Degradation of the persistent organic pollutant [14C]heptachlor in Japanese field soils.

The fate of [(14)C]heptachlor in Saitama soil and the degradation of [(14)C]heptachlor in four Japanese field soils over 112 d after application were investigated. Heptachlor was degraded mainly to cis-heptachlor epoxide by a biotic process and to 1-hydroxychlordene by an abiotic process in the field soils. Volatilization of heptachlor and cis-heptachlor epoxide from the soil was observed over the experimental period. The amount of 1-hydroxychlordene produced in the soils appeared to be related to the soil water contents. Because heptachlor and heptachlor epoxides are predicted to volatilize to the atmosphere and to persist in soils, these compounds are thought to spread among Japanese environmental compartments even after a ban on their use.

Bioaccumulation and metabolism of [14C]bisphenol A in the brackish water bivalve Corbicula japonica.

The brackish water bivalve mollusk Corbicula japonica was exposed to brackish water containing approximately 9 microg/l [(14)C]bisphenol A (BPA) for 168 h (the uptake phase), and subsequently transferred to clean brackish water for 144 h (the depuration phase) under semi-static conditions. Mono and disulfate conjugates of BPA were detected in the bivalves as major metabolites. At the end of the uptake phase, the visceral mass contained the highest (14)C-concentration, and the monosulfate conjugate of BPA was a major metabolite in the visceral mass. These data suggest that the visceral mass is the major tissue/organ to take up and metabolize BPA in these bivalves. The BPA concentration in the bivalves readily reached steady state during the uptake phase and immediately decreased in the depuration phase. The accumulation and elimination rates of the mono and disulfate conjugates of BPA were slower than those of BPA.

Stage-dependent differences in effects of carbaryl on population growth rate in Japanese medaka (Oryzias latipes).

Fish embryo toxicology is important because embryos are considered more susceptible than adult fish to the effects of toxic chemicals. Recently, fish embryo bioassay was proposed to replace the conventional fish acute toxicity chemical test of the Organization for Economic Cooperation and Development guidelines because it offers the advantages of fewer reagents, easy handling, and efficient data production. To accelerate the establishment of a chemical toxicity database for the protection of environmental and human health, we need to determine whether the conventional toxicity test can safely be replaced by such fish embryo toxicity tests. For instance, it is unclear how the presence of the chorion moderates the toxic effects of some chemicals. If such chemical toxicities do differ between embryos and, for example, the larval stage, then different toxic effects should appear in later life. We tested the later-life effects of the neurotoxic insecticide carbaryl at sublethal concentrations (0 [control] and 5 and 10 mg/L) in embryos and posthatch larvae of the freshwater fish medaka, Oryzias latipes. Although embryos exposed until hatching showed multiple developmental malformations and reductions in subsequent survival rates over three months, no significant reduction was observed in tolerance to starvation for 7 d and in intrinsic population growth rate (r). Exposure of larvae for 96 h resulted in dose-responsive vertebral fracture, significant reduction in tolerance to starvation for 7 d, and reduced three-month survival rate; r was reduced significantly and consistently. These results suggested that posthatch larvae were more susceptible than embryos to carbaryl exposure and that the toxic cascades may differ between larvae and embryos. The influences of carbaryl exposure on population growth rate differed significantly with developmental stage.

Estrogenic modulation of CYP3A38, CYP3A40, and CYP19 in mature male medaka (Oryzias latipes).

We examined cytochrome P450 production and activity and circulating hormone concentrations in male medaka exposed to 17beta-estradiol (E2) or 17alpha-ethinylestradiol (EE2). Intraperitoneal injection of E2 at 1, 10, or 100 microg/g-fish completely suppressed CYP3A38 protein production and suppressed CYP3A40 protein levels by 89%, 52%, or 47%, respectively. CYP3A38 and CYP3A40 mRNA expression was unaltered, and CYP3A enzymatic activity initially increased and then decreased with increasing E2 dose. Males co-cultured with females were exposed to a markedly high concentration (43 ng/L) of E2 secreted by females. CYP3A protein levels in co-cultured males were suppressed. Serum testosterone (TE) and 11keto-testosterone levels in co-cultured males were downregulated to 40% of pre-exposure levels. Serum E2 levels increased in co-cultured males or males exposed to EE2. Testicular CYP19, which converts TE to E2, increased by 9.5 times in males exposed to 50 ng/L EE2 and by 21.5 times in those exposed to 100 ng/L EE2. Male medaka exposed to EE2 showed increased serum Vtg levels. Estrogenic exposure induced Vtg production, suppressed CYP3A protein production, downregulated TE metabolism, and enhanced CYP19 activity. Serum E2 endogenously induced by CYP19 could contribute to Vtg induction in male medaka.