DDT In Fish Research Articles

Bioaccumulation and human health risk assessment of DDT and its metabolites (DDTs) in yellowfin tuna (Thunnus albacares) and their prey from the South China Sea

DDTs were detected in yellowfin tuna (Thunnus albacares, 92.1–221.8 ng‧g−1 lipid weight) and their prey (54.9–93.5 ng‧g−1 lipid weight) from the South China Sea (SCS). DDT levels reported in this study were lower than those of the previous studies indicated the recent mitigation of DDT contamination in the SCS. Higher DDT levels were observed in fat abdominal muscle than lean dorsal muscle in adult yellowfin tuna. Meanwhile, DDT levels in adult yellowfin tuna were higher than the young ones. The composition profiles of DDT and its metabolites suggested DDTs in fish in the SCS were mainly derived from the historical use of technical DDTs. DDTs were biomagnified through food chains with the trophic magnification factor of 2.5. Risk assessment results indicated that dietary exposure to DDTs through lifetime fish consumption from the SCS would pose little cancer and noncarcinogenic risk to coastal residents.

Source apportionment of DDTs in maricultured fish: a modeling study in South China.

Fish is one of the most important nutrition sources for humanity. Contaminant exposure risk in fish farming will eventually deliver to the crowd through diet. China is the largest fish producing as well as exporting country, where mariculture plays an important role in fish production, especially in South China. Previous investigations indicated that a variety of compartments in farming areas of South China Sea were polluted by persistent organic pollutants, including DDT (dichlorodiphenyltrichloroethane) and its derivatives, some of which is designated as DDTs. In the present study, Hailing Bay and Daya Bay of Guangdong Province, China, were selected as the study sites and DDTs as the target compounds. A fish enrichment model was developed to assess the relative contributions of various pathways to the mass loadings of DDTs in the fish. Average concentrations (and concentration ranges) of DDTs in various environmental compartments of Hailing Bay and Daya Bay were included in modeling and analysis. Modeling results indicated that fish food and seawater contributed approximately the same proportions for the DDTs in maricultured fish. Antifouling paint was supposed to be the primary source of water DDTs in mariculture zone of Hailing Bayand Daya Bay, which contributed 69% of the total DDTs to the mariculture water. We suggest that in order to protect people from consuming highly contaminated maricuture zone fish, the most effective and feasible methods are using environment-friendly antifouling paint and applying less polluted fish food in the fish reproduction process.

The residual levels and health risks of hexachlorocyclohexanes (HCHs) and dichloro-diphenyl-trichloroethanes (DDTs) in the fish from Lake Baiyangdian, North China

The tissue and organs (muscle, brain, liver, and gill) of four species of freshwater fish from Lake Baiyangdian were analyzed for hexachlorocyclohexanes (HCHs) and dichloro-diphenyl-trichloroethanes (DDTs). The distribution characteristics were analyzed for HCHs and DDTs in various tissue and organs, which determined the health risks for humans. The research results showed that the wet weight content of all HCHs (∑HCHs) ranged from 0.05 ∼ 14.53ng g(-1), with a mean of 3.47ng g(-1). The wet weight content of all DDTs (∑DDTs) ranged from ND to 8.51ng g(-1), with a mean of 2.41ng g(-1). For the various species of fish, the residual level of ∑HCHs was relatively higher in chub and grass carp and lowest in snakehead. The residual level of ∑DDTs was the highest in snakehead and did not exhibit a significant variance in the other three species. For the various tissues and organs, the contents of HCHs and DDTs were both highest in the fish liver, second highest in the fish gill, and lowest in the fish brain and muscle. Among the four types of isomers, the residual level of γ-HCH was relatively higher, while the residual level of α-HCH was the lowest. The content of p,p'-DDE was significantly greater to other forms of DDT and its isomer. The residual levels of HCHs and DDTs in fish were both below the national standard. However, the carcinogenic risk from the HCHs in parts of the tissue and organs of four fish species in Lake Baiyangdian exceeded the screen value threshold set by USEPA.

Persistence of organochlorine chemical residues in fish from the Tombigbee River (Alabama, USA): Continuing risk to wildlife from a former DDT manufacturing facility

Organochlorine pesticide and total polychlorinated biphenyl (PCB) concentrations were measured in largemouth bass from the Tombigbee River near a former DDT manufacturing facility at McIntosh, Alabama. Evaluation of mean p, p′- and o, p′-DDT isomer concentrations and o, p′- versus p, p′-isomer proportions in McIntosh bass indicated that DDT is moving off site from the facility and into the Tombigbee River. Concentrations of p, p′-DDT isomers in McIntosh bass remained unchanged from 1974 to 2004 and were four times greater than contemporary concentrations from a national program. Total DDT in McIntosh bass exceeded dietary effect concentrations developed for bald eagle and osprey. Hexachlorobenzene, PCBs, and toxaphene concentrations in bass from McIntosh also exceeded thresholds to protect fish and piscivorous wildlife. Whereas concentrations of DDT and most other organochlorine chemicals in fish have generally declined in the U.S. since their ban, concentrations of DDT in fish from McIntosh remain elevated and represent a threat to wildlife.

Uptake, elimination, and biotransformation of aqueous and dietary DDT in marine fish

To understand the biokinetics and potential risks of p,p'-dichlorodiphenyltrichloroethane (DDT) and its metabolites, p,p'-dichlorodiphenyldichloroethylene (DDE) and p,p'-dichlorodiphenyldichloroethane (DDD), in fish, we exposed the black sea breams (Acanthopagrus schlegeli) to aqueous and dietary DDTs and then evaluated the bioaccumulation, distribution, biotransformation, and elimination of DDTs under controlled laboratory conditions. The fish rapidly accumulated DDTs from both routes of exposure, particularly the gills and viscera. Elimination of DDTs following aqueous or dietary uptake was slow, and biotranslocation of DDTs was significant during the exposure period but negligible during the depuration period. The biotransformation process was more significant following dietary exposure. During depuration, DDE was the major biotransformed product in the sea breams' carcasses while DDD was the major product in the gills and viscera. However, DDD had a significantly higher elimination rate than DDE and, subsequently, the fish retained more DDE in the body. Intraspecies variability in the elimination and biotransformation processes in fish was observed. We demonstrated that the route of exposure significantly affected the fate and biokinetics of DDTs in fish. The application of a dynamic model provided a tool for quantifying the elimination and biotransformation of DDT in fish. The present study provided insights into the bioaccumulation and biotransformation pathways of DDT in fish that could have important ecotoxicological implications.

DDT in fish from the Bulgarian region of the Black Sea

In spite of a worldwide reduction in the utilization of organochlorine pesticides (OCPs), they are still a problem for the aquatic environment and human health. The Black Sea is still being polluted with persistent chemicals, including OCPs. Aquatic organisms (sprat, scad, bluefish, shad, belted bonito, goby, and black mussel) with different feeding behaviours were sampled on a seasonal basis from the Bulgarian region of the Black Sea, and the concentrations of 13 OCP residues were determined. Although many of the OCPs were not detected in the samples, in all samples 1,1,1-trichloro-2,2-bis(4-chlorophenyl) ethane (DDT) was present mainly in the form of its metabolites 1,1-dichloro-2,2-bis(4-chlorophenyl) ethane (DDD) and 1,1-dichloro-2,2-bis(4-chlorophenyl) ethylene (DDE). Only about 12% of the total DDT was present as the parent compound pp-DDT, which suggests that it was not being used recently in the region. The total DDT concentrations were generally below 150 μg kg−1 fresh weight, but higher levels—up to 354 μg kg−1 fresh weight—were also measured for fish species with a high fat content. Between-species differences were observed, even when the concentrations were presented on a fat-level basis. DDT concentrations did not show any significant changes over the 2-yr sampling period. Fish sampled in the northern areas of the Bulgarian Black Sea coast seemed to contain higher DDT levels than those from the southern areas, suggesting a major (historical) influence of the Danube River. For permanent monitoring purposes, the utility of Black Sea gobies and scad should be considered.

Levels and distribution of organochlorines in fish from Indonesia

Organochlorines such as PCBs, DDTs, HCHs, CHLs and HCB were determined in pooled whole body homogenized of fish samples collected from five locations during 1998 and 2003 in order to understand their contamination status, temporal and spatial variation in Indonesian waters. PCBs and DDTs were the predominant contaminants with concentrations from 9.7 to 2700 ng/g lipid wt. and 12 to 1100 ng/g lipid wt., respectively, while HCHs (nd-24 ng/g lipid wt.), CHL compounds (nd-81 ng/g lipid wt.) and HCB (0.22–28 ng/g lipid wt.) were one to two orders of magnitude lower. Among the locations, PCBs and CHLs were higher in the samples from highly industrialized and thickly populated-locations, whereas OC pesticides such as DDTs and HCHs were particularly more prominent in suburban and rural areas. Levels of OCs observed in the waters surrounding Java Island were higher than those in Sumatra Island, implying significant use of OCs in highly populated Java Island. Concentrations of PCBs and DDTs in fish from Jakarta Bay were significantly lower in the samples collected in 2003 as compared to fish in 1998, indicating decreasing trend of these compounds in the Indonesian environment. Recent estimated average daily intakes of PCBs (0.81 μg/person/day), DDTs (1.1 μg/person/day), HCHs (0.018 μg/person/day), CHLs (0.010 μg/person/day) were much lower than the threshold values recommended by various agencies, suggesting minimal risk of this compound via fish ingestion to Indonesians.

Monitoring of persistent organic pollutants (POPs): examples from Lake Vättern, Sweden.

Lake Vättern in southern Sweden is a large oligotrophic lake with high surface to catchment area ratio (ca. 0.4) and a water residence time of 60 years. The lake combines sensitivity to atmospheric POP-pollution with general susceptibility for effects of POPs and slow concentration decline. Time series, from the 1960s until 1996, of PCBs and DDT in fish and data on TCDD in sediment of L. Vättern are presented and compared to other large lakes. The long time dataset of POPs in Arctic char (Salvelinus salvelinus) shows a significant annual decline of about 5% for PCBs and 13% for DDT. These rates are in agreement with other studies. Nutrients as well as biological effects and factors affecting the fate of POPs in oligotrophic lakes with long residence times are discussed. We propose that oligotrophic clear lakes are important ecosystems for monitoring POPs in biota.

Organochlorines in deep-sea fish from the Nordfjord

Hepatic levels of OCs (Organochlorines) were analysed in deep-sea fish from the Nordfjord in Norway. Levels of PCBs in the present study exceed background levels in fish from Norwegian water by a factor of 1.5 to 50, and DDTs by one to two orders of magnitude. DDTs in fish from the Nordfjord have previously been attributed to DDT use in fruit orchards. The present levels of DDTs show that the decline usually found in biota in Scandinavia since the 1970s is not found in the deep-sea fish in Nordfjord. There is no known local PCB source that can explain the elevated levels in the present study. This indicates that the fjord efficiently accumulates atmospheric contaminants. Chlordanes and HCB were less important, and HCHs were not detected.

Pesticides and food safety

This report reviews recent developments regarding the environmental, toxicological, and regulatory issues surrounding pesticide residues in food. Factors affecting the establishment of regulatory limits are discussed. Pesticides monitored by state and federal agencies are compiled and the need for improvements in analytical techniques and enforcement procedures in governmental monitoring programs is pointed out. Specific incidents of concern related to pesticides in food including EDB in grain and grain products, aldicarb in watermelon, demeton-methyl in wine, DDT in fish, S,S,S-tributylphosphorotrithioate in chili peppers, and daminozide in apples and processed apple products are described. The National Academy of Science's study on the Environmental Protection Agency's (EPA) method for setting tolerances for pesticide residues is discussed, especially the dietary cancer risk estimates from pesticides and the inconsistencies in regulating oncogenic pesticides in raw and processed foods existing under the Delaney Clause. The EPA's Tolerance Assessment System is identified to improve the quality of the tolerance establishment process. New California laws to ensure food safety include mandated activities in identifying the toxicological data gaps for pesticides and evaluating pesticide tolerances. Already initiated, tighter regulatory activities at both the federal and the state levels are expected to improve scientific information development, regulatory decisions, and public health protection.

Temperature and accumulation of DDT by sea mullet ( Mugil cephalus L.)

Accumulation of tech-DDT by the sea mullet Mugil cephalus L. was investigated at 15, 20, 25 and 30°C. Tissue residues of p, p′-DDT in fish increased with temperature reflecting an increase in metabolic rate. Metabolic degradation of p, p′-DDT to p, p′-DDD was also indicated. Rate of uptake of p, p′-DDT (mg kg −1 h −1) was not positively correlated with temperature and decreased with time at 15, 25 and 30°C. These results suggest that the uptake of DDT from water can be regulated by M. cephalus.

Residues of PCB's and DDT in the western Lake Superior ecosystem

Fish from western Lake Superior (1972-73) contained DDT and PCB residues at concentrations greater than o.1 ppm. The most predominant PCB's were those containing 3 to 6 chlorine atoms per molecule, and GLC data indicated that the mixtures were most like the commercial product Aroclor 1254(2). Other chlorinated contiminants identified by GC/MS analyses and occurring at concentrations less than 0.1 ppm were hexachlorobenzene (C6Cl6), chlordane, nonaclor, and dieldrin. Lindane, which has been previously reported in Lake Superior, was below the detection limit of approximately 0.01 ppm. The relationship between the size of lake trout and the concentration of total DDT in the fish was compared to measurements reported in previous studies. The comparison suggests that DDT residues have declined since 1968. The concentration of PCBs was estimated to be 0.8 ng/L in Lake Superior water and 0.1 ppm in large zooplankton. The apparent bioconcentration factor for PCBs in Lake Superior fish ranged from 10(5) to 10(6). The concentration of total DDT and PCBs in the larger Lake Superior fish exceeded the 5 ppm tolerance level established by the U.S. Food and Drug Administration for these chemicals in fish tbe used for human consumption.

System simulation to test environmental policy: DDT

An example has been given showing how system simulation can be used to arrive at conclusions of use to policymakers about the future consequences of current actions even in the case where complete information about the system is not available. The particular example studied is the general movement of DDT in the global eco‐system. The results suggest that, even if DDT usage were stabilized or decreased in 1972, the concentration of DDT in fish would continue to rise for another 2–50 years depending on the specific form of the DDT abatement policy.