National Status and Trends: Bioeffects Program - Sabine Lake, Texas Database
National Centers for Coastal Ocean Science
Data Set
(DS)
| ID: 39077
| Published / External
Created: 2017-04-05
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Last Modified: 2023-10-17
Project (PRJ) | ID: 37215
ID: 39077
Data Set (DS)
* Discovery• First Pass
» Metadata Rubric
Item Identification
* » Title | National Status and Trends: Bioeffects Program - Sabine Lake, Texas Database |
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Short Name | SAL_metadata |
* Status | Completed |
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• Publication Date | 2008-05-01 |
* » Abstract |
The toxicity of sediments in Sabine Lake, Texas, and adjoining Intracoastal Waterway canals was determined as part of bioeffects assessment studies managed by NOAA's National Status and Trends Program. The study area encompassed all of Sabine Lake, portions of the Sabine River, portions of the Neches River, portions of the Neches-Sabine Canal at the confluence of the two rivers, portions of Sabine Pass channel entrance, and an area in the Gulf of Mexico near the entrance channel. A stratified-random sampling design similar to those used in previous surveys conducted nationwide by NOAA was applied in Sabine Lake. The study area was subdivided into 22 irregular-shaped strata. Strata established within channels were further subdivided into three substrata to improve spatial coverage. Only one location each was sampled within each substratum, whereas three locations were sampled in each of the larger undivided strata.Surficial sediment samples were collected during August, 1995 from 66 randomly-chosen locations. Laboratory toxicity tests were performed as indicators of potential ecotoxicological effects in sediments. A battery of tests was performed to generate information from different phases (components) of the sediments. Tests were selected to represent a range in toxicological endpoints from acute to chronic sublethal responses. Toxicological tests were conducted to measure: reduced survival of adult amphipods exposed to solid-phase sediments; impaired fertilization success and abnormal morphological development in gametes and embryos, respectively, of sea urchins exposed to pore waters; reduced metabolic activity of a marine bioluminescent bacteria exposed to organic solvent extracts; and induction of a cytochrome P-450 reporter gene system in exposures to solvent extracts of the sediments.Chemical analyses were performed on portions of each sample to quantify the concentrations of trace metals, polynuclear aromatic hydrocarbons, and chlorinated organic compounds. Correlation analyses were conducted to determine the relationships between measures of toxicity and concentrations of potentially toxic substances in the samples.The full report is available online at http://www.ccma.nos.noaa.gov/about/coast/nsandt/musselmethods.aspx |
* Purpose |
Specific objectives of the study were to: (1) the incidence and degree of toxicity of sediments throughout the study area; (2) the spatial patterns (or gradients) in chemical contamination and toxicity, if any, throughout the study area; (3) the spatial extent of chemical contamination and toxicity; (4) the statistical relationships between measures of toxicity and concentrations of chemicals in the sediments. The dataset objective is to report information about chemical residues in sediment, sediment toxicity, and benthic infauna characteristics of the system. |
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Other Citation Details | |
• Supplemental Information |
PRINCIPAL INVESTIGATORS Edward Long, NOAA Ocean Service, National Status and Trends Program; Jawed Hameedi, NOAA Ocean Service, National Status and Trends Program; Michelle Harmon, NOAA Ocean Service, National Status and Trends Program; Gail Sloane, Florida Department of Environmental Protection; Scott Carr, US Geological Survey; James Biedenbach, US Geological Survey; Tom Johnson, US Geological Survey; John Scott, Science Applications International Corporation; Cornelia Mueller, Science Applications International Corporation; Jack Anderson, Columbia Analytical Services, Inc.; Terry Wade, Texas A and M University; Bobby Presley, Texas A and M University SAMPLE COLLECTION INVESTIGATORS Michelle Harmon, NOAA Ocean Service, National Status and Trends Program; Edward Long, NOAA Ocean Service, National Status and Trends Program SAMPLE PROCESSING INVESTIGATORS - Contaminant analyses: Organic and inorganic chemicals in sediment: Texas A and M University, Geochemical and Environmental Research Group, College Station, TX SAMPLE PROCESSING INVESTIGATORS - Benthos: Barry A. Vittor and Associates, Inc., 8060 Cottage Hill Road, Mobile, AL 36695 Report: http://www.nbi.noaa.gov/ SAMPLE PROCESSING INVESTIGATORS - Toxicity and Bioassays: MicroTox Assay: Tests were run by the US Geological Survey (Columbia Environmental Research Center, Marine Ecotoxicology Research Station, Texas A and M University, Corpus Christi, TX 78412), using extracts prepared by ABC Laboratories, Columbia, MO. Sea Urchin Assay: US Geological Survey, Columbia Environmental Research Center, Marine Ecotoxicology Research Station, Texas A and M University, Corpus Christi, TX 78412. Amphipod Assays: Science Applications International Corporation, Narragansett, RI. P450 Human Reporter Gene System: Columbia Analytical Services, Inc., Carlsbad, CA. |
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Keywords
Theme Keywords
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ISO 19115 Topic Category | biota |
ISO 19115 Topic Category | environment |
NOS Data Explorer Topic Category | Environmental Monitoring |
None | amphipod |
None | analytes |
None | benthic |
None | bioassay |
None | butyltins |
None | chemical |
None | contaminants |
None | date |
None | estuary |
None | infauna |
None | inorganic |
None | latitude |
None | location |
None | longitude |
None | Microtox |
None | NCCOS Research Data Type > Field Observation |
None | NCCOS Research Priority > Long-term Monitoring |
None | NCCOS Research Priority > Stressors, Impacts, Mitigation, and Restoration (SIMR) |
None | NCCOS Research Topic > Bioeffects/Toxicity |
None | NCCOS Research Topic > Chemical Contaminants |
None | NCCOS Research Topic > Monitoring |
None | organic |
None | organochlorines |
None | P450 human reporter gene system |
None | PAH |
None | parameter |
None | PCB |
None | pesticides |
None | polychlorinated biphenyls |
None | polynuclear aromatic hydrocarbons |
None | region |
None | sea urchin fertilization |
None | sediment |
None | Site |
None | state |
None | station |
None | toxicity |
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* Spatial Keywords
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None | Gulf of Mexico Coast |
None | NCCOS Research Location > Geographic Area > Coastal Ocean |
None | NCCOS Research Location > Region > Gulf of Mexico |
None | NCCOS Research Location > U.S. States and Territories > Texas |
None | Sabine Lake |
None | Texas |
None | United States |
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Physical Location
• » Organization | National Centers for Coastal Ocean Science |
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• » City | Silver Spring |
• » State/Province | MD |
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• » Location Description |
Data Set Information
* Data Set Scope Code | Data Set |
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• Maintenance Frequency | None Planned |
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» Data Presentation Form | |
• Entity Attribute Overview |
The dataset is composed of relational files each listed below. The "SITES" data file reports information regarding the planned sampling locations and the actual locations. The geographical information provided for a sampling site (the estuary stratum and site) is useful when interpreting the results of other data files. Link for the SITES data http://ccma.nos.noaa.gov/about/coast/nsandt/ba/Sites/SAL_Site.txt The "INDICATOR" data file reports the results of analyses for chemical/microbial analytes, toxicity endpoints, and benthic infauna indices. Link for the INDICATOR data dictionary http://ccma.nos.noaa.gov/about/coast/nsandt/download.aspx |
Entity Attribute Detail Citation |
NOAA National Status and Trends Program |
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Distribution Liability |
These data were prepared by an agency of the United States Government. Neither the United States Government nor any agency thereof, nor any of their employees, make any warranty, expressed or implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of any information, apparatus, product, or process disclosed in this report, or represents that its use would not infringe privately owned rights. Reference therein to any specific commercial product, process, or service by trade name, trademark, manufacturer, or otherwise does not necessarily constitute or imply its endorsement, recommendation, or favoring by the United States Government or any agency thereof. Any views and opinions of authors expressed herein do not necessarily state or reflect those of the United States Government or any agency thereof. Although all data have been used by NOAA, no warranty, expressed or implied, is made by NOAA as to the accuracy of the data and/or related materials. The act of distribution shall not constitute any such warranty, and no responsibility is assumed by NOAA in the use of these data or related materials. |
Data Set Credit |
Support Roles
* » Support Role | Data Steward |
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* » Date Effective From | 2008-05-01 |
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Position | NCCOS Scientific Data Coordinator |
Email Address | NCCOS.data@noaa.gov |
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* » Support Role | Distributor |
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* » Date Effective From | 2008-05-01 |
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Position | NCCOS Scientific Data Coordinator |
Email Address | NCCOS.data@noaa.gov |
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* » Support Role | Metadata Contact |
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* » Date Effective From | 2008-05-01 |
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Position | NCCOS Scientific Data Coordinator |
Email Address | NCCOS.data@noaa.gov |
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* » Support Role | Point of Contact |
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* » Date Effective From | 2008-05-01 |
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Email Address | NCCOS.data@noaa.gov |
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* » Support Role | Principal Investigator |
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* » Date Effective From | 2008-05-01 |
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Person | Piniak, Greg |
Email Address | greg.piniak@noaa.gov |
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Currentness Reference | Ground Condition |
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Extent Group 1 / Geographic Area 1
* » W° Bound | -94.08783 |
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* » E° Bound | -93.72916 |
* » N° Bound | 30.0917 |
* » S° Bound | 29.6167 |
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* » Start | 1995 |
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* » Security Class | Unclassified |
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• » Data Access Constraints |
None |
• Data Use Constraints |
NOAA requests that all individuals who download NOAA data acknowledge the source of these data in any reports, papers, or presentations. If you publish these data, please include a statement similar to: "Some or all of the data described in this article were produced by the "NOAA's Ocean Service through its National Status and Trends Program (NSandT)" |
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» Download URL | https://products.coastalscience.noaa.gov/collections/ltmonitoring/nsandt/default.aspx |
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» Download URL | https://products.coastalscience.noaa.gov/collections/ltmonitoring/nsandt/default.aspx |
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URL | https://products.coastalscience.noaa.gov/collections/ltmonitoring/nsandt/default.aspx |
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URL | https://coastalscience.noaa.gov/projects/detail?key=237 |
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Activity Time | 2016-09-21 |
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Activity Time | 2017-04-05 |
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Converted from Content Standard for Digital Geospatial Metadata (version FGDC-STD-001-1998) using 'fgdc_to_inport_xml.pl' script. Contact Tyler Christensen (NOS) for details. |
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MEASUREMENT QUALITY OBJECTIVESSite location - Field logistics were conducted aboard the NOAA Ship Ferrell and its launch. Vessel positioning and navigation were aided with a differential-corrected, Global Positioning System (GPS) unit and a compensated LORAN C unit. The two systems generally agreed well when both were operational. Coordinates are expressed in units to the nearest 0.0001 decimal degrees. An acceptable tolerance goal for siting was that the sampling location be established within 0.2nm (+/- 120ft) of the given coordinates. In the event the vessel could not navigate to the site (i.e., too shallow) or the bottom type was not appropriate (i.e., rock or shellfish bed) then the first alternate site was substituted. In the event the first alternate could not be sampled then the second alternate site was sampled. Organic and Inorganic Contaminants - The measurement quality objectives of the Sabine Lake Project specify accuracy and precision requirements of 30% for organic analytes and 15% for inorganic analytes in sediment samples. Water column measurements - Depth was recorded from the vessel's instrumentation to the nearest 0.1 foot.Benthic taxonomy-The minimum acceptable sorting efficiency was 95%. The minimum acceptable taxonomic efficiency was 95%. |
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Conceptual Consistency |
All chemical contaminant values have been rounded to three significant digits. To accommodate the wide range of values, all concentration values have been formatted to the thousandth unit (0.001). The actual precision is as listed below. Metals, variable ug/g; Butlytins 0.01 ng Sn/g; PAHs 0.1 ng/g; PCBs 0.01 ng/g; Pesticides 0.01 ng/g; DATA QUALITY ASSURANCE PROCEDURES Organic and Inorganic Contaminants - QA procedures include blanks, spiked samples, and standard reference materials with each batch of samples. Any batch failing to meet the specifications presented in Section 9.1 would be reanalyzed or rejected. Benthic taxonomy- At a minimum, 10 percent of all samples were resorted and recounted on a regular basis. Ten percent of samples were randomly selected and re-identified. A voucher collection composed of representative individuals of each species encountered in the project was accumulated and retained. |
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» If Delay is Longer than Latency of Automated Processing, Indicate Under What Authority Data Access is Delayed |
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Process Step Number | 1 |
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» Description |
DATA ACQUISITION/FIELD SAMPLING Sediment sampling procedures are described in the report available for download at http://ccma.nos.noaa.gov/about/coast/nsandt/download.aspx DATA PREPARATION AND SAMPLE PROCESSING Fields are arranged as follows: Sample Type; Field Holding; Lab Storage; Max Holding SEDIMENT 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 and Microtox); Wet ice (4C); Freezer (-20C); 1 year BENTHOS Taxonomy; 10% buffered formalin; Transfer to 70% ethanol; Indefinitely |
Process Date/Time | 1995-01-01 00:00:00 |
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Process Step Number | 2 |
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» Description |
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. |
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Process Step Number | 3 |
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» Description |
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. |
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Catalog Details
Catalog Item ID | 39077 |
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Metadata Record Created By | Tyler Christensen |
Metadata Record Created | 2017-04-05 12:50+0000 |
Metadata Record Last Modified By | SysAdmin InPortAdmin |
» Metadata Record Last Modified | 2023-10-17 16:12+0000 |
Metadata Record Published | 2017-04-17 |
Owner Org | NCCOS |
Metadata Publication Status | Published Externally |
Do Not Publish? | N |
Metadata Workflow State | Published / External |
Metadata Last Review Date | 2017-04-17 |
Metadata Review Frequency | 1 Year |
Metadata Next Review Date | 2018-04-17 |
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