekday holidays. These limitiations may be modified as agreed to by the contractor and the FS.

9

Sunset Campground Rehabilitation Project Project Description

Water Quality Measures:  Prior to construction, SMUD will file an Erosion Control Measures Plan with the FS for approval. The plan will include measures to control erosion, stream sedimentation, dust, and soil mass movement attributable to the project. Following approval, the plan will be submitted to FERC.  During construction, no equipment maintenance or refueling will be conducted within 100 feet of Union Valley Reservoir.  All stockpiled soil will be covered to minimize soil erosion when not actively being used, prior to forecast rain, and during rain events.  Soil stabilization and erosion control best management practices (BMPs) will be implemented to minimize soil erosion on newly graded or exposed soil areas resulting from construction.  SMUD will not use tightly woven fiber netting, plastic mono-filament netting, or similar material for erosion control or other purposes to minimize the chances for wildlife to be trapped, injured, or killed.  The contractor will implement BMPs per the Caltrans Storm Water Quality Handbooks for Construction Sites to ensure erosion and sediment control. BMPs may include, but are not limited to, SS-1 (Scheduling), SS-2 (Preservation of Existing Vegetation), WE-1 (Wind Erosion Control), TC-1 (Stabilized Construction Entrance), WM-3 (Stockpile Management), WM-4 (Spill Prevention and Control), WM-6 (Hazardous Waste Management), NS-3 (Paving and Grinding Operations), NS-9 (Vehicle and Equipment Fueling), and NS-10 (Vehicle and Equipment Maintenance), per the Caltrans Storm Water Quality Handbooks for Construction Sites. A site specific SWPPP will prescribe placement and application of the above BMPs and any others deemed necessary.

Hazardous Material Measures:  SMUD will comply with the Hazardous Substances Plan during implementation of the project.  Prior to any hazardous materials being brought onsite, the contractor shall provide Safety Data Sheets to the SMUD CMI for approval.  All hazardous materials will be stored in labeled and chemical-compatible containers in accordance with federal, state, and local regulations. All hazardous waste containers shall be stored in secondary containment.  When a fuel-driven compressor or generator is used, it will be placed in an industry standard secondary containment that will capture any fuel or oil drips and be located a minimum of 100 feet from Union Valley Reservoir.

10

Sunset Campground Rehabilitation Project Project Description

 All fuel and oil will be stored in upland staging areas in watertight containers with appropriate, industry standard secondary containment to prevent any spillage or leakage from delivering to receiving water.

Biological Resource Measures1:  Environmental Training: Contractors working on SMUD projects near special- status species or their habitats will receive environmental awareness training prior to beginning work activities. The training will include review of environmental laws and guidelines that must be followed by all personnel to reduce or avoid effects on special-status species during construction.  Inadvertent Discovery: If occurrences of FS, U.S. Fish and Wildlife Service (USFWS), or CDFW sensitive plant or wildlife species are detected prior to or during construction of the project, the licensee (i.e., SMUD) shall immediately stop work and notify the FS, CDFW, and USFWS. If the FS, USFWS, or CDFW determine that project-related activities are adversely affecting sensitive species, SMUD shall, in consultation with the FS, CDFW, and USFWS, develop and implement appropriate protection measures.

Cultural Resources Measures:  SMUD will comply with the Final HPMP during implementation of the project. Specifically, measures and procedures for inadvertent discovery of human remains on federal lands and unanticipated discovery of a previously unidentified cultural resources will be implemented.

Vegetation and Invasive Weeds Measures:  Vegetation and Invasive Weed Management Plan: SMUD is currently consulting with the FS to develop a Final Vegetation and Invasive Weed Management Plan (VIWMP). If the VIWMP is completed and approved by the FS prior to project implementation, SMUD will comply with the plan during project implementation. If the VIWMP is not finalized prior to project implementation, the following measures will be implemented to prevent the spread or introduction of non-native invasive plants:

o Equipment Cleaning: All equipment and vehicles (FS, SMUD, and contracted) used for project implementation must be free of invasive plant material before moving into the project area. Equipment will be considered clean when visual inspection does not reveal soil, seeds, plant material, or other such debris.

o Cleaning shall occur at a vehicle washing station or steam-cleaning facility before the equipment and vehicles enter the project area.

1 Additional measures will be developed and/or refined in the Biological Evaluations to be prepared for the project.

11

Sunset Campground Rehabilitation Project Project Description

o When working in known invasive plant infestations or designated invasive plant units, equipment shall be cleaned before moving to other FS system lands.  Staging Areas: Equipment, materials, or crews will not be staged in invasive plant-infested areas unless ENF-approved treatment measures (e.g., herbicide or other treatment of weeds, clearing of staging areas, tarps/pallets for material storage) have been implemented prior to project initiation.  Control Areas: Where feasible, invasive plant infestations will be designated as Control Areas—areas where equipment traffic and soil-disturbing project activities would be excluded. If Control Areas are designated, they will be identified on project maps and delineated in the field with flagging.  Project-related Disturbance: The amount of ground and vegetation disturbance in staging and construction areas will be minimized.  Early Detection: Any additional infestation discovered prior to or during project implementation will be reported to the Forest Botanist or their designated appointee for prioritization and assessment for treatment.  Post-Project Monitoring: After the project is completed SMUD will monitor any areas where ground disturbance has occurred for 3 years as part of ongoing invasive species monitoring.  Gravel, Fill, and Other Materials: All gravel, fill, straw or other materials will be weed-free. When possible, onsite sand, gravel, rock, or organic matter will be used. Otherwise, weed-free materials will be obtained from sources that have been approved by the ENF.

12

Sunset Campground Rehabilitation Project Project Description

TABLES

Sunset Campground Rehabilitation Project Project Description

Table 1. Existing and Proposed Amenities

Existing Proposed

Picnic Fire Bear Proposed Campsite Grill Class PAOT PAOT Table Ring Box Action Shady Loop 1 1 1 1 1 Single 6 Single 6 2 1 1 1 1 Single 6 Removed 0 3 1 1 1 1 Single 6 Host single 6 4 2 1 2 1 Double 12 Double 12 5 1 1 1 1 Single 6 Single 6 6 1 1 1 1 Single 6 Single 6 7 1 1 1 1 Single 6 Removed 0 8 1 1 1 1 Single 6 Single 6 9 1 1 1 1 Single 6 Single 6 10 1 1 1 1 Single 6 Single 6 11 1 1 1 1 Single 6 Removed 0 12 1 1 1 Single 6 Single 6 13 1 1 1 1 Single 6 Single 6 14 1 1 1 1 Single 6 Single 6 15 1 1 1 1 Single 6 Single 6 16 1 1 1 1 Single 6 Single 6 17 1 1 1 1 Single 6 Single 6 18 1 1 1 1 Single 6 Single 6 19 1 1 1 1 Single 6 Single 6 20 1 1 1 1 Single 6 Removed 0 21 1 1 1 1 Single 6 Single 6 22 1 1 1 1 Single 6 Single 6 23 1 1 1 1 Single 6 Single 6 24 1 1 1 1 Single 6 Single 6 25 1 1 1 1 Single 6 Single 6 26 2 1 2 1 Double 12 Double 12 27 1 1 1 1 Single 6 Single 6 28 1 1 1 1 Single 6 Removed 0 29 1 1 1 1 Single 6 Single 6 30 1 1 1 1 Single 6 Single 6 31 1 1 1 1 Single 6 Single 6 32 2 1 2 1 Double 12 Double 12 33 1 1 1 1 Single 6 Single 6 34 1 1 1 1 Single 6 Single 6 35 1 1 1 1 Single 6 Single 6 36 1 1 1 1 Single 6 Single 6 Meadow Loop 37 1 1 1 0 Single 6 Single 6 38 1 1 1 0 Single 6 Single 6

Sunset Campground Rehabilitation Project Project Description

Table 1. Existing and Proposed Amenities

Existing Proposed Picnic Fire Bear Proposed Campsite Grill Class PAOT PAOT Table Ring Box Action 39 1 1 1 0 Single 6 Single 6 40 2 1 2 0 Double 12 Double 12 41 1 1 1 0 Single 6 Single 6 42 1 1 1 0 Single 6 Single 6 43 1 1 1 0 Single 6 Single 6 44 1 1 1 0 Single 6 Double 12 45 1 1 1 0 Single 6 Single 6 46 1 1 1 0 Single 6 Single 6 47 1 1 1 0 Single 6 Single 6 48 1 1 1 0 Single 6 Single 6 49 1 1 1 0 Single 6 Single 6 50 1 1 1 0 Single 6 Single 6 51 2 1 2 0 Double 12 Double 12 52 1 1 1 0 Single 6 Single 6 53 1 1 1 0 Single 6 Single 6 54 1 1 1 0 Single 6 Single 6 55 1 1 1 0 Single 6 Single 6 56 2 1 1 0 Double 12 Double 12 57 1 1 1 0 Single 6 Single 6 58 1 1 1 0 Single 6 Single 6 59 1 1 1 0 Single 6 Single 6 60 1 1 1 0 Single 6 Single 6 61 1 1 1 0 Host 6 Host single 6 62 1 1 1 0 Single 6 Single 6 63 1 1 1 0 Single 6 Single 6 64 2 1 2 0 Double 12 Double 12 65 1 1 1 0 Single 6 Single 6 66 2 1 2 0 Double 12 Double 12 67 1 1 1 0 Single 6 Single 6 68 1 1 1 0 Single 6 Double 12 69 1 1 1 0 Single 6 Single 6 70 1 1 1 0 Single 6 Single 6 71 1 1 1 0 Single 6 Single 6 72 1 1 1 0 Single 6 Single 6 73 1 1 1 0 Single 6 Single 6 74 1 1 1 0 Single 6 Single 6 75 1 1 1 0 Single 6 Single 6 76 2 1 2 0 Double 12 Triple 18 77 2 1 1 0 Double 12 Double 12 78 1 1 1 0 Single 6 Single 6 Group ------Group 30

Sunset Campground Rehabilitation Project Project Description

Table 1. Existing and Proposed Amenities

Existing Proposed Picnic Fire Bear Proposed Campsite Grill Class PAOT PAOT Table Ring Box Action Sunset Loop 79 1 1 1 0 Single 6 Single 6 80 1 1 1 0 Single 6 Single 6 81 1 1 1 0 Single 6 Single 6 82 1 1 1 0 Single 6 Removed 0 83 1 1 1 0 Single 6 Double 12 84 1 1 1 0 Single 6 Single 6 85 1 1 1 0 Single 6 Single 6 86 1 1 1 0 Single 6 Single 6 87 1 1 1 0 Single 6 Removed 0 88 1 1 1 0 Single 6 Removed 0 89 1 1 1 0 Single 6 Single 6 90 1 1 1 0 Single 6 Single 6 91 1 1 1 0 Single 6 Single 6 92 1 1 1 0 Single 6 Single 6 93 1 1 1 0 Single 6 Double 12 94 1 1 1 0 Single 6 Single 6 95 1 1 1 0 Single 6 Single 6 96 1 1 1 0 Single 6 Single 6 97 1 1 1 0 Single 6 Single 6 98 1 1 1 0 Single 6 Double 12 99 1 1 1 0 Single 6 Removed 0 100 1 1 1 0 Single 6 Single 6 101 1 1 1 0 Single 6 Single 6 102 1 1 1 0 Single 6 Single 6 103 1 1 1 0 Single 6 Removed 0 104 1 1 1 0 Single 6 Double 12 105 1 1 1 0 Single 6 Single 6 106 1 1 1 0 Single 6 Single 6 107 1 1 1 0 Single 6 Single 6 108 1 1 1 0 Single 6 Single 6 109 1 1 1 0 Single 6 Double 12 110 1 1 1 0 Single 6 Single 6 111 1 1 1 0 Single 6 Single 6 112 1 1 1 0 Single 6 Single 6 113 1 1 1 0 Single 6 Single 6 114 1 1 1 0 Single 6 Single 6 115 1 1 1 0 Single 6 Single 6 116 1 1 1 0 Single 6 Double 12 117 1 1 1 0 Single 6 Single 6 118 1 1 1 0 Single 6 Single 6

Sunset Campground Rehabilitation Project Project Description

Table 1. Existing and Proposed Amenities

Existing Proposed Picnic Fire Bear Proposed Campsite Grill Class PAOT PAOT Table Ring Box Action 119 1 1 1 0 Single 6 Single 6 120 1 1 1 0 Single 6 Single 6 121 1 1 1 0 Single 6 Single 6 122 1 1 1 0 Single 6 Single 6 123 1 1 1 0 Single 6 Single 6 124 1 1 1 0 Single 6 Double 12 126 1 1 1 0 Single 6 Single 6 127 1 1 1 0 Single 6 Removed 0 128 1 1 1 0 Single 6 Double 12 129 1 1 1 0 Single 6 Single 6 130 1 1 1 0 Single 6 Single 6 131 1 1 1 0 Single 6 Single 6 New Host Single 6 Single 6 Location Total 141 130 139 36 852 882

Sunset Campground Rehabilitation Project Project Description

Table 2. Summary of Existing and Proposed Amenities

Existing Proposed Toilet Toilet Shower Two- Two- Two- Two- Campsite Single Double Triple Host Group Shower Single Double Triple Host Group seat seat seat seat Vault Flush Vault Flush Shady 33 3 0 0 0 4 0 0 27 3 0 1 0 3 0 0 Loop Meadow 36 7 0 1 0 6 0 0 34 8 1 1 1 7 1 1 Loop Sunset 51 0 0 0 0 5 0 0 37 8 0 1 0 5 0 0 Loop TOTALS 120 10 0 1 0 15 0 0 98 19 1 3 1 15 1 1

Sunset Campground Rehabilitation Project Project Description

Table 3. Construction Vehicles and Equipment

Equipment Quantity

Tractors Small Loader 2 Large Loader 1 Skid Steer Loader 2 Large Excavator 1 Medium Excavator 1 Small Excavator 2 Backhoe 2 Compaction Equipment Large Vibratory Roller 2 Small Vibratory Roller 2 Hand Vibratory Compactor 2 Paving Equipment Asphalt Paver 1 Asphalt Miller 1 Trucks Work Trucks 4 Delivery Trucks 2 Concrete Truck 2 Asphalt Distribution Truck 4 Dump Truck 4 Lifting Crane 1 Cleaning Sweeper Truck 1 Water Truck 1 Vegetation Removal Chainsaw 3

Sunset Campground Rehabilitation Project Project Description

FIGURES

       

NOTES: 1. STAGING AREAS WILL BE FINALIZED BASED ON FINAL DESIGN TO MINIMIZE DISTURBANCE. STAGING AND LAYDOWN AREAS ARE TYPICALLY LOCATED Legend WHERE LARGE DISTURBANCES ARE PROPOSED SUCH AS DOUBLE SITES AND SUNSET CAMPGROUND QUANTITIES THE GROUP SITE. PROJECT BOUNDARY 2. DISTURBANCE AND IMPROVEMENT AREA WILL BE LIMITED TO THE PENINSULA SINGLE CAMPSITES 123 WITHIN THE FERC AND ENF BOUNDARY. IMPROVEMENTS WILL BE DESIGNED TO LIMIT DISTURBANCE BY KEEPING NEW FEATURES WITHIN THE EXISTING FAMILY CAMPSITES 8 FOOTPRINT TO THE EXTENT FEASIBLE. & VAULT TOILETS 15 & FAUCETS 33 DUMPSTERS 19

SHEET INDEX

% % UNION VALLEY RESERVOIR

FERC BOUNDARY SHADY LOOP

UNION VALLEY RESERVOIR FASHODA CG (NOT A PART)

MEADOW LOOP

RV STATION $ SHEET 2 $ SUNSET BOAT RAMP SUNSET LOOP (NOT A PART) UNION VALLEY RESERVOIR

ENGINEER/CONSULTANT 1 Tab: 0 300 600

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SUNSET CAMPGROUND REHABILITATION PROJECT LOCATION OF EXISTING FACILITIES Jesse Carlson -

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R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Master\Initial Basemap\SUNSET_base.dwg

Plot Stamp: File:                

UNION VALLEY RESERVOIR & Legend & 81 CAMPSITE FASHODA CAMPGROUND NOT A PART OF SUNSET CAMPGROUND PROJECT FAUCET BATHROOM

TRASH RECEPTACLE

CULVERT

WATERLINE

PROJECT BOUNDARY

% % EXISTING DUMP STATION

0 80 160

SUNSET BOAT RAMP NOT A PART OF SUNSET CAMPGROUND PROJECT

$ $

SHEET INDEX UNION VALLEY RESERVOIR

ENGINEER/CONSULTANT 2 Tab:

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SUNSET CAMPGROUND REHABILITATION PROJECT LOCATION OF EXISTING FACILITIES RV DUMP STATION AND ENTRANCE Jesse Carlson -

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R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Master\Initial Basemap\SUNSET_base.dwg

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UNION VALLEY RESERVOIR Legend 81 CAMPSITE

FAUCET & & BATHROOM

TRASH RECEPTACLE

CULVERT EXISTING WATER TANK WATERLINE

PROJECT BOUNDARY

BALD EAGLE NEST

% % 15 13

17 12 11 8 7 0 80 160

19

14 18 16 9 10 4

20 6 22 25 5 27 21 1 $ 50 3 $ 48 29 36

30 35 24 51 23 33 2

49 46 28 52 26 34 47 54 45 53 31 32 68

55 44 ENGINEER/CONSULTANT 3

Tab: 66 57 43 67 # #

SUNSET CAMPGROUND REHABILITATION PROJECT LOCATION OF EXISTING FACILITIES SHADY LOOP SHEET INDEX Jesse Carlson -

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Plot Stamp: File:            19     

14 18 16 10 9 UNION VALLEY 6 RESERVOIR 20 Legend 22 25 & 81 CAMPSITE & 5 27 FAUCET 21 1 50 48 29 BATHROOM36

30 35TRASH RECEPTACLE 24 51 23 33 CULVERT 0 80 160 49 28 52 46 WATERLINE 69 26 PROJECT BOUNDARY34 70 47 54 45 53 31 32 68

55 44 % 66 % 71 57 43 67 72 42 58 56 41 73 64 SHEET INDEX 74 59 40 65 60 39 62 76 63 37 38 61

75 83 $ 78 $ 77 80

79 82

UNION VALLEY ENGINEER/CONSULTANT

4 RESERVOIR Tab:

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Plot Stamp: File:                 73

74

76

& Legend & 86 84 88 75 81 CAMPSITE 92 90 94 83 FAUCET 95 77 BATHROOM 97 85 98 87 82 TRASH RECEPTACLE 96 93 CULVERT 81 0 80 160 91 89 WATERLINE

99 PROJECT BOUNDARY

101 105 100 106 % % 107 102 111 109

103 104

110 108 SHEET INDEX

115 130 117 113 112 131 $ UNION VALLEY $ RESERVOIR 114 116 118 128 119 129 125 127 121

120 124 126 122 123 ENGINEER/CONSULTANT 5 Tab:

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SUNSET CAMPGROUND REHABILITATION PROJECT LOCATION OF EXISTING FACILITIES SUNSET LOOP Jesse Carlson -

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R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Master\Initial Basemap\SUNSET_base.dwg

Plot Stamp: File:                 CONCEPT PLAN NOTES UNION VALLEY 1. CAMPSITE LAYOUTS SHOWN ARE A DEPICTION OF THE PROPOSED DESIGN INTENT RESERVOIR AND MAY CHANGE BASED ON ACTUAL SITE CONDITIONS. CAMPSITES WILL BE DESIGNED TO FIT WITHIN EXISTING TOPOGRAPHY AND NATURAL FEATURES SUCH AS TREES AND BOULDERS. 2. THE SITES ARE APPROXIMATELY 1200 SF FOR SINGLE, 2400 SF FOR DOUBLE, AND & 3600 SF FOR TRIPLE SITES. CAMPSITE AREAS WILL INCORPORATE NATURAL & FEATURES AND BE GRADED AT A 2-3% CROSS SLOPE IN ANY DIRECTION. Darold Perry DATE Supervisor, Hydro License Implementation 3. THE CAMPGROUND ROAD WILL BE 10' WIDE WITH 1' GRAVEL SHOULDERS ON SHADY LOOP - SEE SHEET 2 Sacramento Municipal Utility District EITHER SIDE. THE CURVE DESIGN WILL BE BASED ON AASHTO VEHICLE STANDARDS FOR A MOTOR HOME AND BOAT TRAILER (MH/B) WITH LENGTH OF 53' AND WIDTH OF 8'. ROADWAY WIDENING WILL BE INCORPORATED IN TO FUTURE Richard Thornburgh DATE PHASES OF DESIGN AS REQUIRED; BASED ON SURVEY INFO, EXISTING FEATURES, District Ranger Pacific Ranger District VEHICLE TURNING MOVEMENTS, ETC. Eldorado National Forest 4. TO CREATE A USER FRIENDLY CAMPGROUND, A UNIVERSAL DESIGN WILL BE UTILIZED TO ALLOW MAXIMUM ACCESS TO EVERYONE. GUIDELINES TO BE USED INCLUDES FSORAG, FSTAG, AND ABAAS. 5. TREES GREATER THAN 10" DIAMETER WILL BE AVOIDED IF POSSIBLE AND REMOVED AS NECESSARY. ALL SMALLER TREES AND BRUSH IS CONSIDERED CLEARING AND GRUBBING. 6. STORMWATER DRAINAGE AND WATER SYSTEM WILL BE FASHODA CG INCORPORATED INTO THE 60% DESIGN PHASE. (NOT A PART UNION VALLEY % 7. SPEED CONTROL MEASURES WILL BE DESIGNED AND RESERVOIR % INCORPORATED INTO THE 60% DESIGN PHASE. OF PROJECT)

RV DUMP ENTRY KIOSK - STATION - SEE SHEET 5 SEE SHEET 5

LEGEND FERC BOUNDARY - PROJECT LIMITS SUNSET BOAT RAMP GROUP PROPOSED SINGLE CAMPSITE BULLETIN BOARD (NOT A PART $ CAMPSITE $ PROPOSED DOUBLE CAMPSITE EXISTING CULVERT - REDESIGN OF PROJECT) PROPOSED TRIPLE CAMPSITE BEACH ACCESS TRAIL

EXISTING CAMPSITE TO BE REMOVED PROPOSED WATER TANK

HOST CAMPSITE PROPOSED ENTRY KIOSK

HOST SEPTIC TANK PROPOSED RV DUMP STATION

NEW PAVED PARKING SPUR PROPOSED 8-STALL SHOWER FACILITY

NEW PAVED CAMPGROUND ROAD PROPOSED GROUP CAMPSITE

AC OVERLAY ENTRANCE ROAD FIRE RING OR GRILL

SUNSET CAMPGROUND BEAR BOX ENGINEER/CONSULTANT TOTAL PROPOSED VAULT TOILET # OF # OF TOTAL PROPOSED EXISTING EXISTING PROPOSED PAOT* PAOT* PROPOSED FLUSH TOILET TABLE SINGLE CAMPSITES 122** 101 732 606 0 200 400 DOUBLE CAMPSITES 10 19 120 228 TRASH BIN EXISTING DRAINAGE FLOW PATH # # TRIPLE CAMPSITES 0 1 0 18 EXISTING FAUCET PROPOSED GATE GROUP CAMPSITES 0 1 0 30 TOTAL 132 122 852 882 ENTRY ROAD REPAIR/PATCH AREA VAULT TOILETS 15 15 N/A N/A

FLUSH TOILETS 0 1 N/A N/A SPEED CONTROL MEASURES

FAUCETS 32 36 N/A N/A

*PAOT - PERSONS AT ONE TIME **INCLUDES HOST AT SUNSET LOOP Map 3a  R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Figures\SUNSET_concept.dwgOVERVIEW Tab:

Plot Stamp: - Jesse Carlson 11/17/2016 12:26 PM File:                

LEGEND

UNION VALLEY PROPOSED SINGLE CAMPSITE RESERVOIR PROPOSED DOUBLE CAMPSITE

EXISTING CAMPSITE TO BE REMOVED & & HOST CAMPSITE

HOST SEPTIC TANK

NEW PAVED PARKING SPUR

PROPOSED WATER TANK NEW PAVED CAMPGROUND ROAD

AC OVERLAY ENTRANCE ROAD

PROPOSED VAULT TOILET

PROPOSED TRASH BIN

PROPOSED FAUCET

PROPOSED BULLETIN BOARD

EXISTING CULVERT - REDESIGN

PROPOSED BEACH ACCESS TRAIL % 13 % PROPOSED WATER TANK 15 12 PROPOSED FIRE RING OR GRILL 17 11 19 8 PROPOSED BEAR BOX 7 16 PROPOSED TABLE 14 EXISTING DRAINAGE FLOW PATH

10 9 ENTRY ROAD REPAIR/PATCH AREA 18 4 20 6 PROPOSED GATE SPEED CONTROL MEASURE 22 TYP. 24' 21 25 5 1 27 TYP. 12' 36 3 $ 50 $ 29 TYP. 16' 48 51 30 23 24 35 33 2 TYP. 24' 46 49 26 TYP. 20' 69 52 28 34

53 47 54 45 31 32 68 TO ICE HOUSE RD. 55 & BOAT RAMP ENGINEER/CONSULTANT 66 44 57 FASHODA WAY 67 43 58 0 80 160 # 42 #

SHEET INDEX Map 3b 

Plot Stamp: - Jesse Carlson 11/17/2016 12:26 PM R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Figures\SUNSET_concept.dwgLOOP 1 File: Tab:                 14 10 9 18 LEGEND 20 6 UNION VALLEY PROPOSED SINGLE CAMPSITE PROPOSED TRASH BIN RESERVOIR 22 PROPOSED DOUBLE CAMPSITE PROPOSED FAUCET & & TYP. 24' PROPOSED TRIPLE CAMPSITE PROPOSED BULLETIN BOARD 21 25 5 PROPOSED GROUP CAMPSITE EXISTING CULVERT - REDESIGN 1 27 TYP. 12' 36 50 EXISTING CAMPSITE TO BE REMOVED PROPOSED BEACH ACCESS TRAIL 29 TYP. 16' 48 HOST CAMPSITE PROPOSED WATER TANK 51 30 23 24 35 33 HOST SEPTIC TANK 2 PROPOSED 8-STALL SHOWER FACILITY TYP. 24' 46 PROPOSED FIRE RING OR GRILL 49 NEW PAVED PARKING SPUR 70 26 69 52 28 NEW PAVED34 CAMPGROUND ROAD PROPOSED BEAR BOX

53 47 AC OVERLAY ENTRANCE ROAD PROPOSED TABLE/SERVICE TABLE 54 45 31 PROPOSED VAULT TOILET EXISTING DRAINAGE FLOW PATH 32 68 55 PROPOSED FLUSH TOILET ENTRY ROAD REPAIR/PATCH AREA 44 66 PROPOSED GATE PROPOSED VEGETATION SCREENING % 57 FASHODA WAY % SPEED CONTROL MEASURE 71 67 43 58 72 42 56 41 74 64 73 65 40 39 59 76 60 63 62

37 61 38

75 FASHODA WAY

$ $ 77 80 TYP. 20' TYP. 16' 79

SHEET INDEX

FASHODA WAY

UNION VALLEY ENGINEER/CONSULTANT RESERVOIR

# 0 80 160 #

Map 3c 

Plot Stamp: - Jesse Carlson 11/17/2016 12:26 PM R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Figures\SUNSET_concept.dwgLOOP 2 File: Tab:                 74 73

LEGEND

PROPOSED SINGLE CAMPSITE

PROPOSED DOUBLE CAMPSITE & & 86 94 84 75 EXISTING CAMPSITE TO BE REMOVED 88 92 90 PROPOSED CAMPSITE HOST 97 95 83 PROPOSED HOST SEPTIC TANK 85 77 PROPOSED PAVED PARKING SPUR 98 87 93 PROPOSED PAVED CAMPGROUND ROAD

96 AC OVERLAY ENTRANCE ROAD 91 89 82 81 PROPOSED VAULT TOILET 99 PROPOSED TRASH BIN

PROPOSED FAUCET 107 105 100 101 106 PROPOSED BULLETIN BOARD

% TYP. 12' EXISTING CULVERT - REDESIGN %

102 109 PROPOSED BEACH ACCESS

TYP. 16' 111 PROPOSED FIRE RING OR GRILL TYP. 24' 103 104 PROPOSED BEAR BOX PROPOSED TABLE 110 FASHODA WAY 108 EXISTING DRAINAGE FLOW PATH TYP. 20' ENTRY ROAD REPAIR/PATCH AREA

PROPOSED GATE

113 SPEED CONTROL MEASURE 117 115 131

UNION VALLEY 114 130 $ 112 $ RESERVOIR 118 116

119 128 125 121 127 129

TYP. 12.0' 120 SHEET INDEX

126

122 123 124 ENGINEER/CONSULTANT

# 0 80 160 #

Map 3d 

Plot Stamp: - Jesse Carlson 11/17/2016 12:26 PM R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Figures\SUNSET_concept.dwgLOOP 3 File: Tab:                

& & ABANDONED CAMPING UNIT

FASHODA WAY CONCRETE PAD PROPOSED ENTRY KIOSK TYP. 20'

“ 100' FASHODA WAY “ “ 22' PROPOSED % % ACCESSIBLE RV TYP. 20' 12.0' DUMP STATION 10' REMOVE EXISTING DUMP FACILITY (UNDERGROUND TANKS AND FEATURES) PROPOSED ROAD INSTALL UNDERGROUND WASTEWATER STORAGE REALIGNMENT VAULT. SIZE/VOLUME TO BE DETERMINED AT 60% DESIGN STAGE BASED ON EXISTING VOLUME/DESIGN USE AND CLEANING CYCLE ENTRANCE KIOSK

RV DUMP STATION

$ LEGEND $

PROPOSED PAVED CAMPGROUND ROAD

AC OVERLAY ENTRANCE ROAD

ENTRY ROAD REPAIR/PATCH AREA

CONCRETE PAD

ENTRANCE KIOSK

DUMP STATION

PROPOSED GATE ENGINEER/CONSULTANT RV DUMP SPEED CONTROL MEASURE KIOSK

# 0 40 80 #

SHEET INDEX Map 3e 

Plot Stamp: - Jesse Carlson 11/17/2016 12:26 PM R:\Reno Projects\E316103601 - SMUD Sunset Campground\AutoCAD\Figures\SUNSET_concept.dwgRV and ENTRY File: Tab:         Sunset Campground Rehabilitation Project Project Description

APPENDIX A

Upper American River Project (FERC Project No. 2101) USDA-FS 4(e) Condition No. 45 j. - Sunset Campground Enhancements

Sunset Campground Rehabilitation Project Project Description

j. Sunset Campground

Within 5 years of license issuance, the licensee shall redesign and reconstruct the 131 unit campground, retaining existing family unit capacity on existing footprint, to meet the current FS design standards and requirements of the ADA, and add a Group Site. The following describes the specific elements of this condition.

 Replace all 15 two-unit vault toilets with a combination of vault and flush toilets (where septic system is feasible).

 Relocate some toilets to reduce the distance between them and to avoid the steeper sections of the roads that have grades over 10 percent.

 Construct paved turnouts in front of each toilet, and provide a paved access route to the toilet entrances.

 Construct one eight-stall shower facility with toilet (including septic system). Construct potable water filling station for recreational vehicles.

 Engineer and reconstruct water storage and distribution system, sized to accommodate new flush toilets, recreational vehicle filling station and shower units.

 Replace any non-accessible faucet units with new units of ADA- approved design.

 Provide a level and compacted surface on the sidesand in front of each faucet unit.

 Construct a campground entrance station with building to serve the Sunset peninsula facilities.

 Pave access and all interior campground roads.

 Where feasible, reconstruct and pave all spurs to 16-foot minimum widths and 25- or 50- foot lengths, with slopes and cross slopes at 2 percent or less. Set barrier rocks 4 feet apart for access from spur to unit.

 Replace all tables with accessible ones, level surfaces, and provide 36 inches of clearance around tables.

 Replace all grills that have exceeded their service life, and reset newer grills to accessible cooking surface height of 30 to 36 inches. Provide 36 inches of clear level area around pedestal grills.

Sunset Campground Rehabilitation Project Project Description

 Grade tent pads to provide 1,200 square feet each, with a maximum cross-slope of 3 percent in all directions. Where feasible, construct raised tent pads for accessibility (27 potential campsites have been identified). Regrade pathways between camp units and spurs/roadways.

 Formalize access routes to the shoreline from the Campground, and consider erosion (wave action) control measures along shoreline.

 Replace control valve at the sanitary dump station to a lever-type valve of accessible  design.

 Add a group site (30 PAOT) on the south side of the access road near Loop 2.

 Construct trash bin pads with paved approaches, and purchase or retrofit refuse  containers for accessibility and bear resistance.

 Install bear-proof food lockers at all camp units.

 Provide vegetative screening, and use natural materials to restrict indiscriminate pedestrian and bicycle traffic within and between campsites and use areas.

 Regrade pathways between camp units and spurs/roadways.