Johnson 2017 SFEWS.Pdf

Total Page:16

File Type:pdf, Size:1020Kb

Johnson 2017 SFEWS.Pdf Peer Reviewed Title: Science Advancements Key to Increasing Management Value of Life Stage Monitoring Networks for Endangered Sacramento River Winter-Run Chinook Salmon in California Journal Issue: San Francisco Estuary and Watershed Science, 15(3) Author: Johnson, Rachel C., National Marine Fisheries Service, National Oceanic and Atmospheric Administration Windell, Sean, California Sea Grant Fellowship, Delta Stewardship Council Brandes, Patricia L., U.S. Fish and Wildlife Service Conrad, J. Louise, California Department of Water Resources Ferguson, John, Anchor QEA Goertler, Pascale A. L., California Department of Water Resources Harvey, Brett N., California Department of Water Resources Heublein, Joseph, National Marine Fisheries Service, National Oceanic and Atmospheric Administration Israel, Joshua A., U.S. Bureau of Reclamation Kratville, Daniel W., California Department of Fish and Wildlife Kirsch, Joseph E., U.S. Fish and Wildlife Service Perry, Russell W., U.S Geological Survey Pisciooto, Joseph, California Department of Fish and Wildlife Poytress, William R., U.S. Fish and Wildlife Service Reece, Kevin, U.S. Fish and Wildlife Service Swart, Brycen G., National Marine Fisheries Service, National Oceanic and Atmospheric Administration Publication Date: 2017 Permalink: http://escholarship.org/uc/item/6751j957 Acknowledgements: We thank Doug Killam, Colin Purdy, Arnold Ammann, Mike O’Farrell, and Noble Hendrix for contributing relevant information and thoughtful presentations for our synthesis effort. We thank members of the Interagency Ecological Program (IEP) Winter-Run Project Work Team and Science Management Team for reviews of early drafts. Discussions and comments from Steve Lindley, Will Satterthwaite, Ted Sommer, Vanessa Tobias, Alison Collins, Lauren Yamane, Brian Pyper, Peter Klimley, and an anonymous reviewer greatly improved the manuscript. We thank Charleen Gavette (National Marine Fisheries Service) for creating Figure 1, which displays existing eScholarship provides open access, scholarly publishing services to the University of California and delivers a dynamic research platform to scholars worldwide. monitoring and our summary evaluation. We greatly appreciate the support of the IEP agency directors in initiating this effort and commitment toward improving core monitoring to help manage this valuable resource. Keywords: Chinook Salmon, monitoring, conceptual models, life stage survival, migration, diversity Local Identifier(s): jmie_sfews_36508 Abstract: doi: https://doi.org/10.15447/sfews.2017v15iss3art1 A robust monitoring network that provides quantitative information about the status of imperiled species at key life stages and geographic locations over time is fundamental for sustainable management of fisheries resources. For anadromous species, management actions in one geographic domain can substantially affect abundance of subsequent life stages that span broad geographic regions. Quantitative metrics (e.g., abundance, movement, survival, life history diversity, and condition) at multiple life stages are needed to inform how management actions (e.g., hatcheries, harvest, hydrology, and habitat restoration) influence salmon population dynamics. The existing monitoring network for endangered Sacramento River winter-run Chinook Salmon (SRWRC, Oncorhynchus tshawytscha) in California’s Central Valley was compared to conceptual models developed for each life stage and geographic region of the life cycle to identify relevant SRWRC metrics. We concluded that the current monitoring network was insufficient to diagnose when (life stage) and where (geographic domain) chronic or episodic reductions in SRWRC cohorts occur, precluding within- and among-year comparisons. The strongest quantitative data exist in the Upper Sacramento River, where abundance estimates are generated for adult spawners and emigrating juveniles. However, once SRWRC leave the upper river, our knowledge of their identity, abundance, and condition diminishes, despite the juvenile monitoring enterprise. We identified six system-wide recommended actions to strengthen the value of data generated from the existing monitoring network to assess resource management actions: (1) incorporate genetic run identification; (2) develop juvenile abundance estimates; (3) collect data for life history diversity metrics at multiple life stages; (4) expand and enhance real-time fish survival and movement monitoring; (5) collect fish condition data; and (6) provide timely public access to monitoring data in open data formats. To illustrate how updated technologies can enhance the existing monitoring to provide quantitative data on SRWRC, we provide examples of how each recommendation can address specific management issues Copyright Information: Copyright 2017 by the article author(s). This work is made available under the terms of the Creative Commons Attribution4.0 license, http://creativecommons.org/licenses/by/4.0/ eScholarship provides open access, scholarly publishing services to the University of California and delivers a dynamic research platform to scholars worldwide. SEPTEMBER 2017 RESEARCH Science Advancements Key to Increasing Management Value of Life Stage Monitoring Networks for Endangered Sacramento River Winter-Run Chinook Salmon in California Rachel C. Johnson1, 2, *, Sean Windell3, Patricia L. Brandes4, J. Louise Conrad5, John Ferguson6, Pascale A. L. Goertler5, Brett N. Harvey5, Joseph Heublein7, Joshua A. Israel8, Daniel W. Kratville9, Joseph E. Kirsch4, Russell W. Perry10, Joseph Pisciotto9, William R. Poytress11, Kevin Reece5, and Brycen G. Swart7 Volume 15, Issue 3 | Article 1 ABSTRACT https://doi.org/10.15447/sfews.2017v15iss3art1 A robust monitoring network that provides * Corresponding author: [email protected] quantitative information about the status of imperiled 1 Fisheries Ecology Division, Southwest Fisheries Science Center, species at key life stages and geographic locations National Marine Fisheries Service, National Oceanic and over time is fundamental for sustainable management Atmospheric Administration, Santa Cruz, CA 95060 USA of fisheries resources. For anadromous species, 2 Center for Watershed Sciences, University of California Davis management actions in one geographic domain Davis, CA 95616 USA can substantially affect abundance of subsequent 3 California Sea Grant Fellowship, Delta Stewardship Council Sacramento, CA 95814 USA life stages that span broad geographic regions. 4 U.S. Fish and Wildlife Service Quantitative metrics (e.g., abundance, movement, Lodi, CA 95240 USA survival, life history diversity, and condition) at 5 California Department of Water Resources multiple life stages are needed to inform how West Sacramento, CA 95691 USA management actions (e.g., hatcheries, harvest, 6 Anchor QEA, Seattle, WA 98101 USA hydrology, and habitat restoration) influence salmon 7 California Central Valley Office, West Coast Region, population dynamics. The existing monitoring National Marine Fisheries Service, National Oceanic and Atmospheric Administration, Sacramento, CA 95814 USA network for endangered Sacramento River winter- 8 Bay-Delta Office, U.S. Bureau of Reclamation run Chinook Salmon (SRWRC, Oncorhynchus Sacramento, CA 95825 USA tshawytscha) in California’s Central Valley was 9 Fisheries Branch, California Department of Fish and Wildlife compared to conceptual models developed for each Sacramento, CA 95811 USA life stage and geographic region of the life cycle to 10 Western Fisheries Research Center, U.S. Geological Survey identify relevant SRWRC metrics. We concluded that Cook, WA 98605 USA the current monitoring network was insufficient to 11 Red Bluff Fish and Wildlife Office, U.S. Fish and Wildlife Service Red Bluff, CA 96080 USA diagnose when (life stage) and where (geographic domain) chronic or episodic reductions in SRWRC cohorts occur, precluding within- and among-year comparisons. The strongest quantitative data exist in the Upper Sacramento River, where abundance estimates are generated for adult spawners and emigrating juveniles. However, once SRWRC leave the upper river, our knowledge of their identity, SAN FRANCISCO ESTUARY & WATERSHED SCIENCE VOLUME 15, ISSUE 3, ARTICLE 1 abundance, and condition diminishes, despite the to manage flooding risk and water supply reliability, juvenile monitoring enterprise. We identified six given the extreme seasonal and annual climate system-wide recommended actions to strengthen the variation. For example, numerous water storage value of data generated from the existing monitoring facilities capture surface runoff. This reduces network to assess resource management actions: downstream flooding risk in wet years, and provides (1) incorporate genetic run identification; (2) develop reliable water supply for 25 million people and juvenile abundance estimates; (3) collect data for irrigation for millions of hectares of farmland even life history diversity metrics at multiple life stages; in years with below-average precipitation. The timing (4) expand and enhance real-time fish survival and and magnitude of flows released from the storage movement monitoring; (5) collect fish condition data; facilities is heavily regulated to meet multiple state- and (6) provide timely public access to monitoring wide objectives, including water storage and supply, data in open data formats. To illustrate how updated flood control, recreation, and fish and wildlife technologies can enhance the existing monitoring conservation. to provide quantitative data on SRWRC, we
Recommended publications
  • 0 5 10 15 20 Miles Μ and Statewide Resources Office
    Woodland RD Name RD Number Atlas Tract 2126 5 !"#$ Bacon Island 2028 !"#$80 Bethel Island BIMID Bishop Tract 2042 16 ·|}þ Bixler Tract 2121 Lovdal Boggs Tract 0404 ·|}þ113 District Sacramento River at I Street Bridge Bouldin Island 0756 80 Gaging Station )*+,- Brack Tract 2033 Bradford Island 2059 ·|}þ160 Brannan-Andrus BALMD Lovdal 50 Byron Tract 0800 Sacramento Weir District ¤£ r Cache Haas Area 2098 Y o l o ive Canal Ranch 2086 R Mather Can-Can/Greenhead 2139 Sacramento ican mer Air Force Chadbourne 2034 A Base Coney Island 2117 Port of Dead Horse Island 2111 Sacramento ¤£50 Davis !"#$80 Denverton Slough 2134 West Sacramento Drexler Tract Drexler Dutch Slough 2137 West Egbert Tract 0536 Winters Sacramento Ehrheardt Club 0813 Putah Creek ·|}þ160 ·|}þ16 Empire Tract 2029 ·|}þ84 Fabian Tract 0773 Sacramento Fay Island 2113 ·|}þ128 South Fork Putah Creek Executive Airport Frost Lake 2129 haven s Lake Green d n Glanville 1002 a l r Florin e h Glide District 0765 t S a c r a m e n t o e N Glide EBMUD Grand Island 0003 District Pocket Freeport Grizzly West 2136 Lake Intake Hastings Tract 2060 l Holland Tract 2025 Berryessa e n Holt Station 2116 n Freeport 505 h Honker Bay 2130 %&'( a g strict Elk Grove u Lisbon Di Hotchkiss Tract 0799 h lo S C Jersey Island 0830 Babe l Dixon p s i Kasson District 2085 s h a King Island 2044 S p Libby Mcneil 0369 y r !"#$5 ·|}þ99 B e !"#$80 t Liberty Island 2093 o l a Lisbon District 0307 o Clarksburg Y W l a Little Egbert Tract 2084 S o l a n o n p a r C Little Holland Tract 2120 e in e a e M Little Mandeville
    [Show full text]
  • Upper Sacramento River Summary Report August 4Th-5Th, 2008
    Upper Sacramento River Summary Report August 4th-5th, 2008 California Department of Fish and Game Heritage and Wild Trout Program Prepared by Jeff Weaver and Stephanie Mehalick Introduction: The 400-mile long Sacramento River system is the largest watershed in the state of California, encompassing the McCloud, Pit, American, and Feather Rivers, and numerous smaller tributaries, in total draining nearly one-fifth of the state. From the headwaters downstream to Shasta Lake, referred to hereafter as the Upper Sacramento, this portion of the Sacramento River is a designated Wild Trout Water (with the exception of a small section near the town of Dunsmuir, which is a stocked put-and-take fishery) (Figure 1). The California Department of Fish and Game’s (DFG) Heritage and Wild Trout Program (HWTP) monitors this fishery through voluntary angler survey boxes, creel census, direct observation snorkel surveys, electrofishing surveys, and habitat analyses. The HWTP has repeated sampling over time in a number of sections to obtain trend data related to species composition, trout densities, and habitat condition to aid in the management of this popular sport fishery. In August 2008, the HWTP resurveyed four historic direct observation survey sections on the Upper Sacramento. Methods: Surveys occurred between August 4th and 5th, 2008 with the aid of HWTP personnel and DFG volunteers. Sections were identified prior to the start of the surveys using GPS coordinates, written directions, and past experience. Fish were counted via direct observation snorkel surveys, an effective survey technique in many streams and creeks in California and the Pacific Northwest (Hankin & Reeves, 1988).
    [Show full text]
  • Sacramento River Flood Control System
    A p pp pr ro x im a te ly 5 0 M il Sacramento River le es Shasta Dam and Lake ek s rre N Operating Agency: USBR C o rt rr reek th Dam Elevation: 1,077.5 ft llde Cre 70 I E eer GrossMoulton Pool Area: 29,500 Weir ac AB D Gross Pool Capacity: 4,552,000 ac-ft Flood Control System Medford !( OREGON IDAHOIDAHO l l a a n n a a C C !( Redding kk ee PLUMAS CO a e a s rr s u C u s l l Reno s o !( ome o 99 h C AB Th C NEVADA - - ^_ a a Sacramento m TEHAMA CO aa hh ee !( TT San Francisco !( Fresno Las Vegas !( kk ee e e !( rr Bakersfield 5 CC %&'( PACIFIC oo 5 ! Los Angeles cc !( S ii OCEAN a hh c CC r a S to m San Diego on gg !( ny ii en C BB re kk ee ee k t ee Black Butte o rr C Reservoir R i dd 70 v uu Paradise AB Oroville Dam - Lake Oroville Hamilton e M Operating Agency: CA Dept of Water Resources r Dam Elevation: 922 ft City Chico Gross Pool Area: 15,800 ac Gross Pool Capacity: 3,538,000 ac-ft M & T Overflow Area Black Butte Dam and Lake Operating Agency: USACE Dam Elevation: 515 ft Tisdale Weir Gross Pool Area: 4,378 ac 3 B's GrossMoulton Pool Capacity: 136,193Weir ac-ft Overflow Area BUTTE CO New Bullards Bar Dam and Lake Operating Agency: Yuba County Water Agency Dam Elevation: 1965 ft Gross Pool Area: 4,790 ac Goose Lake Gross Pool Capacity: 966,000 ac-ft Overflow Area Lake AB149 kk ee rree Oroville Tisdale Weir C GLENN CO ee tttt uu BB 5 ! Oroville New Bullards Bar Reservoir AB49 ll Moulton Weir aa nn Constructed: 1932 Butte aa CC Length: 500 feet Thermalito Design capacity of weir: 40,000 cfs Design capacity of river d/s of weir: 110,000 cfs Afterbay Moulton Weir e ke rro he 5 C ! Basin e kk Cre 5 ! tt 5 ! u Butte Basin and Butte Sink oncu H Flow from the 3 overflow areas upstream Colusa Weir of the project levees, from Moulton Weir, Constructed: 1933 and from Colusa Weir flows into the Length: 1,650 feet Butte Basin and Sink.
    [Show full text]
  • March 2021 | City of Alameda, California
    March 2021 | City of Alameda, California DRAFT ALAMEDA GENERAL PLAN 2040 CONTENTS 04 MARCH 2021 City of Alameda, California MOBILITY ELEMENT 78 01 05 GENERAL PLAN ORGANIZATION + THEMES 6 HOUSING ELEMENT FROM 2014 02 06 LAND USE + CITY DESIGN ELEMENT 22 PARKS + OPEN SPACE ELEMENT 100 03 07 CONSERVATION + CLIMATE ACTION 54 HEALTH + SAFETY ELEMENT 116 ELEMENT MARCH 2021 DRAFT 1 ALAMEDA GENERAL PLAN 2040 ACKNOWLEDGMENTS CITY OF ALAMEDA PLANNING BOARD: PRESIDENT Alan H. Teague VICE PRESIDENT Asheshh Saheba BOARD MEMBERS Xiomara Cisneros Ronald Curtis Hanson Hom Rona Rothenberg Teresa Ruiz POLICY, PUBLIC PARTICIPATION, AND PLANNING CONSULTANTS: Amie MacPhee, AICP, Cultivate, Consulting Planner Sheffield Hale, Cultivate, Consulting Planner Candice Miller, Cultivate, Lead Graphic Designer PHOTOGRAPHY: Amie MacPhee Maurice Ramirez Alain McLaughlin MARCH 2021 DRAFT 3 ALAMEDA GENERAL PLAN 2040 FORWARD Preparation of the Alameda General Plan 2040 began in 2018 and took shape over a three-year period during which time residents, businesses, community groups, and decision-makers reviewed, revised and refined plan goals, policy statements and priorities, and associated recommended actions. In 2020, the Alameda Planning Board held four public forums to review and discuss the draft General Plan. Over 1,500 individuals provided written comments and suggestions for improvements to the draft Plan through the General Plan update website. General Plan 2040 also benefited from recommendations and suggestions from: ≠ Commission on People with Disabilities ≠ Golden
    [Show full text]
  • UC Davis San Francisco Estuary and Watershed Science
    UC Davis San Francisco Estuary and Watershed Science Title A Note on Delta Outflow Permalink https://escholarship.org/uc/item/89k7b61m Journal San Francisco Estuary and Watershed Science, 14(3) ISSN 1546-2366 Author Monismith, Stephen G. Publication Date 2016 DOI https://doi.org/10.15447/sfews.2016v14iss3art3 License https://creativecommons.org/licenses/by/4.0/ 4.0 Peer reviewed eScholarship.org Powered by the California Digital Library University of California OCTOBER 2016 SPECIAL ISSUE: THE STATE OF BAY–DELTA SCIENCE 2016, PART 2 A Note on Delta Outflow Stephen G. Monismith1 Volume 14, Issue 3 | Article 3 KEY WORDS doi: http://dx.doi.org/10.15447/sfews.2016v14iss3art3 1 Department of Civil and Environmental Engineering Sacramento–San Joaquin Delta, San Francisco Bay. Stanford University Suisun Bay, Suisun Marsh, Delta outflow, Dayflow, Stanford, CA 94305 USA tides, salinity, wind stress, hydrodynamics [email protected] INTRODUCTION ABSTRACT The 2013–2015 drought, which has seen California’s water supply storage brought down to historic lows, Outflow from the Sacramento–San Joaquin Delta has focused attention on the management of the flow is a key parameter used in the management of the of water from the Sacramento–San Joaquin Delta San Francisco Bay–Delta system. At present we can (Delta) into San Francisco Bay. This “Delta Outflow” estimate this by assuming a steady state balance is used to maintain desired salinities in Suisun Bay of inflows and outflows (Dayflow) or by direct and Suisun Marsh as well as to keep salinities in the measurement. In this paper, I explore differences Delta sufficiently low to maintain water quality for between observed sub-tidal variations in measured drinking and to irrigate Delta farmlands.
    [Show full text]
  • A Century of Delta Salt Water Barriers
    A Century of Salt Water Barriers in the Delta By Tim Stroshane Policy Analyst Restore the Delta June 5, 2015 edition Since the late 19th century, California’s basic plan for water resource development has been to export water from the Sacramento River and the Delta to the San Joaquin Valley and southern California. Unfortunately, this basic plan ignores the reality that the Delta is the very definition of an estuary: it is where fresh water from the Central Valley’s rivers meets salt water from tidal flow to the Delta from San Francisco Bay. Productive ecosystems have thrived in the Delta for millenia prior to California statehood. But for nearly a century now, engineers and others have frequently referred to the Delta as posing a “salt menace,” a “salinity problem” with just two solutions: either maintain a predetermined stream flow from the Delta to Suisun Bay to hydraulically wall out the tide, or use physical barriers to separate saline from fresh water into the Delta. While readily admitting that the “salt menace” results from reduced inflows from the Delta’s major tributary rivers, the state of California uses salt water barriers as a technological fix to address the symptoms of the salinity problem, rather than the root causes. Given complex Delta geography, these two main solutions led to many proposals to dam up parts of San Francisco Bay, Carquinez Strait, or the waterway between Chipps Island in eastern Suisun Bay and the City of Antioch, or to use large amounts of water—referred to as “carriage water”— to hold the tide literally at bay.
    [Show full text]
  • California Regional Water Quality Control Board Central Valley Region Karl E
    California Regional Water Quality Control Board Central Valley Region Karl E. Longley, ScD, P.E., Chair Linda S. Adams Arnold 11020 Sun Center Drive #200, Rancho Cordova, California 95670-6114 Secretary for Phone (916) 464-3291 • FAX (916) 464-4645 Schwarzenegger Environmental http://www.waterboards.ca.gov/centralvalley Governor Protection 18 August 2008 See attached distribution list DELTA REGIONAL MONITORING PROGRAM STAKEHOLDER PANEL KICKOFF MEETING This is an invitation to participate as a stakeholder in the development and implementation of a critical and important project, the Delta Regional Monitoring Program (Delta RMP), being developed jointly by the State and Regional Boards’ Bay-Delta Team. The Delta RMP stakeholder panel kickoff meeting is scheduled for 30 September 2008 and we respectfully request your attendance at the meeting. The meeting will consist of two sessions (see attached draft agenda). During the first session, Water Board staff will provide an overview of the impetus for the Delta RMP and initial planning efforts. The purpose of the first session is to gain management-level stakeholder input and, if possible, endorsement of and commitment to the Delta RMP planning effort. We request that you and your designee attend the first session together. The second session will be a working meeting for the designees to discuss the details of how to proceed with the planning process. A brief discussion of the purpose and background of the project is provided below. In December 2007 and January 2008 the State Water Board, Central Valley Regional Water Board, and San Francisco Bay Regional Water Board (collectively Water Boards) adopted a joint resolution (2007-0079, R5-2007-0161, and R2-2008-0009, respectively) committing the Water Boards to take several actions to protect beneficial uses in the San Francisco Bay/Sacramento-San Joaquin Delta Estuary (Bay-Delta).
    [Show full text]
  • Summary of Findings About Circulation and the Estuarine Turbidity Maximum in Suisun Bay, California by David H
    USGS o 23 science for a changing world Summary of Findings About Circulation and the Estuarine Turbidity Maximum in Suisun Bay, California by David H. Schoellhamer and Jon R. Burau Suisun Bay, California, is the (landward) and ebb (seaward) cur­ the tidally-averaged (residual) move­ most landward subembayment of San rents. Tidal currents are strongest dur­ ment of water caused by river inflow Francisco Bay (fig. 1) and is an impor­ ing full and new moons, called spring or wind. Tidal and residual currents tant ecological habitat (Cloern and tides, and weakest during half moons, carry and mix (transport) salt, others, 1983; Jassby and others, 1995). called neap tides. This sloshing back sediment, plankton, and other constit­ During the 1960s and 1970s, data col­ and forth is usually much greater than uents. Saltwater is heavier than lected in Suisun Bay were analyzed to develop a conceptual model of how water, salt, and sediment move within 122°30' 122°00' 121°30' 38°30' and through the Bay. This conceptual model has been used to manage fresh­ water flows from the Sacramento-San Joaquin Delta to Suisun Bay to improve habitat for several threatened GRIZZLY BAY Reserve Fleet and endangered fish species. Instru­ Channel / mentation used to measure water IONKERB AY $ Carquinez SACRAMENTO- velocity, salinity, and suspended- Strait SAN JOAOUIN RIVER DELTA solids concentration (SSC) greatly 5A<- improved during the 1980s and 1990s. The U.S. Geological Survey (USGS) Suisun \ 38°00' Cutoff Mallard has utilized these new instruments to Island collect one of the largest, high-quality hydrodynamic and sediment data sets DELTA available for any estuary.
    [Show full text]
  • CALIFORNIA FISH and GAME "CONSERVATION of WILDLIFE THROUGH EDUCATION"
    REPRINT FROM CALIFORNIA FISH and GAME "CONSERVATION OF WILDLIFE THROUGH EDUCATION" VOLUME 49 OCTOBER 1963 NUMBER 4 FOOD OF YOUNG-OF-THE-YEAR STRIPED BASS (ROCCUS SAXATILIS) IN THE SACRAMENTO- SAN JOAQUIN RIVER SYSTEM' 2 WILLIAM HEUBACH, ROBERT J. TOTH, AND ALAN M. McCREADY California Deportment of Fish and Game Inland Fisheries Branch INTRODUCTION Young-of-the-year striped bass were studied to obtain a comprehen- sive knowledge of their year-round diet in the Sacramento-San Joaquin River system. This knowledge will help explain variations in migra- tion, growth, and year-class strength, which will in turn aid in predicting the effects of future environmental changes on striped bass. One such change will occur in the near future with the development of the California Water Plan. This plan will drastically alter water flow and salinity patterns in the Delta, thus changing the distribution and relative abundance of striped bass food organisms. Knowledge of the striped bass diet is necessary to insure adequate consideration for this species in the project design. The movement of threadfin shad ( Dorosonia petenense) into the Delta will bring about another change. These fish have dramatically altered other environments after becoming established (Kimsey at al., 1957), and they have already started to migrate into the Delta from upstream reservoirs where they were introduced in 1959 and 1960 to provide more forage for warmwater game fish. Kimsey (1958) theorized that they might compete with small striped bass, stating, "Some competition for food would be certain to occur and there is a possibility that it would be severe.
    [Show full text]
  • Northern Calfornia Water Districts & Water Supply Sources
    WHERE DOES OUR WATER COME FROM? Quincy Corning k F k N F , M R , r R e er th th a a Magalia e Fe F FEATHER RIVER NORTH FORK Shasta Lake STATE WATER PROJECT Chico Orland Paradise k F S , FEATHER RIVER MIDDLE FORK R r STATE WATER PROJECT e Sacramento River th a e F Tehama-Colusa Canal Durham Folsom Lake LAKE OROVILLE American River N Yuba R STATE WATER PROJECT San Joaquin R. Contra Costa Canal JACKSON MEADOW RES. New Melones Lake LAKE PILLSBURY Yuba Co. W.A. Marin M.W.D. Willows Old River Stanislaus R North Marin W.D. Oroville Sonoma Co. W.A. NEW BULLARDS BAR RES. Ukiah P.U. Yuba Co. W.A. Madera Canal Delta-Mendota Canal Millerton Lake Fort Bragg Palermo YUBA CO. W.A Kern River Yuba River San Luis Reservoir Jackson Meadows and Willits New Bullards Bar Reservoirs LAKE SPAULDING k Placer Co. W.A. F MIDDLE FORK YUBA RIVER TRUCKEE-DONNER P.U.D E Gridley Nevada I.D. , Nevada I.D. Groundwater Friant-Kern Canal R n ia ss u R Central Valley R ba Project Yu Nevada City LAKE MENDOCINO FEATHER RIVER BEAR RIVER Marin M.W.D. TEHAMA-COLUSA CANAL STATE WATER PROJECT YUBA RIVER Nevada I.D. Fk The Central Valley Project has been founded by the U.S. Bureau of North Marin W.D. CENTRAL VALLEY PROJECT , N Yuba Co. W.A. Grass Valley n R Reclamation in 1935 to manage the water of the Sacramento and Sonoma Co. W.A. ica mer Ukiah P.U.
    [Show full text]
  • Field Assessment of Avian Mercury Exposure in the Bay-Delta Ecosystem
    Assessment of Ecological and Human Health Impacts of Mercury in the Bay-Delta Watershed CALFED Bay-Delta Mercury Project Subtask 3B: Field assessment of avian mercury exposure in the Bay-Delta ecosystem. Draft Final Report Submitted to Mark Stephenson Director Marine Pollution Studies labs Department of Fish and Game Moss Landing Marine Labs 7544 Sandholt Rd. Moss Landing, Ca 95039 Submitted by: Dr. Steven Schwarzbach USGS Biological Research Division Western Ecological Research Center 7801 Folsom Blvd. Sacramento California 95826 and Terry Adelsbach US Fish and Wildlife Service Sacramento Fish and Wildlife Office Environmental Contaminants Division 2800 Cottage Way, Sacramento Ca. 95825 1 BACKGROUND The Bay/Delta watershed has a legacy of mercury contamination resulting from mercury mining in the Coast Range and the use of this mercury in the amalgamation method for extraction of gold from stream sediments and placer deposits in the Sierra Nevada. Because mercury, and methylmercury in particular, strongly bioaccumulate in aquatic foodwebs there has been a reasonable speculation that widespread mercury contamination of the bay/delta from historic sources in the watershed could be posing a health threat to piscivorous wildlife. As a result this systematic survey of mercury exposure in aquatic birds was conducted in both San Francisco Bay and the Sacramento/San Joaquin Delta. The Delta component of the survey was subtask 3b of the CalFed mercury project. The San Francisco Bay component of the project was conducted at the behest of the California Regional Water Quality Control Board, Region 2, San Francisco Bay. Results of both projects are reported on here because of overlap in methods and species sampled, the interconnectedness of the Bay/Delta estuary and the need to address avian wildlife risk of mercury in the region as a whole.
    [Show full text]
  • Fort Funston
    Excerpt from Geologic Trips San Francisco and the Bay Area by Ted Konigsmark ISBN 0-9661316-4-9 GeoPress All rights reserved. No part ofthis book may be reproduced without written permission in writing, except for critical articles or reviews. For other geologic trips see: www.geologictrips.com Ocean Great Hwy Sloat Blvd Beach 19th Ave Beach L ak e M er Bluff ce d Viewing Platform Blvd Skyline Fort Funston Edge of bluff Pacific vd Bl Ocean Day John Fort Funston is on a bluff made up of I-280 sedimentary rocks of the Merced Formation. The Merced Formation was deposited in a M e small sedimentary r c basin that formed along e the San Andreas fault d during the last two F m million years. I - 2 8 1 0 ay hw Hig Mussel Rock S a Trip 5. n A FORT FUNSTON nd re a Geologic Site s fa u l 1/2 Mile t 98 Trip 5. FORT FUNSTON Recent and Ancient Beaches and Dunes The Franciscan rocks are covered by a blanket of younger sedimentary rocks at many places in and around San Francisco. During the trip to Fort Funston you will learn how these sedimentary rocks were formed. The first stop is at Ocean Beach, where you will see how beach sand and sand dunes are presently being deposited along the shoreline. You will then continue to Fort Funston, where you will see how similar sedimentary rocks, called the Merced formation, were deposited in a small basin along the San Andreas fault about half-a-million years ago.
    [Show full text]