Assessment of host resistance to Trichinella spiralis in mice following preinfection exposure to 2,3,7,8-TCDD.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) has been reported to decrease host resistance to a variety of infectious agents when exposure occurs prior to infection. Resistance to viral infection has been observed at doses as low as 0.1 microgram TCDD/kg body wt, well below the thymolytic dose in mice. In the present study, female B6C3F1 mice were exposed to a single intraperitoneal injection of 0, 0.1, 1.0, 10.0, or 30.0 micrograms TCDD/kg 7 days prior to infection to determine the effects of TCDD exposure on resistance to the nematode parasite Trichinella spiralis. Exposure to 10 or 30 micrograms TCDD/kg delayed adult parasite elimination from the small intestine. Significantly more larvae were released by female parasites and greater numbers of encysted larvae were recovered from the muscle of mice exposed to TCDD. Proliferative responses of splenocytes and mesenteric lymph node cells stimulated with T. spiralis antigen were significantly suppressed at exposure levels of TCDD > or = 1.0 microgram/kg 7 days after infection and in splenocytes only at 14 days after infection, demonstrating the greater sensitivity of proliferative responses to TCDD exposure than actual host resistance to Ts infection. Suppressed proliferation was observed at doses which produced TCDD concentrations > or = 0.2 pmol/g of lymphoid tissue on Day 7 of infection. In addition, it was determined that infected mice had higher TCDD levels than noninfected mice given the same dose. These results suggest an interaction between TCDD exposure and infection, i.e., that exposure to TCDD altered the host response to infection, while infection delayed elimination of TCDD from the host.

Assessment of the immunotoxic potential of the fungicide dinocap in mice.

The immunotoxic potential of dinocap was evaluated in female C57BL/6J mice following in vivo and in vitro exposure to this fungicide. In in vivo studies, groups of mice were dosed by gavage with technical grade dinocap at dosages ranging from 12.5 to 50 mg/kg per day for 7 or 12 days and selected immune functions examined. Mice dosed at 50 mg/kg per day dinocap died after 4 days of dosing. Twelve days of dosing with dinocap at 25 mg/kg per day resulted in decreased thymus weights and cellularity, and increased spleen weights. No changes were observed in body weight, absolute differential peripheral leukocyte counts, the lymphoproliferative responses to B- or T-cell mitogens, the mixed lymphocyte reaction, or natural killer (NK) cell activity of spleen cells from mice exposed to dinocap. Lymphoproliferative responses to concanavalin A (Con A) and phytohemagglutinin (PHA), however, were reduced in thymocytes from mice dosed at 25 mg/kg per day dinocap. The cytotoxic T lymphocyte (CTL) response to P815 mastocytoma cells was enhanced in mice exposed for 7 days to 25 mg/kg per day dinocap. Exposure of mice for 7 days to 25 mg/kg per day dinocap also caused a significant reduction in the IgM and IgG plaque-forming cell (PFC) response to sheep red blood cells (SRBC). A time-course study indicated that dinocap-induced suppression of the IgM PFC response was due to a delay in the peak PFC response to SRBC. In vitro studies using murine thymocytes cultured with dinocap (10 micrograms/ml for 72 h) resulted in suppression of the proliferative response to Con A and PHA. Exposure of thymocytes to dinocap in vitro for as little as 30 min resulted in suppression of the mitogen-stimulated response in the absence of any apparent direct cytotoxic effect. These results suggest that dinocap alters the immune system of the mouse, however, these effects are relatively modest in terms of adverse immune function and are only seen at relatively high exposure levels.

Immunotoxicologic assessment of subacute exposure of rats to carbon tetrachloride with comparison to hepatotoxicity and nephrotoxicity.

The immunotoxicity, hepatotoxicity, and nephrotoxicity of subacute exposure to carbon tetrachloride (CCl4) were evaluated in young adult (8-9 weeks old) male Fischer 344 rats dosed by gavage with CCl4 for 10 consecutive days at 0, 5, 10, 20 or 40 mg/kg/day. Two days following the last treatment rats were evaluated for alterations in immune function by monitoring the following: body and lymphoid organ weights; mitogen and mixed leukocyte reaction lymphoproliferative responses; natural killer cell activity; and cytotoxic T lymphocyte responses. A separate group of similarly dosed rats was immunized with sheep red blood cells (SRBC) on Day 9 of dosing, and the primary antibody response was assessed 4 days later. Hepatic and renal toxicity were assessed 2 days after the last treatment by monitoring organ weights, serum indicators of hepatic and renal damage, and hepatic cytochrome P450 levels, as well as by histological evaluation. Significant increases in relative liver weights were observed in rats dosed at 40 mg/kg/day. Histologically, these livers displayed mild to moderate vacuolar degeneration and minimal to mild hepatocellular necrosis. In addition, serum levels of aspartate aminotransferase and alanine aminotransferase were elevated at this dosage, as well as at 20 mg/kg/day. There were no renal effects observed at these dosages of CCl4. In addition, no consistent alterations were observed in the immune parameters examined in these same animals nor in the rats immunized with SRBC. Furthermore, there was no difference in the antibody response to SRBC in another set of rats dosed at 40, 80 or 160 mg/kg/day CCl4. These results indicate that CCl4 is not immunotoxic in the rat at dosages that produce overt hepatotoxicity.