1 DEPARTMENT of the INTERIOR Fish
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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 -
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. -
Subsidence Reversal for Tidal Reconnection
PERFORMANCE MEASURE 4.12: SUBSIDENCE REVERSAL FOR TIDAL RECONNECTION Performance Measure 4.12: Subsidence Reversal for Tidal Reconnection Performance Measure (PM) Component Attributes Type: Output Performance Measure Description 1 Subsidence reversal 0F activities are located at shallow subtidal elevations to prevent net loss of future opportunities to restore tidal wetlands in the Delta and Suisun Marsh. Expectations Preventing long-term net loss of land at intertidal elevations in the Delta and Suisun Marsh from impacts of sea level rise and land subsidence. Metric 1. Acres of Delta and Suisun Marsh land with subsidence reversal activity located on islands with large areas at shallow subtidal elevations. This metric will be reported annually. 2. Average elevation accretion at each project site presented in centimeters per year. This metric will be reported every five years. Baseline 1. In 2019, zero acres of subsidence reversal on islands with large areas at shallow subtidal elevations. 2. Short-term elevation accretion in the Delta at 4 centimeters per year. 1 Subsidence reversal is a process that halts soil oxidation and accumulates new soil material in order to increase land elevations. Examples of subsidence reversal activities are rice cultivation, managed wetlands, and tidal marsh restoration. DELTA PLAN, AMENDED – PRELIMINARY DRAFT NOVEMBER 2019 1 PERFORMANCE MEASURE 4.12: SUBSIDENCE REVERSAL FOR TIDAL RECONNECTION Target 1. By 2030, 3,500 acres in the Delta and 3,000 acres in Suisun Marsh with subsidence reversal activities on islands, with at least 50 percent of the area or with at least 1,235 acres at shallow subtidal elevations. 2. An average elevation accretion of subsidence reversal is at least 4 centimeters per year up to 2050. -
Suisun Marsh Fish Report 2011 Final.Pdf
SUISUN MARSH FISH STUDY Trends in Fish and Invertebrate Populations of Suisun Marsh January 2011 - December 2011 Annual Report for the California Department of Water Resources Sacramento, California Teejay A. O'Rear and Peter B. Moyle Department of Wildlife, Fish, and Conservation Biology University of California, Davis July 2012 SUMMARY Suisun Marsh, at the geographic center of the San Francisco Estuary, is important habitat for introduced and native fishes. With funding from the California Department of Water Resources (DWR), the University of California, Davis, Suisun Marsh Fish Study has systematically monitored the marsh's fish populations since 1980. The purpose of the study has been to determine the environmental factors affecting fish abundance and distribution within the context of evolving water management. In 2011, we conducted 259 otter trawls and 74 beach seines. Our catches of plankton- feeding macroinvertebrates and fishes were strongly influenced by the interaction of high Delta outflows, low salinities, and the cold winter and spring. The prolonged low salinities severely reduced the population of overbite clams (Potamocorbula amurensis) in the southwest marsh, in addition to delaying the appearance of Black Sea jellyfish (Maeotias marginata) medusae until very late in the year. Species that ultimately benefit from high flows for spawning, due to either increased floodplain inundation [e.g., Sacramento splittail (Pogonichthys macrolepidotus)] or reduced salinities [e.g., white catfish (Ameiurus catus)], recruited to the marsh in high numbers. Additionally, delta smelt (Hypomesus transpacificus) reached their highest abundance in the marsh since 2001, which was likely due to the combination of (1) high flows both reducing entrainment and promoting plankton blooms, (2) colder water during spring creating more favorable spawning conditions, and (3) appropriate temperatures and salinities occurring in the marsh during autumn. -
Suisun Marsh Fish Report 2018 Final.Pdf
Trends in Fish and Invertebrate Populations of Suisun Marsh January 2018 - December 2018 Annual Report for the California Department of Water Resources Sacramento, California Teejay A. O'Rear*, Peter B. Moyle, and John R. Durand Department of Fish, Wildlife, and Conservation Biology Center for Watershed Sciences University of California, Davis October 2020 *Corresponding author: [email protected] SUMMARY Suisun Marsh, at the geographic center of the northern San Francisco Estuary, is important habitat for native and non-native fishes. The University of California, Davis, Suisun Marsh Fish Study, in partnership with the California Department of Water Resources (DWR), has systematically monitored the marsh's fish populations since January 1980. The study’s main purpose has been to determine environmental and anthropogenic factors affecting fish distribution and abundance. Abiotic conditions in Suisun Marsh during calendar-year 2018 returned to fairly typical levels following the very wet year of 2017. Delta outflow was generally low, with higher-than- average outflows only occurring in April when Yolo Bypass flooded. Salinities in 2018 were about average, in part because of Suisun Marsh Salinity Control Gates operations in late summer. Water temperatures were mild, being higher than average in winter and autumn and slightly below average during summer. Water transparencies were typical in winter and spring but, as has become a pattern since the early 2000s, were higher than average in summer and autumn. Dissolved-oxygen concentrations were consistent throughout the year, with only two instances of low values being recorded, both in dead-end sloughs. Fish and invertebrate catches in Suisun Marsh in 2018 told two main stories: (1) many fishes benefit from higher flows and lower salinities in Suisun Marsh while some invasive invertebrates do not; and (2) Suisun Marsh is disproportionately valuable to fishes of conservation importance. -
Trends in Fish and Invertebrate Populations of Suisun Marsh January 2017
Trends in Fish and Invertebrate Populations of Suisun Marsh January 2017 - December 2017 Annual Report for the California Department of Water Resources Sacramento, California Teejay A. O'Rear, Peter B. Moyle, and John R. Durand Department of Fish, Wildlife, and Conservation Biology Center for Watershed Sciences University of California, Davis January 2019 SUMMARY Suisun Marsh, at the geographic center of the northern San Francisco Estuary, is important habitat for native and non-native fishes. The University of California, Davis, Suisun Marsh Fish Study, in partnership with the California Department of Water Resources (DWR), has systematically monitored the marsh's fish populations since January 1980. The study’s main purpose has been to determine environmental and anthropogenic factors affecting fish distribution and abundance. Calendar year 2017 was wet and warm. Very high Delta outflows resulted in nearly freshwater conditions throughout Suisun Marsh from January to July, with lower-than-average salinities persisting until November. Matching the local climate, water temperatures were generally warmer than usual. Unlike most of the last 10 years when water transparencies greatly increased relative to the average in summer and autumn, water transparencies stayed near or below average for the latter half of 2017. Dissolved oxygen (DO) concentrations were sufficient for marsh fishes except in March in upper Goodyear Slough, when DO concentrations dipped below 3 milligrams per liter (mg/L). The aquatic community of Suisun Marsh responded to the wet, warm conditions. Non- native overbite clams (Potamocorbula amurensis), which require a salinity of at least 2 parts per thousand (ppt) for successful reproduction, were never abundant in 2017. -
Embryonic and Larval Development of Sacramento Splittail, Pogonichthys Macrolepidotus Xin Deng1*, Swee J
MARCH 2012 Embryonic and Larval Development of Sacramento Splittail, Pogonichthys macrolepidotus Xin Deng1*, Swee J. Teh2, Serge I. Doroshov,1 and Silas S. O. Hung1 ABSTRACT KEY WORDS Embryonic and larval development of Sacramento splittail, embryo, larva, development splittail (Pogonichthys macrolepidotus) was char- acterized from zygote to metamorphosis in labora- INTRODUCTION tory conditions. Fertilized eggs were obtained from induced and natural tank spawning of adults caught Sacramento splittail is a cyprinid endemic to in the Yolo Bypass of the Sacramento River. Splittail California’s Central Valley and the San Francisco produced transparent adhesive eggs with a moder- Estuary (Meng and Moyle 1995; Moyle 2002). It is ate perivitelline space. Duration of embryonic devel- the only extant species in genus Pogonichthys, after opment from fertilization to hatching was 100 h the extinction of the congeneric Clear Lake splittail at 18 ± 0.5 °C. Newly hatched larvae were 5.2 to P. ciscoides in the 1970s (Moyle 2002). Splittail has 6.0 mm total length with no mouth opening. Yolk- been listed as a species of special concern by the sac larvae were demersal and absorbed the yolk California Department of Fish and Game since 1989, within 10 days post-hatch. Exogenous feeding started then as threatened by the U.S. Fish and Wildlife at 6 days post-hatch, concomitant with swim bladder Service in 1999, primarily due to low population inflation and swim-up movement. Fin differentia- abundance during drought years in 1987 to 1992 tion began at approximately 10 d post-hatch (ca. 8.3 (Meng and Moyle 1994, 1995; Sommer and others to 8.85 mm total length) and was completed at 50 d 1997, 2007, 2008; Moyle and others 2004). -
Sites Reservoir Project Public Draft EIR/EIS
6. Surface Water Resources 6.1 Introduction This chapter describes Existing Conditions (the environmental setting) and Sites Reservoir Project (Project)-related changes to surface water resources in the Extended, Secondary, and Primary study areas. Detailed descriptions and maps of these three study areas are provided in Chapter 1 Introduction, and summarized descriptions are included in this chapter. Surface water resources generally include reservoirs, rivers, and diversions. Permits and authorizations for surface water resources are presented in Chapter 4 Environmental Compliance and Permit Summary. The regulatory setting for surface water resources is presented in Appendix 4A Environmental Compliance. This chapter also includes a description of the surface water supply facilities operations and resulting surface water resources characteristics of California’s major water systems that are relevant to the Project: the Central Valley Project (CVP), a federal project that is operated and maintained by the Bureau of Reclamation (Reclamation), the State Water Project (SWP), operated and maintained by the California Department of Water Resources (DWR), and associated tributary rivers and streams. A schematic showing the layout of these two water systems, with the relative location of the Project, is shown in Figures 6-1A, 6-1B, and 6-1C. A comparison of these characteristics has been made between the Existing Conditions/No Project/No Action Condition, and the four action alternatives (Alternatives A, B, C, and D). Unless noted, all numbers shown related to storages, flows, exports, and deliveries in this chapter are generated from the CALSIM II computer simulation model. Appendix 6A Modeling of Alternatives, Appendix 6B Water Resources System Modeling, and Appendix 6C Upper Sacramento River Daily River Flow and Operations Modeling describe the assumptions and the analytical framework used in the surface water modeling analyses. -
DRAFT Sonoma Creek Watershed Enhancement Plan
DRAFT Sonoma Creek Watershed Enhancement Plan An owner’s manual for the residents & landowners of the Sonoma Creek Watershed. Prepared by: The Sonoma Resource Conservation District in conjunction with the people of the Sonoma Creek Watershed and collaboration with the Sonoma Ecology Center. TABLE OF CONTENTS ACRONYMS .................................................................................................................................. 6 ACKNOWLEDGEMENT .............................................................................................................. 8 SECTION 1. INTRODUCTION AND BACKGROUND.............................................................. 9 CHAPTER 1: INTRODUCTION .............................................................................................. 10 PURPOSE OF THE SONOMA CREEK WATERSHED ENHANCEMENT PLAN....................................... 10 PROCESS FOR DEVELOPING THE PLAN ........................................................................................ 10 STAKEHOLDER GROUPS ............................................................................................................. 11 ORGANIZATION OF THE PLAN ..................................................................................................... 14 WATERSHED GOALS ................................................................................................................... 15 CHAPTER 2: WATERSHED DESCRIPTION AND HISTORY ............................................... 18 WATERSHED BOUNDARY OVERVIEW ........................................................................................ -
Conceptual Model for Managed Wetlands in Suisun Marsh
Initial Draft Conceptual Model for Managed Wetlands in Suisun Marsh Compiled by Department of Fish and Game (DFG) and Suisun Resource Conservation District (SRCD) staff Contributors: Laureen Barthman – Thompson (DFG) Kristin Bruce (SRCD) Sarah Estrella (DFG) Paul Garrison III (DFG) Craig Haffner (SRCD) Julie Niceswanger (DFG) Gina Van Klompenburg (DFG) Bruce Wickland (SRCD) With input from: Dennis Becker Laurie Briden Cecilia Brown Steve Chappell Steve Culberson Cassandra Enos Chris Enright Bellory Fong Terri Gaines Jasper Lament Conrad Jones Victor Pacheco Facilitated by: Zachary Hymanson Stuart Siegel 1 Table of Contents 1.0 MANAGED WETLAND MANAGEMENT GOALS AND ASSUMPTIONS .................................. 5 2.0 CURRENT CONDITIONS .................................................................................................................... 5 2.1 PHYSICAL .......................................................................................................................................... 6 2.1.1 Applied water salinity .................................................................................................................. 6 2.1.2 Slough water salinity / Marsh-wide salinity gradient (DWR 2001) ............................................. 7 2.1.3 Soils .............................................................................................................................................. 7 2.1.4 Water year ................................................................................................................................... -
Distribution and Abundance of Shrimp, Plankton, and Benthos in Suisun Marsh
Distribution, and abundance of shrimp, plankton and benthos in Suisun Marsh: Tidal marsh as a refuge for native species Project Information 1. Proposal Title: Distribution, and abundance of shrimp, plankton and benthos in Suisun Marsh: Tidal marsh as a refuge for native species 2. Proposal applicants: Peter B. Moyle, University of California, Davis 3. Corresponding Contact Person: Ahmad Hakim-Elahi Regents of University of California Office of Vice Chancelor of Research Sponsored Programs 118 Everson 1 Shields Avenue University of California Davis, CA 95616 530 752-2075 [email protected] 4. Project Keywords: Estuarine/Tidal Ecology Nonnative Invasive Species Trophic Dynamics and Food Webs 5. Type of project: Research 6. Does the project involve land acquisition, either in fee or through a conservation easement? No 7. Topic Area: Shallow Water, Tidal and Marsh Habitat 8. Type of applicant: University 9. Location - GIS coordinates: Latitude: 38.182 Longitude: -121.998 Datum: Describe project location using information such as water bodies, river miles, road intersections, landmarks, and size in acres. The project is located within Suisun Marsh, Solano County, California. Research activities will take place in numerous waterbodies of Suisun Marsh including Peytonia, Boynton, Suisun, Spring Branch (First Mallard Branch), Cutoff, Montezuma, Nurse, Denverton, Goodyear and Cordelia sloughs. The Suisun Marsh is located in the San Francisco Estuary and is approximately 60,000 acres in size. 10. Location - Ecozone: 2.1 Suisun Bay & Marsh 11. Location - County: Solano 12. Location - City: Does your project fall within a city jurisdiction? No 13. Location - Tribal Lands: Does your project fall on or adjacent to tribal lands? No 14. -
Landscape Change in Suisun Marsh AMBER DAWN MANFREE
Landscape Change in Suisun Marsh By AMBER DAWN MANFREE B.A. (Sonoma State University) 1995 M.A. (University of California, Davis) 2012 DISSERTATION Submitted in partial satisfaction of the requirements for the degree of DOCTOR OF PHILOSOPHY in Geography in the OFFICE OF GRADUATE STUDIES of the UNIVERSITY OF CALIFORNIA DAVIS Approved: _____________________________________ Peter B. Moyle, Chair _____________________________________ Deborah L. Elliott-Fisk _____________________________________ Jay R. Lund Committee in Charge 2014 i UMI Number: 3646341 All rights reserved INFORMATION TO ALL USERS The quality of this reproduction is dependent upon the quality of the copy submitted. In the unlikely event that the author did not send a complete manuscript and there are missing pages, these will be noted. Also, if material had to be removed, a note will indicate the deletion. UMI 3646341 Published by ProQuest LLC (2014). Copyright in the Dissertation held by the Author. Microform Edition © ProQuest LLC. All rights reserved. This work is protected against unauthorized copying under Title 17, United States Code ProQuest LLC. 789 East Eisenhower Parkway P.O. Box 1346 Ann Arbor, MI 48106 - 1346 Amber Dawn Manfree September 2014 Geography Landscape Change in Suisun Marsh Abstract Suisun Marsh is a 470 km2 wetland situated between the Sacramento-San Joaquin Delta and San Pablo Bay in the San Francisco Estuary. Today, about 80 percent of the marsh plain is privately owned by duck hunting clubs and managed in accordance with conservation agreements. A complex network of sloughs weaves through the Marsh, providing habitat for numerous aquatic species. Together the waterways and marsh plain support a stunning array of species, provide exurban open space, and are increasingly called upon to meet regional conservation objectives.