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                <gmx:Anchor xlink:href="https://www.fisheries.noaa.gov/inport/item/39258" xlink:actuate="onRequest" xlink:title="InPort Catalog ID">39258</gmx:Anchor>
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        <gco:CharacterString>In order to determine the current status of and to detect any long-term trends in the environmental quality of U.S. nearshore waters, NOAA initiated the National Status and Trends program in 1984 with its National Benthic Surveillance Project.  The primary objective of the Benthic Surveillance Project was to quantify concentrations of a suite of organic and inorganic contaminants in the livers of fish and surficial sediments from selected sites in the coastal and estuarine waters of the United States. In addition, the levels of certain indicators of the biological effects of these contaminants were measured.  Incidences of visible lesions, including fin erosion, have been noted and histopathological examinations of various tissues have been carried out.  Originally histopathological examinations determined the prevalence of any identifiable disease conditions in samples of liver, kidney, and gill tissue.In addition, the Benthic Surveillance Project tested fish livers from 30 locations in 1991 to identify the concentrations of DNA xenobiotic adducts.  DNA xenobiotic adducts are a bioindicator of exposure to genotoxic compounds.  Measurement of biological markers such as DNA xenobiotic adducts have been used to improve the evaluation of contaminant exposure and responses in indigenous fish, and thus reinforce the connection between exposure to toxic chemicals and the observed injuries.</gco:CharacterString>
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            <gco:CharacterString>Cape Fear River, Horseshoe Shaol</gco:CharacterString>
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            <gco:CharacterString>Charlotte Harbor, Cape Haze</gco:CharacterString>
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            <gco:CharacterString>Chesapeake Bay, Chester River</gco:CharacterString>
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            <gco:CharacterString>Chesapeake Bay, James River</gco:CharacterString>
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            <gco:CharacterString>Chesapeake Bay, Patuxent River</gco:CharacterString>
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            <gco:CharacterString>Choctawhatchee Bay, Choctawhatchee Bay</gco:CharacterString>
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            <gco:CharacterString>Dana Point Harbor, Outside</gco:CharacterString>
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            <gco:CharacterString>Delaware Bay, Cherry Island Range</gco:CharacterString>
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            <gco:CharacterString>Gulf of Mexico</gco:CharacterString>
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            <gco:CharacterString>Lower Laguna Madre, Long Island</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; California</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; Louisiana</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; Maine</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; Maryland</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; Massachusetts</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; Mississippi</gco:CharacterString>
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            <gco:CharacterString>NCCOS Research Location &gt; U.S. States and Territories &gt; New Jersey</gco:CharacterString>
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            <gco:CharacterString>The analytical instruments were calibrated by standard laboratory procedures including: constructing calibration curves, running blank and spiked quality control samples and analyzing standard reference materials.  To assess the reproducibility of results every tissue sample was analyzed in duplicate.</gco:CharacterString>
          </gmd:evaluationMethodDescription>
          <gmd:result gco:nilReason="missing" />
        </gmd:DQ_ConceptualConsistency>
      </gmd:report>
      <gmd:lineage>
        <gmd:LI_Lineage>
          <gmd:statement gco:nilReason="missing" />
          <gmd:processStep>
            <gmd:LI_ProcessStep>
              <gmd:description>
                <gco:CharacterString>The primary collection apparatus was Otter trawls.  Occasionally, fish were taken with hook and line, or with seine nets. These alternate collection methods were necessary because larger fish, such as older Atlantic croaker, were able to avoid an Otter trawl, or were found in untrawlable habitats such as shallow water, along marsh edges, and over oyster reefs.  Fish liver tissue samples were analyzed for DNA-xenobiotic adducts in liver via Phosphorus 32-postlabeling assay to indicate genotoxic exposure. The analysis of DNA adducts by Phosphorus 32-postlabeling is a multistep process involving a series of biochemical reactions.  First, DNA is hydrolyzed enzymatically to 3'monophosphates.  The digest is then enriched in xenobiotic-modified mononucleotides by the selective removal of normal nucleotides.  Following the enrichment step the adducted DNA is enzymatically labeled at the 5'-hydroxyl position with [Phosphorus 32] phosphate to form [5'-Phosphorus 32] deoxyribonucleoside 3',5'-bisphosphates.  Separation of the Phosphorus 32-labeled adducts is usually accomplished by two-dimensional, thin-layer chromatography (TLC) on polyethyleneimine (PEI)-modified cellulose sheets.  Autoradiography or storage phosphor imaging (Reichert et al., 1992) is then used to locate the radiolabeled adducts on the chromatogram (Reichert and French, 1994).The analytical instruments were calibrated by standard laboratory procedures including: constructing calibration curves, running blank and spiked quality control samples and analyzing standard reference materials.</gco:CharacterString>
              </gmd:description>
              <gmd:dateTime>
                <gco:DateTime>1991-01-01T00:00:00</gco:DateTime>
              </gmd:dateTime>
            </gmd:LI_ProcessStep>
          </gmd:processStep>
        </gmd:LI_Lineage>
      </gmd:lineage>
    </gmd:DQ_DataQuality>
  </gmd:dataQualityInfo>
</gmi:MI_Metadata>