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INCOSIFH PROJECT WORKING PACKAGE 5 NORTHERN GULF OF CALIFORNIA STUDY CASE Diego Lercari Objectives Implement a spatial ecosystem model (Ecospace) for the Northern Gulf of California Run simulations of actual MPA effectiveness on the conservation of vaquita and totoaba and for fisheries enhancement (catch & value) Examine effects of size and placement (new designs) on the effectiveness of MPAs for conservation and fisheries What is being modeled with Ecospace? NGC ecosystem and fisheries 34 FUNCTIONAL GROUPS 8 fleets – 3 ports Shrimp trawling (2) Artisanal shrimp (3) Fish gillnets (3) Explicitly: vaquita Phocoena sinus Totoaba macdonaldi 2 Shrimp species ENDANGERED SPECIES MPAs in the NGC Biosphere reserve (buffer zone & core zone) Vaquita refugee Shrimp coastal exclusion zone Compilation of Ecospace inputs ECOPATH MODEL Line coast for base map: coastline extractor 7 Habitat types Bathymetry : Carriquiry et al 2001 Sediment texture : Carriquiry et al 2001 Other Primary productivity estimations Alles, 2005 SEAWIFS Santamaria – Alvarez, 1995 Pegau et al., 2002 group’s distribution: HABITAT ASSIGNEMENT Rojas Bracho et al., 2006 (VAQUITA) Pedrin & Aleman, 1996 (FISH & SHRIMP) Actual MPAs designs Management programme BR Decree RB DOF 1993 Decree DOF 2005 Main areas of fleets operations DOF 1993 Cudney et al 1998 – fisherman's interviews Fishing restricted in the model applying very high fishing coast where fishing does not occurs Circulation patterns – advection fields Calderon et al., 2003 Marinone, 2003 Dispersion rates ? Feeding rates? Vulnerabilities? Those which reflect know distributions patterns? Question addressed Are the MPAs in the NGC effective to enhance the vaquita and totoaba populations? Which MPAs designs could optimize the vaquita and totoaba conservation? How this enhancement impacts in the catch and value obtained by the different fleets? Starting Scenarios Actual MPAs design No fishing inside the vaquita refugee No fishing inside the buffer zone No fishing inside the vaquita distribution area No MPAs Shrimp trawling inside bays Other designs…ecoseed? Model problems VAQUITA AND JUVENILES TOTOABA TEND TO DISAPPEAR!! •FISHERIES EFFECT? •PREY AVAILABILITY? •PREDATION INCREASE? DESPITE THIS … FACTS OR ARTIFACTS? MPAs SIMULATION RESULTS NO VAQUITA REFUGEE YES VAQUITA REFUGEE DISTRIBUTION PATTERNS UNCHANGED! ALL MPAs CLOSED ALL MPAs CLOSED + NO FISHING IN VAQUITA DISTR. GENERAL SIMULATED BIOMASS CHANGES JUVENILE TOTOABA 1.70E-05 1.68E-05 1.66E-05 VAQUITA 1.64E-05 1.32E-06 1.30E-06 1.28E-06 1.26E-06 1.24E-06 1.22E-06 1.20E-06 1.18E-06 1.16E-06 1.14E-06 1.62E-05 1.60E-05 1.58E-05 ACTUAL REFUGEE CLOSED VAQUITA AREA CLOSED VAQUITA AREA ADULT TOTOABA ACTUAL REFUGEE CLOSED VAQUITA AREA 1.03E-05 1.03E-05 1.03E-05 1.03E-05 1.02E-05 1.02E-05 1.02E-05 1.02E-05 1.02E-05 1.01E-05 ACTUAL REFUGEE