Trace organic contaminants, including toxaphene and trifluralin, in cotton field soils from Georgia and South Carolina, USA

Residues of organic contaminants--including toxaphene, DDT, trifluralin, hexachlorocyclohexanes, polychlorinated biphenyls, polycyclic aromatic hydrocarbons (PAHs) and nonylphenol--were measured in 32 cotton field soils collected from South Carolina and Georgia in 1999. Toxaphene, trifluralin, DDT and PAHs were the major contaminants found in these soils. The maximum concentration of toxaphene measured was 2,500 ng/g dry weight. Trifluralin was detected in all the soils at concentrations ranging from 1 to 548 ng/g dry weight. Pesticide residues were not proportional to soil organic carbon content, indicating that their concentrations were a reflection of application history and dissipation rates rather than air-soil equilibrium. Soil extracts were also subjected to in vitro bioassays to assess dioxinlike, estrogenic, and androgenic/glucocorticoid potencies. Relatively more polar fractions of the soils elicited estrogenic and androgenic/glucocorticoid activities, but the magnitude of response was much less than those found in coastal marine sediments from industrialized locations.

Butyltin exposure causes a rapid decrease in cyclic AMP levels in human lymphocytes

Natural killer (NK) cells are a subset of lymphocytes that are capable of killing tumor cells, virally infected cells, and antibody-coated cells. Butyltins (BTs) are used in a variety of consumer products and industrial applications. Tributyltin (TBT) is found in dairy products, meat, and fish. Dibutyltin (DBT) is found in plastic products, beverages stored in PVC pipes during manufacturing, and poultry products. BTs appear to increase the risk of cancer and viral infections in exposed individuals. This increased risk may be due in part to the inhibitory effect of these compounds on the cytotoxic function of NK cells. A 24-h exposure of NK cells to 200 nM TBT or 1.5 microM DBT decreased the cytotoxic function of NK cells by greater than 90%. Higher concentrations of TBT and DBT decreased the cytotoxic function of NK cells (by greater than 90%) after only a 1-h exposure. A 24-h exposure to either TBT or DBT decreased intracellular ATP levels by about 30%. However, as much as a 1-h exposure to either 300 nM TBT or 10 microM DBT caused no significant decrease in ATP levels. Thus, a decrease in ATP levels is a longer-term consequence of BT exposure. Intracellular levels of cAMP are decreased by as much as 80% within 5 min of exposure to either TBT or DBT. This rapid decline in cAMP levels in NK cells may be a consequence of BT exposure that is related to the rapid decrease in the cytotoxic function of NK cells.

Phenyltin inhibition of the cytotoxic function of human natural killer cells

Phenyltin (PT) contamination has been reported in water, sediment, and fish. However, the role of PT in weakening human immune function mediated through natural killer (NK) lymphocytes has not been elucidated. In this study, we report the effects of in vitro exposure to triphenyltin (TPT), diphenyltin (DPT), and monophenyltin (MPT) on the function of human NK cells. Exposure to TPT (1 microM, for 1 h) inhibited the tumor killing capacity of NK cells by 85%. Exposure of NK cells to DPT for 1 h (5 microM) and 24h (1.5 microM) reduced tumor lysis by greater than 90%. A 24-h exposure of NK cells to 5 microM MPT reduced tumor lysis by greater than 80%. Assays assessing the ability of NK cells to bind to tumor cells showed that a 24-h pretreatment with TPT, DPT, or MPT reduced NK cell binding to tumor cells by greater than 50%. The toxic potential of the PTs followed the order TPT > DPT > MPT. In comparison with butyltins (BTs), in vitro effects of PTs revealed that these compounds are relatively less toxic to NK cells than BTs. The results of this study provide evidence that phenyltin compounds are immunotoxic to human NK cells under in vitro experimental conditions.

Occurrence of butyltin residues in sediment and mussel tissues from the lower-most Tennessee River and Kentucky Lake, U.S.A

Surface sediments and mussel samples were collected at six selected locations in the lower-most Tennessee River and Kentucky Lake, U.S.A. and analyzed for butyltin (BT) derivatives. In sediments, total BT concentrations ranged from 6.8 to 356 ng g-1 dry wt. A wide range of concentrations in sediments suggested the presence of localized area of contamination. In mussel tissues, total BT concentrations varied between 26-107 ng g-1 dry wt. BT levels were comparable to the levels reported in mussels from some coastal sites as well as a few freshwater ecosystems. Leaching of tributyltin-containing anti-fouling paints in the ocean-going ships is a source of tributyltin, and discharge of municipal sewage and industrial waste waters in to this watershed may account for the presence of the monobutyltin and dibutyltin derivatives detected in the samples. To our knowledge, this is the first report on the butyltin concentrations in sediment and mussel tissues from the lower-most Tennessee River and Kentucky Lake.

Immunotoxicity of environmentally relevant concentrations of butyltins on human natural killer cells in vitro

The widespread environmental contamination, bio-accumulation, and toxic effects of butyltins (BTs) in wildlife is well documented, but the role of BTs in debilitating human immune function mediated through natural killer (NK) lymphocytes (a primary immune defense against tumor and virally infected cells) has not been described. In this study, we assessed the effects of in vitro exposure to a range of concentrations (encompassing environmentally relevant concentrations) of MBT, DBT, and TBT on human natural killer lymphocytes obtained from adult male and female donors. TBT inhibited the tumor-killing capacity of NK cells when the NK cells were pretreated in vitro at 200 nM for as little as 1 h. Inhibition of NK cytotoxic function ranged from 40 to greater than 90%. The toxic potential of butyltins followed the order of TBT > DBT > MBT. Conjugation assays revealed that after a 24-h exposure to TBT, there was about a 50% decrease in NK cell binding to tumor cells, indicating alteration of the NK cell receptors for tumor cells. Analysis of whole-blood samples for BTs revealed the presence of detectable concentrations of MBT, DBT, and TBT in all of the donors, indicating possible exposure of NK cells to BTs in the blood. The results of this study provide evidence that butyltin compounds significantly inhibit NK cell function and possible NK cell-mediated immunotoxic potential in humans.

Distribution of selected PCB congeners in the Babcock Street sewer district: a multimedia approach to identify PCB sources in combined sewer overflows (CSOs) discharging to the Buffalo River, New York

To evaluate sources of PCBs in combined sewer overflows (CSOs) to the Buffalo River, New York, combined sewage, sanitary flow, atmospheric wet and dry depositions, and street dust samples were collected from the Babcock Street sewer district and analyzed. Total PCB concentrations (sum of the PCB congeners quantitated) in particulate and dissolved phases of sanitary flow were 101-269 ng g-1 dry weight and <0.2 ng L-1, respectively. PCBs in the atmospheric dry and wet deposition samples were close to the method detection limit (a few pg/cm2 day-1 and <0.2 ng L-1, respectively). Average concentrations of total PCBs were noticeable in both dissolved (64 ng/l-1) and particulate (907 ng g-1 dry weight) phases in CSOs. Total PCBs in aggregates of street dust samples were between 53 and 1,700 ng g-1 dry weight, with the highest concentrations at sites nearest an industrial area that was previously remediated for PCB contamination. PCB congeners 153, 138, 101, 118, and 180 contributed >50% of the total PCB load in street dust samples. PCB congener composition in the particulate phase of CSOs reflects the congener pattern of the street dusts. In this context, it can be suggested that the local contaminated street dusts are one of the potential sources of PCBs in CSOs, which is a source of PCBs to the Buffalo River.

Temporal trends of persistent organochlorine residues in human adipose tissue from Japan, 1928-1985

Trend monitoring of organochlorine contaminants, viz. PCBs, DDTs, HCHs and CHLs, was carried out by using formalin-preserved adipose tissue of Japanese males from 1928 through 1985 for understanding the long-term trends in their contamination levels. The highest residual concentrations were observed during the periods of maximum production (or import) and usage of these compounds in Japan. Time trends of the contaminants varied with the usage pattern and their physico-chemical properties. Effectiveness of government regulations on the production and use of organochlorines was seen faster in the case of DDTs and HCHs, which showed a prominent declining trend in their residues, whereas PCB levels exhibited a continuing increase and maintained a steady state even after two decades of a ban on their production, indicating that the exposure to PCBs is still prevailing. Generally, in terms of the spatial view, unlike aquatic fauna from the point-source environment (aquatic ecosystem) humans in the non-point-source environment (terrestrial habitat) revealed a slower rate of reduction in organochlorine residue burdens.

Temporal trends of organochlorine residues in lizard goby Rhinogobius flumineus from the river Nagaragawa, Japan

PCBs, DDTs, HCHs (BHCs) and Chlordane compounds were analyzed in lizard goby, Rhinogobius flumineus collected from the River Nagaragawa, Japan during the period from 1968 to 1986. High residue levels of PCBs, DDTs and HCHs were found during late 1960s and early 1970s. From early 1970s, the residual levels started declining and the lowest levels were reached during the 1980s. In 1986, the residual concentrations of PCBs, DDTs and HCHs were 150, 6.2 and 2.2 ng/g which were 100, 100 and 210 times less than the highest values recorded during the years 1969, 1968 and 1970 respectively. Unlike these pollutants, residual concentrations of chlordane compounds have showed about a 5-fold increase from 5.4 ng/g in 1970 and reached the level of 25 ng/g in 1986.