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                <gmx:Anchor xlink:href="https://ror.org/05ba43f71" xlink:actuate="onRequest">NOAA National Centers for Coastal Ocean Science (NCCOS)</gmx:Anchor>
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                <gmx:Anchor xlink:href="https://ror.org/05ba43f71" xlink:actuate="onRequest">NOAA National Centers for Coastal Ocean Science (NCCOS)</gmx:Anchor>
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                <gmx:Anchor xlink:href="https://ror.org/05ba43f71" xlink:actuate="onRequest">NOAA National Centers for Coastal Ocean Science (NCCOS)</gmx:Anchor>
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                <gmx:Anchor xlink:href="https://ror.org/05ba43f71" xlink:actuate="onRequest">NOAA National Centers for Coastal Ocean Science (NCCOS)</gmx:Anchor>
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        <gco:CharacterString>Marine sediment and water column samples were collected in nearshore habitats around the island of St. John, USVI during two sampling trips in late 2021 and early 2022 and following the landfall of two Category 5 hurricanes, Irma (landfall 2017-09-06) and Maria (landfall 2017-09-20). Marine sediment samples were analyzed for trace metals, organochlorine pesticides, polychlorinated biphenyl (PCB) compounds, polycyclic aromatic hydrocarbons (PAH), butyltins, pharmaceuticals and personal care products (PPCP) and biological (Clostridium perfringens) contaminants. Water column samples were filtered over solid phase extraction columns (Oasis HLB, Waters Corp.) and analyzed for pharmaceuticals and personal care products, including UV filters (sunscreens). We also collected seawater turbidity, pH, temperature, salinity and conductivity measurements at each embayment in 2021. Sediment interstitial water (porewater) was used in a sea urchin embryo development toxicity (SUETOX) assay to determine the relative benthic health at each site. Water samples for contaminant chemistry and sediment porewater for the SUETOX assay were collected between 2021-08-16 and 2021-08-21 while sediment samples for contaminant analyses were collected 2022-01-22 – 2022-03-07. Chemical analyses of the seawater and sediment samples occurred between 2022-03-30 and 2023-11-13. Total organic carbon and grain size analyses were also performed on the sediment samples from 2022, as those data can influence the results of each of those tests.</gco:CharacterString>
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        <gco:CharacterString>Funding Agency: US DOC; NOAA; NOS; National Centers for Coastal Ocean Science (NCCOS)</gco:CharacterString>
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        <gco:CharacterString>Funding Agency: National Park Service PMIS #244615 under Inter Agency Agreement #P20PG00222</gco:CharacterString>
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        <gco:CharacterString>Funding Agency: Coral Reef Conservation Program Project #1133</gco:CharacterString>
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        <gco:CharacterString>NCCOS Partners: NOAA NOS NCCOS, Stressor Detection and Impacts Division, Ecotoxicology Branch</gco:CharacterString>
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              <gmd:title>
                <gco:CharacterString>CoRIS Discovery Thesaurus</gco:CharacterString>
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          <gmd:keyword>
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          <gmd:keyword>
            <gco:CharacterString>EARTH SCIENCE &gt; Biosphere &gt; Zoology &gt; Corals &gt; Reef Monitoring and Assessment &gt; In Situ Chemical</gco:CharacterString>
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          <gmd:keyword>
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          </gmd:keyword>
          <gmd:type>
            <gmd:MD_KeywordTypeCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_KeywordTypeCode" codeListValue="theme">theme</gmd:MD_KeywordTypeCode>
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          <gmd:thesaurusName>
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                <gco:CharacterString>CoRIS Theme Thesaurus</gco:CharacterString>
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      <gmd:descriptiveKeywords>
        <gmd:MD_Keywords>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/59a203f9-f818-42a6-8d00-4301385cafc3" xlink:actuate="onRequest">EARTH SCIENCE &gt; AGRICULTURE &gt; AGRICULTURAL CHEMICALS &gt; PESTICIDES</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/fbec5145-79e6-4ed0-a804-6228aa6daba5" xlink:actuate="onRequest">EARTH SCIENCE &gt; BIOLOGICAL CLASSIFICATION</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/7437925f-7e10-4c96-af36-f3532ec24276" xlink:actuate="onRequest">EARTH SCIENCE &gt; BIOLOGICAL CLASSIFICATION &gt; BACTERIA/ARCHAEA</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/8e5371ad-4e70-48cf-9109-bfe995b7230c" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; MARINE ENVIRONMENT MONITORING &gt; MARINE SUBMERGED DEBRIS</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/d594fc9c-556b-4eb5-9ec3-0d2126ca9cd5" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; MARINE ENVIRONMENT MONITORING &gt; MARINE SURFACE ELEMENTS &gt; MARINE SURFACE DEBRIS</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/ce4b2c6e-3d69-4cf1-8416-c36e5f9b1b2c" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; MARINE SEDIMENTS</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/f8411549-a72d-44cd-9b7b-6953ec22f8da" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; MARINE SEDIMENTS &gt; SEDIMENT CHEMISTRY</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/6eb3919b-85ce-4988-8b78-9d0018fd8089" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/d3055f47-258e-4556-a885-54cd1fff4680" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; ORGANIC CARBON</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/4433600b-f323-458a-b295-352f939aab6b" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; PH</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/ed925b43-db83-4cbb-8347-3dc0081bb8f4" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN CHEMISTRY &gt; PIGMENTS</gmx:Anchor>
          </gmd:keyword>
          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/f0d83687-bc0a-4491-bb3e-697f1018da13" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN OPTICS &gt; TURBIDITY</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/46206e8c-8def-406f-9e62-da4e74633a58" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; OCEAN TEMPERATURE &gt; WATER TEMPERATURE</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/7041e51c-e2de-405a-b154-6016f624f54f" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; SALINITY/DENSITY &gt; CONDUCTIVITY</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/7e95b5fc-1d58-431a-af36-948b29fa870d" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; SALINITY/DENSITY &gt; SALINITY</gmx:Anchor>
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            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/ff13560a-161c-4ac9-b79c-4910936cf465" xlink:actuate="onRequest">EARTH SCIENCE &gt; OCEANS &gt; WATER QUALITY &gt; SEA SURFACE CONTAMINANTS</gmx:Anchor>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/dff4d4af-e1e0-4991-884b-a1c088a802b2" xlink:actuate="onRequest">EARTH SCIENCE &gt; SOLID EARTH &gt; GEOMORPHIC LANDFORMS/PROCESSES &gt; COASTAL LANDFORMS &gt; CORAL REEFS</gmx:Anchor>
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          <gmd:type>
            <gmd:MD_KeywordTypeCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_KeywordTypeCode" codeListValue="theme">theme</gmd:MD_KeywordTypeCode>
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              <gmd:title>
                <gco:CharacterString>Global Change Master Directory (GCMD) Science Keywords</gco:CharacterString>
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                    <gco:Date>2026</gco:Date>
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                          <gmd:linkage>
                            <gmd:URL>https://forum.earthdata.nasa.gov/app.php/tag/GCMD%2BKeywords</gmd:URL>
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                <gco:CharacterString>NCCOS Research Areas</gco:CharacterString>
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                <gco:CharacterString>NCCOS Research Data Types</gco:CharacterString>
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            <gco:CharacterString>Biological analyses</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Butyltins</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Chemical contaminant analyses</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Clostridium perfringens</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Coral reefs</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Grain size analysis and total carbon</gco:CharacterString>
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            <gco:CharacterString>Heavy metals</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Hydrocarbons</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Marine sediment</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Organochlorines (pesticides and polychlorinated biphenyl compounds, PCBs)</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Organotins</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Pesticides</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Pharmaceuticals and personal care products</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Pharmaceuticals and personal care products (PPCP)</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Pollution monitoring</gco:CharacterString>
          </gmd:keyword>
          <gmd:keyword>
            <gco:CharacterString>Sea urchin embryo development toxicity test</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Sediment toxicity</gco:CharacterString>
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          <gmd:keyword>
            <gco:CharacterString>Water quality analysis</gco:CharacterString>
          </gmd:keyword>
          <gmd:type>
            <gmd:MD_KeywordTypeCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_KeywordTypeCode" codeListValue="theme">theme</gmd:MD_KeywordTypeCode>
          </gmd:type>
          <gmd:thesaurusName>
            <gmd:CI_Citation>
              <gmd:title>
                <gco:CharacterString>Provider Keywords</gco:CharacterString>
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      </gmd:descriptiveKeywords>
      <gmd:descriptiveKeywords>
        <gmd:MD_Keywords>
          <gmd:keyword>
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          <gmd:keyword>
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          <gmd:keyword>
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          <gmd:keyword>
            <gmx:Anchor xlink:href="https://cmr.earthdata.nasa.gov/kms/concept/d5c27e06-b779-44e7-9e0f-579a00cedba0" xlink:actuate="onRequest">SEDIMENT CORERS &gt; SEDIMENT CORERS</gmx:Anchor>
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          <gmd:keyword>
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          <gmd:type>
            <gmd:MD_KeywordTypeCode codeList="https://data.noaa.gov/resources/iso19139/schema/resources/Codelist/gmxCodelists.xml#MD_KeywordTypeCode" codeListValue="instrument">instrument</gmd:MD_KeywordTypeCode>
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Report in preparation: May LA, McDonald EM, Toline CA, Kelley T, Pisarski E, Kothera R, Moffitt Z, Videtto E, Woodley CM. 2024. Post-hurricane assessment of chemical contaminants in nearshore waters and marine sediments at two St. John, USVI National Parks. NOAA Technical Memorandum NOS NCCOS XXX, Charleston, SC. xx pages.

Sampling design and field collections
Sediment and seawater samples were collected under National Park Service permit numbers VICR-2021-SCI-0006 and VIIS-2021-SCI-0023. Sampling for water column and marine sediments was conducted during two field excursions in consecutive years (2021 and 2022). The first sampling trip occurred between 8/16/2021 and 8/21/2021. At the time, all samples for analysis were collected, however marine sediment samples collected for contaminant analyses, frozen and shipped to the contractor laboratory in Texas arrived thawed. A subsequent sampling trip was planned to replace the sediment samples. Sampling for the replacement samples occurred 1/22/2022 – 3/7/2022. Sediment samples from the second sampling event arrived at the contract laboratory in good condition and were used for multiple analyses (trace metals, grain size, total carbon/total organic carbon (TC/TOC), organochlorines (OC), polycyclic aromatic hydrocarbons (PAH), UV filters, pharmaceuticals and personal care products (PPCP), and the biological indicator, Clostridium perfringens). Seawater samples for PPCP and UV filter analysis and marine sediment samples for the sea urchin embryo development toxicity (SUETOX) assay were collected from select sites/bays around the island (36) during the 2021 sampling trip. For embayments, these samples were collected in the center of the bay and nearshore (within ~10 ft of the intertidal zone, depth &lt;1.5 m). For four sites, only one sample was collected: VIIS dock, VIIS boat ramp, Turner Bay, Kiddel Bay. For four embayments on the south side of the island (Water Bay, Otter Bay, Princess Bay and Borck Bay), a second set of samples was collected by divers on SCUBA from a deeper location within the bay (~15-25 ft depth). These sites had been impacted by boat wrecks following hurricanes Irma and Maria in 2017. At all sites, sample handlers donned clean nitrile gloves prior to sample collection and wore no personal care products (sunscreens, etc).
Water sample collection and processing
Seawater samples (~ 4 L) were collected in precleaned amber glass bottles during the first (2021) field excursion and filtered over solid phase extraction (SPE) columns (Oasis HLB, 6 cc, 500 mg bed mass, Cat. #186000115, Waters Corp., Milford, MA) at the temporary field laboratory using a vacuum manifold and trap apparatus. Seawater was collected from each embayment at the central, nearshore point as described above, or near mid-bay for the few deeper sites. SPE columns were prepared per manufacturer’s instructions, sealed with Parafilm® and wrapped in clean aluminum foil prior to use. The seawater sample was acidified (addition of ~700 μL conc. HCl/ L seawater) and filtered by vacuum filtration over the SPE column. The filtered volume was recorded for each sample/site (range: 710 – 3400 mL). The volume filtered depended upon the particulate load in the seawater, which would inhibit flow. Following filtration (3-4 mL residual seawater remained in the column), the columns were sealed in Parafilm® wrapped in clean aluminum foil, labeled and frozen at -20 °C. Columns were placed in a cooler on ice and transported to the NOAA laboratory in Charleston, SC. Upon arrival, columns were stored at -40 °C until analysis.

Marine sediment collection and processing
Marine sediment samples for contaminant chemistry, trace metals, Clostridium perfringens and UV filter analyses were collected in precleaned, clear glass jars (125 -250 mL) on the 2022 sampling trip. Grain size sediment samples were also collected on the 2022 sampling trip. Samples designated for the sea urchin embryo development toxicity (SUETOX) test were collected on the 2021 sampling trip. Jars and tubes were placed in dive bags and sample collectors on snorkel and wearing clean nitrile gloves at each sampling site, opened the collection vessels at depth. Sediment was collected by coring the sediment with the open jar or tube, then resealing the vessel with the lid at depth. Samples were placed on ice and transported to the field laboratory. Jar lids were loosened and samples for chemical and biological contaminants analyses were frozen at (-40 °C) prior to shipment on ice to the analytical laboratory. Tubes of sediment for grain size analysis were held at 4 °C, then shipped to the analysis laboratory on ice (chilled, not frozen). Sediment for the SUETOX test was transported to the field laboratory at held at 4 °C until the interstitial water (porewater) was extracted (no longer than 48 h). Sediment porewater was siphoned from each sediment collection jar with a clean 10-mL glass pipet. Porewater was clarified by centrifugation (1200 x g for 20 min) and the supernatant was placed in a clean Teflon bag and sealed with a rod and clip combination. The porewater samples were frozen (-20 °C) and shipped on ice for analysis at the Charleston, SC NOAA laboratory. Samples were stored at -80 °C until analysis.
Water quality analysis
Water quality parameters were collected at each embayment around the island during the 2021 sampling trip. Conductivity, temperature and salinity were measured using a ThermoOrion multimeter at the central, nearshore site at each embayment or at the mid-bay area for deeper sites. Turbidity and pH were determined by collecting a 50 mL seawater sample in a clean 50 mL polypropylene tube at the central, nearshore location and transporting it at ambient temperature back to the field laboratory. Turbidity was measured on a well-mixed sample aliquot (15 mL) using a Hach 2100P turbidimeter per manufacturer’s instructions. The pH was measured on the remaining subsample of the 50 mL seawater aliquot using a portable pH meter.
Grain size analysis and total carbon
Grain size analysis was performed by Azimuth Geo Services using SOP GS 92-01, which incorporated a series of sieving and settling procedures and using a deflocculant compound to reduce clumping. Particle fractions were dried, weighed and the deflocculant mass was subtracted. A standard sediment was used to determine the precision of the sample sediment measurements. Grain sizes were reported as particle fractions according to the Wentworth scale. Total organic carbon analysis was performed using the Lloyd Khan method (1988) using high temperature combustion, followed by removal of residual moisture and mass determination.

Chemical contaminant analyses
Pharmaceuticals and personal care products The extraction and analysis of PPCPs in seawater and sediment followed a modified version of US Environmental Protection Agency method 1694 (USEPA, 2007) and are detailed in Bratkovics and Sapozhnikova (2011) and Apeti et al. (2018). Briefly, for seawater samples, samples were acidified to pH=2 with hydrochloric acid, spiked with isotopically labeled internal standards, then processed through hydrophilic-lipophilic balance (HLB) solid phase extraction (SPE) cartridges. Analytes of interest were eluted with methanol and acetone, and then concentrated to 4 mL. For sediment samples, 2 g of wet material, fortified with isotopically labeled internal standards, was extracted via sonication using a phosphate buffer/acetonitrile solution. Extracts were concentrated to remove the acetonitrile, stabilized with ethylenediaminetetraacetic acid (EDTA), processed through HLB SPE cartridges, eluted with methanol and acetone and concentrated to 4 mL. For both seawater and sediment extracts, 1 mL of the final extract was used for analysis using high performance liquid chromatography with triple quadrupole tandem mass spectrometery (Agilent 1100 HPLC/AB Sciex API 4000 MS/MS). Analysis was performed in both positive and negative electrospray ionization modes. The instrument was calibrated prior to running each analyte class (r2 ≥ 0.995). All data was analyzed using Analyst software.
Metals, hydrocarbons, organics analysis of marine sediments (TDI Brooks)
The marine sediment samples collected in St. John, USVI were analyzed for 261 organic and inorganic contaminants by TDI-Brooks, International. The contaminant screening process included assays for organochlorine pesticides (33 compounds), butyltins (4 compounds), polychlorinated biphenyls (PCBs, 157 congeners), polycyclic aromatic hydrocarbons (PAHs, 51 analytes), and trace metals (16 elements) using protocols from the NOAA National Status and Trends Program (Kimbrough et al., 2006; Kimbrough and Lauenstein, 2006). Sediments were also analyzed for total organic carbon (TOC) and grain size, since organic carbon is positively correlated to sediment contaminant loads and the silt and clay proportions of sediments may preferentially bind organic contaminants (Hassett et al., 1980; Shine and Wallace, 2000).
Biological analyses
Clostridium perfringens in marine sediments
Determination of the number of Clostridium perfringens colony forming units (CFU) in each marine sediment sample were performed by the TDI Brooks contract laboratory using a standard method (American Society for Testing and Materials D5916-96). Briefly, sediment samples (1-10 g, held at 4 °C) were diluted with 5 mL deionized water, vortexed, sonicated and the resulting water was transferred to a separate vessel. The sediment was mixed with fresh deionized water (3 x 10 mL and 1 x 5 mL) and shaken before decanting into the vessel (total of 40 mL extracted sediment). The sediment extract was filtered (0.45 μm) and the membrane filter was placed onto C. perfringens selective media (mCP) and incubated at 44.5 °C for 24 h. Presumptive yellow C. perfringens CFU were counted, then exposed to ammonium hydroxide for 10 s. CFU that turn from yellow to magenta were confirmed as C. perfringens.

Sea urchin embryo development toxicity test
Sediment porewater toxicity was determined according to a standard method (American Society for Testing and Materials E1563-98) and as detailed in May et al. (2022). Briefly, sediment porewater was thawed at 4 °C for 48 h. Porewater salinity, pH and ammonia nitrogen were measured and the salinity was adjusted to 36 ± 1 ppt using dry artificial sea salts (Tropic Marin, Wartenburg, Germany) or Type 1 water for each sample. Green sea urchin (Lytechinus variegatus) embryos (~0.5 h old) were exposed to 5 mL of each sediment porewater sample (~200 embryos per vial, n = 4) at 26 °C for 48 h under ambient lighting in a static test. Artificial seawater (ASW, 36 ppt, Tropic Marin) and 4 mg/L sodium dodecyl sulfate in ASW were used as assay negative and positive controls, respectively. Following exposure, embryo developmental stage was scored (target: 100 embryos per vial): 1) normally developed pluteus, 2) malformed pluteus, 3) underdeveloped embryo (prism to early pluteus stage), or 4) arrested development (cell-stage, blastula or gastrula). Percent normal development was calculated from the total number of embryos scored per replicate vial.</gco:CharacterString>
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Units: sediment particle fractions according to the Wentworth scale;
Observation Category: laboratory analysis;
Sampling Instrument: sieve and balance;
Sampling and Analyzing Method: Azimuth Geo Services SOP GS 92-01 (contract laboratory unpublished standard operating procedure);
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Units: percent of sediment mass;
Observation Category: laboratory analysis;
Sampling Instrument: sieve and balance;
Sampling and Analyzing Method: Lloyd Khan method (1988);
Data Quality Method: USEPA (1988). Determination of Total Organic Carbon in Sediment (Lloyd Khan Method). U.S. Environmental Protection Agency, Region II, Edison, New Jersey. Available at: http://www.nj.gov/dep/srp/guidance/rs/lloydkahn.pdf</gco:CharacterString>
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Units: µg/g dry weight of sediment;
Observation Category: laboratory analysis;
Sampling Instrument: ICP-MS (Inductively coupled plasma-mass spectrometry, atomic adsorption spectrometry (AAS), or atomic fluorescence spectrometry;
Sampling and Analyzing Method: NOAA National Status and Trends Protocol (Kimbrough, K. L., and G. G. Lauenstein (Editors). 2006. Major and Trace Element Analytical Methods of the National Status and Trends Program: 2000-2006. Silver Spring, MD. NOAA Technical Memorandum NOS NCCOS 29, 19 pp.);
Data Quality Method: For any trace metals that were detected in the method blank at greater than two times the minimum detectable limit (Fe and Pb), the values for each sample were multiplied by the sample mass, then the result was subtracted from the associated method blank and this value was normalized to the mass of the blank.  For PAH analytes naphthalene and biphenyl, some of the methods blanks greater than 2x the minimum detectable limit (likely due to contamination). For those two analytes, we subtracted the method blank from each analytical run and reported the revised value as the analyte concentration.</gco:CharacterString>
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Units: ng/g dry weight of sed;
Observation Category: laboratory analysis;
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Sampling and Analyzing Method: Kimbrough KL, Lauenstein GG, Johnson WE, editors. (2006). Organic Contaminant Analytical Methods of the National Status and Trends Program: Update 2000-2006. NOAA Technical Memorandum NOS NCCOS 30. 137 pp.;
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Units: ng/g dry weight of sediment;
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Sampling and Analyzing Method: Kimbrough KL, Lauenstein GG, Johnson WE, editors. (2006). Organic Contaminant Analytical Methods of the National Status and Trends Program: Update 2000-2006. NOAA Technical Memorandum NOS NCCOS 30. 137 pp.;
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Units: ng Sn/g dry weight of sediment;
Observation Category: laboratory analysis;
Sampling Instrument: gas chromatography/flame photometric detection;
Sampling and Analyzing Method: Kimbrough, K. L., G. G. Lauenstein and W. E. Johnson (Editors). 2006. Organic Contaminant Analytical Methods of the National Status and Trends Program: Update 2000-2006. NOAA Technical Memorandum NOS NCCOS 30. 137 pp.;
Data Quality Method: Kimbrough, K. L., G. G. Lauenstein and W. E. Johnson (Editors). 2006. Organic Contaminant Analytical Methods of the National Status and Trends Program: Update 2000-2006. NOAA Technical Memorandum NOS NCCOS 30. 137 pp.</gco:CharacterString>
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Units: ng/g dry weight of sediment or µg/L of seawater;
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Sampling Instrument: high performance liquid chromatography with triple quadrupole tandem mass spectrometry (Agilent 1100 HPLC/AB Sciex API 4000 MS/M;
Sampling and Analyzing Method: Modified version of US Environmental Protection Agency method 1694; Bratkovics S, Sapozhnikova Y. (2011). Determination of seven commonly used organic UV filters in fresh and saline waters by liquid chromatography-tandem mass spectrometry [10.1039/C1AY05390F]. Analytical Methods, 3(12): 2943-2950. https://doi.org/10.1039/C1AY05390F; Apeti D, Wirth E, Leight AK, Mason A, Pisarski, E. (2018). An Assessment of Contaminants of Emerging Concern in Chesapeake Bay, MD and Charleston Harbor, SC. NOAA Technical Memorandum NOS NCCOS 240. Silver Spring, MD. 104 pp. https://doi:10.25923/p4nc-7m71;
Data Quality Method: Modified version of US Environmental Protection Agency method 1694; Bratkovics S, Sapozhnikova Y. (2011). Determination of seven commonly used organic UV filters in fresh and saline waters by liquid chromatography-tandem mass spectrometry [10.1039/C1AY05390F]. Analytical Methods, 3(12): 2943-2950. https://doi.org/10.1039/C1AY05390F; Apeti D, Wirth E, Leight AK, Mason A, Pisarski, E. (2018). An Assessment of Contaminants of Emerging Concern in Chesapeake Bay, MD and Charleston Harbor, SC. NOAA Technical Memorandum NOS NCCOS 240. Silver Spring, MD. 104 pp. https://doi:10.25923/p4nc-7m71</gco:CharacterString>
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Units: percent normal embryos;
Observation Category: laboratory analysis;
Sampling Instrument: microscope for embryo evaluation;
Sampling and Analyzing Method: May LA, McDonald EM, Kothera RT, Toline CA, McDonough V, Moffitt ZJ, et al. (2022) Assessment of sediment porewater toxicity in Biscayne National Park with sea urchin (Lytechinus variegatus) embryos. PLoS ONE 17(12): e0278695. https://doi.org/10.1371/journal.pone.0278695;
Data Quality Method: May LA, McDonald EM, Kothera RT, Toline CA, McDonough V, Moffitt ZJ, et al. (2022) Assessment of sediment porewater toxicity in Biscayne National Park with sea urchin (Lytechinus variegatus) embryos. PLoS ONE 17(12): e0278695. https://doi.org/10.1371/journal.pone.0278695</gco:CharacterString>
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Units: Colony forming units (CFU);
Observation Category: laboratory analysis;
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Sampling and Analyzing Method: American Society for Testing and Materials protocol D5916-96.
Data Quality Method: American Society for Testing and Materials protocol D5916-96.</gco:CharacterString>
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