%0 Journal Article %J Mar Pollut Bull %D 2019 %T A passive sampling model to predict PAHs in butter clams (Saxidomus giganteus), a traditional food source for Native American tribes of the Salish Sea Region. %A D James Minick %A Paulik, L Blair %A Richard P Scott %A Molly Kile %A Diana Rohlman %A Kim A Anderson %K Animals %K Bivalvia %K Consumer Product Safety %K Environmental Monitoring %K Food Contamination %K Humans %K Indians, North American %K Polycyclic Aromatic Hydrocarbons %K Shellfish %K Water Pollutants, Chemical %X

Native Americans face disproportionate exposures to environmental pollution through traditional subsistence practices including shellfish harvesting. In this study, the collection of butter clams (Saxidomus giganteus) was spatially and temporally paired with deployment of sediment pore water passive samplers at 20 locations in the Puget Sound region of the Salish Sea in the Pacific Northwest, USA, within adjudicated usual and accustomed tribal fishing grounds and stations. Clams and passive samplers were analyzed for 62 individual PAHs. A linear regression model was constructed to predict PAH concentrations in the edible fraction of butter clams from the freely dissolved fraction (C) in porewater. PAH concentrations can be predicted within a factor of 1.9 ± 0.2 on average from the freely dissolved PAH concentration in porewater using the following equation: PAHClam=4.1±0.1×PAHporewater This model offers a simplified, cost effective, and low impact approach to assess contaminant levels in butter clams which are an important traditional food.

%B Mar Pollut Bull %V 145 %P 28-35 %8 2019 Aug %G eng %R 10.1016/j.marpolbul.2019.05.020 %0 Journal Article %J Environ Toxicol Chem %D 2017 %T Diffusive flux of PAHs across sediment-water and water-air interfaces at urban superfund sites. %A D James Minick %A Kim A Anderson %K Air %K Cities %K Geologic Sediments %K Hazardous Waste Sites %K Oregon %K Polycyclic Aromatic Hydrocarbons %K Rivers %K Water %K Water Pollutants, Chemical %X

Superfund sites may be a source of polycyclic aromatic hydrocarbons (PAHs) to the surrounding environment. These sites can also act as PAH sinks from present-day anthropogenic activities, especially in urban locations. Understanding PAH transport across environmental compartments helps to define the relative contributions of these sources and is therefore important for informing remedial and management decisions. In the present study, paired passive samplers were co-deployed at sediment-water and water-air interfaces within the Portland Harbor Superfund Site and the McCormick and Baxter Superfund Site. These sites, located along the Willamette River (Portland, OR, USA), have PAH contamination from both legacy and modern sources. Diffusive flux calculations indicate that the Willamette River acts predominantly as a sink for low molecular weight PAHs from both the sediment and the air. The sediment was also predominantly a source of 4- and 5-ring PAHs to the river, and the river was a source of these same PAHs to the air, indicating that legacy pollution may be contributing to PAH exposure for residents of the Portland urban center. At the remediated McCormick and Baxter Superfund Site, flux measurements highlight locations within the sand and rock sediment cap where contaminant breakthrough is occurring. Environ Toxicol Chem 2017;36:2281-2289. © 2017 SETAC.

%B Environ Toxicol Chem %V 36 %P 2281-2289 %8 2017 09 %G eng %N 9 %R 10.1002/etc.3785 %0 Journal Article %J Environ Toxicol Chem %D 2012 %T An approach for calculating a confidence interval from a single aquatic sample for monitoring hydrophobic organic contaminants. %A Matzke, Melissa M %A Sarah E Allan %A Kim A Anderson %A Katrina M Waters %K Confidence Intervals %K Environmental Monitoring %K Hydrophobic and Hydrophilic Interactions %K Pilot Projects %K Polycyclic Hydrocarbons, Aromatic %K Water Pollutants, Chemical %K Water Pollution, Chemical %X

The use of passive sampling devices (PSDs) for monitoring hydrophobic organic contaminants in aquatic environments can entail logistical constraints that often limit a comprehensive statistical sampling plan, thus resulting in a restricted number of samples. The present study demonstrates an approach for using the results of a pilot study designed to estimate sampling variability, which in turn can be used as variance estimates for confidence intervals for future n = 1 PSD samples of the same aquatic system. Sets of three to five PSDs were deployed in the Portland Harbor Superfund site for three sampling periods over the course of two years. The PSD filters were extracted and, as a composite sample, analyzed for 33 polycyclic aromatic hydrocarbon compounds. The between-sample and within-sample variances were calculated to characterize sources of variability in the environment and sampling methodology. A method for calculating a statistically reliable and defensible confidence interval for the mean of a single aquatic passive sampler observation (i.e., n = 1) using an estimate of sample variance derived from a pilot study is presented. Coverage probabilities are explored over a range of variance values using a Monte Carlo simulation.

%B Environ Toxicol Chem %V 31 %P 2888-92 %8 12/2012 %G eng %N 12 %1 http://www.ncbi.nlm.nih.gov/pubmed/22997050?dopt=Abstract %R 10.1002/etc.2014 %0 Journal Article %J Environ Toxicol Chem %D 2012 %T Bridging environmental mixtures and toxic effects. %A Sarah E Allan %A Brian W Smith %A Robyn L Tanguay %A Kim A Anderson %K Biological Assay %K Environmental Monitoring %K Polycyclic Hydrocarbons, Aromatic %K Rivers %K Water Pollutants, Chemical %X

Biological Response Indicator Devices Gauging Environmental Stressors (BRIDGES) is a bioanalytical tool that combines passive sampling with the embryonic zebrafish developmental toxicity bioassay to provide a quantitative measure of the toxicity of bioavailable complex mixtures. Passive sampling devices (PSDs), which sequester and concentrate bioavailable organic contaminants from the environment, were deployed in the Willamette and Columbia Rivers within and outside of the Portland Harbor Superfund site in Portland, OR, USA. Six sampling events were conducted in the summer and fall of 2009 and 2010. Passive sampling device extracts were analyzed for polycyclic aromatic hydrocarbon (PAH) compounds and screened for 1,201 chemicals of concern using deconvolution-reporting software. The developmental toxicity of the extracts was analyzed using the embryonic zebrafish bioassay. The BRIDGES tool provided site-specific, temporally resolved information about environmental contaminant mixtures and their toxicity. Multivariate modeling approaches were applied to paired chemical and toxic effects data sets to help unravel chemistry-toxicity associations. Modeling elucidated spatial and temporal trends in PAH concentrations and the toxicity of the samples and identified a subset of PAH analytes that were the most highly correlated with observed toxicity. Although the present study highlights the complexity of discerning specific bioactive compounds in complex mixtures, it demonstrates methods for associating toxic effects with chemical characteristics of environmental samples.

%B Environ Toxicol Chem %V 31 %P 2877-87 %8 12/2012 %G eng %N 12 %1 http://www.ncbi.nlm.nih.gov/pubmed/23001962?dopt=Abstract %R 10.1002/etc.2018 %0 Journal Article %J Environ Sci Technol %D 2012 %T Impact of the deepwater horizon oil spill on bioavailable polycyclic aromatic hydrocarbons in Gulf of Mexico coastal waters. %A Sarah E Allan %A Brian W Smith %A Kim A Anderson %K Environmental Monitoring %K Gulf of Mexico %K Petroleum Pollution %K Polycyclic Hydrocarbons, Aromatic %K Water Pollutants, Chemical %X

An estimated 4.1 million barrels of oil and 2.1 million gallons of dispersants were released into the Gulf of Mexico during the Deepwater Horizon oil spill. There is a continued need for information about the impacts and long-term effects of the disaster on the Gulf of Mexico. The objectives of this study were to assess bioavailable polycyclic aromatic hydrocarbons (PAHs) in the coastal waters of four Gulf Coast states that were impacted by the spill. For over a year, beginning in May 2010, passive sampling devices were used to monitor the bioavailable concentration of PAHs. Prior to shoreline oiling, baseline data were obtained at all the study sites, allowing for direct before and after comparisons of PAH contamination. Significant increases in bioavailable PAHs were seen following the oil spill, however, preoiling levels were observed at all sites by March 2011. A return to elevated PAH concentrations, accompanied by a chemical fingerprint similar to that observed while the site was being impacted by the spill, was observed in Alabama in summer 2011. Chemical forensic modeling demonstrated that elevated PAH concentrations are associated with distinctive chemical profiles.

%B Environ Sci Technol %V 46 %P 2033-9 %8 02/2012 %G eng %N 4 %1 http://www.ncbi.nlm.nih.gov/pubmed/22321043?dopt=Abstract %R 10.1021/es202942q %0 Journal Article %J Chemosphere %D 2011 %T Estimating risk at a Superfund site using passive sampling devices as biological surrogates in human health risk models. %A Sarah E Allan %A Gregory J Sower %A Kim A Anderson %K Animals %K Environmental Monitoring %K Fishes %K Humans %K Models, Statistical %K Neoplasms %K Oregon %K Polycyclic Hydrocarbons, Aromatic %K Public Health %K Risk Assessment %K Rivers %K Time Factors %K Water Pollutants, Chemical %X

Passive sampling devices (PSDs) sequester the freely dissolved fraction of lipophilic contaminants, mimicking passive chemical uptake and accumulation by biomembranes and lipid tissues. Public Health Assessments that inform the public about health risks from exposure to contaminants through consumption of resident fish are generally based on tissue data, which can be difficult to obtain and requires destructive sampling. The purpose of this study is to apply PSD data in a Public Health Assessment to demonstrate that PSDs can be used as a biological surrogate to evaluate potential human health risks and elucidate spatio-temporal variations in risk. PSDs were used to measure polycyclic aromatic hydrocarbons (PAHs) in the Willamette River; upriver, downriver and within the Portland Harbor Superfund megasite for 3 years during wet and dry seasons. Based on an existing Public Health Assessment for this area, concentrations of PAHs in PSDs were substituted for fish tissue concentrations. PSD measured PAH concentrations captured the magnitude, range and variability of PAH concentrations reported for fish/shellfish from Portland Harbor. Using PSD results in place of fish data revealed an unacceptable risk level for cancer in all seasons but no unacceptable risk for non-cancer endpoints. Estimated cancer risk varied by several orders of magnitude based on season and location. Sites near coal tar contamination demonstrated the highest risk, particularly during the dry season and remediation activities. Incorporating PSD data into Public Health Assessments provides specific spatial and temporal contaminant exposure information that can assist public health professionals in evaluating human health risks.

%B Chemosphere %V 85 %P 920-7 %8 10/2011 %G eng %N 6 %1 http://www.ncbi.nlm.nih.gov/pubmed/21741671?dopt=Abstract %R 10.1016/j.chemosphere.2011.06.051 %0 Journal Article %J Chemosphere %D 2010 %T Exploiting lipid-free tubing passive samplers and embryonic zebrafish to link site specific contaminant mixtures to biological responses. %A Hillwalker, Wendy E %A Sarah E Allan %A Robyn L Tanguay %A Kim A Anderson %K Animals %K Embryo, Nonmammalian %K Embryonic Development %K Environmental Monitoring %K Lipids %K Rivers %K Water Pollutants, Chemical %K Zebrafish %X

The Biological Response Indicator Devices Gauging Environmental Stressors (BRIDGES) bio-analytical tool was developed in response to the need for a quantitative technology for assessing the toxicity of environmentally relevant contaminant mixtures. This tool combines passive samplers with the embryonic zebrafish model. When applied in an urban river it effectively linked site specific, bioavailable contaminant mixtures to multiple biological responses. Embryonic zebrafish exposed to extracts from lipid-free passive samplers that were deployed at five locations, within and outside of the Portland Harbor Superfund Megasite, displayed different responses. Six of the eighteen biological responses observed in 941 exposed zebrafish were significantly different between sites. This demonstrates the sensitivity of the bio-analytical tool for detecting spatially distinct toxicity in aquatic systems; bridging environmental exposure to biological response.

%B Chemosphere %V 79 %P 1-7 %8 03/2010 %G eng %N 1 %1 http://www.ncbi.nlm.nih.gov/pubmed/20172587?dopt=Abstract %R 10.1016/j.chemosphere.2010.02.001 %0 Journal Article %J Sci Total Environ %D 2006 %T Selenium accumulation patterns in lotic and lentic aquatic systems. %A Hillwalker, Wendy E %A Paul C Jepson %A Kim A Anderson %K Animals %K Carbon %K Ecosystem %K Environmental Monitoring %K Fishes %K Food Chain %K Geologic Sediments %K Invertebrates %K Rivers %K Selenium %K Time Factors %K Water Movements %K Water Pollutants, Chemical %X

Selenium (Se) concentrations in water column, sediment and insect compartments were measured over 3 years, in conjunction with selected physicochemical parameters, from lotic (flowing water) and lentic (standing water) sites within a single watershed in Utah, USA. There was evidence for steady-state concentrations of total [Se] in the insects, sediment and detritus, while there was no correlation between these concentrations and the concentration in surface water. Insect Se burden may therefore provide a more accurate measurement of food web accumulation risk than surface water Se concentration. The importance of organism-specific factors on Se transfer to higher trophic levels was revealed by the steady-state Se body burden within the same insect taxa occupying similar environmental compartments in both aquatic systems. Additionally, however, insect Se body burdens, even within similar taxa, were up to 7 times greater within the lentic compared with the lotic system, and site-specific biogeochemical processes are also likely to play a role in the pattern and level of Se accumulation between hydrogeochemically different aquatic systems occurring within the same watershed. Though a site-specific relationship was apparent between organic content and sediment and detritus Se concentrations, this factor did not account for insect Se accumulation differences between the lotic and lentic aquatic habitats. If carbon content is to be used as a site-specific predictor of Se accumulation potential, further investigations of it's influence on the food web accumulation rate of Se are required.

%B Sci Total Environ %V 366 %P 367-79 %8 07/2006 %G eng %N 1 %1 http://www.ncbi.nlm.nih.gov/pubmed/16487574?dopt=Abstract %R 10.1016/j.scitotenv.2005.12.024 %0 Journal Article %J Environ Sci Technol %D 2006 %T Temporal bioavailability of organochlorine pesticides and PCBs. %A D Sethajintanin %A Kim A Anderson %K Animals %K Biological Availability %K DDT %K Dichlorodiphenyl Dichloroethylene %K Dichlorodiphenyldichloroethane %K Environmental Pollutants %K Hydrocarbons, Chlorinated %K Insecticides %K Oregon %K Pesticides %K Polychlorinated Biphenyls %K Rivers %K Seasons %K Water Pollutants, Chemical %X

Because PCBs and organochlorine pesticides continue to be of global concern, studies that address information gaps, such as factors and influences of spatial and temporal effects on contaminant bioavailability, are valuable. The present study focused on the spatial and temporal distribution of bioavailable organochlorine pesticides and PCBs in surface waters of a contaminated harbor. Passive sampling devices were intensively deployed adjacent to various land uses on the Willamette River, OR, including Portland Harbor and McCormick and Baxter Superfund sites, during summer and fall, extreme conditions, 2001-2004. An increase of bioavailable sigmaDDTs (sum of p,p'-DDT, p,p'-DDD, and p,p'-DDE) concentrations was strongly affected bythe local historic production of DDTs and temporal changes in river conditions. The increase of bioavailable p,p'-DDD and high DDD/DDE ratios observed during summer indicates conditions favoring anaerobic reductive processes. In contrast to sigmaDDTs, the bioavailable concentrations and daily loads of dieldrin and PCBs increased during fall, especially during episodic rainstorms. On the basis of the PCB congener profiles, PCB inputs from urban runoff /sewer overflows were considered likely current sources of bioavailable PCB into the Harbor. The exceedence of the U.S. national and Oregon water quality criteria was a function of the temporal variability of each bioavailable contaminant. This illustrates the impacts associated with temporal changes of bioavailable organochlorine distributions in surface waters and the significance of considering realistic temporal, bioavailability, and site-specific conditions in risk assessment and water quality management.

%B Environ Sci Technol %V 40 %P 3689-95 %8 06/2006 %G eng %N 12 %1 http://www.ncbi.nlm.nih.gov/pubmed/16830528?dopt=Abstract %0 Journal Article %J Environ Sci Technol %D 2005 %T Environmental stresses and skeletal deformities in fish from the Willamette River, Oregon. %A Villeneuve, Daniel L %A Curtis, Lawrence R %A Jeffrey J Jenkins %A Warner, Kara E %A Tilton, Fred %A Kent, Michael L %A Watral, Virginia G %A Cunningham, Michael E %A Markle, Douglas F %A D Sethajintanin %A Krissanakriangkrai, Oraphin %A Johnson, Eugene R %A Grove, Robert %A Kim A Anderson %K Animals %K Benzofurans %K Bone and Bones %K Dioxins %K Female %K Fishes %K History, Ancient %K Hydrocarbons, Chlorinated %K Metals, Heavy %K Oocytes %K Oregon %K Organophosphorus Compounds %K Ovary %K Pesticides %K Polychlorinated Biphenyls %K Polycyclic Hydrocarbons, Aromatic %K Rivers %K Trematoda %K Trematode Infections %K Water Pollutants, Chemical %X

The Willamette River, one of 14 American Heritage Rivers, flows through the most densely populated and agriculturally productive region of Oregon. Previous biological monitoring of the Willamette River detected elevated frequencies of skeletal deformities in fish from certain areas of the lower (Newberg pool [NP], rivermile [RM] 26 - 55) and middle (Wheatland Ferry [WF], RM 72 - 74) river, relative to those in the upper river (Corvallis [CV], RM 125-138). The objective of this study was to determine the likely cause of these skeletal deformities. In 2002 and 2003, deformity loads in Willamette River fishes were 2-3 times greater at the NP and WF locations than at the CV location. There were some differences in water quality parameters between the NP and CV sites, but they did not readily explain the difference in deformity loads. Concentrations of bioavailable metals were below detection limits (0.6 - 1 microg/ L). Concentrations of bioavailable polychlorinated biphenyls (PCBs) and chlorinated pesticides were generally below 0.25 ng/L. Concentrations of bioavailable polycyclic aromatic hydrocarbons were generally less than 5 ng/L. Concentrations of most persistent organic pollutants were below detection limits in ovary/oocyte tissue samples and sediments, and those that were detected were not significantly different among sites. Bioassay of Willamette River water extracts provided no evidence that unidentified compounds or the complex mixture of compounds present in the extracts could induce skeletal deformities in cyprinid fish. However, metacercariae of a digenean trematode were directly associated with a large percentage of deformities detected in two Willamette River fishes, and similar deformities were reproduced in laboratoryfathead minnows exposed to cercariae extracted from Willamette River snails. Thus, the weight of evidence suggests that parasitic infection, not chemical contaminants, was the primary cause of skeletal deformities observed in Willamette River fish.

%B Environ Sci Technol %V 39 %P 3495-506 %8 05/2005 %G eng %N 10 %1 http://www.ncbi.nlm.nih.gov/pubmed/15954223?dopt=Abstract %0 Journal Article %J Environ Sci Technol %D 2005 %T Trace analysis of semivolatile organic compounds in large volume samples of snow, lake water, and groundwater. %A Usenko, Sascha %A Hageman, Kimberly J %A Schmedding, Dave W %A Staci M Simonich %K Chemistry Techniques, Analytical %K Environmental Monitoring %K Organic Chemicals %K Pesticides %K Snow %K Soil Pollutants %K Solubility %K Volatilization %K Water %K Water Pollutants, Chemical %X

An analytical method was developed for the trace analysis of a wide range of semivolatile organic compounds (SOCs) in 50-L high-elevation snow and lake water samples. The method was validated for 75 SOCs from seven different chemical classes (polycyclic aromatic hydrocarbons, organochlorine pesticides, amides, triazines, polychlorinated biphenyls, thiocarbamates, and phosphorothioates) that covered a wide range of physical-chemical properties including 7 orders of magnitude of octanol-water partition coefficient (log K(ow) = 1.4-8.3). The SOCs were extracted using a hydrophobically and hydrophilically modified divinylbenzene solid-phase extraction device (modified Speedisk). The average analyte recovery from 50 L of reverse osmosis water, using the modified Speedisk, was 99% with an average relative standard deviation of 4.8%. Snow samples were collected from the field, melted, and extracted using the modified Speedisk and a poly(tetrafluoroethylene) remote sample adapter in the laboratory. Lake water was sampled, filtered, and extracted in situ using an Infiltrex 100 fitted with a 1-microm glass fiber filter to trap particulate matter and the modified Speedisk to trap dissolved SOCs. The extracts were analyzed by gas chromatographic mass spectrometry with electron impact ionization and electron capture negative ionization using isotope dilution and selective ion monitoring. Estimated method detection limits for snow and lake water ranged from 0.2 to 125 pg/L and 0.5-400 pg/L, respectively. U.S. historic and current-use pesticides were identified and quantified in snow and lake water samples collected from Rocky Mountain National Park, CO. The application of the analytical method to the analysis of SOCs in large-volume groundwater samples is also shown.

%B Environ Sci Technol %V 39 %P 6006-15 %8 2005 Aug 15 %G eng %N 16 %R 10.1021/es0506511 %0 Journal Article %J Arch Environ Contam Toxicol %D 2004 %T Bioaccumulation profiles of chemical contaminants in fish from the lower Willamette River, Portland Harbor, Oregon. %A D Sethajintanin %A Johnson, Eugene R %A Loper, Bobby R %A Kim A Anderson %K Animals %K Environmental Monitoring %K Environmental Pollutants %K Fishes %K Hazardous Waste %K Insecticides %K Mercury %K Oregon %K Polychlorinated Biphenyls %K Reference Values %K Tissue Distribution %K Water Pollutants, Chemical %X

Twenty-five PCBs (polychlorinated biphenyls), 15 organochlorine (OC) pesticides, and mercury were determined in fish from the Willamette River in Oregon, including a Portland Harbor superfund site. Fish were collected during the summer of 2000 along a 20-mile stretch of the lower Willamette River. Concentrations of sumPCBs (sum of 25 individually determined PCB congeners) and sumDDTs (sum of p,p'-DDT, p,p'-DDE, and p,p'-DDD) in fish ranged from 14 to 530 and from 18 to 510 ng/g-wet weight, respectively. SumPCBs concentrations at all sites exceeded US EPA fish advisory's screening values. Hexachlorobiphenyl congener 153 was the most abundant of the PCBs detected and p,p'-DDE was the most abundant OC pesticide detected. Low levels of dieldrin were detected in fish at all sites with the highest concentration at the superfund site (4.6 ng/g-wet weight), while other OC pesticides tested were near or below detection limits (approximately 2 ng/g). In general, organic chemical contaminant concentrations were highest in fish from the superfund site and were lower further upriver. Smallmouth bass had the highest levels of OC compounds of three fish species examined. They also had the largest site-to-site variations whereas black crappie had little variation throughout the study area. Mercury levels in fish ranged from 13 to 520 ng/g. Historical fish residue data are limited from the Portland Harbor superfund site, what data is available is over a decade old, generally consisted of only a few fish (< or = 3) and analyses quantified only a few PCB congeners (< 3).

%B Arch Environ Contam Toxicol %V 46 %P 114-23 %8 01/2004 %G eng %N 1 %1 http://www.ncbi.nlm.nih.gov/pubmed/15025171?dopt=Abstract %0 Journal Article %J J AOAC Int %D 2001 %T Bioavailable organochlorine pesticides in a semi-arid region of eastern Oregon, USA, as determined by gas chromatography with electron-capture detection. %A Kim A Anderson %A Johnson, Eugene R %K Biological Availability %K Chromatography, Gas %K Chromatography, Gel %K Data Interpretation, Statistical %K Hydrocarbons, Chlorinated %K Insecticides %K Oregon %K Pesticide Residues %K Quality Control %K Time Factors %K Water Pollutants, Chemical %X

A group of dissolved-bioavailable organochlorine (OC) pesticides and inorganic anions in water and total OC pesticides in sediments were measured in the Malheur Watershed, a semi-arid region in the western United States, over a 2-year period. OC pesticide levels were compared with those from a 1990 study of the lower section of the river, the most recent data available. After calculating the dissolved fraction from the 1990, study it seems that DDD and dieldrin levels have decreased in the water by 50-70%, while DDE and DDT have changed little. Although banned nearly 30 years ago, DDT is still persistent throughout the Malheur River basin/watershed because it was found in all water samples tested. All of the OC pesticides tested during the 2-year study are well below the criterion continuous concentration for aquatic community exposure as defined by the U.S. Environmental Protection Agency (EPA). OC pesticides appear to be decreasing, however, at lower Ontario there remains a human health risk (EPA Human Health Risk Water Quality Criteria) for DDT, because this criteria includes daily consumption of water and fish from the river. Overall, although the upper forest watershed sites have lower OC pesticide concentrations, they represent an important contribution to the total DDT load to this watershed, a source not previously acknowledged. The large increase in DDT and sigmaDDT between the Ontario sites may indicate a possible historical point source of contamination or historical preferential deposition of contamination. Normalized sediment (sigmaDDT/organic carbon) strongly correlates with dissolved water sigmaDDT.

%B J AOAC Int %V 84 %P 1371-82 %8 09/2001 %G eng %N 5 %1 http://www.ncbi.nlm.nih.gov/pubmed/11601456?dopt=Abstract