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E. Long (1994)
Magnitude and extent of sediment toxicity in Tampa Bay, Florida
L. Doyle, E. Vleet, W. Sackett, N. Blake, G. Brooks (1985)
Hydrocarbon Levels in Tampa Bay Final Report
Namrata Sarda, G. Burton (1995)
Ammonia variation in sediments : spatial, temporal and method-related effectsEnvironmental Toxicology and Chemistry, 14
T. Pearson, R. Rosenberg (1978)
Macrobenthic succession in relation to organic enrichment and pollution of the marine environment, 16
E. Long, D. Macdonald, Charles Cairncross (1991)
Status and trends in toxicants and the potential for their biological effects in Tampa Bay, Florida
C. Krone, Donald Brown, D. Burrows, R. Bogar, S. Chan, U. Varanasi (1989)
A method for analysis of butyltin species and measurement of butyltins in sediment and English sole livers from Puget SoundMarine Environmental Research, 27
E. Long, D. Macdonald, S. Smith, Fred Calder (1995)
Incidence of adverse biological effects within ranges of chemical concentrations in marine and estuarine sedimentsEnvironmental Management, 19
R. Swartz, F. Cole, J. Lamberson, S. Ferraro, D. Schults, Wa DeBen, H. Lee, R. Ozretich (1994)
Sediment toxicity, contamination and amphipod abundance at a DDT‐ and dieldrin‐contaminated site in San Francisco BayEnvironmental Toxicology and Chemistry, 13
Ralph Smith (1993)
Determination of mercury in environmental samples by isotope dilution/ICPMSAnalytical Chemistry, 65
Rhoads Rhoads, McCall McCall, Yigst Yigst (1978)
Disturbance and production on the estuarine seafloorAm. Sci., 66
W. MacLEOD (1985)
Standard analytical procedures of the NOAA National Analytical Facility, 1985-1986 : extractable toxic organic compounds
Donald Macdonald, R. Carr, Fred Calder, Edward Long, C. Ingersoll (1996)
Development and evaluation of sediment quality guidelines for Florida coastal watersEcotoxicology, 5
G. Gaston (1985)
Effects of hypoxia on macrobenthos of the inner shelf off Cameron, LouisianaEstuarine Coastal and Shelf Science, 20
R. Carr, D. Chapman (1992)
Comparison of Solid-Phase and Pore-Water Approaches for Assessing the Quality of Marine and Estuarine SedimentsChemistry and Ecology, 7
Long Long, Carr Carr, Thursby Thursby, Wolfe Wolfe (1995)
Sediment toxicity in Tampa Bay: Incidence, severity, and spatial extentFla. Sci., 58
E. Long, R. Markel (1992)
An evaluation of the extent and magnitude of biological effects associated with chemical contaminants in San Francisco Bay, California
B. Morgan (1994)
Analysis of Quantal Response Data
R. Carr, Duane Chapman (1995)
Comparison of methods for conducting marine and estuarine sediment porewater toxicity tests—extraction, storage, and handling techniquesArchives of Environmental Contamination and Toxicology, 28
K. Takamura (1996)
Life cycle of the damselfly Calopteryx atrata in relation to pesticide contaminationEcotoxicology, 5
R. Carr, D. Chapman, C. Howard, J. Biedenbach (1996)
Sediment quality triad assessment survey of the Galveston Bay, Texas systemEcotoxicology, 5
M. Hamilton, R. Russo, R. Thurston (1977)
Trimmed Spearman-Karber Method for Estimating Median Lethal Concentrations in Toxicity BioassaysEnvironmental Science & Technology, 11
L. Doyle, G. Brooks, K. Fanning, E. Vleet, R. Byrne, N. Blake (1989)
A characterization of Tampa Bay sediments
A survey of the toxicity of sediments throughout the Tampa Bay estuary was performed as part of the National Oceanic and Atmospheric Administration's National Status and Trends Program. The objectives of the survey were to determine the spatial extent and severity of toxicity and to identify relationships between chemical contamination and toxicity. Three independent toxicity tests were performed: a 10‐d amphipod survival test of the whole sediments with Ampelisca abdita, a sea urchin fertilization test of sediment pore water with Arbacia punctulata, and a 5‐min Microtox® bioluminescence test with solvent extracts of the sediments. Seventy‐three percent of the 165 undiluted sediment pore‐water samples were significantly toxic relative to reference samples with the sea urchin fertilization test. In contrast, only 2% of the 165 samples were significantly toxic in the amphipod tests. The causes of toxicity were not determined. However, concentrations of numerous trace metals, pesticides, polychlorinated biphenyl (PCB) congeners, polycyclic aromatic hydrocarbons (PAHs), and ammonia were highly correlated with pore‐water toxicity. Concentrations of many substances, especially total dichlorodiphenyltrichloroethanes (DDTs), endrin, total PCBs, certain PAHs, lead, and zinc, occurred at concentrations in the toxic samples that equaled or exceeded concentrations that have been previously associated with sediment toxicity.
Environmental Toxicology and Chemistry – Oxford University Press
Published: Jul 1, 1996
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