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Central Valley Project Integrated Resource Plan
Summary Report Central Valley Project Integrated Resource Plan U.S. Department of the Interior Bureau of Reclamation Mid-Pacific Region TABLE OF CONTENTS TABLE OF CONTENTS BACKGROUND ..........................................................................................................................................................5 STUDY APPROACH ...................................................................................................................................................7 CLIMATE IMPACTS ON WATER SUPPLIES AND DEMANDS ...............................................................................11 COMPARISON OF PROJECTED WATER SUPPLIES AND DEMANDS .................................................................21 PERFORMANCE OF POTENTIAL FUTURE WATER MANAGEMENT ACTIONS .................................................27 PORTFOLIO TRADEOFFS .......................................................................................................................................37 CVP IRP STUDY LIMITATIONS ................................................................................................................................39 ACRONYMS AND ABBREVIATIONS USED IN FIGURES ......................................................................................41 Tables Table 1. Simulation Suites and Assumptions Inlcuded in Each Portfolio .............................................................27 Figures Figure 1a. Projected changes in Temperature in Ensemble-Informed Transient Climate Scenarios between 2012 -
The Saltiest Springs in the Sierra Nevada, California
The Saltiest Springs in the Sierra Nevada, California Scientific Investigations Report 2017–5053 U.S. Department of the Interior U.S. Geological Survey Cover. Photograph of more than a dozen salt-evaporation basins at Hams salt spring, which have been carved by Native Americans in granitic bedrock. Saline water flows in light-colored streambed on left. Photograph by J.S. Moore, 2009. The Saltiest Springs in the Sierra Nevada, California By James G. Moore, Michael F. Diggles, William C. Evans, and Karin Klemic Scientific Investigations Report 2017–5053 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior RYAN K. ZINKE, Secretary U.S. Geological Survey William H. Werkheiser, Acting Director U.S. Geological Survey, Reston, Virginia: 2017 For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment—visit http://www.usgs.gov or call 1–888–ASK–USGS. For an overview of USGS information products, including maps, imagery, and publications, visit http://store.usgs.gov. Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this information product, for the most part, is in the public domain, it also may contain copyrighted materials as noted in the text. Permission to reproduce copyrighted items must be secured from the copyright owner. Suggested citation: Moore, J.G., Diggles, M.F., Evans, W.C., and Klemic, K., 2017, The saltiest springs in the Sierra Nevada, California: U.S. -
Smith, J.R. Et Al., 2007. Acoustic Monitoring of Mokelumne River
•3 Two hatchery smolts moved upstream Acoustic Monitoring of from the release site into the Cosumnes River. They held there for >30 days and then moved up the Sacramento River Mokelumne River •4 Oncorhynchus mykiss PRELIMINARY RESULTS James R. Smith1 , Michelle L. Workman1, 2 3 • All hatchery smolts were detected at least once by the receiver grid. Time from release to last detection ranged from 1 to 114 Joseph E. Merz , Walter Heady , and days 1 • All hatchery reconditioned kelts were detected. Time ranged from 1 to 81 days. Joseph J. Miyamoto • Forty-Seven of sixty-four (73%) of wild O. mykiss were detected by combined stationary and mobile tracking techniques. • Time from release to last detection ranged from 1-136 days for stationary receivers and from 5 to 173 days for 1 East Bay Municipal Utility District, 1 Winemasters Way, Lodi, CA 95240 mobile tracking. 2 Cramer Fish Sciences, 636 Hedburg Way #22, Oakdale, CA 95361 3 University of California, Santa Cruz, Long Marine Lab, 100 Shaffer Rd., Santa Cruz, CA 95060 70% 60% Project funded by the California Urban Water Agencies 50% 40% 30% 20% 10% 0% Percent of Release Group Vicinity of Mokelumne Sacramento Delta/Bay None INTRODUCTION Release River River The Mokelumne River Fish Hatchery (Hatchery) has released over 2 million smolt Detections through 7/13/2007 steelhead, Oncorhyncus mykiss, in the lower Mokelumne River since 1995, however, fewer than 750 adults have returned to the Hatchery since 1996. There have been limited data Hatchery Smolts n=57 Reconditioned Kelts n=7 Wild Caught Various n=64 Detections occurred in four major categories: 1)detections in vicinity of release site; collected on the movements of these fish once released. -
Spring Gap-Stanislaus Project Is Located in Calaveras and Tuolumne Counties, CA on the Middle Fork Stanislaus River (Middle Fork) and South Fork Stanislaus River
Hydropower Project License Summary STANISLAUS RIVER, CALIFORNIA SPRING GAP-STANISLAUS HYDROELECTRIC PROJECT (P-2130) Photo Credit: California State Water Board This summary was produced by the Hydropower Reform Coalition Stanislaus River, CA STANISLAUS RIVER, CA SPRING GAP-STANISLAUS HYDROELECTRIC PROJECT (P-2130) DESCRIPTION: The Spring Gap-Stanislaus Project is located in Calaveras and Tuolumne Counties, CA on the Middle Fork Stanislaus River (Middle Fork) and South Fork Stanislaus River. Owned. The project, operated by Pacific Gas and Electric Company (PG&E), has an installed capacity of 87.9 MW and occupies approximately 1,060 acres of federal land within the Stanislaus National Forest. Both the Middle and South Forks are popular destinations for a variety of outdoor recreation activities. With a section of the lower river designated by the State of CA as a Wild Trout Fishery, the Middle Fork is widely considered to be one of California’s best wild trout fisheries. The South Fork on the other hand, with its high gradient and steep rapids, is a popular whitewater kayaking and rafting destination. A. SUMMARY 1. License application filed: December 26, 2002 2. License Issued: April 24, 2009 3. License expiration: March 31, 2047 4. Capacity: Spring Gap- 6.0 MW Stanislaus- 81.9 MW 5. Waterway: Middle & North Forks of the Stanislaus River 6. Counties: Calaveras, Tuolumne 7. Licensee: Pacific Gas & Electric Company (PG&E) 8. Licensee Contact: Pacific Gas and Electric Company P.O. Box 997300 Sacramento, CA 95899-7300 9. Project area: The project is located in the Sierra Nevada mountain range of north- central California. -
The Geography and Dialects of the Miwok Indians
UNIVERSITY OF CALIFORNIA PUBLICATIONS IN AMERICAN ARCHAEOLOGY AND ETHNOLOGY VOL. 6 NO. 2 THE GEOGRAPHY AND DIALECTS OF THE MIWOK INDIANS. BY S. A. BARRETT. CONTENTS. PAGE Introduction.--...--.................-----------------------------------333 Territorial Boundaries ------------------.....--------------------------------344 Dialects ...................................... ..-352 Dialectic Relations ..........-..................................356 Lexical ...6.................. 356 Phonetic ...........3.....5....8......................... 358 Alphabet ...................................--.------------------------------------------------------359 Vocabularies ........3......6....................2..................... 362 Footnotes to Vocabularies .3.6...........................8..................... 368 INTRODUCTION. Of the many linguistic families in California most are con- fined to single areas, but the large Moquelumnan or Miwok family is one of the few exceptions, in that the people speaking its various dialects occupy three distinct areas. These three areas, while actually quite near together, are at considerable distances from one another as compared with the areas occupied by any of the other linguistic families that are separated. The northern of the three Miwok areas, which may for con- venience be called the Northern Coast or Lake area, is situated in the southern extremity of Lake county and just touches, at its northern boundary, the southernmost end of Clear lake. This 334 University of California Publications in Am. Arch. -
Shasta Dam Fish Passage Evaluation
Mission Statements The mission of the Department of the Interior is to protect and provide access to our Nation’s natural and cultural heritage and honor our trust responsibilities to Indian Tribes and our commitments to island communities. The mission of the Bureau of Reclamation is to manage, develop, and protect water and related resources in an environmentally and economically sound manner in the interest of the American public. Contents Contents Page Chapter 1 Introduction ................................................................................ 1-1 Project Background ........................................................................................ 1-3 Central Valley Salmon and Steelhead Recovery Plan ............................. 1-4 2009 NMFS Biological Opinion .............................................................. 1-5 Shasta Dam Fish Passage Evaluation ...................................................... 1-6 Purpose and Need .......................................................................................... 1-7 Objectives ...................................................................................................... 1-7 Study Area ..................................................................................................... 1-8 River Selection Process............................................................................ 1-9 Shasta Lake ............................................................................................ 1-10 Upper Sacramento River Watershed ..................................................... -
Delta Sediment Measurements to Support Numerical Modeling of Sediment-Turbidity
Delta sediment measurements to support numerical modeling of sediment-turbidity Scott Wright, David Schoellhamer, Tara Morgan, Dan Whealdon-Haught, Matt Marineau USGS Sacramento CWEMF annual meeting 17 April 2012, Sacramento CA U.S. Department of the Interior U.S. Geological Survey Sediment-turbidity modeling in the Delta Delta sediment modeling is useful for a variety of reasons: - fish habitat (e.g. Delta smelt) - tidal wetlands, restoration, sea-level rise - navigation - levee integrity Robust models require data for set- up, calibration, and testing The Delta is large and very complex. Several data gaps exist with respect to development and testing of numerical sediment models We began a project to fill these data gaps in December 2010, funded by the Federal Task Force on the Delta Sediment model data requirements Hydrodynamics: - bathymetry and levee topography - flows and velocities at upstream model boundaries - water levels at downstream boundary and interior - bed roughness (e.g. Manning’s n, drag coefficients) Sediment: - Sediment loads at upstream model boundaries - Sediment concentrations at interior points - Size distributions of sediment on the bed - Sediment erosion/entrainment rates - Size distributions and settling velocities of suspended sediment Sediment-turbidity monitoring 17 turbidity and sediment flux stations, co-located with flow gages Network is designed to monitor incoming sediment loads and track movement of turbidity and sediment throughout the Delta Sediment-turbidity monitoring Sac River @ Freeport Miner -
California Central Valley Steelhead Distinct Population Segment Factsheet
California Central Valley Steelhead Distinct Population Segment Factsheet Author List Brian Ellrott, National Oceanic and Atmospheric Administration Fisheries Howard Brown, National Oceanic and Atmospheric Administration Fisheries Rachel Johnson, National Oceanic and Atmospheric Administration Fisheries, Southwest Fisheries Science Center California Central Valley Steelhead Distinct Population Segment (DPS) Definition Naturally spawned anadromous O. mykiss (steelhead) originating below natural and manmade impassable barriers from the Sacramento and San Joaquin rivers and their tributaries; excludes such fish originating from San Francisco and San Pablo Bays and their tributaries. This DPS includes steelhead from the Coleman National Fish Hatchery Program, the Feather River Fish Hatchery Program, and the Mokelumne River Hatchery Program. Federal Endangered Species Act Listing Status Listed as threatened since 1998. Historical Distribution Prior to dam construction, and other large-scale habitat changes, California Central Valley steelhead were distributed throughout the Sacramento and San Joaquin rivers (Busby et al. 1996; NMFS 1996b, McEwan 2001). Steelhead were found from the upper Sacramento and Pit rivers (now inaccessible due to Shasta and Keswick dams) south to the Kings and possibly the Kern River systems, and in both east- and west-side Sacramento River tributaries (Yoshiyama et al. 1996). Lindley et al. (2006) estimated that historically there were at least 81 independent Central Valley steelhead populations distributed primarily throughout the eastern tributaries of the Sacramento and San Joaquin rivers. Presently, impassable dams block access to 80 percent of historically available habitat, and block access to all historical spawning habitat for about 38 percent of historical steelhead populations (Lindley et al. 2006). Steelhead populations may have been extirpated from their entire historical range in the San Joaquin Valley and most of the larger basins of the Sacramento River. -
Evidence of Spawning by Green Sturgeon, Acipenser Medirostris, in the Upper Sacramento River, California
Environ Biol Fish DOI 10.1007/s10641-006-9085-5 GREEN STURGEON Evidence of spawning by green sturgeon, Acipenser medirostris, in the upper Sacramento River, California Kurtis Brown Received: 7 July 2005 / Accepted: 17 May 2006 Ó Springer Science+Business Media B.V. 2006 Abstract This study reports the only direct evi- family (Moyle et al. 1992). Despite its wide geo- dence of spawning of green sturgeon, Acipenser graphic distribution in the northern Pacific medirostris, in the upper Sacramento River, CA. Ocean, the green sturgeon is considered a rare or Two green sturgeon eggs were collected with vulnerable species in the United States and Can- substrate mats immediately below Red Bluff ada (Birstein 1993; Moyle et al. 1994; Cambell Diversion Dam. One green sturgeon larva was 1997). The green sturgeon is identified as a spe- collected with a larval net at Bend Bridge. We cies of special concern by California Department concluded that green sturgeon spawn in the upper of Fish and Game (CDFG) and a species of Sacramento River, both above and below RBDD. concern by the U.S. Fish and Wildlife Service Temperature ranges in the study area (10–15°C) (USFWS). The only known spawning populations are similar to conditions used in successful artifi- in North America are in the Klamath, Rogue, and cial rearing of green sturgeon and do not appear Sacramento rivers, all of which have flow regimes to be a limiting factor to successful spawning of that are affected by water projects (Moyle et al. green sturgeon; however, suitable habitat up- 1994). The operational regime of Red Bluff stream of RBDD is inaccessible when dam gates Diversion Dam (RBDD), an agricultural diver- are lowered. -
Brood Year 2018 Juvenile Salmonid Production and Passage Indices at Red Bluff Diversion Dam
BROOD YEAR 2018 JUVENILE SALMONID PRODUCTION AND PASSAGE INDICES AT RED BLUFF DIVERSION DAM Prepared for: U.S. Bureau of Reclamation 2018 Annual RBDD Juvenile Fish Monitoring Report Prepared by: Scott D. Voss and William R. Poytress U.S. Fish and Wildlife Service Red Bluff Fish and Wildlife Office 10950 Tyler Road Red Bluff, CA 96080 August 2020 Disclaimer The mention of trade names or commercial products in this report does not constitute endorsement or recommendation for use by the federal government. The correct citation for this report is: Voss, S. D. and W. R. Poytress. 2020. Brood year 2018 juvenile salmonid production and passage indices at the Red Bluff Diversion Dam. Report of U.S. Fish and Wildlife Service to U.S. Bureau of Reclamation, Sacramento, CA. ii Brood year 2018 juvenile salmonid production and passage indices at Red Bluff Diversion Dam. Scott D. Voss and William R. Poytress U.S. Fish and Wildlife Service Red Bluff Fish and Wildlife Office Abstract.― Brood year 2018 (BY2018) juvenile winter Chinook salmon estimated passage at Red Bluff Diversion Dam (RBDD) was 1,168,263 for fry and pre-smolt/smolts combined. The fry-equivalent rotary trap juvenile production index (JPI) was the highest value reported in the last five years; estimated at 1,477,529 with the lower and upper 90% confidence intervals (CI) extending from 824,706 to 2,130,352 juveniles, respectively. The estimated egg-to-fry (ETF) survival rate, based on the BY2018 winter Chinook fry-equivalent JPI was 26.6%, slightly above the 21-year average ETF survival rate of 25.0%. -
2000 Angler Survey 1
State of California The Resources Agency DEPARTMENT OF FISH AND GAME CENTRAL VALLEY SALMON AND STEELHEAD HARVEST MONITORING PROJECT 2000 ANGLER SURVEY 1: Prepared by Kyle Murphy Associate Biologist (MarineIFisheries) and Tom Schroyer, Mike Harris, and Duane Massa Biolog~sts(MarineEisheries) -I1 Th~swork was supported by funds provided by the U.S. Fish and Wildlife Service, Comprehensive Assessment & Monitoring Program (CAMP), as part of a cooperative agreement with the California Department of Fish and Game pursuant to the Central Valley Project Improvement Act (PL. 102-575). SUMMARY In October 1992, the Central Valley Project Improvement Act (CVPIA) was signed into law. One objective of the CVPIA is to restore the abundance of natural fish stocks in Central Valley rivers and streams. To achieve this objective, the CVPIA requires the development of restoration actions that ensure sustainable, long-term populations of native anadromous fish stocks. Section 3406(b)(16) of the CVPIA specifies the development of a monitoring and assessment program to evaluate the effectiveness of implemented restoration actions. The Comprehensive Assessment and Monitoring Program (CAMP) was established for this purpose. The CAMP program recommends monitoring of both adult and juvenile fish populations. It was recommended that adult monitoring include spawner returns (escapement) as well as in-river recreational, ocean recreational and commercial harvest estimates. In 1998, the California Department of Fish and Game (CDFG) began the Central Valley Salmon and Steelhead Harvest Monitoring Project to help enumerate the number of adult chinook salmon and steelhead resulting from natural production in Central Valley rivers and streams. This long-term harvest monitoring project will determine annual estimates of the total in-river harvest. -
Red Bluff Diversion Dam Final EIS/EIR
Appendix B Fishery Resources APPENDIX B Fishery Resources Affected Environment The fishery resources in the Sacramento River near the Red Bluff Diversion Dam (RBDD) consist of a diverse assemblage of fish species including native and non-native (introduced species). Table B-1 provides a species list of those fish that may likely be found at or near RBDD at some time during their life history. Of those species shown in Table B-1, four groups of fish species will be discussed together in this section because of their family relationship, life history characteristics, legal status, and occurrence within the project area. These groups include: • Native anadromous salmonids (NAS) • Other native anadromous fish (NAO) • Non-native anadromous fish (NNA) • Resident native and non-native fish (RN and RNN) TABLE B-1 Fish Found in the Sacramento River near RBDD Common Name Scientific Name Group Native Introduced Chinook salmona Oncorhynchus tshawytscha NASb X Steelheadc Oncorhynchus mykiss irideus NAS X Sockeye salmon Oncorhynchus nerka NNASd Xe Pink salmon Oncorhynchus gorbuscha NNAS Xf Pacific lamprey Lampetra tridentata NAOg X River lamprey Lampetra ayresi NAO X Green sturgeon Acipenser medirostris NAO X White sturgeon Acipenser transmontanus NAO X Striped bass Morone saxatilis NNAh X American shad Alosa sapidissima NNA X Rainbow trouti Oncorhynchus mykiss RNj X Hitch Lavinia exilicauda RN X Sacramento splittail Pogonichthys macrolepidotus RN X Hardhead Mylopharodon conocephalus RN X Sacramento pikeminnow Ptychocheilus grandis RN X Speckled dace