Nearshore Pink Shrimp Densities and Habitat Limitations in Biscayne Bay: A Saptiotemporal Analysis of 10 Years of Data

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Nearshore Pink Shrimp Densities and Habitat Limitations in Biscayne Bay: A Saptiotemporal Analysis of 10 Years of Data Ian C. Zink 1,2, Joan A. Browder 2, Diego Lirman 1, Joseph E. Serafy 1,2 GEER 2017 - Apr. 20 th, 2017 Coral Springs, FL 1 University of Miami, Coral Gables, FL 2 NOAA NMFS SEFSC, Miami, FL

Pink Shrimp: Farfantepenaeus duorarum Marsh Mangrove Seagrass Reef Pelagic Modified from Criales et al. 2007

Comprehensive Everglades Restoration Plan (CERP) Yesterday Today Tomorrow Biscayne Bay Salinity Interim Goal: reestablish common mesohaline to oligohaline conditions in mainland near shore zones, and reduce the frequency and rapidity of salinity fluctuations derived from pulse releases of fresh water from canals. RECOVER 2008 Biscayne Bay Pink Shrimp Abundance Interim Goal: increase juvenile pink shrimp density at peak abundance during the August-October period in optimal habitat (seagrass).2 m -2 in nearshore optimal habitat from Shoal Point to Turkey Point RECOVER 2005

Biscayne Bay Coastal Wetlands Project (BBCWP)

Biscayne IBBEAM Bay - Epifaunal EpifuanalMonitoring: Survey: 10 Yrs 10 Years+ (2005-2014) FIELD: Water Temperature ( C), Salinity (ppt), Water Depth (m), Sediment Depth (m), Species Specific Submerged Aquatic Vegetation (SAV) % Cover, SAV Canopy Height (cm), Epifaunal Community In Triplicate LABORATORY: Sorting, Identification, Carapace Length (CL: mm), Total Length (TL: mm), Sex, Database Compilation, Quality Control

Study Objectives: 1) Establish baseline juvenile pink shrimp density trends (pre-restoration) 2) Identify environmental factors that limit juvenile pink shrimp density 3) Quantify spatiotemporal trends in juvenile pink shrimp densities Analyses were conducted with α = 0.10

Results: Quantile Regression Temperature: Quadratic Salinity: Log-Linear Water Depth: Quadratic SAV % Cover: Linear

Results: Spatiotemporal Density and Habitat Trends Wet Avg. Density: 0.61 ± 1.06 m -2 Dry Season Avg. Density: 1.11 ± 1.49 m -2 Significant season and year effects (PERMANOVA) 12.2 % of observations >2 shrimp m -2 (n = 114, N = 940) 5% year-seasons (2006D) not sig. diff. from 2 shrimp m -2 14.9% of sites (n=7) not sig. diff. from 2 shrimp m -2

Results: Procrustean Analyses Shrimp Density Salinity Temperature 2005D Water Depth SAV % Cover 2014W m 2 X,Y r r 2 p value Temperature 0.713 0.536 0.287 < 0.0001 Salinity 0.772 0.478 0.228 < 0.0001 Water Depth 0.718 0.531 0.282 0.0019 SAV % Cover 0.819 0.425 0.181 0.0792 S Sampling Sites N

Results: Spatiotemporal Density Hierarchical Clusters

Results: Site Clusters Correlations

Results: Year-Season Clusters Correlations

Results: Year-Season Clusters Correlations

Conclusions and Implications: CERP Adaptive Management Pink shrimp density higher in dry season Present Interim Goal focus is wet season (i.e., late summer/early fall): change focus to dry season? Shrimp densities are presently below target (for the most part ) Canal Zone: salinity stability yielding increased in SAV cover: direct and indirect density improvements? Will mesohaline shoreline target improve pink shrimp abundance? Expansion of mesohaline conditions could negatively impact pink shrimp abundance if mesohaline <10 ppt but reductions of hypersalinity and extreme salinity variability should positively impact abundance Pink shrimp believed to exhibit (species-specific) seagrass association Pink shrimp limited by total SAV % cover, not individual seagrass spp.

Acknowledgements: PhD Committee: Diego Lirman, Joseph Serafy, Joan Browder, Jiangang Luo, David Die IBBEAM: Diego Lirman, Joan Browder, Sarah Bellmund, Joseph Serafy, Herve Jobert Present and Past Field Work: Jeremy Hall, Eric Buck, Tom Jackson, Gladys Liehr, Laura Petteway, Ana Griefen, Michelle Harangody, Robin Cascioli, Michelle La Martina, Katarzyna Kulpa, Stephanie Schopmeyer, Rolando Santos, Crawford Drury, Kelly Peebles, Ania Wachnicka, Dalton Hesley, Herve Jobert, and many volunteers! GIS Mapping Assistance: Katarzyna Kulpa Funding: USACE on behalf of the RECOVER group of the CERP Habitat Program at NOAA National Marine Fisheries Service Student Travel Fund and Graduate Career Development Fund, RSMAS