Western Atlantic Bluefin Tuna: Median estimates of spawning biomass and recruitment (ICCAT)

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Atlantic Bluefin Tuna (Thunnus thynnus) is a large, highly migratory species which ranges throughout the Atlantic ocean However the vast majority of spawning occurs only in the Gulf of Mexico, and Mediterranean Sea Exploitation has been historically high, and stocks declined steeply in the 1970s (ICCAT) Western Atlantic Bluefin Tuna: Median estimates of spawning biomass and recruitment (ICCAT)

Current information on spawning habitat is partially obtained from larval distributions Annual spring (April June) plankton surveys targeting bluefin tuna larvae have been completed across the northern Gulf of Mexico since 1977 Sampling methods included bongo net tows, neuston net tows, and CTD casts for environmental data Loop Current Depth (m)

Bluefin larval abundance and distributions in the Gulf of Mexico have been highly variable spatially and temporally over the past 30 years 1983: Eastern distribution 2001: Western distribution Neuston tow Bongo tow Much of this variability can be accounted for by interannual variation in the strength and position of oceanographic features, such as the Loop Current, warm Loop Current eddies and low salinity river plumes A simple modeling approach was used to identify oceanographic habitats of low, and high, favorability for the collection of bluefin tuna larvae

Algorithms sequentially split the dataset into two groups using environmental variables Each split attempts to separate conditions which are favorable, and unfavorable, for larval bluefin tuna occurrence Each station sampled can be classified into one of the terminal nodes, which gives a probability of larval occurrence Classification tree model of favorable larval bluefin tuna habitat All samples N = 998 Date < 8 th May N =375 SSS < 36.42 N = 244 SSS > 36.42 N = 131 T200m < 21.0 N =902 Moon Phase < 0.51 N = 291 Date > 8 th May N =527 T200m > 21.0 N =96 Moon Phase > 0.51 N = 236 Moon > 0.26 N = 173 SST < 23.37 N = 23 SST > 23.37 N = 108 SST < 28.5 N = 276 SST > 28.5 N = 15 Plankton (log) < 1.64 N = 84 Plankton (log) > 1.64 N = 152 Longitude < 87.0 N = 49 Longitude > 87.0 N = 22 Longitude > 87.8 N = 70 SST < 25.6 N = 24 Longitude < 87.8 N = 82 SST > 25.6 N = 58 (Muhling et al., submitted)

A variety of variables defined the habitat model, however most bluefin tuna larvae were collected at surface temperatures from ~ 23.5 to 28.5 C, and cooler temperatures at 200m depth Although well adapted to survive cold water on feeding grounds, adult bluefin tuna are less well adapted to very warm waters (Blank et al., 2004) Adult bluefin tuna during spawning season in the Gulf of Mexico may prefer areas where surface temperatures are ~ 24 27 C (Teo et al., 2007). Water of ~25 C may best favor larval development (Miyashita et al., 2000) How might this species respond to climate change conditions? 1983 Sampled station Larval BFT Predicted favorable habitat for larval bluefin tuna in 1983, and larval catch locations

Climate-related effects on bluefin tuna spawning in the Gulf of Mexico are likely to be related to temperature and salinity changes, and physical oceanographic regimes To assess the climate-related changes in regional physical oceanographic features, we will use a high-resolution (10km) regional ocean model constrained with boundary conditions obtained from the IPCC models under three CO 2 emission scenarios The regional ocean model will be initialized and integrated for 1970 to 2000 using the IPCC models under the climate of the 20th century scenario. Then, the same model will be further integrated between 2000 and 2100 under the three CO 2 emission scenarios Once the model down-scaling has been completed, we will assess the effects of a range of climate change scenarios on bluefin tuna spawning patterns, and on the GOM ecosystem

Model downscaling has not yet been completed However, we used temperature predictions from a suite of IPCC models under scenario SRES A1B to make preliminary assessments on potential changes in spawning habitat We first ranked, and weighted, each model on its ability to hindcast temperature in each of the four zones of the Gulf of Mexico for the last 30 years of the 20 th century, compared to recorded observations Models were assessed on their ability to replicate the mean, and variance, of temperature at the surface, 100m depth and 200m depth for the months of April, May and June Model Model Ranking Model Weight ingv_echam4 1 0.88 bccr_bcm2_0 2 0.82 miroc3_2_medres 3 0.76 gfdl_cm2_1 4 0.76 iap_fgoals1_0_g 5 0.62 mri_cgcm2_3_2a 6 0.59 csiro_mk3_0 7 0.53 ncar_ccsm3_0 8 0.53 csiro_mk3_5 9 0.50 cnrm_cm3 10 0.38 cccma_cgcm3_1_t63 11 0.38 miub_echo_g 12 0.32 giss_aom 13 0.26 mpi_echam5 14 0.26 gfdl_cm2_0 15 0.24 giss_model_e_h 16 0.09 ncar_pcm1 17 0.06 giss_model_e_r 18 0.00 ipsl_cm4 19 0.00

May surface temperatures are predicted to increase between ~ 1.5 and 2.0 C 29 Northwest 29 Northeast 28 28 Temperature 27 26 Temperature 27 26 25 25 30 Southwest 31 Southeast 29 30 Temperature 28 27 Temperature 29 28 26 27 Weighted mean Maximum model Minimum model

May temperatures at 200m are predicted to increase ~ 1.5 C 20 19 Northwest 21 20 Northeast Temperature 18 17 Temperature 19 18 17 16 16 15 15 21 20 Southwest 24 23 Southeast Temperature 19 18 17 Temperature 22 21 16 20 15 19 Weighted mean Maximum model Minimum model

Predicting habitat extent The classification model was re-run to include only temperature at the surface, and at 200m depth The projected temperature conditions in the Gulf of Mexico from IPCC models were run through the classification model Changes in theoretically favorable habitat for larval bluefin tuna was then assessed Classification model constructed using only temperature All samples N = 1101 SST < 23.4 N =114 T200m < 21.3 N =1106 SST > 23.4 N =892 T200m > 21.3 N =95 T200m < 17.1 N = 699 T200m > 17.1 N = 193 SST < 28.8 N = 686 SST > 28.8 N = 13 SST < 25.6 N = 30 SST > 25.6 N = 163

April: Good habitat moves further north, as northern shelf is no longer prohibitively cool May: Good habitat across US EEZ is largely lost. Some habitat remains in the northwest June: Habitat is largely lost, across the Gulf of Mexico Projected changes in favorable habitat extent between the present, and 2085-2095 April May June

The proportion of grid points that were classified as likely to contain larvae showed a decrease over time, with decreases in May and June more pronounced than in April The probability of collecting larvae currently peaks at the end of May Although spawning tends to occur at temperatures above 24C, triggers for adult bluefin tuna spawning are not well known 0.6 Proportion of stations in favorable habitat 0.4 Larval catches with date (1982 2006) Proportion of favorable stations (/1) 0.5 0.4 0.3 0.2 0.1 April May June Proportion of positive stations 0.3 0.2 0.1 0 0 2 Apr 22 Apr 12 May 1 Jun 21 Jun 11 Jul Date

Distributions of larvae are ultimately determined by adult spawning locations. However, little is known about the preferred spawning habitat of adult bluefin tuna Tagging data suggest that areas with surface temperatures of ~ 24 27 C may be preferred (Teo et al., 2007). Temperatures of > 30 C are likely to be highly unfavorable Distributions of these ranges under projected temperature conditions were examined Projected changes in theoretical adult bluefin tuna habitat extent between the present, and 2085-2095 Adult habitat Colder than preferred Preferred Warmer than preferred Physiological limit April May June

A suite of climate models predict substantial temperature increases in the Gulf of Mexico through the 21 st century. Changes will occur at the surface, and at depth Spawning habitat for bluefin tuna may be reduced in size, and favorable conditions may occur earlier in the season Downscaling climate models will enable us to examine the projected behavior of mesoscale oceanographic features, such as the Loop Current, and eddies Future work will also examine potential effects of changes in salinity on spawning habitat Further work is needed on adult bluefin tuna spawning habitat preferences

NOAA/NMFS South East Fisheries Science Centre Early Life History Group Stock Assessment Division Pascagoula Laboratory Kim Williams Joanne Lyczkowski-Shultz David Hanisko Denice Drass Walter Ingram Rosentiel School of Marine and Atmospheric Science Andrew Bakun Fisheries and the Environment (FATE) University of South Florida Frank Muller-Karger Sennai Habtes ROFFS Ocean Fishing Forecasting Service Mitch Roffer Greg Gawlikowsi Matt Upton The University of Southern Mississippi Jim Franks Bruce Comyns NASA - Biodiversity and Ecological Forecasting National Research Council (NRC) Plankton Sorting and Identification Center, Szczecin, Poland Dr Bill Richards Img: V. Ticina