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At least 19 recordsLinked to original sources
PubMed1994

[Chlordane accumulations in adipose tissue of mice chronically exposed to chlordanes in indoor air].

Chlordane concentrations were analyzed in the adipose tissue of mice after prolonged inhalation of low levels of chlordanes in indoor air. After inhalation of 4.22-11.36 micrograms/m3 chlordanes (total of 5 compounds) in air for 1-6 months, high levels of chlordanes (4.19-11.63 ppm, total of 5 compounds and 2 metabolites) were found in the adipose tissue. Transnanochlor, which accounted for only 14% of the total chlordane in the inhaled air, showed a high percentage (50%) in the adipose tissue, followed by 2 metabolites, i.e., oxychlordane (25%) and heptachlorepoxide (22%). Little transchlordane, cis-chlordane, or heptachlor, which accounted for high percentages of the total chlordane inhaled, was detected in the adipose tissue. A low level of cis-nonachlor was observed in the adipose tissue, and its percentage was similar to that in the air (2%). The level of chlordane exposure and the adipose tissue chlordane concentration was closely correlated (r = 0.9077, p < 0.01), showed a dose-effect relationship. These findings suggest that chlordanes such as trans-nonachlor, oxychlordane, and heptachlorepoxide may accumulate in the adipose tissue of people living in an environment containing even low levels of chlordanes and that there is a risk from indoor air contamination by chlordanes.

Adipose Tissue↗
PubMed1979

Absorption and elimination of 14C-cis-chlordane and 14C-photo-cis-chlordane by goldfish Caraccius auratus.

Photo-cis-chlordane is accumulated by goldfish to a greater extent than cis-chlordane during a 16-hr exposure to 5 parts per billion (ppb) of each insecticide. However, the concentration of photo-cis-chlordane in vital organs (brain, nervous system, heart, liver, kidneys) during the 1-, 2-, and 4-day exposure is less than that of cis-chlordane. Only the swim bladder shows a much higher concentration of photo-cis-chlordane than cis-chlordane. These differences could hardly account for twice the higher toxicity of the former to goldfish. The transfer of pre-exposed fish to insecticide-free water resulted in faster elimination of photo-cis-chlordane than cis-chlordane; after five weeks, about 90% of the former was eliminated as compared with only 58% of the latter. High residues of both insecticides in the bile and the intestine during the initial period of exposure indicate a biliary route of elimination.

Absorption↗
PubMed2002

Chlordane enantiomers and temporal trends of chlordane isomers in arctic air.

A 14-year data set (1984-1998) for chlordane compounds in arctic airwas examined to discern temporal trends. trans-Chlordane (TC), cis-chlordane (CC), and trans-nonachlor (TN) declined significantly (p < 0.001-0.02), with apparent times for 50% reduction of 4.9-9.7 y. The isomer fraction of TC = (TC/(TC + CC) also declined significantly (p < 0.001 -0.014) over the same time period. The enantiomeric composition of TC and CC was determined in air samples collected at arctic stations in Canada (1993-1996), Russia (1994), and Finland (1998), and a temperate station on the Swedish west coast (1998). Enantiomer fractions, EF = (+)/[(+) + (-)], were significantly different from measured EFs of racemic standards (0.498-0.501) at all stations for TC (p < 0.001) and two stations for CC (p < 0.001 to <0.05). These observations suggest changing source composition of chlordane in arctic air, with a greater proportion of weathered residues in recent years, possibly derived from soils. Identification of nonracemic (mean EFs = 0.662-0.703) heptachlor exo-epoxide (HEPX) at the four air stations further exemplifies contributions of soil emissions to long-range transport of chlordane-related compounds.

Air Pollutants↗
PubMed1976

On effect of chlordane on the blood glucose and of glucose administration on the acute chlordane toxicity in Meriones hurrianae Jerdon, the indian desert gerbil.

The effect of 25, 50 and 75 mg/kg body wt. chlordane on the blood glucose level and of glucose administration in chlordane intoxicated Indian desert gerbils are investigated. Chlordane produces hyperglycemia and lowers the glucose tolerance indicating an impairment in the uptake and utilization of glucose in intoxicated gerbils. The possible reasons for these effects are discussed.

Animals↗
PubMed2004

Liquid chromatographic separation of the enantiomers of trans-chlordane, cis-chlordane, heptachlor, heptachlor epoxide and alpha-hexachlorocyclohexane with application to small-scale preparative separation.

Analytical high-performance liquid chromatographic separations of the individual enantiomers of five polychlorinated compounds were obtained on polysaccharide stereoselective HPLC columns. The enantiomers of the pesticides trans-chlordane, cis-chlordane and heptachlor were separated on CHIRALCEL OD using a hexane mobile phase. The enantiomers of the heptachlor metabolite, heptachlor epoxide, were separated on CHIRALPAK AD using a methanol mobile phase. The enantiomers of alpha-hexachlorocyclohexane (alpha-HCH), were separated on CHIRALCEL OJ using a hexane/2-propanol mobile phase. Similar chromatographic conditions using preparative columns were used to isolate approximately 250 mg of each of the individual enantiomers. The purified individual enantiomers have been submitted for testing of their endocrine disruptor (ED) activity.

Chlordan↗
PubMed1987

Direct suppression of cultured spleen cell responses by chlordane and the basis for differential effects on in vivo and in vitro immunocompetence.

Immunosuppression by gamma-chlordane was examined by the direct addition of chlordane to cultured spleen cells from untreated B6C3F1 mice. Both cell-mediated and humoral immune responses were markedly suppressed upon in vitro exposure. The mixed lymphocyte response and the proliferative response to both B- and T-cell mitogens were significantly suppressed at micromolar concentrations of chlordane. The antibody response to sheep erythrocytes (SRBC) was suppressed 90% at 10 microM chlordane. The kinetics of the SRBC response were not altered by chlordane. Addition of chlordane to the antibody cultures on various days indicated an effect at the early stages of the response. Previous studies with chlordane failed to demonstrate immunosuppression following in vivo exposure. The possibility that chlordane was metabolized in vivo to a less immunosuppressive form was studied by examining the effect of the major metabolite, oxychlordane, on the in vitro antibody response and by incubating splenocytes with chlordane and a liver S9 preparation prior to culture with SRBC. Oxychlordane was immunosuppressive by itself, and the activity of chlordane was unaltered in the co-culture experiments. The association of chlordane with serum components was evaluated in vitro in cultures of mouse bone-marrow cells (BMC). The chlordane-induced suppression of [3H]thymidine incorporation by BMC was reversed by the addition of mouse or human serum. In summary, chlordane produces marked suppression of in vitro immune responses via an apparent antiproliferative action. The failure of chlordane to produce in vivo immunosuppression may be related to extensive association of chlordane with serum components.

Animals↗
PubMedDate not supplied

Characterization of the pesticide chlordane in estuarine river sediments.

Sediments are increasingly recognized as both carrier and potential source of contaminants in aquatic environments. This study investigated the characteristics and spatial distribution of total chlordane and its three most abundant compounds, including alpha-chlordane, gamma-chlordane, and trans-nonachlor, in sediments from the Cedar and Ortega rivers, Florida, USA, using geographic information system (GIS)-based kriging analyses and field measurements. Kriging analysis showed that two areas, one from the Cedar River area and the other from the northern end of the Ortega River area, were contaminated. The maximum concentrations of total chlordane, gamma-chlordane, alpha-chlordane, and trans-nonachlor in the sediments were, respectively, 101.8, 20.1, 26.3, and 19.2 microg/kg. A plot of total organic carbon (TOC)-normalized chlordane concentrations showed that effects of grain size on sediment chlordane contamination were negligible. A principal axis analysis further revealed that a linear correlation existed between alpha-chlordane and total chlordane as well as between gamma-chlordane and total chlordane, whereas no correlation existed between trans-nonachlor and total chlordane. Comparison of total chlordane concentration with Florida Sediment Assessment Guidelines showed that the Cedar River and the northern end of the Ortega River had total chlordane concentrations above the probable effect level (4.79 microg/kg), which could pose a potential risk to aquatic life.

Chlordan↗
PubMed2004

Plant uptake and translocation of highly weathered, soil-bound technical chlordane residues: data from field and rhizotron studies.

It has been observed that plants are susceptible to uptake from soil and in planta transport of technical chlordane, in spite of its hydrophobicity and sequestration within the soil matrix due to weathering. Field and rhizotron studies were conducted with Cucurbitaceae planted in highly weathered, chlordane-contaminated soil to investigate details of soil-to-plant contaminant uptake. In the field-work, Cucurbita pepo L. (zucchini) was grown in soil at four levels of chlordane contamination: Clean (<limits of quantitation, 5 ng/g), low (average, 370 ng/g), medium (average, 1,951 ng/g), and high (average, 4,572 ng/g). The analysis of plant tissues (root, stem, leaf, and fruit) resulted in the detection of chlordane consistently at the highest concentration in the root tissue at each level of soil contamination. As the soil chlordane concentration increased, the average chlordane concentration in the root tissue increased as follows: Clean, 370 ng/g; low, 8,130 ng/g; medium, 21,800 ng/g; high, 29,400 ng/g. Further analysis of the field-grown plants showed distinct differences in both the proportional distribution of chlordane among the plant tissues and the pattern of the chlordane residues in each tissue type. These differences are attributed to plant uptake from soil versus uptake from air. In the rhizotron studies, uptake of chlordane residues by C. pepo L. was compared with that of another Cucurbitaceae, Cucumis sativus L. (cucumber). Xylem sap from the rhizotron-grown plants was collected and analyzed for chlordane, in addition to determination of chlordane residues in soil, roots, and aerial plant tissue. Component fractions and enantiomer fractions of both chiral and achiral chlordanes were followed through soil, root, xylem sap, and aerial tissue compartments. They indicate that the xenobiotic residues translocate enantioselectively from the soil matrix into and through the plant environment with genera-specific patterns. The determination of chlordanes at ng/g concentration explicitly for the first time in the xylem sap of plants grown in contaminated soil confirms the presence of a soil-sequestered and highly hydrophobic organic contaminant within the aqueous plant environment.

Air↗