All Appendices for Informal Biological Evaluation for Mosquito Source
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Section 3.4 Biological Resources 3.4- Biological Resources
SECTION 3.4 BIOLOGICAL RESOURCES 3.4- BIOLOGICAL RESOURCES 3.4 BIOLOGICAL RESOURCES This section discusses the existing sensitive biological resources of the San Francisco Bay Estuary (the Estuary) that could be affected by project-related construction and locally increased levels of boating use, identifies potential impacts to those resources, and recommends mitigation strategies to reduce or eliminate those impacts. The Initial Study for this project identified potentially significant impacts on shorebirds and rafting waterbirds, marine mammals (harbor seals), and wetlands habitats and species. The potential for spread of invasive species also was identified as a possible impact. 3.4.1 BIOLOGICAL RESOURCES SETTING HABITATS WITHIN AND AROUND SAN FRANCISCO ESTUARY The vegetation and wildlife of bayland environments varies among geographic subregions in the bay (Figure 3.4-1), and also with the predominant land uses: urban (commercial, residential, industrial/port), urban/wildland interface, rural, and agricultural. For the purposes of discussion of biological resources, the Estuary is divided into Suisun Bay, San Pablo Bay, Central San Francisco Bay, and South San Francisco Bay (See Figure 3.4-2). The general landscape structure of the Estuary’s vegetation and habitats within the geographic scope of the WT is described below. URBAN SHORELINES Urban shorelines in the San Francisco Estuary are generally formed by artificial fill and structures armored with revetments, seawalls, rip-rap, pilings, and other structures. Waterways and embayments adjacent to urban shores are often dredged. With some important exceptions, tidal wetland vegetation and habitats adjacent to urban shores are often formed on steep slopes, and are relatively recently formed (historic infilled sediment) in narrow strips. -
Don Edwards San Francisco Bay National Wildlife Refuge 2020
Don Edwards San Francisco Bay National Wildlife Refuge U.S. Fish and Wildlife Service 2020 -2021 Waterfowl Hunting Regulations These Regulations along with maps and directions are available at: http://www.fws.gov/refuge/Don_Edwards_San_Francisco_Bay/hunting.html General Information The Don Edwards San Francisco Bay National Wildlife Refuge (refuge) contains approximately 10,580 acres of tidal areas and salt ponds that are open to waterfowl hunting (Map 1). Season opening and closing dates are determined by the State of California. Check the California Waterfowl Regulations (https://www.wildlife.ca.gov/Hunting) each season for these dates. Hunters must comply with all State and Federal regulations including regulations listed under 50 CFR 32.24, and the refuge-specific regulations described below. Permit Requirements Hunters 18 years of age or older will need to have: 1) a valid California hunting license; 2) a valid, signed Federal Duck Stamp; 3) a California Duck Validation; 4) a Harvest Information Program (HIP) Validation; and 5) identification that includes a photograph (e.g., driver’s license). Junior and Youth hunters need the following: Junior/Youth Hunter Summary 15 yrs old or 16-17 yrs old w/ Jr 18 yrs old w/ Jr under (Youth) license (Junior) license (Junior) Participate in post-season youth hunt? Yes Yes No Needs a California hunting license? Yes Yes Yes Needs a HIP Validation? Yes Yes Yes Needs a Federal Duck Stamp? No Yes Yes Needs a State Duck Stamp (validation)? No No No Needs an adult accompanying them on regular hunt days? Yes No No Needs an adult accompanying them for youth hunt days? Yes Yes Yes It is required that all hunters possess a Refuge Waterfowl Hunting Permit when hunting in the Alviso Ponds. -
Goga Wrfr.Pdf
The National Park Service Water Resources Division is responsible for providing water resources management policy and guidelines, planning, technical assistance, training, and operational support to units of the National Park System. Program areas include water rights, water resources planning, regulatory guidance and review, hydrology, water quality, watershed management, watershed studies, and aquatic ecology. Technical Reports The National Park Service disseminates the results of biological, physical, and social research through the Natural Resources Technical Report Series. Natural resources inventories and monitoring activities, scientific literature reviews, bibliographies, and proceedings of technical workshops and conferences are also disseminated through this series. Mention of trade names or commercial products does not constitute endorsement or recommendation for use by the National Park Service. Copies of this report are available from the following: National Park Service (970) 225-3500 Water Resources Division 1201 Oak Ridge Drive, Suite 250 Fort Collins, CO 80525 National Park Service (303) 969-2130 Technical Information Center Denver Service Center P.O. Box 25287 Denver, CO 80225-0287 Cover photos: Top: Golden Gate Bridge, Don Weeks Middle: Rodeo Lagoon, Joel Wagner Bottom: Crissy Field, Joel Wagner ii CONTENTS Contents, iii List of Figures, iv Executive Summary, 1 Introduction, 7 Water Resources Planning, 9 Location and Demography, 11 Description of Natural Resources, 12 Climate, 12 Physiography, 12 Geology, 13 Soils, 13 -
Attachment Iii: Baseline Status and Cumulative Effects for the San Francisco Bay Listed Species
ATTACHMENT III: BASELINE STATUS AND CUMULATIVE EFFECTS FOR THE SAN FRANCISCO BAY LISTED SPECIES 1 TABLE OF CONTENTS 1: ALAMEDAWHIPSNAKE ............................................................................................ 6 1.1 CUMULATIVE EFFECTS ...................................................................................... 6 1.2 ENVIRONMENTAL BASELINE........................................................................... 6 1.2.1 Factors affecting species within the action area ............................................... 6 1.2.1.1 Urban development .................................................................................... 7 1.2.1.2 Fire suppression ......................................................................................... 9 1.2.1.3 Predation .................................................................................................... 9 1.2.1.4 Grazing practices ..................................................................................... 10 1.2.1.5 Non-native species ................................................................................... 10 1.2.2 Baseline Status ................................................................................................ 11 1.3 REFERENCES ...................................................................................................... 13 2: BAY CHECKERSPOT BUTTERFLY ....................................................................... 14 2.1 CUMULATIVE EFFECTS .................................................................................. -
Bothin Marsh 46
EMERGENT ECOLOGIES OF THE BAY EDGE ADAPTATION TO CLIMATE CHANGE AND SEA LEVEL RISE CMG Summer Internship 2019 TABLE OF CONTENTS Preface Research Introduction 2 Approach 2 What’s Out There Regional Map 6 Site Visits ` 9 Salt Marsh Section 11 Plant Community Profiles 13 What’s Changing AUTHORS Impacts of Sea Level Rise 24 Sarah Fitzgerald Marsh Migration Process 26 Jeff Milla Yutong Wu PROJECT TEAM What We Can Do Lauren Bergenholtz Ilia Savin Tactical Matrix 29 Julia Price Site Scale Analysis: Treasure Island 34 Nico Wright Site Scale Analysis: Bothin Marsh 46 This publication financed initiated, guided, and published under the direction of CMG Landscape Architecture. Conclusion Closing Statements 58 Unless specifically referenced all photographs and Acknowledgments 60 graphic work by authors. Bibliography 62 San Francisco, 2019. Cover photo: Pump station fronting Shorebird Marsh. Corte Madera, CA RESEARCH INTRODUCTION BREADTH As human-induced climate change accelerates and impacts regional map coastal ecologies, designers must anticipate fast-changing conditions, while design must adapt to and mitigate the effects of climate change. With this task in mind, this research project investigates the needs of existing plant communities in the San plant communities Francisco Bay, explores how ecological dynamics are changing, of the Bay Edge and ultimately proposes a toolkit of tactics that designers can use to inform site designs. DEPTH landscape tactics matrix two case studies: Treasure Island Bothin Marsh APPROACH Working across scales, we began our research with a broad suggesting design adaptations for Treasure Island and Bothin survey of the Bay’s ecological history and current habitat Marsh. -
Biotic Evaluation Dias and Hobbs City of Fremont
BIOTIC EVALUATION DIAS AND HOBBS CITY OF FREMONT, ALAMEDA COUNTY, CALIFORNIA By: LIVE OAK ASSOCIATES, INC. Rick Hopkins, Ph.D., Principal, Senior Ecologist Pamela Peterson, Sr. Project Manager, Plant/Wetland Ecologist Katrina Krakow, M.S., Project Manager, Staff Ecologist For: Robson Homes Attn: Jake Lavin 2185 The Alameda, Suite 150 San Jose, CA 95126 April 3, 2014 Project No. 1821-01 TABLE OF CONTENTS 1.0 INTRODUCTION ....................................................................................................... 4 2.0 EXISTING CONDITIONS .......................................................................................... 8 2.1 BIOTIC HABITATS/LAND USES .................................................................................................................... 10 2.1.1 PASTURE ...................................................................................................................................................... 10 2.1.2 RUDERAL FIELD ........................................................................................................................................ 13 2.1.3 DEVELOPED ................................................................................................................................................ 14 2.1.3 EUCALYPTUS GROVE ............................................................................................................................... 15 2.2 MOVEMENT CORRIDORS ............................................................................................................................ -
Distribution and Abundance
DISTRIBUTION AND ABUNDANCE IN RELATION TO HABITAT AND LANDSCAPE FEATURES AND NEST SITE CHARACTERISTICS OF CALIFORNIA BLACK RAIL (Laterallus jamaicensis coturniculus) IN THE SAN FRANCISCO BAY ESTUARY FINAL REPORT To the U.S. Fish & Wildlife Service March 2002 Hildie Spautz* and Nadav Nur, PhD Point Reyes Bird Observatory 4990 Shoreline Highway Stinson Beach, CA 94970 *corresponding author contact: [email protected] PRBO Black Rail Report to FWS 2 EXECUTIVE SUMMARY We conducted surveys for California Black Rails (Laterallus jamaicensis coturniculus) at 34 tidal salt marshes in San Pablo Bay, Suisun Bay, northern San Francisco Bay and western Marin County in 2000 and 2001 with the aims of: 1) providing the best current information on distribution and abundance of Black Rails, marsh by marsh, and total population size per bay region, 2) identifying vegetation, habitat, and landscape features that predict the presence of black rails, and 3) summarizing information on nesting and nest site characteristics. Abundance indices were higher at 8 marshes than in 1996 and earlier surveys, and lower in 4 others; with two showing no overall change. Of 13 marshes surveyed for the first time, Black Rails were detected at 7 sites. The absolute density calculated using the program DISTANCE averaged 2.63 (± 1.05 [S.E.]) birds/ha in San Pablo Bay and 3.44 birds/ha (± 0.73) in Suisun Bay. At each survey point we collected information on vegetation cover and structure, and calculated landscape metrics using ArcView GIS. We analyzed Black Rail presence or absence by first analyzing differences among marshes, and then by analyzing factors that influence detection of rails at each survey station. -
San Francisco Bay Joint Venture
The San Francisco Bay Joint Venture Management Board Bay Area Audubon Council Bay Area Open Space Council Bay Conservation and Development Commission The Bay Institute The San Francisco Bay Joint Venture Bay Planning Coalition California State Coastal Conservancy Celebrating years of partnerships protecting wetlands and wildlife California Department of Fish and Game California Resources Agency 15 Citizens Committee to Complete the Refuge Contra Costa Mosquito and Vector Control District Ducks Unlimited National Audubon Society National Fish and Wildlife Foundation NOAA National Marine Fisheries Service Natural Resources Conservation Service Pacific Gas and Electric Company PRBO Conservation Science SF Bay Regional Water Quality Control Board San Francisco Estuary Partnership Save the Bay Sierra Club U.S. Army Corps of Engineers U.S. Environmental Protection Agency U.S. Fish and Wildlife Service U.S. Geological Survey Wildlife Conservation Board 735B Center Boulevard, Fairfax, CA 94930 415-259-0334 www.sfbayjv.org www.yourwetlands.org The San Francisco Bay Area is breathtaking! As Chair of the San Francisco Bay Joint Venture, I would like to personally thank our partners It’s no wonder so many of us live here – 7.15 million of us, according to the 2010 census. Each one of us has our for their ongoing support of our critical mission and goals in honor of our 15 year anniversary. own mental image of “the Bay Area.” For some it may be the place where the Pacific Ocean flows beneath the This retrospective is a testament to the significant achievements we’ve made together. I look Golden Gate Bridge, for others it might be somewhere along the East Bay Regional Parks shoreline, or from one forward to the next 15 years of even bigger wins for wetland habitat. -
Controlling Algerian Sea Lavender in San Francisco Estuary Tidal Marshes
Invasive Limonium Treatment in the San Francisco Estuary DREW KERR TREATMENT PROGRAM MANAGER FOR THE INVASIVE SPARTINA PROJECT CALIFORNIA INVASIVE PLANT COUNCIL SYMPOSIUM OCTOBER 25, 2017 Limonium duriusculum (LIDU; European sea lavender) in the San Francisco Estuary • First discovered in the San Francisco Estuary in 2007 (Strawberry Marsh/Richardson Bay in Marin County) • Leaves 30-40 mm x 5-9 mm (LxW) • Basal rosette that produces branching inflorescences (30-50 cm) • Flowering spikelets with purple From Archbald & Boyer 2014 corollas (petals) Limonium ramosissimum (LIRA; Algerian sea lavender) in the San Francisco Estuary • First discovered in the San Francisco Estuary in 2007 (Sanchez Marsh in San Mateo County, just south of SFO) • Leaves 80-100 mm x 15-20 mm (LxW) • Basal rosette that produces branching inflorescences (30- 50 cm) • Flowering spikelets From Archbald & Boyer 2014 with purple corollas (petals) Limonium species in San Francisco Estuary Non-native Limonium ramosissimum (left) & Native Limonium californicum (right) Ideal Marsh (May 2017) with both plants bolting Limonium species in San Francisco Estuary Native Limonium californicum playing well with other marsh plants at Ideal Marsh Limonium species in San Francisco Estuary Non-native Limonium ramosissimum forming a monoculture at Ideal Marsh This plant may very well have allelopathic properties, to so effectively exclude all other plants Research into Invasive Limonium Katharyn Boyer’s Lab at San Francisco State University Two students studied invasive Limonium for their -
Of 8 COASTAL CONSERVANCY Staff Recommendation October 21, 2010 NAPA RIVER
COASTAL CONSERVANCY Staff Recommendation October 21, 2010 NAPA RIVER SALT MARSH RESTORATION PROJECT Project No. 01-022-01 Project Manager: Betsy Wilson RECOMMENDED ACTION: Authorization to disburse up to $75,000 to support the design, permitting, and other work associated with implementation of the Napa River Salt Marsh Restoration Project. LOCATION: The northern edge of San Pablo Bay, bounded in the east by the Napa River and the west by Sonoma Creek, in Napa County (Exhibit 1) PROGRAM CATEGORY: San Francisco Bay Area Conservancy EXHIBITS Exhibit 1: Project Location and Site Map RESOLUTION AND FINDINGS: Staff recommends that the State Coastal Conservancy adopt the following resolution pursuant to Sections 31160-31165 of the Public Resources Code: “The State Coastal Conservancy hereby authorizes disbursement of up to seventy-five thousand dollars ($75,000) to support the design, permitting, and other work associated with implementation of the Napa River Salt Marsh Restoration Project.” Staff further recommends that the Conservancy adopt the following findings: “Based on the accompanying staff report and attached exhibits, the State Coastal Conservancy hereby finds that: 1. The proposed project is consistent with the Conservancy’s current Project Selection Criteria and Guidelines. 2. The proposed project is consistent with Chapter 4.5 of Division 21 of the California Public Resources Code (Sections 31160-31165) regarding the Conservancy’s mandate to address the resource and recreation goals of the San Francisco Bay Area.” Page 1 of 8 NAPA RIVER SALT MARSH RESTORATION PROJECT PROJECT SUMMARY: The Napa River Salt Marsh Restoration Project involves the restoration of nearly 10,000 acres of former commercial salt ponds to a mix of tidal marsh and managed ponds, as well as delivery of recycled water to aid in the removal of bittern (a byproduct of salt production) that is stored in one of the ponds. -
Economic Evaluation of Sea-Level Rise Adaptation Strongly Influenced By
Economic evaluation of sea-level rise adaptation strongly influenced by hydrodynamic feedbacks Michelle A. Hummela,1 , Robert Griffinb,c , Katie Arkemab,d, and Anne D. Guerryb,d aDepartment of Civil Engineering, University of Texas at Arlington, Arlington, TX 76019; bThe Natural Capital Project, Stanford University, Stanford, CA 94305; cSchool for Marine Science and Technology, University of Massachusetts Dartmouth, Dartmouth, MA 02747; and dSchool of Environmental and Forest Sciences, University of Washington, Seattle, WA 98195 Edited by Peter H. Gleick, Pacific Institute for Studies in Development, Environment, and Security, Oakland, CA, and approved May 30, 2021 (received for review December 17, 2020) Coastal communities rely on levees and seawalls as critical pro- culture carried down the Mississippi, widespread acid rain in the tection against sea-level rise; in the United States alone, $300 northeastern United States originating from power plants in the billion in shoreline armoring costs are forecast by 2100. However, Midwest that led to revisions of the Clean Air Act in 1990, and despite the local flood risk reduction benefits, these structures the visual impacts on adjacent property owners from the Cape can exacerbate flooding and associated damages along other Wind offshore wind farm near Nantucket, MA, that led to its parts of the shoreline—particularly in coastal bays and estuaries, eventual demise after more than a decade of litigation. Spatial where nearly 500 million people globally are at risk from sea- externalities are also common and varied in the context of shore- level rise. The magnitude and spatial distribution of the economic line protection and management. In river systems, it has long impact of this dynamic, however, are poorly understood. -
Species and Community Profiles to Six Clutches of Eggs, Totaling About 861 Eggs During California Vernal Pool Tadpole Her Lifetime (Ahl 1991)
3 Invertebrates their effects on this species are currently being investi- Franciscan Brine Shrimp gated (Maiss and Harding-Smith 1992). Artemia franciscana Kellogg Reproduction, Growth, and Development Invertebrates Brita C. Larsson Artemia franciscana has two types of reproduction, ovovi- General Information viparous and oviparous. In ovoviviparous reproduction, the fertilized eggs in a female can develop into free-swim- The Franciscan brine shrimp, Artemia franciscana (for- ming nauplii, which are set free by the mother. In ovipa- merly salina) (Bowen et al. 1985, Bowen and Sterling rous reproduction, however, the eggs, when reaching the 1978, Barigozzi 1974), is a small crustacean found in gastrula stage, become surrounded by a thick shell and highly saline ponds, lakes or sloughs that belong to the are deposited as cysts, which are in diapause (Sorgeloos order Anostraca (Eng et al. 1990, Pennak 1989). They 1980). In the Bay area, cysts production is generally are characterized by stalked compound eyes, an elongate highest during the fall and winter, when conditions for body, and no carapace. They have 11 pairs of swimming Artemia development are less favorable. The cysts may legs and the second antennae are uniramous, greatly en- persist for decades in a suspended state. Under natural larged and used as a clasping organ in males. The aver- conditions, the lifespan of Artemia is from 50 to 70 days. age length is 10 mm (Pennak 1989). Brine shrimp com- In the lab, females produced an average of 10 broods, monly swim with their ventral side upward. A. franciscana but the average under natural conditions may be closer lives in hypersaline water (70 to 200 ppt) (Maiss and to 3-4 broods, although this has not been confirmed.