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Kevin T. Hill Fisheries Resources Division Southwest Fisheries Science Center
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Historical overview Sardine population & mgmt since recovery Stock assessment process Assessment data Biology, Fisheries, Surveys 2010 assessment results Harvest policy & management issues
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5-year averages of estimated sardine population biomass, AD 420-1970; Age-structured estimates shown in red; Extreme population variability even in absence of fishing; periods of peak abundance ~ 50-60 years link to environmental forcing is assumed Typical population dynamic for an ‘R-selected’ species: small body, rapid growth, early maturation, high fecundity, short generation time, and the ability to disperse offspring widely Sardine scale-deposition in the Santa Barbara Basin (Soutar & Isaacs 1969; Baumgartner et al. 1992). “Little Ice Age”
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Early Sardine Science & Management Intense fishery sampling, ageing with scales and otoliths; Catch-effort studies (lunar-month); Tagging studies (still the best available); Early efforts by CDFG biologists to set caps and limit reduction fishing; Agency responses to declining catch were mixed & conflicting; ‘Marine Research Committee’, later renamed ‘CalCOFI’, was established by CA legislature in 1949 to ‘study the sardine problem’; Actions by the CA legislature were too little and too late to avoid eventual moratorium 23 years after Monterey fishery collapsed CalCOFI Sampling
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Tagging (1935-1944)
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1980 s : low abundance, confined to SCA; minor fisheries in SCA & ENS 1990 s : Expansion offshore and north to Central California; CCA fishery begins; Pop’n growth = 33%; Sardine in OR, WA, and BC 2000 s : Fisheries in PNW Seasonal movements N-S, inshore/offshore San Pedro Ensenada Washington Oregon Monterey British Columbia 2000 s 90 s 80 s
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Space-time distribution of Pacific sardine subpopulations (Felix-Uraga et al. 2004, 2005) WINTER SPRING SUMMERFALL SPRING
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Biology: Age, Growth, Maturity Biology: Age, Growth, Maturity Fishery: Tonnage, Size & Age Composition Fishery: Tonnage, Size & Age Composition Abundance: Resource Survey, CPUE, Age & Size Composition Abundance: Resource Survey, CPUE, Age & Size Composition Population Dynamics Model: Birth, Growth, Reproduction, Death Reconstruct past population trend & productivity. Estimate present abundance for resource managers. Population Dynamics Model: Birth, Growth, Reproduction, Death Reconstruct past population trend & productivity. Estimate present abundance for resource managers. Stock Status Optimum Yield (socioeconomic and ecosystem considerations)
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Fishery Data (tonnage, size, age of removals): Pacific Northwest (PNW) Central California (CCA) Southern California (SCA) Ensenada (ENS) Fishery-Independent Data (time series of abundance): CDFG & SWFSC egg production surveys: DEPM or TEP time series, depending on adult sampling; 1985-2010 West Coast Sardine Aerial Survey (industry funded): Current assessment includes estimates for OR-WA region, 2009 & 2010 Assessment Model: ‘Stock Synthesis’ (Richard Methot, NOAA) Fully integrated, forward-projecting, length and age-structured, highly flexible
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Length-at-ageWeight-at-length
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Season 1 (Jul-Dec)Season 2 (Jan-Jun)
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Season 1 (Jul-Dec) Season 2 (Jan-Jun)
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Low egg density (P 0 ); Spawning fraction ~10% (≤avg); Females slightly larger; SSB total = 105,220 mt; SSB female = 58,447 mt (0.42); Lowest DEPM biomass estimate since mid-1990s
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DEPM (female SSB) q = 0.1715 TEP (total SSB) q = 0.4568
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SS model tuned prior to inclusion of aerial est.; Catchability fixed to q=1; Length comp fit with dome-shaped selectivity; Selectivity assumptions not explored during STAR, but inconsistent with PNW fishery selectivity which is fit to asymptotic shape 173,390 mt (0.4)1,236,910 mt (0.9)
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537,173 mt
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Independent peer-review (NMFS and PFMC): Stock Assessment Review Panel (4-5 scientists) Scientific and Statistical Committee (~16 scientists) CPS Management Team (agency scientists) CPS Advisory Subpanel (fishing industry & 1 NGO rep) Management action: Pacific Fishery Management Council (PFMC) ▪ adopt assessment; apply harvest formula; allocate by season/sector NMFS Southwest Region (SWR) ▪ Proposed and final regulations published in Federal Register Catch monitoring and Enforcement ▪ (CDFG, ODFW, WDFW, NOAA) Season closure (NMFS-SWR)
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Stock biomass (age 1+, mt)Cutoff (mt) Harvest Fraction U.S. Distribution U.S. Harvest for 2011 (mt) 537,173150,0000.150.8750,526 HG 2010 = (BIOMASS 2009 – CUTOFF) FRACTION DISTRIBUTION To determine an appropriate (sustainable) FRACTION value: F MSY = 0.248649805(T 2 )−8.190043975(T)+67.4558326 where T ( o C) is the running average sea-surface temperature at Scripps Pier during the three preceding seasons (July-June), and exploitation FRACTION is bounded between 5% and 15%. Maximum catch allowed = 200,000 mt
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Mean three- season SST (°C) at Scripps Equilibrium spawning biomass (mt) Maximum sustained yield (MSY) Spawning biomass at MSY (B MSY )F MSY (%) 16.5700,0009274,0000.04 17.02,700,000156,0001,272,0000.16 17.3>4,000,000346,0001,819,0000.26 The spawner-recruit model was used to estimate changes in deterministic maximum sustained yield (MSY) reference points due to changes in environmental conditions associated with three-season SST at SIO, with 16.5-17.3 ° C being the inter-quartile SST range since 1916:
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Sardine will continue to: have rapid fluctuations in abundance/distribution; be utilized by predators, including humans. Researchers and managers will: have lagged response to changes in the resource; depend on labor-intensive data collection and time series; require more funding to ‘do it right’ Approach: minimize risk through conservative harvest policies; design surveys & methods applicable to all CPS; strive for international management agreements
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