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        <gmd:MD_TopicCategoryCode>biota</gmd:MD_TopicCategoryCode>
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        <gco:CharacterString>PRINCIPAL INVESTIGATORS Edward R. Long, National Oceanic and Atmospheric Administration; Gail M. Sloane, Florida Department of Environmental Protection; Geoffrey I. Scott, Brian Thompson, National Marine Fisheries Service; R. Scott Carr, James Biedenbach, U. S. Geological Survey; Terry L. Wade, Bobby J. Presley, Texas A &amp; M University; K. John Scott, Cornelia Mueller, Science Applications International Corporation; Geri Brecken-Fols, Barbara Albrecht, TRAC Laboratories, Inc.; Jack W. Anderson, Columbia Analytical Services, Inc.; G. Thomas Chandler, University of South Carolina SAMPLE COLLECTION INVESTIGATORSEdward Long, Michelle Harmon, Scott Frew, Heather Boswell, and DonnaTurgeon (NOAA, National Status and Trends Program); Richard Moravic and David Meyer (Florida Department of Environmental Protection); and Ramesh Peter Buch (Dade County Florida Department of Environmental Resources Management)SAMPLE PROCESSING INVESTIGATORS - Chemical analyses of organic and inorganic contaminants in sediment:Texas A &amp; M University, Geochemical and Environmental Research Group, College Station, TXSAMPLE PROCESSING INVESTIGATORS - Benthos:Barry A. Vittor &amp; Associates, Inc., 8060 Cottage Hill Road, Mobile, AL 36695Report: http://www.nbi.noaa.gov/products/reports/1996%20Biscayne%20Bay%20BCA%20Report.pdfSAMPLE PROCESSING INVESTIGATORS - Toxicity and Bioassays:MicroTox Assay: Tests were run by the National Marine Fisheries Service laboratory in Charleston, SC Sea Urchin Assay: US Geological Survey, Columbia Environmental Research Center, Marine Ecotoxicology Research Station, Texas A &amp; M University, Corpus Christi, TX 78412.Amphipod Assays: Science Applications International Corporation, Narragansett, RI. and TRAC Laboratories, Inc. in Pensacola, FLP450 Human Reporter Gene System: Columbia Analytical Services, Inc., Carlsbad, CA.Copepod life cycle assay :The University of South Carolina</gco:CharacterString>
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                <gco:CharacterString>DATA ACQUISITION/FIELD SAMPLINGSediment sampling procedures are described in the report available for download at http://www8.nos.noaa.gov/cit/nsandt/download/documents/BI1/BI1_report.pdfDATA PREPARATION AND SAMPLE PROCESSINGFields are arranged as follows:Sample Type; Field Holding; Lab Storage; Max HoldingSEDIMENT: Organic contaminants; Wet ice (4C); Freezer (-20C); 1 year;Inorganic contaminants; Wet ice (4C); Freezer (-20C); 1 year;Total organic Carbon; Wet ice (4C); Freezer (-20C); 1 year;Grain size; Wet ice (4C); Refrigerated (4C); 1 year;TOXICITY BIOASSAY:Whole sediment and porewater bioassays; Wet ice (4C); Refrigerated (4C); 2 weeks;Organic extract (P450 &amp; Microtox); Wet ice (4C); Freezer (-20C); 1 year;BENTHOS:Taxonomy; 10% buffered formalin; Transfer to 70% ethanol; Indefinitely;</gco:CharacterString>
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                <gco:CharacterString>Chemicals with similar structural properties were summed and reported as "Totals" in addition to their individual measured concentrations. The components of these totals are as follows:Total DDT = sum of concentrations of ortho and para forms of parent and metabolites 2,4'DDE; 4,4'DDE; 2,4'DDD; 4,4'DDD; 2,4'DDT and 4,4'DDT.Total Chlordane = sum of concentrations of four compounds alpha-chlordane, trans-nonachlor, heptachlor, heptachlorepoxide.Total Dieldrin = sum of concentrations of two compounds aldrin and dieldrin.Total Butyl tin = sum of concentrations of parent compound and metabolites monobutyltin, dibutyltin, tributyltin, tetrabutyltin [concentrations are in terms of tin].Total PCB = the sum of the concentrations of eighteen congeners: PCB8, PCB18, PCB28, PCB44, PCB52, PCB66, PCB101, PCB105, PCB118, PCB128, PCB138, PCB153, PCB170, PCB180, PCB187, PCB195, PCB206, and PCB209.Total low molecular weight (lmw) PAHs = sum of concentrations of twelve 2- and 3-ring PAH compounds: naphthalene, 2-methylnaphthalene, 1-methylnaphthalene, biphenyl, 2,6-dimethylnaphthalene, acenaphthene, acenaphthylene, 1,6,7-trimehtylnaphthalene, fluorine, phenanthrene, 1-methylphenanthrene, and anthracene.Total high molecular weight (hmw) PAHs = sum of concentrations of twelve 4-and more-ring PAH compounds: fluoranthene, pyrene, benz[a]anthracene, chrysene, benzo[b]fluorantene, benzo[k]fluoranthene, benzo[e]pyrene, benzo[a]pyrene, perylene, dibenzathracene, indeno[1,2,3-cd]pyrene, and benzo[ahi]perylene.Total PAH = low molecular weight PAHs plus high molecular weigh PAHs (sum of 24 PAH compound concentrations).Several numerical indices were chosen for analysis and interpretation of the macroinfaunal data. Infaunal abundance is reported as the total number of individuals per station and the total number of individuals per square meter (= density). Taxa richness is reported as the number of taxa represented in a given site location. Taxa diversity, which is often related to the ecological stability and environmental "quality" of the benthos, was estimated by the Shannon-Weiner Index (Shannon and Weaver, 1949).In order to quantify and compare the equitability in the fauna to the taxa diversity for a given area, Pielou's Evenness Index J' (Pielou, 1966) was calculated as J' = H'/lnS, where lnS = H'max, or the maximum possible diversity, when all taxa are represented by the same number of individuals; thus, J' = H' /H' max.</gco:CharacterString>
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                <gco:CharacterString>Project Related References:Pielou, E.C. 1966. The Measurement of Diversity in Different Types of Biological Collections. J. Theoretical Biology 13:131-144.Shannon, L.C. and W. Weaver. 1949. The Mathematical Theory of Communication. Univ. of Illinois Press, Urbana, Ill. 117 p.</gco:CharacterString>
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        <gco:CharacterString>This metadata was automatically generated from the Content Standard for Digital Geospatial Metadata standard (version FGDC-STD-001-1998) using the 2016-01-11 version of the FGDC RSE to ISO 19115-2 transform.</gco:CharacterString>
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        <gco:CharacterString>Translated from FGDC 2025-03-24T13:28:29.978Z</gco:CharacterString>
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