California’s Gold: Ensuring a profitable and sustainable sea urchin fishery Sarah Teck 14 April 2011 CINMS J. Maassen
Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz California’s Gold (5 th largest fishery) ~66% is harvested from here incabrain.com ~52% is landed here
Red urchin fishery landings have dropped Data: CDF&G ~ 52 ~11 million lbs
Red urchin ex-vessel prices have dropped ~$34 ~$6 million ~ 52 ~11 million lbs Data: CDF&G
Red urchin effort has changed over time Data: CDF&G
83 mm S CA; seasonal limit # days per week 76 min size limit Moratorium on permits 89 mm N CA; seasonal limit # days per week El Niño ↓ Japanese economy ↑ market competition
(Kalvass and Hendrix 1997)
Quality not only quantity and size as with all fished species, need to consider: population size individual size with urchins, also need to consider gonad quality, and how it varies across: seasons islands (or space)
P= R 2 =0.71 Value increases with gonad quality
% gonad of whole body weight Quality varies seasonally west central east
% gonad of whole body weight Quality varies seasonally west central east {
% gonad of whole body weight Quality varies seasonally west central east { }
% gonad of whole body weight Quality varies seasonally west central east { }
New strategy for fishing sea urchins To take advantage of the high quality roe at the time when and locations where it is available, fish more in winter and in places where roe is of the highest quality. to increase profits to urchin fishermen to benefit sea urchin populations
California’s Gold: Investigating the effect of management strategies on the red sea urchin fishery and population Sarah Teck, Sarah Rathbone, Sarah Valencia, Nick Shears, Scott Hamilton, Jenn Caselle, Steve Gaines Photo: CINMS Photo: J. Maassen
Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz California’s Gold (5 th largest fishery) ~66% is harvested from here ~52% is landed here
Gonad quality not just size with fished species need to wait for individuals and population growth with urchins also need to wait for seasonal gonad quality gonad weight / whole body weight OR gonad: somatic index (GSI) need to understand more detailed ecological information on temporal and spatial variability of gonad quality fisheries management
Outline III. Ecology What drives variability in red urchin populations over time and space? How do urchins and fishery profits respond to various management regimes? IV. Management How does gonad quality explain behavior of fishermen? II. Fishing behavior What drives variability in gonad quality (and price) over time? I.Fished quality
What drives variability in gonad quality (and price) over time? I.Fished quality Fishermen as optimal foragers multiple linear regression – seasonality – space – ecological drivers (kelp etc.) – environmental predictors – time or date? – water temp? – day length?
Santa Barbara Port sampling 400 boats surveyed 200 boats GSI Dec 2008-present location, effort, landings, GSI, price…
Port sampling fished sites
P= R 2 =0.71 price is highly correlated with GSI
GSI is highly variable
variation partially explained by space west central east
GSI varies seasonally west central east
GSI decreases during spawning west central east spawning
GSI increases during regrowth west central east spawninggonadal regrowth
Outline How does gonad quality explain behavior of fishermen? II. Fishing behavior What drives variability in gonad quality (and price) over time? I.Fished quality
How does gonad quality explain behavior of fishermen? II. Fishing behavior Model to predict fishing behavior (typically density is important, but in this fishery it is quality) areas with high GSI will have high effort and over time the GSI will be driven down by high effort—then fishermen move…
Outline III. Ecology What drives variability in red urchin populations over time and space? How does gonad quality explain behavior of fishermen? II. Fishing behavior What drives variability in gonad quality (and price) over time? I.Fished quality
Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz III. Ecology What drives variability in red urchin populations over time and space? Regression model to predict GSI Temperature, abiotic factors Reserve versus fished Community data
Steep temperature gradient (Blanchette et al 2007) Regression model to predict GSI Temperature, abiotic factors Reserve versus fished Community data
(Behrens & Lafferty 2004, Lafferty & Behrens 2005) Regression model to predict GSI Temperature, abiotic factors Reserve versus fished Community data Reserves may affect GSI
Purple sea urchin Strongylocentrotus purpuratus Compete with reds for kelp Currently no commercial fishery Smaller than reds (max ~80mm) Forms urchin barrens long-term monitoring sites deforested by purples ~33% of the time—mostly in the east Red sea urchin Strongylocentrotus franciscanus max ~150 mm Regression model to predict GSI Temperature, abiotic factors Reserve versus fished Community data Purples compete with reds
Partnership for Interdisciplinary Studies of Coastal Oceans (PISCO) ecosystem research and monitoring (fish and benthic subtidal sampling) 32 sites summer sites summer 2010
Santa Barbara San Miguel Santa Rosa Anacapa Santa Cruz GSI is higher in the west a a ab b bc cd d d bcd
Red urchin landings Purple urchin abundance 2007 Shears in prep, NPS—KFM, CDFG data
Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins Long-term ( ) E Santa Cruz and Anacapa Shears in prep, NPS—KFM data
Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins Long-term ( ) E Santa Cruz and Anacapa Shears in prep, NPS—KFM data
Long-term ( ) E Santa Cruz and Anacapa Shears in prep, NPS—KFM data Biomass (gm -2 ) Density (m -2 ) kelp purple urchins red urchins Red urchins have persistently higher biomass inside of the reserves. Reproductive output is ~4 times higher in kelp forests versus urchin barrens
manipulate ecology of a managed area to increase profits Purple urchin removals in historical red urchin fishing grounds? kelp restoration
Outline III. Ecology What drives variability in red urchin populations over time and space? How do urchins and fishery profits respond to various management regimes? IV. Management How does gonad quality explain behavior of fishermen? II. Fishing behavior What drives variability in gonad quality (and price) over time? I.Fished quality
How do urchins and fishery profits respond to various management regimes? IV. Management
Management goals time population size FoFo F reduced F historical today
Management goals time population size FoFo F reduced F historical today
Management goals time population size or fishery profit FoFo F seasonal quota F historical today
Profits may increase with TURFs fishermen race to harvest year-round vs. waiting for optimal quality How much more $ would they make, if they waited? delaying harvest through spatial property rights, TURF’s (Territorial Use Rights in Fisheries) fishermen’s profits
GSI equal across space (sometimes) west central east equal
GSI unequal across space (other times) west central east equalunequal E,C W,C
Management strategy evaluation (MSE) framework urchin population + urchin fishery “operating model” (ex: current actual status) Data collection (ex: size structure of population and catch with sampling error) Data assessment (ex: compare the mean size of the catch to a target size) Management strategy (ex: set a goal for the next year: if the mean size is < 90 mm, then reduce fishing pressure by 10,000 lbs) run simulation 100 times… and see what maximizes pop and fishery benefits… and evaluate multiple strategies
Assess management strategies Seasonal quota (TAC) Individual quotas Minimum size limits Maximum size limits Limited entry Area closures TURFs Combination of various strategies
Summary… future goals II. Ecology high kelp and low competitor densities will likely correlate with high red urchin GSI (what are the main drivers?) GSI explains much of the variability in red urchin fishery profits…but what else? I.Fishery a variable management regime over time and space will likely increase fishermen’ profits… (need to take into account the ecological & biological drivers) III. Management
THANKS TO… Commercial Fishermen of Santa Barbara: urchin divers, H. Liquornik, S. Mutz Lab assistants: M. Adams, A. Alger, G. Alongi, K. Asanion, M. Bogeberg, E. Casas, D. Cooper, M. Hunt, S. Meinhold, W. Meinhold, A. Poppenwimer, J. Roh, R. Shen, T. Shultz, A. Stroud, K. Treiberg, O. Turnross, A. Wong, PISCO dive team: K. Davis, A. Parsons-Field, E. Nickisch, J. Benson, P. Carlson, L. Hesla, E. Hessell, C. Lantz, JA Macfarlan, C. Pierre, D. Salazar, B. Selden, A. Soccodato, N. Spindel, S. Windell, EEMB/Bren: Gaines lab, Lenihan lab J. Lorda, L. Pecquerie
Current regulations Northern CA: – 89 mm minimum size limit – Jul closed and May-Sept 12 days per month Southern CA: – 83 mm minimum size limit – Apr-Oct 4 days a week open
Management evaluation framework (adaptive management) Population model + Fisheries model Alter fleet dynamics, then assess population and fisheries models Optimal management strategy (ex: set guidelines for a seasonal catch limit) (ex: how much more would biomass and profits increase with a seasonal catch limit?)
Australia’s Commonwealth Scientific and Industrial Research Organisation (CSIRO):
Australia’s Commonwealth Scientific and Industrial Research Organisation (CSIRO):