FINAL (Department of Homeland Security-FEMA Seal) Programmatic Environmental Assessment (PEA) for Typical Recurring Actions Flood, Earthquake, Fire, Rain, and Wind Disasters in California Prepared for Federal Emergency Management Agency Region IX 1111 Broadway, Suite 1200 Oakland, California 94607 December 2003 [NISTAC Symbol] Nationwide Infrastructure Support Technical Assistance Consultants A Joint Venture of URS Group, Inc., and Dewberry & Davis LLC 500 12th Street, Suite 200 Oakland, California 94607 Contract No. EMW-97-CO-0173 Task Order 61 15293557.00100 Table of Contents Section 1 ONE Introduction 1-1 1.1 Disaster Programs 1-1 1.1.1 Overview 1-1 1.1.2 Response 1-1 1.1.3 Recovery 1-1 1.1.4 Prevention and Mitigation 1-2 1.2 Regulatory Background 1-2 1.3 The Programmatic Environmental Assessment 1-3 1.4 Actions Not Covered by this Programmatic Environmental Assessment 1-5 1.4.1 Statutory Exclusions 1-5 1.4.2 Categorical Exclusions 1-5 1.4.3 Actions Requiring an Environmental Assessment Instead of a Programmatic Environmental Assessment 1-6 1.4.4 Actions Requiring an Environmental Impact Statement 1-6 1.5 Actions Covered by the Programmatic Environmental Assessment 1-6 1.6 Purpose of and Need for Action 1-6 1.7 California Environmental Quality Act and Applicable Permits 1-7 1.8 Using the Programmatic Environmental Assessment 1-7 1.8.1 Organization of the Programmatic Environmental Assessment 1-7 1.8.2 Use of the Programmatic Environmental Assessment 1-8 1.8.3 Other Complementary Programmatic Documents 1-8 Section 2 TWO Description of Proposed Actions and Alternatives 2-1 2.1 No Action Alternative 2-2 2.2 Nonemergency Debris Removal 2-2 2.3 Constructing, Modifying, or Relocating Facilities 2-3 2.3.1 Upgrading or Otherwise Modifying Buildings 2-3 2.3.2 Providing Temporary Facilities 2-4 2.3.3 Acquiring and Demolishing Existing Facilities 2-4 2.3.4 Repairing, Realigning, or Otherwise Modifying Roads, Trails, Utilities, and Rail Lines 2-5 2.3.5 Constructing New Facilities or Relocating Existing Facilities 2-5 2.3.6 Relocating the Function of an Existing Facility 2-6 2.3.7 Extending the Pressurized Water Service Area 2-6 2.3.8 Developing Demonstration Projects 2-6 2.4 Actions Involving Watercourses and Coastal Features 2-6 2.4.1 Repairing, Stabilizing, or Armoring Embankments 2-7 2.4.2 Creating, Widening, Clearing, or Dredging a Waterway 2-7 2.4.3 Constructing or Modifying a Water Crossing 2-8 2.4.4 Constructing or Modifying a Water Detention, Retention, or Storage Facility 2-9 2.4.5 Constructing or Modifying Other Flood Control Structures 2-10 2.4.6 Constructing or Modifying a Coastal Feature 2-10 2.5 Vegetation Management 2-10 2.5.1 Mechanical or Hand Clearing of Vegetation 2-11 2.5.2 Herbicidal Treatments 2-11 2.5.3 Prescribed Burns 2-12 2.5.4 Biological Control 2-12 2.6 Publication and Revision of Flood Insurance Rate Maps 2-12 Section 3 THREE Affected Environment 3-1 3.1 Geology, Seismicity, and Soils 3.1-1 3.1.1 Regulatory Background 3.1-1 3.1.2 Geology, Geologic Hazards, and Soils in California 3.1-4 3.2 Air Quality 3.2-1 3.2.1 Regulatory Background 3.2-1 3.2.2 Air Quality in California 3.2-3 3.3 Water Resources 3.3-1 3.3.1 Regulatory Background 3.3-1 3.3.2 Discussion of Water Resources in California 3.3-5 3.4 Biological Resources 3.4-1 3.4.1 Regulatory Background 3.4-1 3.4.2 Biological Resources in California 3.4-5 3.5 Cultural Resources 3.5-1 3.5.1 Regulatory Background 3.5-1 3.5.2 Cultural Resources in California 3.5-3 3.6 Socioeconomics and Public Safety 3.6-1 3.6.1 Regulatory Background 3.6-1 3.6.2 Socioeconomic Conditions in California 3.6-2 3.7 Land Use and Planning 3.7-1 3.7.1 Regulatory Background 3.7-1 3.7.2 Land Uses in California 3.7-2 3.8 Public Services and Recreation 3.8-1 3.8.1 Fire Protection 3.8-1 3.8.2 Police Protection 3.8-2 3.8.3 Public Schools 3.8-2 3.8.4 Public Parks 3.8-2 3.8.5 Public Utilities 3.8-3 3.9 Transportation 3.9-1 3.9.1 Regulatory Background 3.9-1 3.9.2 Transportation in California 3.9-1 3.10 Noise 3.10-1 3.10.1 Regulatory Background 3.10-1 3.10.2 Existing Noise in California 3.10-3 3.11 Hazardous Materials and Wastes 3.11-1 3.11.1 Regulatory Background 3.11-1 3.11.2 Hazardous Materials and Wastes and the Affected Environment 3.11-3 3.12 Visual Resources 3.12-1 3.12.1 Regulatory Background 3.12-1 3.12.2 Visual Resources in California 3.12-1 Section 4 FOUR Environmental Consequences of Actions and Alternatives 4-1 4.1 Geology, Seismicity, and Soils 4.1-1 4.1.1 No Action Alternative 4.1-1 4.1.2 General Consequences of Proposed Actions 4.1-1 4.1.3 Consequences Attributable to Specific Actions 4.1-1 4.2 Air Quality 4.2-1 4.2.1 No Action Alternative 4.2-1 4.2.2 General Consequences of Proposed Actions 4.2-1 4.2.3 Consequences Attributable to Specific Actions 4.2-2 4.3 Water Resources 4.3-1 4.3.1 No Action Alternative 4.3-1 4.3.2 General Consequences of Proposed Actions 4.3-1 4.3.3 Consequences Attributable to Specific Actions 4.3-2 4.4 Biological Resources 4.4-1 4.4.1 No Action Alternative 4.4-1 4.4.2 General Consequences of Proposed Actions 4.4-1 4.4.3 Consequences Attributable to Specific Actions 4.4-2 4.5 Cultural Resources 4.5-1 4.5.1 No Action Alternative 4.5-1 4.5.2 General Consequences of Proposed Actions 4.5-1 4.5.3 Consequences Attributable to Specific Actions 4.5-2 4.6 Socioeconomics and Public Safety 4.6-1 4.6.1 No Action Alternative 4.6-1 4.6.2 General Consequences of Proposed Actions 4.6-1 4.6.3 Consequences Attributable to Specific Actions 4.6-2 4.7 Land Use and Planning 4.7-1 4.7.1 No Action Alternative 4.7-1 4.7.2 General Consequences of Proposed Actions 4.7-1 4.7.3 Consequences Attributable to Specific Actions 4.7-1 4.8 Public Services and Recreation 4.8-1 4.8.1 No Action Alternative 4.8-1 4.8.2 General Consequences of Proposed Actions 4.8-1 4.8.3 Consequences Attributable to Specific Actions 4.8-1 4.9 Transportation 4.9-1 4.9.1 No Action Alternative 4.9-1 4.9.2 General Consequences of Proposed Actions 4.9-1 4.9.3 Consequences Attributable to Specific Actions 4.9-1 4.10 Noise 4.10-1 4.10.1 No Action Alternative 4.10-1 4.10.2 General Consequences of Proposed Actions 4.10-1 4.10.3 Consequences Attributable to Specific Actions 4.10-1 4.11 Hazardous Materials and Wastes 4.11-1 4.11.1 No Action Alternative 4.11-1 4.11.2 General Consequences of Proposed Actions 4.11-1 4.11.3 Consequences Attributable to Specific Actions 4.11-1 4.12 Visual Resources 4.12-1 4.12.1 No Action Alternative 4.12-1 4.12.2 General Consequences of Proposed Actions 4.12-1 4.12.3 Consequences Attributable to Specific Actions 4.12-1 4.13 Comparison of Environmental Consequences 4.13-1 Section 5 FIVE - Public Participation Process 5-1 Section 6 SIX - References 6-1 6.1 Description of Proposed Actions and Alternatives (Section 2.0) 6-1 6.2 Geology, Seismicity, and Soils (Section 3.1) 6-1 6.3 Air Quality (Section 3.2) 6-3 6.4 Water Resources (Section 3.3) 6-4 6.5 Biological Resources (Section 3.4) 6-4 6.6 Cultural Resources (Section 3.5) 6-4 6.7 Socioeconomics and Public Safety (Section 3.6) 6-4 6.8 Land Use and Planning (Section 3.7) 6-4 6.9 Public Services and Recreation (Section 3.8) 6-4 6.10 Noise (Section 3.10) 6-5 6.11 Hazardous Materials (Section 3.11) 6-5 6.12 Visual Resources 6-6 Tables 3.1-1 Geologic Hazards 3.1-2 Notable California Earthquakes 3.1-3 Explanation of Selected Soil Taxonomic Terms 3.2-1 Emission Thresholds That Trigger Applicability of the General Conformity Rule in Tons per Year Based on Air Quality Attainment Designation in California 3.2-2 State and Federal Ambient Air Quality Standards 3.2-3 North Coast Air Basin Attainment Status 3.2-4 San Francisco Air Basin Attainment Status 3.2-5 North Central Coast Air Basin Attainment Status 3.2-6 South Central Coast Air Basin Attainment Status 3.2-7 South Coast Air Basin Attainment Status 3.2-8 San Diego Air Basin Attainment Status 3.2-9 Northeast Plateau Air Basin Attainment Status 3.2-10 Sacramento Valley Air Basin Attainment Status 3.2-11 San Joaquin Valley Air Basin Attainment Status 3.2-12 Great Basin Valley Air Basin Attainment Status 3.2-13 Mojave Desert Air Basin Attainment Status 3.2-14 Salton Sea Air Basin Attainment Status 3.2-15 Mountain Counties Air Basin Attainment Status 3.2-16 Lake County Air Basin Attainment Status 3.2-17 Lake Tahoe Air Basin Attainment Status 3.3-1 California Wild and Scenic Rivers 3.3-2 California Watershed Hydrologic Areas 3.5-1 Summary Descriptions of Cultural Resources Sites in California 3.6-1 State and County Demographics 3.10-1 Population Density and Average Day-Night Noise Levels Correlation 3.10-2 Estimating Existing Noise Exposure 3.11-1 California Asbestos NESHAP Air Pollution Control Districts 4-1 Typical Construction BMPs 4-2 Impact Matrix of Actions and Alternatives by Resource Area Figures 3.1-1 California Geomorphic Provinces 3.1-2 California Ecological Subregions 3.2-1 California Air Basins 3.2-2 California Air Districts 3.2-3 California Counties 3.2-4 South Coast Air Basin 3.3-1 California Watersheds 3.3-2 California Groundwater Basins Appendices A Example of a Memorandum for an Action Where the PEA Is the Only Documentation Necessary to Comply with NEPA B Example of a Supplemental Environmental Assessment C Memorandum of Understanding with the U.S. Fish and Wildlife Service D Agreement Regarding Section 7 Consultation on the Endangered Species Act When the U.S. Army Corps of Engineers (USACE) Serves as Lead Agency E Programmatic Biological Opinion / Programmatic Incidental Take Statement for FEMA- 1155-DR-CA F Programmatic Biological Assessment for the National Marine Fisheries Service G National Marine Fisheries Service Concurrence Letter H Programmatic Agreement with the California State Historic Preservation Officer (SHPO) for Future Declared Disasters I List of Agencies to Receive Copies of Draft and Final Programmatic Environmental Assessments J Comment Letters on the Draft PEA K Cumulative Public Notice Published for the FEMA 1203-DR-CA Disaster Acronyms ºF °Fahrenheit ACHP Advisory Council on Historic Preservation ACCM asbestos-containing construction material ACM asbestos-containing material A-P Act Alquist-Priolo Earthquake Fault Zoning Act APCD Air Pollution Control District AQMD Air Quality Management District AST aboveground storage tank BACT best available control technology BFE base flood elevation BLM Bureau of Land Management BMPs Best Management Practices CAA Clean Air Act CAAQS California Ambient Air Quality Standards Caltrans California Department of Transportation CARA California River Assessment CARB California Air Resources Board CBC California Building Code CCAA California Clean Air Act CCR California Code of Regulations CDF California Department of Forestry and Fire Protection CDFG California Department of Fish and Game CEPA California Environmental Protection Agency CEQ Council on Environmental Quality CEQA California Environmental Quality Act CERCLA Comprehensive Environmental Response, Compensation, and Liability Act CESA California Endangered Species Act CFR Code of Federal Regulations CNEL community noise equivalent level CO carbon monoxide CTC California Transportation Commission CVP Central Valley Project CWA Clean Water Act DBA a-weighted decibel(s) DNL(Ldn) day-night averaged sound level EA Environmental Assessment EFH Essential Fish Habitat EIS Environmental Impact Statement EO Executive Order ESA (federal) Endangered Species Act FEMA Federal Emergency Management Agency FIRM Flood Insurance Rate Map FONSI Finding of No Significant Impact GCR General Conformity Rule HUD Department of Housing and Urban Development LBP lead-based paint Leq equivalent sound level MAF million acre-feet Mph mile(s) per hour NAAQS National Ambient Air Quality Standards NEHRP National Earthquake Hazard Reduction Program NEPA National Environmental Policy Act NESHAP National Emission Standards for Hazardous Air Pollutants NFIP National Flood Insurance Program NHPA National Historic Preservation Act NOAA Fisheries National Marine Fisheries Service NO2 nitrogen dioxide NOx nitrogen oxides NPDES National Pollutant Discharge Elimination System NPS National Park Service NRCS Natural Resources Conservation Service NRHP National Register of Historic Places NSR New Source Review O3 ozone OES California Office of Emergency Services OPR California Governor's Office of Planning and Research PA Programmatic Agreement PBO Programmatic Biological Opinion PCBs polychlorinated biphenyls PEA Programmatic Environmental Assessment PG&E Pacific Gas and Electric PITS Programmatic Incidental Take Statement PL Public Law PM10 particulate matter smaller than 10 microns in diameter PM2.5 particulate matter smaller than 2.5 microns in diameter PRC Public Resources Code PSD Prevention of Significant Deterioration RACM regulated asbestos containing material RCRA Resource Conservation and Recovery Act RWQCB Regional Water Quality Control Board SARA Superfund Amendments and Reauthorization Act SCE Southern California Edison SDG&E San Diego Gas and Electric SEA Supplemental Environmental Assessment SFHA Special Flood Hazard Area SHPO State Historic Preservation Officer SIP State Implementation Plan SMUD Sacramento Municipal Utility District SO2 sulfur dioxide SWP State Water Project SWRCB State Water Resources Control Board TSCA Toxic Substances Control Act UBC Uniform Building Code URARPAPA Uniform Relocation Assistance and Real Property Acquisitions Policies Act of 1970 USACE U.S. Army Corps of Engineers USC United States Code USEPA U.S. Environmental Protection Agency USFS U.S. Forest Service USFWS U.S. Fish and Wildlife Service UST underground storage tank VOCs volatile organic compounds WDRs Waste Discharge Requirements 1. Section 1 ONE Introduction 1.1 DISASTER PROGRAMS 1.1.1 Overview The Federal Emergency Management Agency (FEMA) administers federal programs for response to, recovery from, and preparation for disasters. Disasters can result from natural events, such as floods, earthquakes, wildland fires, rains, and windstorms, or human-caused events, such as fires and explosions. FEMA administers these programs under the following authorities: * The Robert T. Stafford Disaster Relief and Emergency Assistance Act, Public Law (PL) 93-288, as amended (the Stafford Act), authorizes FEMA to administer response, recovery, and mitigation programs. The Stafford Act was amended by the Disaster Mitigation Act of 2000, PL 106-390. The Stafford Act includes the following FEMA programs: the Public Assistance Program; the Hazard Mitigation Grant Program, pre-disaster mitigation programs, the Fire Management Assistance Grant Program, and the Assistance for Individuals and Households Program. The implementing regulations for these programs are found in Title 44, Code of Federal Regulations (CFR), Parts 204 and 206. * The National Flood Insurance Act, as amended, PL 90-448, and the Flood Disaster Protection Act, PL 93-234, authorize FEMA to administer programs for mapping flood hazards, providing flood insurance, and providing flood mitigation assistance. Implementing regulations for these programs are found in 44 CFR Parts 59-78. Typical actions taken under these authorities are described below. 1.1.2 Response In response to disasters, FEMA is authorized under the Stafford Act to provide state and local governments with the assistance that is essential to respond to immediate threats to life, public health and safety, and property. Response activities include emergency protective measures to save lives, protect public health and safety, and protect improved property. These actions may be undertaken directly by federal agencies or state and local agencies, with FEMA providing funding for extraordinary costs. 1.1.3 Recovery Under the Stafford Act, FEMA may provide funds to repair, restore, or replace disaster-damaged public facilities as well as facilities owned by certain private nonprofit organizations. Eligible facilities include: * Roads and associated features, such as lighting, curbs, and sidewalks * Bridges, culverts, and associated features, such as abutments, headwalls, and erosion protection * Water control facilities, such as embankments, retention basins, and canals * Buildings and equipment * Utilities, such as water and sewer lines and electrical distribution facilities * Mass transit facilities * Parks and recreational facilities Often, the entity applying for assistance (referred to as the "subgrantee") wishes to take advantage of the opportunity presented by the necessary repair of a disaster-damaged facility to make improvements to, or change the design of, the facility. These actions are referred to as "improved projects." In other cases, the subgrantee determines that the public welfare would not be best served by restoring a damaged facility or the function of the facility. Funds originally available for the restoration of the damaged facility may be made available for the expansion or construction of other selected facilities, the purchase of capital equipment, or the funding of hazard mitigation measures. Such actions are referred to as "alternate projects." 1.1.4 Prevention and Mitigation The Stafford Act, the National Flood Insurance Act, and the Flood Disaster Protection Act authorize FEMA to provide assistance with actions that reduce or eliminate threats to public health and safety and the risk of damage to public and private property during future disasters. FEMA may provide funds for mitigation measures applied to a specific facility, such as elevating a flood-prone building above flood elevation or reducing risks to the community at large through such measures as vegetation management to reduce the risk of wildfire. FEMA may also provide funds for the relocation or acquisition of facilities located in areas of hazard, such as floodplains, where repetitive damage is likely to occur. Under the National Flood Insurance Act and the Flood Disaster Protection Act, FEMA administers a nationwide program for the sale of flood insurance. Under this program, called the National Flood Insurance Program (NFIP), the federal government makes available affordable flood insurance to participating communities if those communities agree to adopt certain minimum standards for the management of floodplains. In support of the NFIP, FEMA publishes and maintains Flood Insurance Rate Maps (FIRMs), which depict flood hazards. Communities use these maps for floodplain management, and the lending and insurance industries use the maps for insurance purposes. FEMA revises these maps periodically as conditions affecting floodplains change. 1.2 REGULATORY BACKGROUND The National Environmental Policy Act of 1969 (NEPA) and the Council on Environmental Quality (CEQ) regulations implementing NEPA (40 CFR Parts 1500 through 1508) direct FEMA and other federal agencies to fully understand and take into consideration during decision making the environmental consequences of proposed federal actions (also referred to as projects). FEMA's regulations for NEPA compliance are described in 44 CFR Part 10. They specify that FEMA must comply with NEPA before making federal funds available for disaster response, recovery, and mitigation. Under these regulations, FEMA must use a systematic, interdisciplinary process that includes public involvement to evaluate the impacts of its actions on the environment. The Stafford Act and FEMA's implementing regulations for NEPA provide for the exemption of certain actions from NEPA and the exclusion of other actions from full review under NEPA (as described in Section 1.4). For all other actions, FEMA ensures compliance with NEPA through the preparation of Environmental Assessments (EAs). The EA is a concise public document that serves to provide evidence of the environmental impacts of a proposed action. The assessment includes alternatives to aid in decision making and concludes with one of two findings: a Finding of No Significant Impact (FONSI) or a Notice of Intent to prepare an Environmental Impact Statement (EIS). FEMA must prepare an EIS when significant environmental impacts are anticipated and cannot be mitigated. 1.3 THE PROGRAMMATIC ENVIRONMENTAL ASSESSMENT FEMA has determined through experience that the majority of the typical recurring actions proposed for funding, and for which an EA is required, can be grouped by type of action or location. These groups of actions can be evaluated in a Programmatic Environmental Assessment (PEA) for compliance with NEPA and its implementing regulations without the need to develop and produce a time-consuming, stand-alone EA for every action. This PEA evaluates typical recurring actions undertaken by FEMA within the State of California in preparation for, and in the wake of, disasters. The purpose of this document is to facilitate FEMA's compliance with NEPA by providing a framework to address the impacts of actions typically funded in response to flood, earthquake, fire, rain, and wind disasters and to prevent future disasters resulting from these types of events. This PEA also provides the public and decision-makers with the information required to understand and evaluate the potential environmental consequences of these actions. In addition to meeting the goals of impact identification and disclosure, this PEA addresses the need to streamline the NEPA review process in the interest of FEMA's primary mission of disaster response, recovery, and mitigation. This PEA applies immediately to all actions described in Section 2 of this document that have been proposed for FEMA funding under all open declared flood, earthquake, fire, rain, and wind disasters in California. Open declared disasters are defined as disasters for which FEMA is still providing federal assistance under the Stafford Act. This PEA also applies, at FEMA's discretion, to subsequent disasters to be declared by the president. FEMA would notify the participating interested public and government parties and agencies of the applicability of this PEA to subsequent disasters. The analysis in this PEA has relied on FEMA's historical experience with action typology, description, and consequences, as described in environmental documents from 1994 to 2002. The analysis in this PEA is also based on a review of scientific literature, consultation with regulatory agencies, and expert opinion. A FONSI will be prepared for the proposed actions described and assessed in this PEA. When FEMA has determined that an EA is required for a specific action, FEMA will use this PEA to determine if more site-specific information is available and what level of environmental analysis and documentation is required for the action to comply with NEPA. If the alternatives, levels of analysis, and site-specific information of an action proposed for FEMA funding are fully and accurately described in this PEA, FEMA would prepare a memorandum documenting this determination. This memorandum would state that FEMA has reviewed the proposed action, alternatives, potential impacts, and mitigation and found them to be fully and accurately described by this PEA and the PEA FONSI. Therefore, no further documentation would be required to comply with NEPA. The memorandum would also state that cumulative impacts (as described below) would not occur from the proposed action and alternatives. Because FEMA and the subgrantee would be required to implement the mitigation measures contained in the PEA, the memorandum would summarize the mitigation measures to be undertaken for the action and alternatives. A sample memorandum is provided as Appendix A. If the specific action is expected to (1) create impacts not described in the PEA; (2) create impacts greater in magnitude, extent, or duration than those described in the PEA; or (3) require mitigation measures to keep impacts below significant levels that are not described in the PEA, then a Supplemental Environmental Assessment (SEA) and corresponding FONSI would be prepared to address the specific action. The SEA would be tiered from this PEA, in accordance with 40 CFR Part 1508.28.1 A sample SEA is presented in Appendix B. If, during the preparation of the SEA, it is determined that a more detailed environmental review is required or that the specific action is really a poor fit for the typology described in the PEA, rather than trying to develop an SEA, it would be more effective to revert to the standard EA or EIS process, as required by NEPA and associated federal, state, tribal, and local statutes. Cumulative impacts are defined as environmental effects that are greater in magnitude, extent, or duration than the direct and indirect effects of the proposed FEMA-associated action when combined with the effects of other current and future actions, regardless of the proponent. For example, cumulative impacts could occur to wildlife habitat if a FEMA-funded action to create a fuel-break for a municipality were to occur in the same vicinity and time frame as a prescribed burn undertaken by the U.S. Forest Service (USFS). Individually, these vegetation management actions might allow sufficient habitat for displaced species, but the loss of habitat in both areas could substantially affect wildlife. Similarly, cumulative impacts could occur to hydrology in the case of a FEMA-funded action to widen and harden a waterway upstream from a site where a private entity plans to install a culvert. In this case, each separate action might have negligible effects on a bridge downstream, but the combination of the actions could cause the bridge to be overtopped. Cumulative impacts are not addressed in this PEA because analysis of these impacts requires specific knowledge of other actions occurring or proposed to occur within or near the study area. This information cannot be determined because the study area for this PEA is statewide, and the list of current and future actions that could cause cumulative impacts with FEMA-associated actions is infinite. Cumulative impacts will be considered when determining the compatibility of this PEA for specific actions. If cumulative impacts would be created, these impacts will be considered in an SEA. If no cumulative impacts would be created and the specific action is found to be fully and accurately described in this PEA and PEA FONSI, a prepared memorandum (discussed above) would state that cumulative impacts would not occur from the proposed actions. A description of proposed actions and alternatives is provided in Section 2 (Description of Proposed Actions and Alternatives). 1.4 ACTIONS NOT COVERED BY THIS PROGRAMMATIC ENVIRONMENTAL ASSESSMENT This PEA does not cover any action that meets the criteria for a statutory exclusion, described in 44 CFR 10.8(c), or a categorical exclusion, described in 44 CFR 10.8(d). Also, the PEA does not cover any action that requires a stand-alone EA or EIS. Descriptions of such actions are explained below. 1.4.1 Statutory Exclusions Section 316 of the Stafford Act exempts certain actions from review under NEPA. As listed in 44 CFR 10.8(c), these statutory exclusions include: * Debris removal * Emergency protective measures or other assistance essential to saving lives, protecting public health and safety, and protecting property * Repair, restoration, or replacement actions that do not substantially alter the location, footprint, function, or size of the original facility Improved and alternate actions, described in Section 1.1.3, and mitigation actions, described in Section 1.1.4, do not qualify as statutory exclusions. Even though an action may be statutorily excluded from NEPA, FEMA must still ensure that it complies with other applicable laws and regulations, such as the Endangered Species Act (ESA). However, if FEMA chooses to prepare an EA for this action, the PEA may be applicable. 1.4.2 Categorical Exclusions The CEQ regulations provide for the categorical exclusion of actions that do not individually or cumulatively have a significant impact on the human environment. Neither an EA nor an EIS is required for these actions. FEMA's has identified 19 categorical exclusions, which are described in 44 CFR 10.8(d)(2). Examples of these categorical exclusions include the following: * Acquisition of properties, and associated demolition or removal of structures, in situations where the resulting sites will remain as open space * Planting of indigenous vegetation * Physical relocation of individual structures where FEMA has no involvement in relocation site selection or development * Restoration or retrofit of a facility in a manner that substantially conforms to the predisaster design, function, and location of the facility * Improvements to existing facilities and construction of small-scale mitigation measures in previously developed or disturbed areas with substantially completed infrastructure when those actions do not alter basic functions, exceed the capacity of, or modify the intended land use of the existing facility Certain actions that would otherwise be categorically excluded may be affected by extraordinary circumstances, as described in 44 CFR 10.8(d)(3), such as the presence of endangered species or the presence of archaeological or historical resources. In such cases, the categorical exclusion may not apply, resulting in the need to prepare an EA. The PEA may be applicable to such actions. 1.4.3 Actions Requiring an Environmental Assessment Instead of a Programmatic Environmental Assessment The PEA does not apply to actions: * That do not fall within one of the types of actions described in Section 2 * For which the analysis of impacts of alternatives presented in Section 4 is not applicable or comprehensive In such cases, a separate, stand-alone EA must be prepared. 1.4.4 Actions Requiring an Environmental Impact Statement If FEMA has previously determined that an EIS-level of review is required for an action, that action would not be considered in this PEA. If, in preparing an SEA or a separate EA, FEMA reaches the conclusion that the action has the potential to result in a significant environmental impact that cannot be mitigated such that a FONSI cannot be issued, FEMA must issue a Notice of Intent to Prepare an Environmental Impact Statement. 1.5 ACTIONS COVERED BY THE PROGRAMMATIC ENVIRONMENTAL ASSESSMENT The PEA covers the following types of actions: * Constructing, modifying, or relocating buildings and infrastructure (actions include construction of temporary facilities, restoration of disaster-damaged facilities, and mitigation actions) * Modifying waterways, waterway crossings, and coastal features (category also includes temporary facilities, restored facilities, and mitigation measures) * Vegetation management to reduce the risk of damage from flooding and from wildland fires Specific types of actions are described in Section 2. 1.6 PURPOSE OF AND NEED FOR ACTION FEMA's objectives are to: * Reduce or eliminate immediate threats to life, public health and safety, and improved property resulting from major disasters or emergencies * Repair, restore, or replace public facilities damaged in such events * Reduce or eliminate the risk of future damage or loss associated with such events Without FEMA action, the following would likely result: * The threat of immediate harm or loss to individuals, families, communities, and properties would not be alleviated. * Government agencies and private nonprofit organizations would not have the resources to restore essential public services or to restore, repair, or replace damaged facilities. * Communities would not have the resources to reduce the risk of repetitive damage from future events. Facilities would not be retrofitted to resist future damage; homes, businesses, and public buildings would not be relocated out of high-hazard areas; and threats from hazards such as flooding and wildfire would not be reduced through mitigation actions. 1.7 CALIFORNIA ENVIRONMENTAL QUALITY ACT AND APPLICABLE PERMITS FEMA is responsible for ensuring that its actions comply with all applicable federal laws and regulations. However, in accepting assistance from FEMA, state and local governments as well as private nonprofit organizations must ensure that their actions also comply with applicable state and local laws. It is the subgrantee's responsibility to ensure that an action meets the requirements of the California Environmental Quality Act (CEQA) and to obtain additional permits as applicable. For example, for an action that includes work in a stream channel, the subgrantee is responsible for obtaining a streambed alteration permit from the California Department of Fish and Game (CDFG). Under the CEQ regulations (40 CFR 1500.4), federal agencies must reduce excessive paperwork when complying with NEPA. Methods to attain this goal include incorporating material by reference, integrating NEPA requirements with other environmental review and consultation requirements, and eliminating duplication with state and local documents by preparing joint documents. Therefore, FEMA and subgrantees may cooperate to incorporate NEPA and CEQA documents by reference and prepare joint documents whenever practicable. In many cases, this cooperation consists of the subgrantee referencing the PEA in the CEQA document, as appropriate, and adding action-specific information and impact analysis. FEMA then completely references the CEQA document and all other relevant environmental studies in preparing the SEA. In some instances, the CEQA document and the SEA could be combined into a joint federal-state SEA. 1.8 USING THE PROGRAMMATIC ENVIRONMENTAL ASSESSMENT 1.8.1 Organization of the Programmatic Environmental Assessment This PEA is organized into the following sections: * Section 2 describes the actions that are covered by the PEA. * Section 3 describes the affected environment that provides a basis for measuring the impacts of actions. * Section 4 describes the potential environmental consequences of implementing actions and also provides an Impact Summary Matrix, which allows for convenient comparison of actions. * Section 5 describes the process of public participation and agency coordination in the preparation of this PEA and for its future use. * Section 6 provides the list of references. In addition to the main text, the PEA includes appendices that provide a sample PEA compliance memorandum, a sample SEA, responses from federal and state agencies, and programmatic agreements. 1.8.2 Use of the Programmatic Environmental Assessment The PEA covers the actions and alternatives described in Section 2. As stated above, FEMA will prepare stand-alone EAs for proposed actions and alternatives that cannot be categorized among those described in that section. As stated in Section 1.3, a specific proposed action fully described and assessed in this PEA and the FONSI to this PEA would only require a memorandum regarding the proposed action to comply with NEPA (Appendix A). This PEA will also serve as a general document for SEAs and their corresponding FONSIs to tier from a specific action to comply with NEPA. Actions that have been determined, during the preparation of the SEA, to require a more detailed or broader environmental review will be subject to a standard stand-alone EA or an EIS, as required by NEPA. A sample SEA is provided in Appendix B. 1.8.3 Other Complementary Programmatic Documents FEMA has executed and is in the process of preparing additional programmatic documents and interagency coordination that support the material contained in this PEA. The following provides a brief summary of these documents and their implementation. * Memorandum of Understanding with the U.S. Fish and Wildlife Service (USFWS): As described in more detail in Section 3.4.1.1 of this PEA, Section 7 of the ESA requires FEMA to consult with the USFWS before implementing or funding any action that may affect threatened or endangered species under the jurisdiction of the USFWS. To consolidate and streamline the Section 7 consultation process, FEMA and the USFWS have executed a Memorandum of Understanding that establishes a framework for consultation between FEMA and the USFWS (Appendix C). * Programmatic Consultation with the USFWS: FEMA is in the process of conducting Programmatic Consultation with the USFWS for future disasters throughout California. FEMA anticipates that the Programmatic Consultation it is now conducting with the USFWS will result in a Programmatic Biological Opinion (PBO) and a Programmatic Incidental Take Statement (PITS) for all future flood, earthquake, fire, rain, and wind disasters in California. Details of the Programmatic Consultation process with the USFWS are provided in Section 3.4.1.1. * Programmatic Consultation with National Marine Fisheries Service (NOAA Fisheries): As described in more detail in Section 3.4.1.1 of this PEA, Section 7 of the ESA requires FEMA to consult with NOAA Fisheries before implementing or funding any action that may affect threatened or endangered species under the jurisdiction of NOAA Fisheries. FEMA has conducted this Programmatic Consultation through an informal consultation process with NOAA Fisheries for future disasters throughout California. FEMA submitted a Programmatic Biological Assessment to NOAA Fisheries on August 28, 2003 for all future flood, earthquake, fire, rain, and wind disasters in California. NOAA Fisheries replied to this submission by issuing a letter of concurrence on October 14, 2003. Details of the Programmatic Consultation process with NOAA Fisheries are provided in Section 3.4.1.1. * Agreement regarding Section 7 consultation on the ESA when the U.S. Army Corps of Engineers (USACE) serves as lead agency: Under the Public Assistance Program, situations exist where the estimated cost of the work is less than the amount specified for the fiscal year under 44 CFR 206.203 and published in the Federal Register.2 The subgrantee is often responsible for preparing the application for FEMA grant funding. In some of these situations, a permit may be required or may have been applied for by the subgrantee under Section 404 of the Clean Water Act (CWA) and FEMA, due to the nature of the grant application process for these low-cost projects, is not able to review the action for its compliance or applicability to NEPA. In these situations, the USACE has agreed to be the federal agency responsible for complying with Section 7 of the ESA and the agency that conducts Section 7 consultation for such actions. A copy of this agreement is provided as Appendix D. * Programmatic Agreement (PA) with the California State Historic Preservation Officer (SHPO): As described in more detail in Section 3.5.1.1 of this PEA, FEMA is required to comply with Section 106 of the National Historic Preservation Act (NHPA) before implementing or funding any action that may affect properties included in or eligible for inclusion in the National Register of Historic Places (NRHP). To streamline the Section 106 review process, FEMA, the SHPO, the California Office of Emergency Services (OES), and the Advisory Council on Historic Preservation (ACHP) have executed a disaster-specific PA for each recent disaster in California. In December 2003, these parties executed a PA for future disasters in California. Details of the PAs are provided in Section 3.5.1.1. 2. Section 2 TWO - Description of Proposed Actions and Alternatives This section describes typical actions, including the No Action Alternative, undertaken by FEMA in response to or in preparation for flood, fire, wind, rain, and earthquake disasters. Any action, including the No Action Alternative, has the potential to be the preferred alternative (that is, the proposed action) or an alternative to the proposed action for a specific project being funded by FEMA. The funding level for a specific action or alternative varies in accordance with the circumstances associated with that action or alternative, such as program requirements, location, and other circumstances and contingencies. Actions are described independently of the source or amount of funding. In addition, actions may be reviewed separately unless a physical or functional interdependency exists. All actions considered in this PEA assume that FEMA action is: * Required as a result of a major disaster declaration and is administered in accordance with the Stafford Act and its implementing regulations in 44 CFR Part 206, or * Funded under FEMA's authorities for floodplain management in accordance with the National Flood Insurance Act and the Flood Disaster Protection Act and their implementing regulations in 44 CFR Parts 59-78. Several of the actions described in the following sections could be eligible for one of more categorical exclusions. As discussed in Section 1.4.2 of this PEA, actions that would normally be categorically excluded from NEPA review may have extraordinary circumstances that require an advanced analysis of impacts in the form of an EA. The evaluation of such actions in the PEA may be appropriate. Further, actions that may appear to be eligible for one or more categorical exclusions may involve improvements or other additional actions that would also require analysis in an EA. The PEA may also be applicable to these actions. Nonetheless, actions eligible for categorical exclusions (as described in 44 CFR 10.8[d][2]) should be categorically excluded; the listing of such actions below should not imply that a PEA is always necessary for these actions. Some actions require federal, state, or local permits or coordination. It may be necessary for FEMA to coordinate with the following federal and state agencies when conducting environmental review: * USACE * State Water Resources Control Board (SWRCB) * USFWS * NOAA Fisheries * CDFG * State Lands Commission * California Air Resources Board (CARB) and/or the applicable regional air quality jurisdictions The agencies that FEMA or the subgrantee would need to coordinate with would vary depending on the particular action and the specific affected resources at the site where the action would occur. Some of the actions covered by this PEA and described below typically require coordination with certain agencies. In the description of the proposed actions and alternatives below, this typical coordination activity, when applicable, is discussed. 2.1 NO ACTION ALTERNATIVE Inclusion of a No Action Alternative in the environmental analysis and documentation is required under NEPA and is defined as maintaining the status quo, with no FEMA funding for any alternative action. This alternative evaluates the effects of not providing eligible assistance for a specific action and provides a benchmark against which the alternative actions may be evaluated. Although FEMA would not fund any action under this alternative, it is assumed for the purposes of this PEA that disaster-damaged facilities would be repaired or otherwise restored to pre- disaster conditions with other public or private funds, including insurance payments. It is also assumed that no work would be undertaken on disaster-damaged facilities except for restoration to pre-disaster conditions. Damaged facilities would not be improved, and hazards would remain unmitigated at the disaster-damaged site. Further, no hazard mitigation measures would be undertaken to proactively reduce or prevent disaster damage from occurring in the future. 2.2 NONEMERGENCY DEBRIS REMOVAL Debris removal that is necessary to reduce or eliminate an immediate threat to life, public health and safety, or property is statutorily excluded from the NEPA process by the Stafford Act. However, nonemergency situations, such as in the restoration of facilities, occur where debris removal is necessary. The statutory exclusion does not apply in such situations. For purposes of this document, debris removal performed in these situations is referred to as "nonemergency debris removal." Nonemergency debris removal under this alternative includes: * Removal of rock, silt, sediment, or woody debris that has been deposited by floodwaters in stream channels, bridge and culvert openings, canals, sedimentation basins, sewage treatment ponds, ditches, and other facilities in such a manner as to disrupt normal flows, navigation, recreation, or municipal services * Removal of woody debris from public areas or facilities after wind or fire events that damage or destroy trees * Removal of rock and earth from public areas or facilities after landslides caused by earthquakes or heavy rains * Removal of building rubble from public areas or facilities after earthquakes Removal of material from stream channels usually requires a streambed alteration permit from the CDFG and coordination with the USACE for compliance and permitting under the CWA. All removed debris would be disposed of at approved and licensed disposal sites, in compliance with existing laws and regulations. Any hazardous materials or other contaminants would be removed and disposed of in an appropriate manner. Woody debris and construction materials can be recycled, if recycling facilities exist. 2.3 CONSTRUCTING, MODIFYING, OR RELOCATING FACILITIES Under 44 CFR 206, FEMA is authorized to provide funds for constructing, modifying, or relocating facilities. Relevant action categories are as follows: * Upgrading or otherwise modifying buildings * Providing temporary facilities * Acquiring and demolishing existing facilities * Repairing, realigning, or otherwise modifying roads, trails, utilities, and rail lines * Constructing new facilities or relocating existing facilities * Relocating the function of an existing facility * Extending the pressurized water service area * Developing demonstration projects Actions involving facilities associated with watercourses or coastal features are described in Section 2.4. 2.3.1 Upgrading or Otherwise Modifying Buildings Under this action, FEMA would provide funds to implement changes required by current building codes and standards or otherwise modify existing buildings. Often, these changes have the effect of making the structure more resistant to damage in future events. Typical activities include: * Making buildings more fire resistant (e.g., by replacing roofs and doors with fire-resistant materials) or safer during fires (e.g., by installing sprinkler and alarm systems) * Installing bracing, shear panels, shear walls, anchors, or other features so that buildings are better able to withstand earthquake shaking or high wind loads * Modifying buildings to reduce the risk of damage during floods by elevating structures above the expected flood level or by floodproofing * Modifying buildings to meet another need of a subgrantee, such as with an improved action or an alternate action If a building is located in an identified floodplain and is substantially damaged, the NFIP requires that the building be elevated so that the lowest floor is at or above the base (100-year) flood elevation. Newly constructed buildings, such as those built to replace destroyed facilities must also meet this requirement, if located in floodplains. Structures can be elevated on extended foundation walls, piers, posts, columns, or compacted fill. All materials used below the base flood elevation must be flood resistant. Utilities, such as exterior compressors, must also be elevated above the base flood elevation. A building can also be floodproofed so that floodwaters can encounter it without causing damage to the structure or its contents. "Dry floodproofing" methods involve the installation of flood shields, water-tight doors and windows, earthen barriers, and pumping systems to prevent water from entering the structure. "Wet floodproofing" involves the installation of vents and flood- resistant materials so that water may enter and leave areas of the structure without causing damage. With both dry and wet floodproofing, utilities are modified, elevated, or relocated to prevent floodwaters from accumulating within them. Buildings may also be upgraded to meet codes unrelated to damage from natural hazards, such as upgrades required by changes in capacity or function and upgrades necessary to meet the requirements of the Americans with Disabilities Act. 2.3.2 Providing Temporary Facilities FEMA may provide temporary group housing sites when a disaster renders homes uninhabitable for long periods. Such sites are typically constructed using travel trailers or manufactured housing. Temporary housing that is located in a previously disturbed area and in an area of compatible residential use is categorically excluded from NEPA and, therefore, not covered in this PEA. However, temporary housing located on land not previously disturbed and/or not in a compatible residential area is evaluated in the PEA. Typical activities include: * Developing the pads for dwellings * Constructing ancillary facilities, such as roads, streets, and parking lots * Installing utilities, such as potable water lines, sewer hookups, electricity (including proper street lighting), and telephones lines This action would be implemented if other housing options, such as vacancies in hotel rooms or availability of rental units, are not feasible. Appropriate sites are not to be located in a floodplain, contain wetlands or critical habitat, affect historic properties or archaeological sites, or contain hazardous materials. Installation of housing units and utilities is accomplished in accordance with current codes and standards. After temporary housing is no longer needed at the disaster site, the temporary housing units and associated ancillary facilities are removed by FEMA and the land is restored to its original use. All removed materials would be stored for future use or disposed of in accordance with applicable laws and regulations. FEMA may also provide funding for temporary relocation of essential public services, in the event that the structures housing those services are damaged, destroyed, or otherwise rendered inaccessible by a disaster. In most cases, the lease or purchase of facilities is eligible; however, construction of new facilities may be eligible if this action is cost-effective. Funds are also provided for the upgrades necessary to meet current codes and standards and the installation or modification of appurtenances necessary to operate facilities, such as utilities. 2.3.3 Acquiring and Demolishing Existing Facilities FEMA may provide funds for the acquisition and demolition of existing facilities if they are located in high-hazard areas and are subject to repetitive loss. Typically, these facilities are at a high risk because of (1) damage from flooding; (2) erosion of stream banks, beaches, slopes, or bluffs; (3) landslides; or (4) wildfire. These facilities may consist of private properties, such as houses and commercial buildings, or publicly owned facilities, such as utilities, roads, and bridges. A local government entity purchases private properties on a willing-seller basis, and once the property has been purchased, the property will be dedicated and maintained in perpetuity for uses compatible with open space, recreational, or wetlands management practices, pursuant to 44 CFR 206.434(d) Existing facilities are either removed or demolished. All demolition materials are disposed of at approved and licensed disposal sites, in compliance with applicable laws and regulations. Any hazardous materials or other contaminants are removed and disposed of in an appropriate manner. Construction debris and household materials may be recycled, if recycling facilities exist. Once structures are removed, lots are graded to conform to the local topography and disturbed areas are revegetated with species approved for the local area. Frequently, the local government will develop the acquired land for recreational or open-space uses, such as parks, athletic fields, or walking and bike trails. 2.3.4 Repairing, Realigning, or Otherwise Modifying Roads, Trails, Utilities, and Rail Lines Roads, trails, utilities, and rail lines are typically damaged when floods or heavy rains cause erosion, subsidence, or landslides. Earthquakes may cause similar damage. Repairs are accomplished by replacing earthen material lost during the disaster and replacing the damaged surface, utility line, or, in the case of rail lines, ballast and track. It may be necessary to stabilize the replacement fill using rock, grout, timber walls, or steel sheet piling. Hazard mitigation measures may be installed to prevent future damage. For example, a pipe may be installed to convey drainage beneath a road, thus preventing future washouts, or a utility line may be encased in concrete in an area vulnerable to erosion. If the area of damage is unstable, does not allow for repair, or is subject to repetitive loss, a facility may be realigned so that the area of damage is avoided. Property acquisition or a change in easement may be necessary. Facilities may also be modified as part of improved actions or alternate actions to meet additional needs of the subgrantee. 2.3.5 Constructing New Facilities or Relocating Existing Facilities If a facility is located in a floodplain or other hazard area, is subject to repetitive damage, or has been damaged in such a way that restoration in the current location is not practical or cost- effective, FEMA may fund the construction of a new facility or the physical relocation of the existing facility. Examples of this action include construction of buildings, roads, trails, utilities and utility lines, and rail lines in a different area from the existing facility. The physical relocation of existing facilities is only practical with buildings. In cases of both new facility construction and physical relocation, FEMA may fund the cost of land acquisition and the construction of appurtenant features, such as access roads and utilities. For properties in the hazard area, FEMA would acquire damaged properties, demolish existing structures (except in cases of physical relocation), and place deed restrictions that would limit future uses to open space in perpetuity. New facilities (including buildings, roads, trails, utilities and utility lines, and rail lines) could also be constructed as improved actions or alternate actions to meet additional needs of the subgrantee. 2.3.6 Relocating the Function of an Existing Facility Under this action, FEMA would fund the relocation of the function of a facility to an existing facility that has adequate capacity to handle the additional load with minor modifications, if any. For structures, the occupants and materials would be relocated to alternative structures, traffic would use alternate routes, and utility services would be provided by alternative methods. This action would not entail any major physical construction or addition to the existing facility and, if any work would be required, it would consist of only minor modifications. A typical example is transferring students from a damaged or floodprone school to a suitable existing school nearby, if feasible in terms of capacity and convenience for students, families, and teachers. For properties in the hazard area, FEMA would acquire damaged properties, demolish existing structures, and place deed restrictions that would limit future uses to open space in perpetuity. 2.3.7 Extending the Pressurized Water Service Area As a means of preventing future damage during wildfires, FEMA may fund the extension of pressurized pipelines to a developed area that is prone to repetitive fire damage. Under this action, an existing, pressurized system is extended so that fire hydrants can be installed in the area where damage is likely to occur. Installation, which involves excavation, is typically completed within the road right-of-way. 2.3.8 Developing Demonstration Projects Demonstration projects focus on public education and are designed to highlight procedures that can be employed by the public to reduce property damage during flood, fire, wind, and earthquake disasters. Potential demonstration projects would involve the development of a model facility to demonstrate how hazard mitigation technologies can be used to reduce the potential damage during a disaster. Flood demonstration projects would involve items such as elevating a structure or waterproofing windows and doors that are below the elevation of the 100-year flood event. A fire demonstration project would include vegetation management around a facility and replacing roofs, doors, and windows with fire-resistant materials. Wind and earthquake demonstration projects would include changes to the structural design of buildings to allow them to withstand higher wind velocity or more movement during an earthquake. 2.4 ACTIONS INVOLVING WATERCOURSES AND COASTAL FEATURES Many actions pertain to inland water sources, such as streams, rivers, canyons, and lakes, and coastal features, such as harbors and beaches. Inland water sources may be perennial or may be dry during the summer months. During construction, Best Management Practices (BMPs) are normally employed to reduce soil erosion and prevent or reduce the amount of sediment entering the water source. Work in a stream channel may involve temporary diversion of the channel using sandbags or a cofferdam constructed of fill. Heavy equipment is typically operated from an adjacent road, bank, or other feature; however, in some cases, it may be necessary to operate equipment in a channel area once flow has been diverted. A pipe or a temporary secondary channel may be used to convey the diverted water. The PEA does not apply to flood control works in undeveloped areas or that directly or indirectly serve to protect undeveloped areas. Such an action would require preparation of an EA or an EIS. If an action impacts a natural waterway, alters vegetation adjacent to a stream corridor, or impacts a floodplain, coordination with the USACE, CDFG, and SWRCB may be required. If the action affects a water source that supports anadromous fish species, such as salmon, coordination with the NOAA Fisheries is required. If the action involves channel modifications, changes to the capacity of bridges and culverts, or the installation of attenuation structures, it may be necessary to conduct hydraulic/hydrologic analyses to evaluate the potential effect of changes of downstream flow rates. Relevant categories of actions are as follows: * Repairing, stabilizing, or armoring embankments * Creating, widening, clearing, or dredging a waterway * Constructing or modifying a water crossing * Constructing or modifying a water detention, retention, or storage facility * Constructing or modifying other flood control structures * Constructing or modifying a coastal feature 2.4.1 Repairing, Stabilizing, or Armoring Embankments These actions would involve the repair of earthen or rock embankments damaged by floodwaters. Examples include natural stream banks (such as those in parks); road, trail, and rail line embankments; embankments for irrigation and navigation canals; and levees used for flood control and reclamation. In addition to repair of damaged features, FEMA may fund measures designed to prevent damage in future flood events. In addition to replacing fill material, embankments may be stabilized or armored through: * Placing of rock riprap * Hardening with concrete or soil cement * Installing retaining walls, gabions, or geotextile fabrics * Using bioengineering techniques, such as planting vegetation, placing root wads, or placing willow bundles A combination of these techniques may be employed. For example, rock and geotextiles, when used with root wads and willow bundles, may provide mitigation from erosion while enhancing the natural values of a stream corridor. 2.4.2 Creating, Widening, Clearing, or Dredging a Waterway These actions would be employed to reduce the flood hazard to adjacent lands, facilities, or populated areas. New channels would be constructed to convey excess flows around flood-prone areas during flood events. Drainage swales, earthen channels, concrete channels, or subsurface concrete pipes can be used as a means of conveyance. The new channel would be constructed in a dry environment and connected to the stream after the channel has been completed. The channel may have an inlet weir higher than the elevation of the normal flow so that normal flows would remain in the natural channel. The outlet may be armored with concrete or rock riprap to prevent excessive erosion of the existing channel. Existing channels would be widened to allow a channel to convey a larger volume of water. Conveyance may also be increased by replacing earthen banks or channel bottoms with concrete. To the extent possible, the construction would be conducted from the top of the bank, but many actions would require construction equipment to work in the stream channel. In perennially flowing streams, work in a stream channel would generally be restricted to the low-flow period, and the flow would be diverted around the construction area. A pipe or a temporary secondary channel would be used to convey the diverted water. As an alternative to constructing a bypass or modifying an existing channel, the existing channel may be cleared of vegetation or sediment to increase conveyance. This action is often used in developed areas where modifications are not feasible as well as in areas where years of inadequate maintenance have allowed trees and brush to grow within the channel or sediment and debris to accumulate in the channel or around culverts and bridges. Vegetation may be removed through mechanical means, by hand, or by application of herbicides (see Section 2.5). Vegetation may be removed not only from the channel but also from the banks and high-water areas, thus reducing the risk that floating debris will be trapped by trees or heavy brush. Sediment and debris may be removed by dredging, through use of heavy equipment, or by hand, as described in Section 2.2. All removed debris would be disposed of at approved and licensed disposal sites, in compliance with applicable laws and regulations. Woody debris and vegetation can be recycled, if recycling facilities exist. 2.4.3 Constructing or Modifying a Water Crossing FEMA may fund the repair or replacement of damaged water crossings, the enlargement of openings to allow greater conveyance and to reduce the risk that debris will get trapped during floods, or the installation of bank protection or other means to reduce the risk of erosion. Crossings may also be relocated or improved to avoid high-hazard areas, repetitive damage, or areas where reconstruction is not cost-effective or feasible. Culverts may consist of corrugated metal pipes, reinforced concrete pipes, or reinforced concrete box culverts. The capacity of a culvert crossing may be increased to reduce the risk of flooding to the surrounding area, or the culvert may be modified to prevent overtopping or erosion of the crossing. Typical measures include: * Increasing the size of a culvert or adding additional culvert barrels * Changing the type of culvert * Changing the location or alignment of the culvert * Adding features, such as a headwall, discharge apron, or riprap, to reduce the risk of erosion or damage to the culvert or the crossing If a culvert's capacity is increased substantially, the reduced attenuation of flow could cause increased flooding or erosion downstream. These effects would be evaluated by conducting hydraulic and hydrologic analyses. Similarly, bridges may be modified to increase capacity to reduce the risk of flooding or to reduce the risk of damage to the crossing. Typical actions include: * Widening of existing openings or construction of new openings * Reconfiguring bracing to reduce the risk that debris will be trapped * Installing protective features, such as concrete abutments or riprap, to reduce the risk of damage due to erosion and scour * Replacing a multispan structure with a clear-span structure A bridge may be installed to replace a culvert as a means of increasing the flow capacity of a crossing. If the piers of the bridge are located within the channel of the watercourse, it may be necessary to construct a temporary diversion, as described above. As with culverts, modifications to bridges may attenuate flow and require an analysis of downstream effects on erosion and flooding. Low-water crossings may be installed or improved as an alternative to repairing or replacing a culvert or bridge. Constructing or upgrading a low-water crossing would typically involve hardening the banks and bottom of a water body. A temporary diversion may be necessary during construction activities. As for bridges and culverts, flow attenuation and downstream impacts to erosion and flooding would require evaluation. 2.4.4 Constructing or Modifying a Water Detention, Retention, or Storage Facility Potential actions include the construction, enlargement, or restoration of detention basins, retention basins, sediment ponds, and reservoirs to reduce flood flows or to provide a water source for fighting fires in an area of high fire hazard. The creation and/or enlargement of water storage reservoirs would be most frequently associated with flood disasters, and to a lesser extent fire disasters. Detention dams, retention dams, and sediment ponds would be routinely constructed to temporarily store flood flows so that downstream peak flows would be reduced. The stored water would be released at a slower rate so that the existing drainageways can convey the water without contributing to downstream flooding. All areas disturbed during the construction of the detention dams, retention dams, or sediment ponds would be revegetated with native plant species. This action would also include the repair or restoration of water retention structures. All sediment removed from detention dams, retention dams, and sediment ponds would be disposed of in a manner consistent with federal, state, and local laws and regulations. Frequently in rural areas, fire fighting is heavily constrained by the lack of water that can be used by firefighters. In response to this need, proposed actions may also include the creation of retention dams in locations that can readily be accessed by firefighters either as a direct source of water or as a source of water to fill their water supply trucks. All areas disturbed during the construction of the retention dam would be revegetated with native fire-resistant plant species. 2.4.5 Constructing or Modifying Other Flood Control Structures A flood control structure is a facility designed to prevent floodwaters from entering a flood- prone area. Typical examples include levees (also referred to as dikes) and floodwalls. Actions include: * Repairing damaged facilities, usually during emergency situations * Installing embankment protection, as described in Section 2.4.1 * Raising the height of existing facilities to prevent overtopping in future floods * Constructing new facilities to protect flood-prone areas from damage during future floods * Modifying or installing interior drainage systems to reduce the risk of damage behind levees and floodwalls during heavy rains or flooding events on tributary streams Levees would be repaired or constructed using compacted fill and, in some cases, riprap protection at the base. Bare earth would be seeded with grasses to prevent erosion. Typically, a road would be installed on the crest with gravel to allow for maintenance. Floodwalls, typically built in urban areas, would be constructed using reinforced concrete or grouted, reinforced concrete block. Excavation would be necessary to install footings. Both types of structures would include interior drainage systems that may include pumps for removing accumulated water. 2.4.6 Constructing or Modifying a Coastal Feature These actions would involve the repair, replacement, or construction of facilities in coastal environments, such as estuaries, inlets, harbors, and beaches. These facilities include: * Recreational facilities, such as piers and boat ramps * Facilities for maritime use, such as docks and slips * Shoreline protection devices, such as seawalls, groins, jetties, and revetments * Coastal flood control structures, such as levees Construction activities would be expected to occur in water and would involve driving piles, placing rock or soil, or dredging sand, mud, or other sediment. 2.5 VEGETATION MANAGEMENT Vegetation management would be employed to reduce the risk of wildfire and, as described in Section 2.4, to increase the ability of channels to convey flows, thus reducing the risk of flood damage. These actions may be accomplished using mechanical means, hand clearing, application of herbicides, prescribed burning, or grazing. Some actions may include a combination of these methods. Vegetation management actions in areas where threatened and endangered species are thought to exist would require coordination with the USFWS or NOAA Fisheries. Prescribed burns require coordination with the CARB and/or the applicable regional air quality jurisdictions. Relevant categories of actions are as follows: * Mechanical or hand clearing of vegetation * Herbicidal treatments * Prescribed burns * Biological control 2.5.1 Mechanical or Hand Clearing of Vegetation This action would involve construction, expansion, and/or maintenance of fuel breaks and fuel- reduction zones. For the purpose of this document, fuel breaks are corridors where all woody vegetation has been removed. The purpose of a fuel break would be to reduce the extent of fire and to provide a location in which firefighters can work safely and effectively. Fuel breaks can also be compacted or graded for use as fire access roads. Unlike fuel breaks, fuel-reduction zones (also called shaded fuel breaks) would involve the selective removal of vegetation such that a certain proportion of vegetation is left in place. Fuel- reduction zones differ from untreated-forested areas because in fuel-reduction zones low- and mid-height vegetation has been removed or reduced and the density of mature trees has been reduced. The purpose of fuel-reduction zones is to reduce the speed at which a fire spreads and to create a safer environment for firefighters. To create fuel-reduction zones, dead and diseased trees would be removed, along with high-ignition-potential species, such as eucalyptus or Monterey pine. Low- and mid-height individual plants and limbs would be removed or reduced to minimize fire ladders (vegetation that permits fire to travel from the understory to the canopy). Mechanical removal would use heavy equipment that can uproot, crush, pulverize, or cut the trees and brush being removed. Hand removal would involve the use of chainsaws, axes, and hoes to cut and uproot vegetation. Vegetation downed as a result of mechanical or hand removal would be piled and burned on site, chipped and spread on site, or loaded and hauled from the site. After the removal of the targeted vegetation, cleared areas may be revegetated with native fire-resistant species. The subgrantee would be responsible for the maintenance of created fuel breaks and fuel-reduction zones. On occasion, mechanical and/or hand removal of vegetation would be employed around a much larger area that has been targeted for a prescribed burn, as discussed in Section 2.5.3, to reduce the potential that the set fire will escape from the burn area. 2.5.2 Herbicidal Treatments Actions generally associated with herbicidal treatment include the removal of targeted exotic invasive species within specific areas and the prevention of growth and resprouting (e.g., eucalyptus removal) of undesirable vegetation once an area has been cleared of excessive vegetation by mechanical removal, hand removal, and/or prescribed burns. Only readily accepted and registered chemicals would be used to control the growth of undesired vegetation. After treatment, some areas may be revegetated with locally occurring, native vegetation that is fire resistant. 2.5.3 Prescribed Burns Prescribed burns would be used in areas with high-fire-hazard potential due to the amount of fuel that is on the forest floor. The intent of a prescribed burn is similar to that of the fuel-reduction zones discussed in Section 2.5.1 except that the treatment area is typically larger. Prescribed burns would only be proposed and authorized in areas where it can be ensured that the fire can be controlled and contained within the proposed burn area. As discussed in Section 2.5.1, prescribed burn projects would be frequently combined with mechanical and/or hand removal of vegetation around the perimeter of the proposed burn area, which would help to ensure that the fire is contained. Generally, prescribed burns would be designed to minimize impacts on riparian vegetation adjacent to a perennial stream. Prescribed burns would require interagency coordination by the subgrantee to ensure that all appropriate federal, state, and local agencies have been notified of the action and that all their concerns have been addressed. FEMA requires that the applicant follow the burn procedures outlined in the California Environmental Protection Agency's Forest Management Burning Handbook (CEPA 1994). The burn must be terminated if weather conditions become undesirable. Burn actions can also include the burning of trees and brush that have been piled as the result of mechanical and/or hand removal activities. The burning of these piles would require a burn plan and interagency coordination prior to implementation. 2.5.4 Biological Control Under this action, the subgrantee would allow cattle, horses, goats, sheep, or other livestock to graze on grasses and other vegetation as a means of control. The subgrantee would fence the area proposed for grazing, so that the animals would not graze outside of the proposed area. The type of animals, timing, duration, and stocking rate would be selected based on the targets of the vegetation management plan (i.e., the quantity and quality of residue to remain). 2.6 PUBLICATION AND REVISION OF FLOOD INSURANCE RATE MAPS As described in Section 1, FEMA manages the NFIP. The program is based on an agreement between local communities and the federal government that if a community implements programs to reduce future flood risks, the federal government makes flood insurance available within the community as a financial protection against flood losses that occur. In support of the NFIP, FEMA has undertaken a nationwide effort to identify and map flood hazards. These flood hazards are shown on Flood Insurance Rate Maps (FIRMs), which FEMA produces for each community participating in the program. The FIRMs show identified Special Flood Hazard Areas (SFHAs), which are areas subject to inundation during a flood having a 1 percent chance of occurrence in a given year (also known as the base flood or 100-year flood). FEMA periodically revises FIRMs to reflect changes in hydrologic and hydraulic conditions, to update map information based on more detailed data, or to reflect changes to the built environment, such as the placement of fill in the floodplain or the construction of a flood control channel. These revisions may result in changes to the base flood elevations and floodplain delineations shown on the FIRMs. Communities are required to update their floodplain management ordinances to reflect the revised maps. Development may take place within the SFHA, provided that the development is in compliance with local floodplain ordinances, which must meet the minimum federal requirements (see Section 2.3.1). Local governments are responsible for implementing these floodplain management ordinances. If the community fails to adopt or enforce its floodplain management ordinance, FEMA may sanction the community or suspend it from the NFIP, thereby restricting the financial benefits of participating in the program. However, FEMA has no other authority or responsibility to govern whether and how this development occurs. FEMA's involvement in floodplain management is otherwise limited to publication and revision of the FIRMs, which are categorically excluded from the preparation of an EA or an EIS (44 CFR 10.8[d][2][iii]). Therefore, impacts resulting from the publication and revision of FIRMs are not evaluated further in this PEA. 3. Section 3 THREE - Affected Environment The following subsections discuss the setting and affected environment of 12 resource areas in California: * Geology, Seismicity, and Soils * Air Quality * Water Resources * Biological Resources * Cultural Resources * Socioeconomics and Public Safety * Land Use and Planning * Public Services and Recreation * Transportation * Noise * Hazardous Materials and Wastes * Visual Resources This discussion is broad and regional in nature. It does not include a complete inventory of each resource but does provide information to characterize those resources. 3.1 GEOLOGY, SEISMICITY, AND SOILS Key resource categories and assessment variables described in this section include geology and physical processes, geologic resources, geologic hazards, geomorphology, seismicity and seismic hazards, and soils. 3.1.1 Regulatory Background 3.1.1.1 Federal Laws and Regulations Executive Order 12699: Seismic Safety of Federal and Federally Assisted or Regulated New Building Construction The purposes of these requirements are to: * Reduce risks to the lives of occupants of buildings owned by the federal government, leased for federal uses, or purchased or constructed with federal assistance and to persons who would be affected by the failures of federal buildings in earthquakes * Improve the capability of essential federal buildings to function during or after an earthquake * Reduce earthquake-related losses to public buildings in a cost-effective manner A building means any structure, fully or partially enclosed, used or intended for sheltering persons or property. Under this order each federal agency responsible for the design and construction of a federal or federally funded building must ensure that the building is designed and constructed in accord with appropriate seismic design and construction standards. These standards are promulgated through the National Earthquake Hazard Reduction Program (NEHRP) and are subsequently incorporated into the model building codes that are used as the basis for local building codes in most municipalities. NEHRP periodically publishes new standards; the latest NEHRP standards were published in 2000. This requirement pertains to all building projects for which detailed plans and specifications were initiated subsequent to the issuance of the order. Each federal agency responsible for the construction and lease of a new building must also ensure that the building is designed and constructed in accord with appropriate seismic design and construction standards. Local building codes are used in design and construction and augmented when necessary to achieve appropriate seismic design and construction standards. According to Office of Management and Budget Circular A-119 of January 17, 1980, entitled Federal Participation in the Development and Use of Voluntary Standards, nationally recognized private-sector standards and practices are to be used unless the responsible agency finds that none are available that meet its requirements. This circular states that design criteria should consider the seismic hazards in various areas of the country, as shown in the most recent edition of the American National Standards Institute Standards A58, Minimum Design Loads for Buildings and Other Structures, or subsequent maps adopted for federal use. Local building codes may be used if determined by the responsible agency or by the Interagency Committee for Seismic Safety in Construction to provide adequately for seismic safety. Special seismic standards and practices may be used if required by a unique agency mission. Farmland Protection Policy Act of 1981 The Farmland Protection Policy Act (7 United States Code [USC] 4201 et seq.) and the U.S. Department of Agriculture's implementing procedures require federal agencies to evaluate the effects (direct and indirect) of their activities before taking any action that could result in converting designated prime or unique farmland for nonagricultural purposes. If an action would adversely affect farmland preservation, alternative actions that could avoid or lessen adverse effects must be considered. Federal agencies also must ensure that their programs, to the extent practicable, are compatible with state, local, and private programs to protect farmlands. Determination of the level of impact to prime and unique farmland or farmland of statewide and local importance is done by the lead federal agency, which inventories farmlands affected by the proposed action and scores part of an AD 1006 Form, Farmland Conversion Impact Rating, for each alternative. Through consultation with the Natural Resources Conservation Service (NRCS) staff in the particular county of the proposed action, NRCS completes the AD 1006 Form and determines the level of consideration for protection of farmlands that needs to occur under the Act. 3.1.1.2 State and Local Laws and Regulations 1998 California Building Code The CBC contains the minimum standards for design and construction in California. Local standards other than the CBC may be adopted if those standards are stricter. The CBC incorporates the standards associated with seismic engineering that are detailed in the Uniform Building Code (UBC) of 1997. The 1997 UBC and therefore the 1998 CBC reflect the National Earthquake Loss Reduction Program provisions published in 1994. With the publication of the 2000 NEHRP standards, the 1998 CBC no longer reflects current standards. Consequently, until California adopts a building code reflecting the 2000 NEHRP standards, structures permitted after the 2000 standards became available will not be in compliance with Executive Order (EO) 12699. California Public Resources Code § 25523(a), 20 California Code of Regulations § 1752(b) and (c), and the 1972 Alquist-Priolo Earthquake Fault Zoning Act (Amended 1994) The Alquist-Priolo Earthquake Fault Zoning Act (A-P Act) was passed in 1972 to mitigate the hazard of surface faulting to structures for human occupancy. This state law was a direct result of the 1971 San Fernando Earthquake, which was associated with extensive surface fault ruptures that damaged numerous homes, commercial buildings, and other structures. Surface rupture is the most easily avoided seismic hazard. The main purpose of the A-P Act is to prevent the construction of buildings used for human occupancy on the surface trace of active faults. The act only addresses the hazard of surface fault rupture and is not directed toward other earthquake hazards. The Seismic Hazards Mapping Act, passed in 1990, addresses nonsurface fault rupture earthquake hazards, including liquefaction and seismically induced landslides. The A-P Act requires the State Geologist to establish regulatory zones (known as Earthquake Fault Zones) around the surface traces of active faults and to issue appropriate maps. The maps are distributed to all affected cities, counties, and state agencies for their use in planning and controlling new or renewed construction. Local agencies must regulate most development projects within the zones, including all land divisions and most structures for human occupancy. Single-family wood-frame and steel-frame dwellings of up to two stories that are not part of a development of four units or more are exempt. However, local agencies can be more restrictive than state law requires. Before a proposed action can be permitted, cities and counties must require a geologic investigation to demonstrate that proposed buildings will not be constructed across active faults. An evaluation and written report of a specific site must be prepared by a licensed geologist. If an active fault is found, a structure for human occupancy cannot be placed over the trace of the fault and must be set back from the fault (generally 50 feet). Earthquake Fault Zones are regulatory zones around active faults. The zones are defined by turning points connected by straight lines. Most of the turning points are identified by roads, drainages, and other features on the ground. Earthquake Fault Zones are plotted on topographic maps at a scale of 1 inch equals 2,000 feet. The zones vary in width, but average about 1/4 mile wide. Effective June 1, 1998, the Natural Hazards Disclosure Act requires that sellers of real property and their agents provide prospective buyers with a "Natural Hazard Disclosure Statement" when the property being sold lies within one or more state-mapped hazard areas, including Earthquake Fault Zones. California Public Resources Code Chapter 7.8 and the Seismic Hazards Mapping Act of 1990 This law addresses shaking, landsliding, and liquefaction hazards. It expands from the surface fault-rupture hazard addressed in the A-P Act to other seismic hazards, including shaking, landsliding, and liquefaction. This law requires the State Geologist to prepare seismic hazard maps that cities and counties must use in preparing their general plan safety elements and in regulating new development to avoid or mitigate these seismic hazards. The California Geological Survey (formerly the California Division of Mines and Geology) has adopted regulations for the mapping process under Title 14 of the California Code of Regulations (CCR). The Seismic Hazards Mapping Act of 1990 allows the lead agency to withhold permits until geologic investigations are conducted and mitigation measures are incorporated into plans. This act not only addresses seismically induced hazards, but also includes such things as expansive soils, settlement, and slope stability. Cities and counties may adopt more stringent criteria and policies, as they see fit. Field Act After the 1933 Long Beach earthquake, statewide seismic design and construction requirements were mandated for public schools. Commonly known as the Field Act, these state requirements were extended to the evaluation and retrofitting of existing pre-Field Act buildings with the passage of the Garrison Act (1939) and the Greene Act (1967). The scope of the regulations is found in CBC, Part I, Title 24, Sec. 4-301 et seq. Field Act buildings have stringent construction quality control procedures (required by CCR Title 24 Part 1). The requirements in this act have been reconsidered on several occasions and recommendations have been made for altering them to be more effective. For example, the California Earthquake Hazards Reduction Program in Initiative 1.3 in 1991 laid out a goal for all school districts to identify and reduce unacceptable earthquake hazards in public schools by the year 2000. The Northridge earthquake provided many observations of school damage that was not covered by the act. Privately owned schools are excluded from the Field Act requirements. Also, the requirements relating to hazard reduction of existing pre-act schools does not apply to the California State University or University of California systems, but it does apply to community colleges. 3.1.1.3 Local Laws and Regulations Counties and cities have developed general plans that include county- or city-specific descriptions of existing geology and geologic resources. Shortly after the 1971 San Fernando earthquake, the state legislature passed a requirement that all city and county general plans include a seismic safety element. During the mid-1970s local governments prepared and adopted seismic safety elements to meet statutory deadlines. In l984, the state legislature streamlined general plan requirements, combining the overlapping safety and seismic safety elements into a single safety element. Each planning agency has to prepare, and the legislative body of each county and city has to subsequently adopt, a comprehensive, long-term general plan for the physical development of the county or city, and of any land outside its boundaries that in the planning agency's judgment bears relation to its planning. 3.1.2 Geology, Geologic Hazards, and Soils in California 3.1.2.1 Geomorphic Provinces A brief examination of the rock types, geologic structure, and geomorphology (landscape features) of California shows some distinct regional differences. The term "geomorphic province" is generally defined to be any area that displays a distinctive geologic and landscape character as defined by the amount of relief, types of landforms, orientation of valleys and mountain ridges, and types of vegetation. As the underlying geology is one of the controlling factors that define the geomorphic character of each province, the geology of California is commonly described in terms of its geomorphic provinces. California comprises 12 geomorphic provinces (Figure 3.1-1). These provinces are described from north to south in the following sections. Klamath Mountains Province The Klamath Mountains Province is located in the northwestern corner of California and southwestern corner of Oregon between the northern Coast Ranges and Cascade Range Province. It is made up of several mountain ranges including the Trinity Alps, the Marble Mountains, the Salmon Mountains, and the Siskiyou Mountains. It is a north-trending area that covers approximately 11,800 square miles. This province consists of a rugged topography with peaks and ridges of similar elevations, between 4,900 to 6,900 feet above sea level. No zoned active faults according to the A-P Act exist within this province (Hart 1994). However, many Quaternary and pre-Quaternary low-angle thrust faults occur, such as the South Fork Mountain thrust to the west of the province, which separates the province from the younger rocks of the Coast Ranges. None of these faults are considered active or potential earthquake sources. One substantial earthquake source exists in this region. Beneath the Klamath Mountains, the Gorda plate (a fragment of the Pacific plate) is being subducted1 eastward beneath the North American plate (Ludwin, Weaver, and Crosson 1991; Urhammer 1991). Friction between the overriding North American plate and the Pacific plate has the potential to generate "megathrust" earthquakes, as does deformation within the downgoing plate itself (Heaton and Hartzell 1987). Cascade Range Province The Cascade Range comprises a 500-mile-long chain of volcanoes that extend from northern California into Oregon and Washington. The Cascade Range province in California is the southern tip of the chain and the geology is more similar to that of the Pacific Northwest than to the geology of California. Within California, the province is located between the Klamath Mountains to the west and the Modoc Plateau Province to the east and north of the Great Valley and Sierra Nevada Provinces. One of the most prominent volcanoes of the Cascade Range in California is Mount Shasta, which rises 14,162 feet above sea level. The southernmost peak of the Cascade Range and the second highest peak within the province is Mt. Lassen (10,453 feet), which last erupted sporadically between 1914 and 1921 (Miller 1989). The portion of the Cascade Ranges within California resulted from the subduction of the Gorda Plate. As the subducted plate is pushed into the mantle it heats up and the rocks eventually melt, producing magma. The molten magma is buoyant and rises through the overlying mantle and crust until it is erupted as lava. Successive lava eruptions eventually build up into volcanoes. Mount Shasta has been built up over the last 10,000 years, when at least 13 major eruptions have occurred. During the last 4,500 years, the average interval between eruptions has been 600 years. The most recent eruption occurred about 200 years ago (Miller 1989). Geologic evidence indicates that large eruptions from Mount Shasta are similar to the 1980 eruption of Mount St. Helens in Washington in that they involve explosive eruptions and are accompanied by large debris avalanches that inundate large areas up to several tens of kilometers away from the volcanic cone (Crandell et al. 1984). Evidence of the associated volcanic history can only be traced back to the Eocene Age; before that the geologic history and formations are similar to the Klamath Mountains. Three A-P Act zoned active faults are located within the province: the Cedar Mountain, Hat Creek, and McArthur faults, all of which make up the boundary between the Cascade Range Province and the Modoc Plateau. Each of these faults is capable of generating damaging earthquakes. In addition to these faults, movement of magma within the crust and volcanic eruptions can also be associated with damaging earthquakes. Modoc Plateau Province The Modoc Plateau is a table formed by thick accumulation of volcanic lava flows and tuff beds located to the east of the Cascades. It is an undulating plateau at an elevation of 4,000 to 6,000 feet above sea level. Occasional lakes, marshes, and slow-moving streams cut this plateau. The province is bounded by the Cascade Range on the west and the Basin and Range Province on the east and south. The boundary with the Cascades is marked by the active normal faults2 of the Hat Creek fault zone. Coast Ranges Province The Coast Ranges Province extends from Lompoc in the south to the Oregon border. Northwest- trending ranges and intervening valleys that are generally parallel to major strike-slip faults (e.g., the San Andreas fault) and fold axes characterize the Coast Ranges. The mountains range from 2,000 to 4,000 feet above sea level. The province is bounded to the east by the Great Valley; to the north by the South Fork Mountain fault, which marks the southern extent of the Klamath Mountains; to the south by the Transverse Ranges; and to the west by the Pacific Ocean. The province is naturally divided into North and South Coast Ranges by the depression that is occupied by San Francisco Bay and the Sacramento-San Joaquin River Delta. The Coast Ranges Province is traversed obliquely by the San Andreas fault system, a broad zone of strike-slip faulting3 that marks the boundary between the Pacific and North American plates. This system of faults, including the San Andreas fault itself, has been responsible for the majority of damaging earthquakes in California during historical time. In addition to the active strike-slip faults of the San Andreas system, the Coast Ranges also contain a number of active reverse or thrust faults4, most notably the blind or buried faults that mark the boundary between the Coast Ranges and the Great Valley. These faults have been responsible for several damaging earthquakes during historical time (Wakabayashi and Smith 1994). The northern part of the Coast Ranges Province is dominated by landslide-prone formations. San Francisco Bay Province The San Francisco Bay area has a structurally controlled topography that consists primarily of north- to northwest-trending mountain ranges and intervening valleys that is characteristic of the Coast Ranges geomorphic province. This fabric is subparallel to the San Andreas fault. The Coast Ranges consist of the Mendocino Range to the north of San Francisco Bay, the Santa Cruz Mountains to the west of the Bay, and the Diablo Range to the east of the Bay. San Francisco Bay is a topographic trough formed by a combination of warping and faulting and is underlain by a down-dropped or tilted block (the Bay Block), which acts as a water gap in the Coast Ranges to allow the San Joaquin and Sacramento rivers to drain to the ocean. The Bay is about 56 miles long and from 3 to 5 miles wide. Constrictions divide the Bay into Suisun, San Pablo, and North and South San Francisco bays. The bay is relatively shallow with depths of less than 10 feet except in locations of drowned drainage channels. The deepest point is within the main channel through the Golden Gate, at a depth of approximately 345 feet below sea level. The geology of the Bay area is made up primarily of three different geologic provinces: the Salinian block, Franciscan complex, and the Great Valley sequence. The Salinian block is located west of the San Andreas fault. It is composed primarily of granitic plutonic rocks that are similar to those found in the Sierra Nevada and are believed to be rocks of the Sierra Nevada batholith that have been displaced along the San Andreas fault. To the east of the San Andreas fault and bounded on the west by the Hayward fault is the Franciscan complex. The rocks of the Franciscan complex are prone to landslides. To the east of the Hayward fault is the Great Valley sequence. These rocks are also prone to landsliding. The Great Valley Province The Great Valley Province comprises two elongate northwest- to southeast-trending basins: the Sacramento basin to the northwest and the San Joaquin basin to the southeast. These basins are located between the Coast Ranges to the west and the Sierra Nevada to the east. The Sacramento and San Joaquin rivers drain the basins respectively and both drain to the ocean through San Francisco Bay. The province is approximately 450 miles long and 45 to 55 miles wide and ranges in elevation from below sea level to approximately 400 feet above sea level. Four faults around the boundary of the Great Valley Province have been zoned under the A-P Act: the Buena Vista and Plieto-Wheeler Ridge faults, which make up the boundary with the Coast Ranges and Transverse Ranges to the west and south, respectively, and the Kern Front and White Wolf faults, which mark the boundary with the Sierra Nevada and eastern Transverse ranges, respectively. Sierra Nevada Province The Sierra Nevada Province is a tilted fault block approximately 400 miles long that forms a mountain range 40 to 100 miles wide. It is bound to the west by the Great Valley Province, to the north by the Cascade Range, to the east by the Basin and Range Province, and to the south by the Garlock fault along the northern margin of the Mojave Desert. The eastern face of the Sierra Nevada is the high, steep fault scarp of the Sierra Nevada fault and others that form the Sierra Nevada block. The western side of the Sierra Nevada is the low-sloping back side of the uplifted block containing rocks that disappear under the younger sediments of the Great Valley. Deep river canyons are cut into the western slope as they drain the Sierra Nevada. The northern boundary of the Sierra Nevada province is defined where the bedrock disappears under the Cenozoic volcanic cover of the Cascade Range. Elevations in the province range from 400 feet above sea level to 14,496 feet at the top of Mt. Whitney, the highest point in the lower 48 states. The present topography of the Sierra Nevada is the result of extensive erosion by glaciers during the Holocene, and subsequent downcutting by high energy rivers, including the Kern, Kings, and Tuolumne. The Sierra Nevada has 10 A-P Act zoned faults, 1 within and 9 along the province boundary. The Cleveland Hill fault is within the province. The Garlock fault is along the Mojave Desert boundary. The Honey Lake, Little Lake, Sierra Nevada, Fort Sage, Hilton Creek, and Owens Valley faults are along the boundary with the Basin and Range Province. The Kern Front fault is located along the Great Valley boundary. Basin and Range Province The Basin and Range Province extends from eastern California to central Utah, from southernmost Oregon and Idaho to the north to southern Arizona and southwestern New Mexico and further into Mexico in the south. Within California the province includes a small portion in the northeastern corner of the state and a much larger area in the southern part of the state bordered by the Sierra Nevada to the west and the Mojave Desert to the south. Throughout the Basin and Range province, range-front faults can be found along the base of the ranges. Recent movements on these faults have elevated the ranges relative to the basins. Recent volcanic eruptions have left young cinder cones, craters, and lava flows. Numerous faults are zoned under the A-P Act within the Basin and Range Province: the Fort Sage, Hilton Creek, Sierra Nevada, and Honey Lake faults, which lie on the boundary with the Sierra Nevada, and the Death Valley fault, the Deep Springs fault, the Northern Death Valley fault, the Panamint Valley fault, the Surprise Valley fault, and the White Mountains fault. Mojave Desert Province The Mojave Desert is a region of isolated mountain ranges separated by expanses of desert plains. The Mojave Desert is located south of the Basin and Range Province and is bounded by the Garlock fault to the north, the Colorado River and the California-Nevada border to the east, and the San Gabriel and San Bernardino Mountains and the San Andreas fault to the southwest. The topography of the Mojave Desert is characterized by basins and ranges. However, the topography in the Mojave Desert is much more subdued than that of the Basin and Range Province. The ranges of the Mojave Desert are shorter and lower and the basins are wider. The topography is gentler than the sharp contrasts between ridge and valley of the Basin and Range Province. Numerous faults within the Mojave Desert Province have been zoned by the A-P Act: the Garlock fault along the Sierra Nevada and Basin and Range boundary, the North Frontal and Pinto Mountain faults along the Transverse Ranges boundary, the Burnt Mountain fault, the Eureka Peak fault, the Helendale fault, the Lenwood fault, the Mesquite Lake fault, the Pisgah- Bullion fault, the Calico fault, the Kickapoo fault, the Manix fault, the Newberry fracture zone, and the Upper Johnson Valley fault. These faults have generated three damaging earthquakes in the last 20 years, including the 1992 Moment Magnitude 7.3 Landers and 1999 Moment Magnitude 7.1 Hector Mine earthquakes. Transverse Ranges Provinces The Transverse Ranges Province is a long, narrow, east-west-trending province that consists of a series of mountain ranges and valleys. The province is bordered to the south by the Peninsular Ranges. This boundary is defined by the Santa Monica fault between the Santa Monica Mountains and the Los Angeles Basin. The Mojave Desert borders this province to the north and the east and the Salton Trough/Colorado Desert Province to the southeast. Numerous active faults are zoned by the A-P Act in this province: the Pinto Mountain and North Frontal faults, which make up the Mojave Desert boundary, as well as the Cucamonga fault, the Red Mountain fault, the San Cayetano fault, the San Gabriel fault, the Raymond Hill fault, the San Andreas fault, the San Fernando fault, and the Ventura fault. Los Angeles Basin Province The Los Angeles Basin Province and the surrounding region are being deformed by several active faults that have generated a number of moderate-sized earthquakes, including the 1933 Long Beach, 1971 San Fernando, 1987 Whittier Narrows, and 1994 Northridge events. Faulting is dominated by both strike-slip and thrust motions, either of which is capable of generating damaging earthquakes. The Los Angeles Basin Province is bounded by the San Andreas fault system to the east, the Transverse Ranges to the north, and the Continental Borderland and Peninsular Ranges provinces to the west and south, respectively. The tectonics of the Los Angeles Basin Province are transitional between those of the Transverse Ranges to the north and the Peninsular Ranges to the south. The Los Angeles Basin Province is an east-west elongate basin filled with Mesozoic and Cenozoic sediments that are highly deformed by a complex system of folds and thrust faults, many of which do not reach the earth's surface (so-called blind thrusts). In addition to these thrust faults, the Los Angeles Basin Province is traversed by a number of northwest-striking, right-lateral strike-slip faults, including the Newport-Inglewood, Elsinore, San Jacinto, and San Andreas faults. These strike-slip faults accommodate the majority of the plate motion between the Pacific and North American plates. The complex tectonics of the Los Angeles Basin Province are the result of a prominent left restraining bend ("The Big Bend") in the San Andreas fault as the fault exits Coachella Valley. This fault geometry creates a region of compression that is manifest as the folds and thrust faults of the Los Angeles Basin Province and the Transverse Ranges Province immediately to the north. Peninsular Ranges Province The Peninsular Ranges Province consists of a series of ranges separated by longitudinal valleys that trend northwest to southeast, subparallel to faults of the San Andreas system. These mountains are composed of granitic rock intruded by metamorphic rocks similar to the Sierra Nevada. This province is located in the southwestern part of the state and is bounded to the north by the Transverse Ranges Province, to the east by the Salton Trough/Colorado Desert Province, to the south by Mexico, and to the west by the Continental Borderlands. Five northwest-trending faults within the Peninsular Ranges Province have been zoned by the A-P Act: the Elsinore fault, the Rose Canyon fault, the Newport-Inglewood fault, the San Jacinto fault, and the Whittier fault. Salton Trough/Colorado Desert Province The Salton Trough/Colorado Desert Province is a low-lying barren desert basin about 245 feet below sea level that contains the Salton Sea and the Imperial Desert. It is bordered by the San Andreas fault to the northeast and the San Jacinto fault to the southwest. The trough is a pull- apart basin created by transform fault movement as the Peninsular Ranges pulled away from North America. Four faults within the province have been zoned by the A-P Act: the Brawley fault, the Imperial fault, the San Andreas fault, and the Superstition Hills fault. Continental Borderlands To the west, the Los Angeles Basin is bounded by the Continental Borderlands. The Continental Borderlands seismotectonic province is located in the offshore region of Southern California, extending from offshore Baja to the Channel Islands. This region is characterized by moderate levels of seismicity, with epicenters often being aligned along active fault structures. 3.1.2.2 Geologic Hazards The geologic environment of California comprises a number of potential geologic hazards, which are discussed in the following sections. The specific geologic hazards for each geomorphic province are described in Table 3.1-1. Surface Fault Rupture Surface fault rupture is defined as slip on a fault plane that has propagated upwards to, and has offset or disturbed, the earth's surface. Offset on a fault intersecting the ground surface can create a discrete step or fault scarp if fault slip occurs on a single fault plane or within a narrow fault zone. If fault slip is accommodated over a broader area, then the deformation may manifest as a zone of fracturing and ground cracking with minor amounts of offset on individual fractures; however, the cumulative offset across the entire zone may be substantial. Surface faulting may also arise as a secondary effect from other geologic processes. Secondary surface faulting can be triggered by aquifer compaction and subsidence (e.g., Bawden et al. 2001) or by the effects of strong ground shaking triggering slip on neighboring faults. Surface fault rupture has occurred on a number of faults within the study region during the last 10,000 years (Jennings 1994): the San Andreas fault in 1857 and 1906 (Wallace 1990), the Hayward fault in 1868 (Yu and Segal 1996), the Owen fault in 1872 (Lubetkin and Clark 1988), the San Fernando fault in 1971 (Barrows et al. 1973), the Imperial and Superstition Hills faults in 1981 (Sharp, Rymer, and Lienkaemper 1986), the Landers fault zone in 1992 (Hart, Bryant, and Trieman 1993), and the Bullion Mountains-Lavic Lake faults in 1999 (U.S. Geological Survey, Southern California Earthquake Center, and California Division of Mines and Geology 2000) are examples of surface rupture associated with large, damaging earthquakes during historical time. Areas subject to surface-faulting rupture hazard are zoned by the State of California under the A- P Act (Hart 1994). Maps of areas of potential surface faulting are prepared by and available from California Geological Survey (formerly Division of Mines and Geology). These maps depict the most recently active traces of active faults and a zone around these traces within which future surface faulting may occur. All geomorphic provinces in California, with the exception of the Klamath Mountains, contain active faults that pose a surface-faulting hazard. Because of the high slip rates and high density of faults in the Los Angeles Basin and San Francisco Bay Area, these two regions have the highest likelihood of experiencing surface faulting in the future. Earthquake Ground Shaking Strong earthquake ground shaking is probably the most important seismic hazard that can be expected almost anywhere in California. The amount of earthquake shaking at a particular site is a function of earthquake magnitude; the type of earthquake source (i.e., type of fault), distance between the site and the earthquake source, the geology of the site, and how the earthquake waves decrease or attenuate as they travel from their source to the site in question. The larger the earthquake and the shorter the distance between the earthquake source and the site, the greater the amount of shaking. The geologic materials through which the earthquake energy travels toward the site act to decrease, or attenuate, the amount of shaking. The amount of shaking is expressed in terms of "Peak Horizontal Acceleration" measured in percent of "g," the acceleration of gravity (approximately 9.81 feet per second squared). California has experienced numerous damaging earthquakes during historical time (Stover and Coffman 1993; Toppozada et al. 2000). The 1868 earthquake on the Hayward fault caused widespread damage throughout the eastern San Francisco Bay Area; the 1906 earthquake on the San Andreas fault caused extensive damage in San Francisco and throughout Northern California. More recently, the 1989 Loma Prieta earthquake in the Santa Cruz Mountains and the 1994 Northridge earthquake in San Fernando Valley caused widespread damage in the San Francisco Bay and Los Angeles Basin regions, respectively. A more comprehensive list of damaging earthquakes is provided in Table 3.1-2. Liquefaction Liquefaction is a phenomenon in which the strength and stiffness of a soil is reduced by earthquake shaking. Liquefaction and related phenomena have been responsible for tremendous amounts of damage by historical earthquakes around the world. Liquefaction is the transformation of a granular material from a solid state into a liquefied state as a consequence of increased pore pressure and decreased effective stress (Youd 1973). Increased pore pressures in unconsolidated sediment, especially in western California, are most typically seismically induced deformation. Observed types of ground failure resulting from liquefaction can include sand boils, lateral spreads, ground settlement, ground cracking, and ground warping (Youd and Hoose 1978). Liquefaction occurs in saturated soils. Lateral spreading is the lateral displacement of surficial blocks of sediment as the result of liquefaction in a subsurface. Once liquefaction transforms the subsurface layer into a fluidized mass, gravity may cause the mass to move downslope toward a cut slope or free face (such as a river channel or a canal). Lateral spreads most commonly occur on gentle slopes that range between 0.3° and 3°. When liquefaction occurs, the strength of the soil decreases and the ability of a soil deposit to support foundations for buildings or other structures is reduced. Liquefied soil also exerts higher pressure on retaining walls, which can cause them to tilt or slide. This movement can cause settlement of the retained soil and destruction of structures on the ground surface. The potential for liquefaction is a function of having susceptible soils, shallow groundwater to create saturated conditions, and high enough ground shaking. If any of these conditions are lacking, then the potential for liquefaction is considered low. Subsidence and Uplift Land surface subsidence can result from both natural and human-made phenomena. Natural phenomena include subsidence resulting from tectonic deformations and seismically induced settlements (see liquefaction), soil subsidence due to consolidation, subsidence due to oxidation or dewatering of organic-rich soils, and subsidence related to subsurface cavities. Subsidence or settlement related to human activities includes subsidence caused by decreased pore pressure due to the withdrawal of subsurface fluids, including water and hydrocarbons. Subsidence and uplift are generally only considered a substantial hazard if they occur over human life time. Most of the mechanisms of subsidence and uplift described above occur over geologic time and, therefore, are not considered a potential hazard. Expansive Soils Expansive soils contain mixed-layer clay minerals that increase and decrease in volume on wetting and drying, respectively. Expansive soils are common throughout California and can cause damage to foundations and slabs unless properly treated during construction. Mixed layer clays and potentially expansive soils are present almost everywhere in California. Mass Wasting Mass wasting is downward movement of soils and rock under gravity, including landslides, rock falls, and debris flows. Mass wasting requires source materials, a slope, and a triggering mechanism. Source materials include fractured and weathered bedrock and loose soils. Triggering mechanisms include earthquake shaking, heavy rainfall, and erosion. Volcanic Hazards Potentially hazardous volcanic events can be categorized into three groups: flowage phenomena, eruption of tephra, and emission of volcanic gases. Flowage phenomena include debris avalanches and flows, pyroclastic flows5 and surges, directed blasts, lava flows, and floods. Any erupted volcanic material that moves down slope, such as lava, ash, water, and mud, away from the flanks of the volcano, or down adjacent valleys, constitutes flowage phenomena. The speed and distance at which they can flow is dependent on the composition of the erupted material, which varies for each volcano and type of flow. Most flowage phenomena are devastating, destroying everything in their path either by impact, burial, or ignition if the material is hot (Miller 1989). Floods occur if molten lava melts snow and ice on the volcano, consequently generating debris flows as lava ash and mud. Lahars, hot volcanic mud flows, are some of the most devastating consequences of volcanic activity. Such debris avalanches and flows, pyroclastic flows, and surges are difficult to avoid as their highly mobile, fluid nature allows them to move swiftly downslope away from their source (Miller 1989). Tephra or ash fall consists of combinations of pumice, dense-rock material of various sizes, and mineral crystals. Ash fall is produced by explosive eruptions that propel material from a few meters to several tens of kilometers into the air (Miller 1989). Hazards related to tephra eruptions include high temperatures, burial, and impact of falling blocks. A substantial volume of tephra can collapse structures under its weight and, if it is hot, ignite fires. Hazards associated with ash fall decrease with distance from the volcano. The main hazard at considerable distances from the volcano would be the effects of ash on the respiratory system. Vehicles and machinery would be affected, possibly causing disruptions in transportation, communication, and electrical services (Miller 1989). Gases are often emitted from vents preceding a volcanic eruption and can occur for hundreds or thousands of years after an eruption. Volcanic gases consist of steam with lesser amounts of carbon dioxide, sulfur, and chlorine. Gases are concentrated near vents but are also distributed downwind. As with tephra, hazards from volcanic gases decrease with distance from the vent. Oxidation of sulfur and chlorine gases can lead to the formation of sulfuric and hydrochloric acid aerosols. Such strong acid vapors can be harmful to plants, animals, and people if the vapors are in high concentrations (Miller 1989). Tsunami and Seiche A tsunami (Japanese word meaning "harbor wave") is a water wave or a series of waves generated by an impulsive displacement of the surface of the ocean or other body of water. Tsunamis can travel across oceanic basins and cause damage several thousand miles from their sources. Most tsunamis are caused by a rapid vertical movement along a break in the Earth's crust (i.e., a tectonic fault rupture on the bottom of the ocean resulting in the displacement of the column of water directly above it). The majority of tsunamis are triggered by earthquake rupture along subduction zones. The 1964 Alaska earthquake generated a tsunami that caused widespread damage along the coastline of Northern California. Paleoseismic investigations have also shown that tsunamis resulting from earthquakes on the subduction zone beneath Japan and the Cascadia subduction zone in the Pacific Northwest have also inundated the Pacific coast states (Atwater et al. 1995). A seiche is a periodic oscillation or "sloshing" of water in an enclosed basin such as San Francisco Bay. The period of oscillation can range from minutes to hours. Erosion Erosion is the gradual wearing away of land by water, wind, and general weather conditions. As with weathering, erosion is a natural geological process, but more rapid soil erosion results from poor land use practices, leading to the loss of fertile topsoil and to the silting of dams, lakes, rivers, and harbors. Wind erosion can occur on any soil whose surface is dry, unprotected by vegetation (to bind it at root level and shelter the surface), and consists of light particles. The mechanisms include straightforward picking up of dust and soil particles by the airflow and the dislodging or abrasion of surface material by the impact of particles already airborne. Three classes of erosion by water exist: (1) splash erosion occurs when raindrops strike bare soil, causing it to splash as mud, to flow into spaces in the soil, and to turn the upper layer of soil into a structureless, compacted mass that dries with a hard, largely impermeable crust; (2) surface flow occurs when soil is removed with surface runoff during heavy rain; and (3) channelized flow occurs when a flowing mixture of water and soil cuts a channel, which is then deepened by further scouring. 3.1.2.3 Soils The formation of a soil profile is influenced by five primary factors: climate, topography, soil parent material, biotic influence, and time. Because a wide variation may exist between these factors, even within a relatively small area, any regionwide or statewide summary must be somewhat imprecise and inclusive. The soils descriptions in the following sections are intended to be general in nature and follow the taxonomic terminology used by the U.S. Department of Agriculture. Figure 3.1-2 is a map of California divided into ecological subregions that reflect differences due primarily to variations in climate, topographic relief, and the geographic relationships between subregions and the Pacific Ocean. The following text is modified from Ecological Subregions of California: Section and Subsection Descriptions (Miles and Goudey 1997). Central California Coast This section consists of mountains, hills, valleys, and plains in the southern Coast Ranges of California. It is close enough to the Pacific Ocean for the climate to be modified greatly by marine influence. This section is within the Coast Ranges Province (Figure 3.1-1). The bedrock is primarily Cenozoic marine and nonmarine sedimentary rocks and Mesozoic granitic and ultramafic rocks mantled by alluvial and colluvial deposits. Soils are Alfisols, Entisols, Inceptisols, Mollisols, Ultisols, and Vertisols. Table 3.1-3 provides a brief description of soil taxonomic terminology. Soil temperature regimes are isomesic, mesic, or thermic; soil moisture regimes are xeric, udic, ustic, or aquic. Southern California Coast This section contains mountains, hills, valleys, and plains of the Transverse Ranges and of the Peninsular Ranges that are close enough to the Pacific Ocean for the climate to be modified greatly by marine influence. This section is within both the Transverse and Peninsular Ranges Provinces. The landscape consists of narrow ranges and broad fault blocks, alluviated lowlands, and coastal terraces. Cenozoic marine and nonmarine sedimentary rocks and alluvial deposits underlie the soils of this section. Soils are Alfisols, Entisols, Inceptisols, Mollisols, Ultisols, and Vertisols in combination with thermic, isothermic, or mesic soil temperature regimes and xeric, ustic, or aquic soil moisture regimes. Great Valley This section contains the alluvial plains of Sacramento and San Joaquin valleys. Summers are hot and dry and winters are mild. Oceanic influence on climate is slight in the middle of the Great Valley, which receives some marine air through Carquinez Strait, but little at the north and south ends of the valley. This section coincides with the low fluviatile plain of the Great Valley Province. Holocene and Pleistocene alluvial deposits cover nearly all of this ecological section. Soil orders found here are Alfisols, Aridisols, Entisols, Histisols, Inceptisols, Mollisols, and Vertisols. The soil temperature regime is thermic, and xeric, aquic, or aridic soil moisture regimes are common, depending on soil profile location. Northern California Coast This section encompasses mountains, hills, valleys, and plains in the Northern California Coast Ranges and small parts of the Klamath Mountains that are close enough to the Pacific Ocean for the climate to be modified greatly by marine influence. Summers are characterized by fog, cool temperatures, and higher humidity than found inland. Like the Central California Coast section described above, the Northern California Coast lies within the Coast Ranges geomorphic province typified by somewhat linear ranges, with rounded crests of subequal height separated by parallel valleys. Late Mesozoic rocks of the Franciscan Formation and shelf and slope sedimentary rocks have been folded, faulted, and metamorphosed in this section. Soils on the north coast are Alfisols, Inceptisols, Mollisols, Spodosols (Pygmy Forest), Ultisols, and Vertisols. Typically, soil temperature regimes are isomesic, mesic or thermic, and soil moisture regimes are aquic, udic, ustic, or xeric (moist end of range). Klamath Mountains The Klamath Mountains section is between the Southern Cascade Mountains and the Coast Ranges mountains. Its southern limit is the northern end of the Great Valley. This section coincides with the Klamath Mountains geomorphic province, an uplifted and dissected peneplain formed on strong rocks with extensive monadnock ranges. Mountains in this section have accordant or subequal summits and are generally, but not consistently, aligned north to south. Paleozoic sedimentary and volcanic rocks, and Mesozoic ultramafic, granitic, sedimentary, and volcanic rocks are found here. Soils are Alfisols, Entisols, Inceptisols, Mollisols, and Ultisols in combination with thermic, mesic, frigid, or cryic soil temperature regimes and xeric or aquic soil moisture regimes. Northern California Coast Ranges This section is the interior part of the Northern California Coast Ranges mountains, north of Carquinez Strait. Marine air modifies winter and summer temperatures, but the section is far enough inland from the coast that oceanic effects are greatly diminished and less prevalent than in the Northern California Coast section. This section lies within the Coast Ranges geomorphic province of parallel ranges, folded, faulted, and metamorphosed strata. Late Mesozoic rocks of the Franciscan Formation, Mesozic ultramafic rocks, and Cenozoic volcanic rocks are the common bedrock lithologies in this section. Soil orders found in this ecoregion are Alfisols, Entisols, Inceptisols, and Mollisols in combination with frigid, mesic, or thermic soil temperature regimes and a xeric soil moisture regime. Northern California Interior Coast Ranges This section is the southeastern edge of the Northern California Coast Ranges mountains (south of Cache Creek) and hills and terraces along the west side and north end of Sacramento Valley. Like the above section, this section is part of the Coast Ranges geomorphic province. Bedrock in the Northern California Interior Coast Ranges is late Mesozoic marine shelf and slope sedimentary deposits. Soils are Alfisols, Inceptisols, Mollisols, and Vertisols in combination with thermic soil temperature regime and xeric soil moisture regime. Southern Cascades This section comprises the southern Cascade Ranges. The crest of the mountain chain is aligned toward the north-northwest between the Sierra Nevada and Mount Shasta and toward the north from Mount Shasta northward. The landscape in this section is dominated by volcanic mountains that are variously eroded. This section lies completely within the Cascade Ranges geomorphic province of California. Rocks in this section are Cenozoic volcanic rocks and alluvial deposits of these same rocks. Numerous soil orders have been described in this section: Alfisols, Andisols, Aridisols, Entisols, Inceptisols, Mollisols, Ultisols, and Vertisols. The soil temperature regime is mesic, frigid, or cryic, and the soil moisture regime is xeric, aridic, or aquic. Sierra Nevada This section is the temperate to very cold parts of the Sierra Nevada, which is a north-northwest- trending tilt-block mountain range with a steep eastern side and gentler sloping western side. This ecoregion lies within the Sierra Nevada Range geomorphic province. Mesozoic granitic and ultramafic rocks, Paleozoic and Mesozoic strongly metamorphosed sedimentary and volcanic rocks, and Cenozoic volcanic rocks are present in this range. Locally glacial and fluvial deposits are present as well. Soils are Alfisols, Andisols, Aridisols, Entisols, Inceptisols, Mollisols, and Ultisols in combination with mesic, frigid, or cryic soil temperature regimes and xeric, udic, aridic, or aquic soil moisture regimes. Sierra Nevada Foothills This section comprises the foothills on the western side of the Sierra Nevada, and the southwestern end of the Cascade Ranges, adjacent to the Great Valley. Summers are hot and dry and winters are mild. This ecoregion lies within the Sierra Nevada Range geomorphic province. Mesozoic sedimentary, granitic, volcanic, and ultramafic bedrock is present. Soil orders f