Review of Delta Biological Opinions and Water Supply Impacts

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Presentation transcript:

Review of Delta Biological Opinions and Water Supply Impacts 7/21/2018 9:20 PM Review of Delta Biological Opinions and Water Supply Impacts © 2007 Microsoft Corporation. All rights reserved. Microsoft, Windows, Windows Vista and other product names are or may be registered trademarks and/or trademarks in the U.S. and/or other countries. The information herein is for informational purposes only and represents the current view of Microsoft Corporation as of the date of this presentation. Because Microsoft must respond to changing market conditions, it should not be interpreted to be a commitment on the part of Microsoft, and Microsoft cannot guarantee the accuracy of any information provided after the date of this presentation. MICROSOFT MAKES NO WARRANTIES, EXPRESS, IMPLIED OR STATUTORY, AS TO THE INFORMATION IN THIS PRESENTATION.

Endangered Species Act Regulations Re: SWP & CVP Operations Delta smelt Longfin smelt Chinook Salmon Delta Smelt – USFWS released Bio Opinion (Dec ‘08) Longfin Smelt – Listed as threatened (Jun ‘09) Chinook Salmon/Steelhead/Green Sturgeon/SE Orca – NMFS released Bio Opinion (Jun ‘09) Steelhead Green Sturgeon

Pumping Flexibility Reduced Window restricted even during wet years Regulatory Pumping Restrictions JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Restrictions No Salmon Delta Smelt Longfin Smelt

SWP Water Deliveries Smelt & Salmon Biological Opinion Impacts SWP Contract Entitlement (Table A) = 4.1 million acre-ft Baseline Smelt BiOp Smelt & Salmon

Regulatory Restrictions SWP Reliability Curve with Smelt & Salmon Biological Opinions SWRCB Baseline Regulatory Restrictions USFWS Smelt 50% of time = 2.3 million AF NMFS Salmon Wet Dry

Aggressive Demand Management SWP Reliability Curve with Smelt & Salmon Biological Opinions Aggressive Demand Management Regulatory Restrictions NMFS Salmon Wet Dry

Delta Interim Opportunities Other Stressors Mark-select hatchery Ammonia research & model development Invasive species & predator control Bubble & strobe light curtains Ageria control others

Delta Interim Opportunities Mark-Select Salmon Fishery All hatchery fish marked & can be retained Commercial & recreational fisheries Benefit = 10,875 winter-run at year 12 Reduces commercial harvest by ~ 20% Cost ~ $5 million/yr; 10 cents per fish Adipose fin clip

Delta Interim Opportunities Mark-Select Salmon Fishery States & provinces implementing total salmon marking programs

Fish Salvage vs. Ocean Harvest (Total equivalent adult salmon captured from 1995-2006) Fall-Run Salmon 2.8 million 19,000 Late-Fall Run Salmon 150,000 350 Winter-Run Salmon 44,000 4,000 Spring-Run Salmon 69,000 14,000 Introduction We compared takes of Central Valley Chinook salmon runs captured at the State Water Project (SWP) and Central Valley Project (CVP) salvage Delta water export facilities based on fish salvage data, with those in ocean fisheries. Because the salvage facilities capture primarily juvenile salmon and the ocean fisheries harvest largely adult fish, we converted these to the equivalent number of adults that would have returned to Central Valley rivers and streamsthe mouth of the Sacramento River in the absence of these takes. Methods We summed daily expanded losses of Chinook salmon by race (Fall, Late Fall, Winter, or Spring) at the SWP and CVP salvage export facilities (available at ftp://ftp.delta.dfg.ca.gov/salvage) to obtain juvenile take estimates from 1996-2007 (Table 1). We assumed that these were smolts that would have emigrated to the ocean that year (1995-2006 brood years). Note that these losses included an accounting for indirect losses due to predation in SWP’s Clifton Court Fthe facilities forebay. We assumed that these were smolts that would have emigrated to the ocean that year (1995-2006 brood years). We then calculated the equivalent number of adults and jacks? from each cohort that would have returned to the Sacramento RiverCentral Valley to spawn in the absence of salvage and ocean harvest. To do this, we used rates of survival and maturity for each age as shown in Table 2. We also converted ocean fishery landings to adult equivalents because many of the fish caught were not yet mature and would have remained in the ocean for at least another year. Converting losses at the salvage export facilities and in ocean landings to adult equivalents ensures that the different takes are comparable. We estimated harvest each year, 1996-2007, from total actual landings of all runs and ages of Chinook at ocean ports in California, as reported by the Pacific Fishery Management Council (PFMC 2008). Estimates by age and race are not currently provided by the PFMC. Total ocean landings south of Point Arena are assumed to be primarily Central Valley Chinook salmon (PFMC 2008). Ocean landings of Central Valley Chinook salmon by age were derived using different methodologies for each race. Total ocean landings south of Point Arena are assumed to be primarily Central Valley Chinook salmon as reported by the Pacific Fishery Management Council (PFMC 2008). However, estimates by age and race are not currently provided by the PFMC. We used models to apportion the landings into race, and then into age groups for Central Valley Chinook salmon. The model used in the retrospective analysis of mark selective fisheries was used to derive ocean landings of Fall and Late Fall run Chinook salmon[please briefly describe the algorithms, or reference or attach text for each of these models]. The Fall run was assumed to comprise 90%, and the Late Fall run 5% of the landings. Winter and Spring run landings were hindcast using the Integrated Modeling Framework (IMF) for Sacramento River Winter run and Spring run Chinook salmon, respectively. Using model generated estimates also allowed us to project future landings of older aged fish to complete brood year comparisons (for example age 3 fish from brood year 2005 will be harvested in 2008). Therefore, ocean landings of 2005 and 2006 broods are based largely on predictions of future landings. The resultant estimates of ocean landings by brood year and age for each race are provided in Table 3. In order to make these landings comparable with salvage losses, we calculated the equivalent number of adults that would have returned to the Sacramento River to spawn in subsequent years, using parameters found in Table 2.

Fish Salvage vs. Ocean Harvest (Total equivalent adult salmon captured from 1995-2006) Winter-Run Salmon

Southern California's Water Reserve Levels FULL 2006 2007 2008 NOW EMPTY 2010 ?

Extra Slides

The Delta Sacramento Suisun Bay Stockton State & Federal Pumping Plants

Biological Ops Restrict Southerly Flows Delta Smelt Sacramento The flows from the rivers and tributaries flowing east to west is continually being pushed back and forth tidally (east & west), which provides varying salinity throughout the Delta. The recent biological opinions have significantly restricted water supply flows southerly. Stockton SWP Pumps CVP Pumps 15 15

Supplies Bay Area, Central Valley & Southern Cal Bay-Delta Supplies Bay Area, Central Valley & Southern Cal State Water Project Bay Area – 33% Some regions up to 100% dependent Central Valley – 23 to 90% The Bay Delta is where the rivers of the Sierra merge before heading west toward San Francisco Bay. It is the home of two large water projects, the State Water Project, which supplies mostly urban regions from the Bay area to San Diego, and the federal Central Valley Project, which supplies the state’s agricultural region in the Delta. All told, water directly from the Delta helps to sustain 25 million Californians – statewide – and some of the nation’s most productive farm land. As noted, water that travels through the Delta provides 33% to Northern California, 23 to 90% in Central Valley and 30% to Southern California. Southern Cal – 30%

Delta Fisheries A Downturn for Delta Smelt & Salmon Winter-Run Salmon Delta Smelt

Recent Regulatory Restrictions Causing Supply Cutbacks to State/Fed Contractors 1.5 million AF (20%) 2.5 million AF (40%) Regulations Avg. Yr. * Critical Yr. * Above Normal Yr. ** Delta Smelt (Courts) 770,000 af 330,000 af 1,260,000 af Delta Smelt (USFWS) 500,000 af 120,000 af 1,110,000 af Longfin Smelt (DFG) 0 af 0 af 0 af Chinook Salmon (NMFS) 260,000 af 60,000 af 180,000 af TOTAL 1,530,000 af (27%) 510,000 af (19%) 2,550,000 af (39%) SWRCB D-1641 Baseline = 5.7 maf (average yr); 2.7 maf (critical yr); 6.5 maf (above normal yr) * MWD’s “Most Likely” USFWS Delta Smelt scenario assumed ** MWD’s “High Impact” USFWS Delta Smelt scenario assumed

Phytoplankton Decrease Delta Interim Opportunities Preliminary research indicates ammonia tied to food web decline Ammonia Increase ln (Suisun Bay Phyto Density July to Sept) v June - August Ammonia Loading at Hood Phytoplankton Decrease

Regulatory Restrictions SWP Reliability Curve with Smelt & Salmon Biological Opinions Demand Management Regulatory Restrictions Assure Supply Reliability Implement 2-Gates Project Implement Bay-Delta Conservation Plan Wet Dry