Evaluation of the immunotoxic potential of chlordecone with comparison to cyclophosphamide

Evidence for extensive anaerobic dechlorination and transformation of the pesticide chlordecone (C10Cl10O) by indigenous microbes in microcosms from Guadeloupe soil

The historic use of chlordecone (C₁₀Cl₁₀O) as a pesticide to control banana weevil infestations has resulted in pollution of large land areas in the French West Indies. Although currently banned, chlordecone persists because it adsorbs strongly to soil and its complex bis-homocubane structure is stable, particularly under aerobic conditions. Abiotic chemical transformation catalyzed by reduced vitamin B₁₂ has been shown to break down chlordecone by opening the cage structure to produce C9 polychloroindenes. More recently these C9 polychloroindenes were also observed as products of anaerobic microbiological transformation. To investigate the anaerobic biotransformation of chlordecone by microbes native to the French West Indies, microcosms were constructed anaerobically from chlordecone impacted Guadeloupe soil and sludge to mimic natural attenuation and eletron donor-stimulated reductive dechlorination. Original microcosms and transfers were incubated over a period of 8 years, during which they were repeatedly amended with chlordecone and electron donor (ethanol and acetone). Using LC-MS, chlordecone and degradation products were detected in all the biologically active microcosms. Observed products included monohydro-, dihydro- and trihydrochlordecone derivatives (C₁₀Cl_10-nO₂H_n; n = 1,2,3), as well as “open cage” C9 polychloroindene compounds (C₉Cl_5-nH_3+n n = 0,1,2) and C10 carboxylated polychloroindene derivatives (C₁₀Cl_4-nO₂H_4+n, n = 0–3). Products with as many as 9 chlorine atoms removed were detected. These products were not observed in sterile (poisoned) microcosms. Chlordecone concentrations decreased in active microcosms as concentrations of products increased, indicating that anaerobic dechlorination processes have occurred. The data enabled a crude estimation of partitioning coefficients between soil and water, showing that carboxylated intermediates sorb poorly and as a consequence may be flushed away, while polychlorinated indenes sorb strongly to soil. Microbial community analysis in microcosms revealed enrichment of anaerobic fermenting and acetogenic microbes possibly involved in anaerobic chlordecone biotransformation. It thus should be possible to stimuilate anaerobic dechlorination through donor amendment to contaminated soils, particularly as some metabolites (in particular pentachloroindene) were already detected in field samples as a result of intrinsic processes. Extensive dechlorination in the microcosms, with evidence for up to 9 Cl atoms removed from the parent molecule is game-changing, giving hope to the possibility of using bioremediation to reduce the impact of CLD contamination.

Investigation of post-weaning changes in immunological parameters in male rats

Normal post-weaning changes in immunological parameters were investigated in male Crl:CD(SD) rats (n=7) for matching of ages with children (referential data). The animals received a single intravenous administration of keyhole limpet hemocyanin (KLH) 3mg/kg on day 1 and were euthanized on day 7 at 5, 7, 9, and 11 weeks of age. Furthermore, to investigate age-dependent differences in susceptibility to cyclophosphamide immunotoxicity, the animals were given oral cyclophosphamide 5mg/kgday from days 1 to 8 and intravenous KLH on day 3, and were euthanized on day 9 at the above ages. As a result, the post-weaning development pattern of a continuous increase until 9 weeks of age, followed by a mild decrease at 11 weeks of age, was commonly observed in white blood cell counts and all of its differential counts in peripheral blood, spleen weight, and total cell, CD3+, CD4+, CD8+ and CD45RA+ cell counts in the spleen. This pattern is similar to the development pattern of peripheral blood cell counts in infants, which mostly peaks at 6-12 months of age. Cyclophosphamide decreased almost all of peripheral blood cell counts and lymphocyte subset counts in the thymus and spleen at all ages, to similar degrees. However, decreases in serum anti-KLH IgM and IgG levels were greatest at 9 weeks of age. In conclusion, 9 (immunization at 8) weeks of age in rats was shown to be the most susceptible timing for cyclophosphamide immunotoxicity, likely corresponding to 6-12 months of age in infants.

Effect of sulfur mustard on murine lymphocytes

The effect on spleen cells of a single in vivo treatment with sulfur mustard was analyzed in mice 1 week after intoxication. A marked decrease in the number of total spleen cells was observed in mice receiving high doses of sulfur mustard. Flow cytometric analysis indicated that B-lymphocytes were relatively more affected than T-lymphocytes by this toxic compound. However, the function of remaining B-cells, measured by thymidine incorporation and immunoglobulin secretion in the presence of lipopolysaccharide, was not significantly impaired. In addition, sulfur mustard did not depress T-lymphocyte function since their proliferation in response to concanavalin A or to an anti-CD3 antibody was not affected by the treatment. These results suggest that whereas some observations reported in patients can be found in a murine model, additional in vitro studies with human lymphocytes could more adequately provide further information on sulfur-mustard-induced alterations of the immune system.

Evaluation of the immunotoxicity of low level PCB exposure in the rat

Weanling male Fischer 344 rats were exposed daily by gastric intubation for up to 15 weeks to the polychlorinated biphenyl (PCB) Aroclor 1254 at 0.1, 1, 10, or 25 mg/kg body weight. At 5, 10 and 15 weeks groups of rats were killed and immune functions were evaluated. The immune parameters examined included the following: body and lymphoid organ weights, mitogen-stimulated lymphoproliferative (LP) responses, natural killer (NK) cell activity, mixed lymphocyte reaction (MLR), and cytotoxic T lymphocyte (CTL) response. After 15 weeks of dosing body weights were reduced in rats receiving 25 mg/kg PCB while thymus weights were decreased in rats receiving 10 and 25 mg/kg. NK cell activity was reduced in rats dosed for 15 weeks at 10 and 25 mg/kg. The LP response to phytohemagglutinin was enhanced in rats dosed for 15 weeks at 25 mg/kg PCB. Exposure of rats to PCB did not affect the MLR or CTL responses. Other groups of rats were exposed to cyclophosphamide (CY) and served as positive controls for the immune assays employed. CY induced alterations in all of the immune parameters measured, indicating that this is an appropriate battery of immune function tests which is capable of detecting immune alterations in the rat. Alterations in immune function induced by daily gastric intubation with PCB were accompanied by reductions in body weight and/or hepatomegaly. These results suggest that the observed immune alterations may be related to the overt toxicity of this PCB in the rat.

Immunologic effects of perinatal exposure of rats to dioctyltin dichloride

Studies were conducted to determine the period of immune system development that was most sensitive to perturbation by the known immunotoxicant di-n-octyltin dichloride (DOTC). Fischer 344 rats were exposed prenatally, both pre- and postnatally, or postnatally to DOTC by oral gavage of pregnant and/or lactating females. At various ages, ranging from 3 to 16 wk of age, offspring were examined for a number of immune functions. These included body and lymphoid organ weights; lymphoproliferative responses to B- and T-cell mitogens; natural killer cell activity; and primary antibody response to sheep erythrocytes. Prenatal (10-20 of gestation), pre- and postnatal (d 11-20 of gestation and 2-11 d of age), or postnatal (2-13 d of age) oral dosing of dams with 20-50 mg/kg DOTC resulted in no consistent alteration in immune function in offspring. However, direct oral dosing of rat pups to 5-15 mg/kg DOTC, beginning at 3 d of age and then 3 times per week up to 24 d of age for a total of 10 doses, resulted in significant suppression of the lymphoproliferative response of splenocytes to a T-cell mitogen in 10-wk-old rats (i.e., 7 wk after the last exposure to DOTC). Lymphoproliferative responses returned to control levels by 12 wk of age. In comparison young adult (8 wk old) rats dosed with 10 or 20 mg/kg DOTC under an identical dosing schedule (i.e., 3 times per week for a total of 10 doses) showed no suppression in the mitogen response of splenocytes 4 wk after the last exposure to DOTC. These results suggest that direct dosing of pups during early postnatal life may be the most effective means of inducing immunosuppression with DOTC during immune system development. The results also provide evidence for the greater sensitivity of the developing immune system compared with the fully developed immune system for a known immunotoxicant.

The effects of nickel on immune function in the rat

The immunotoxic potential of NiCl2 was evaluated in Fischer 344 rats following a single intramuscular injection at doses ranging from 10 to 20 mg/kg. Twenty-four hours following treatment, selected cellular and humoral immune function parameters were examined. Significant (P less than 0.05) decreases in body weights were observed in rats injected with 15 and 20 mg/kg NiCl2 as were decreases in spleen weights of rats receiving 20 mg/kg. The lymphoproliferative responses of splenocytes to the T cell mitogens concanavalin A (Con A), phytohemagglutinin (PHA), the T and B cell mitogen pokeweed mitogen (PWM) and the B cell mitogen Salmonella typhimurium mitogen (STM) were not significantly different from controls. No significant differences were observed between control and Ni-treated rats in the primary antibody response to sheep red blood cells (SRBC). On the other hand, natural killer (NK) cell activity was significantly (P less than 0.05) suppressed in rats injected with 10, 15, or 20 mg/kg NiCl2. NK cell suppression was observed in both male and female rats and for both allogeneic W/Fu-G1 target cells as well as xenogeneic YAC-1 target cells. Ni-induced suppression of NK activity was transient, with levels returning to control values within three days following treatment. Ni-induced suppression of NK activity was also manifested by an increase in mortality of rats injected with MADB106 tumor cells. These results extend to a second species our earlier findings that Ni suppresses NK activity.

The effect of biological response modifiers on chronic and latent murine cytomegalovirus infections

Host-mediated antiviral effect of 2 biological response modifiers (BRM), OK-432, and PS-K, against murine cytomegalovirus (MCMV) was evaluated in chronically or latently infected mice. In the early stage of chronic MCMV infection, the BRM-induced resistance was evidenced by decrease in infectious viruses replicated in the salivary glands and by augmented cytotoxic activity of the spleen cells against YAC-1 cells and MCMV-infected mouse embryonic fibroblasts (MEF). In the late stage of chronic MCMV infection, the BRM treatment did not eliminate MCMV from the mice, but did prevent exacerbation of MCMV infection in the salivary glands induced by administration of cyclophosphamide (CY). In mice latently infected by MCMV, BRM treatment suppressed CY-induced reactivation of MCMV in the salivary glands. It was suggested that the antiviral effect of BRM against MCMV in chronically or latently infected mice was based on activation of natural killer (NK) cells and cytotoxic T lymphocytes (CTL).