Search

T-cell-dependent antibody responses (TDAR) are suppressed in female C57BL/6N mice exposed to ≥3.75 mg/kg of perfluorooctanoic acid (PFOA) for 15 days. To determine if suppression of humoral immunity by PFOA is peroxisome proliferator activated receptor alpha (PPARα)-dependent and if suppression is associated with specific targeting of T- or B-cells, three separate experiments were conducted: (1) female PPARα constitutive knockout (PPARα KO; B6.129S4-Ppar(tm1Gonz)N12) and wild-type controls (WT; C57BL/6-Tac) exposed to 0, 7.5, or 30 mg PFOA/kg for 15 days were immunized on Day 11 with a T-cell-dependent antigen and sera then collected for measures of antigen-specific IgM titers (TDAR) 5 days later; (2) female C57BL/6N WT mice exposed to 0, 0.94, 1.88, 3.75, or 7.5 mg PFOA/kg for 15 days were immunized with a T-cell-independent antigen on Day 11 and sera were then collected for analyses of antigen-specific IgM titers (TIAR) 7 days later; and (3) splenic lymphocyte phenotypes were assessed in unimmunized female C57BL/6N WT mice exposed to 0, 3.75, or 7.5 mg PFOA/kg for 10 days to investigate effects of PFOA in the absence of specific immunization. Separate groups of mice were immunized with a T-cell-dependent antigen after 11 days of exposure and splenic lymphocyte sub-populations were assessed after 13 or 15 days of exposure to assess numbers of stimulated cells. The results indicated that exposure to ≥1.88 mg PFOA/kg suppressed the TIAR; exposure to 30 mg PFOA/kg suppressed the TDAR in both PPARα KO and WT mice. The percentage of splenic B-cells was unchanged. Results obtained in the PPARα KO mice indicated that PPARα suppression of TDAR was independent of PPARα involvement. Suppression of the TIAR and the TDAR with minimal lymphocyte sub-population effects suggested that effects on humoral immunity are likely mediated by disruption of B-cell/plasma cell function.

Dibromoacetic acid (DBA) is a disinfection by-product commonly found in drinking water as a result of chlorination/ ozonation processes. The Environmental Protection Agency estimates that more than 200 million people consume disinfected water in the United States. This study was conducted to evaluate the potential immunotoxicological effects of DBA exposure when administered for 28 days via drinking water to B₆C₃F₁ mice, at concentrations of 125, 500, and 1000 mg/L. Multiple endpoints were evaluated to assess innate, humoral, and cell-mediated immune components, as well as host resistance. Standard toxicological parameters were unaffected, with the exception of a dose-responsive increase in liver weight and a decrease in thymus weight at the two highest exposure levels. Splenocyte differentials were affected, although the effects were not dose-responsive. Exposure to DBA did not significantly affect humoral immunity (immunoglobulin M [IgM] plaque assay and serum IgM anti-sheep erythrocyte titers) or cell-mediated immunity (mixed-leukocyte response). No effects were observed on innate immune function in either interferon-γ-induced in vitro macrophage cytotoxic activity or basal natural killer (NK)-cell activity. Augmented NK-cell activity (following exposure to polyinosinic-polycytidylic acid) was decreased at the low dose, however the effect was not dose-responsive. Finally, DBA exposure had no effect on resistance to infection with either Streptococcus pneumoniae or Plasmodium yoelii, or challenge with B16F10 melanoma cells. With the exception of changes in thymus weight, these results indicate that DBA exposure resulted in no immunotoxic effects at concentrations much larger than those considered acceptable in human drinking water.

Organotins are used commercially as agricultural pesticides, antifouling agents, and stabilizers for polyvinyl chloride (PVC) pipe. Mono- and di-substituted methyl and butyltins, used in PVC pipe production, are of concern as they leach from supply pipes into drinking water and have been reported to cause multisystem toxicity, including immunotoxicity. As part of an ongoing study to evaluate immunotoxic effects of organotins, we assessed immune function in adult Sprague-Dawley (CD) rats after exposure to dibutyltin dichloride (DBTC). Individually-housed adult male and female CD rats were given drinking water containing 0, 10, or 25 mg DBTC/L (final concentration) in 0.5% Alkamuls for 28 days. Water bottles were changed and water consumption was monitored twice weekly and body weights (BW) were recorded weekly. Delayed-type hypersensitivity (DTH), primary and secondary antibody responses to sheep red blood cells, and natural killer (NK) cell activity were evaluated in separate groups of treated and control animals on day 29 of exposure. Water consumption was significantly decreased in both sexes at 25 mg DBTC/L. BW, immune organ weights, the DTH response, and NK cell activity did not vary by dose. Different results for antibody responses in male rats were obtained in two experimental replicates. In the first replicate, IgG was elevated at the highest dose whereas in the second replicate, IgM was suppressed. However, as these effects occurred at the high dose of 25 mg DBTC/L, which is a concentration a million times higher than levels of DBTC reported in drinking water, our data suggest that DBTC is unlikely to cause immunotoxicity at concentrations found in drinking water supplies.

A number of regulatory agencies in western Europe, Japan and the United States now include guidelines for evaluating the potential immunotoxicity of chemicals, including drugs, as part of routine toxicity testing. Most testing guidelines recommend observational or functional assays that, based on studies in laboratory animals, are able to detect changes in immune function that are associated with increased susceptibility to infectious or neoplastic cell challenge. To appreciate how well observational and functional endpoints are likely to predict an increased risk of infection in humans, it is important to establish correlations between alterations in human immune function and an increased risk of disease. This review will address the clinical evidence for increased risk of disease in humans with mild to moderate levels of immunosuppression using examples from the literature, discuss specific immune system defects associated with increased rates of infection, and examine factors that impact the interpretation of clinical data. The most comprehensive data bases that address these relationships, those derived from patients with primary immunodeficiency and AIDS, are not discussed in this review. These are extreme examples of immunodeficiency and neither the specific clinical diseases that result, nor eventual outcomes, have much in common with that which occurs in individual with chronic mild-to-moderate immunosuppression.

Monochloramine has been used to provide a disinfecting residual in water distribution systems where it is difficult to maintain an adequate free-chlorine residual or where disinfection by-product formation is of concern. The goal of this study was to characterize the immunotoxic effects of chloramine in female B(6)C(3)F(1) mice when administered via the drinking water. Mice were exposed to chloramine-containing deionized tap water at 2, 10, 20, 100, or 200 ppm for 28 days. No statistically significant differences in drinking water consumption, body weight, body weight gain, organ weights, or hematological parameters between the exposed and control animals were noted during the experimental period. There were no changes in the percentages and numbers of total B-lymphocytes, T-lymphocytes, CD4(+) and CD8(+) T-lymphocytes, natural killer (NK) cells, and macrophages in the spleen. Exposure to chloramine did not affect the IgM antibody-forming cell response to sheep red blood cells (SRBC) or anti-SRBC IgM antibody production. Minimal effects, judged to be biologically insignificant, were observed in the mixed-leukocyte response and NK activity. In conclusion, chloramine produced no toxicological and immunotoxic effects in female B(6)C(3)F(1) mice when administered for 28 days in the drinking water at concentrations ranging from 2-200 ppm.

Dibromoacetic acid (DBA) is a disinfection by-product commonly found in drinking water as a result of chlorination/ ozonation processes. The Environmental Protection Agency estimates that more than 200 million people consume disinfected water in the United States. This study was conducted to evaluate the potential immunotoxicological effects of DBA exposure when administered for 28 days via drinking water to B₆C₃F₁ mice, at concentrations of 125, 500, and 1000 mg/L. Multiple endpoints were evaluated to assess innate, humoral, and cell-mediated immune components, as well as host resistance. Standard toxicological parameters were unaffected, with the exception of a dose-responsive increase in liver weight and a decrease in thymus weight at the two highest exposure levels. Splenocyte differentials were affected, although the effects were not dose-responsive. Exposure to DBA did not significantly affect humoral immunity (immunoglobulin M [IgM] plaque assay and serum IgM anti-sheep erythrocyte titers) or cell-mediated immunity (mixed-leukocyte response). No effects were observed on innate immune function in either interferon-γ-induced in vitro macrophage cytotoxic activity or basal natural killer (NK)-cell activity. Augmented NK-cell activity (following exposure to polyinosinic-polycytidylic acid) was decreased at the low dose, however the effect was not dose-responsive. Finally, DBA exposure had no effect on resistance to infection with either Streptococcus pneumoniae or Plasmodium yoelii, or challenge with B16F10 melanoma cells. With the exception of changes in thymus weight, these results indicate that DBA exposure resulted in no immunotoxic effects at concentrations much larger than those considered acceptable in human drinking water.

Organotins are used commercially as pesticides, antifouling agents, and stabilizers for polyvinyl chloride (PVC) pipe. Mono-and di-substituted butyltins, used in PVC pipe production, are of concern to the United States EPA, they leach from supply pipes into drinking water and are reported multisystem toxicants. We assessed immune function in Sprague-Dawley rats after developmental dibutyltin dichloride (DBTC) exposure. Pregnant rats were given drinking water containing 0, 10, or 25 mg/L of DBTC (final concentration) in 0.5% Alkamuls from gestational Day (GD) 6 through weaning of pups (37 days total). Approximate doses to dams: 1 and 2.5 mg DBTC/kg body weight (BW) during gestation, or 2.0 and 4.4 mg DBTC/kg BW while nursing. Litters were sexed, weighed, and culled to 4 males and 4 females per dam on postnatal Day (PND) 2. Beginning on PND3, litters of half of the dams per dose were gavaged with 0, 1.0, or 2.5 mg DBTC/kg BW 3X/week for 10 doses (maternal + direct treatment); remaining litters were exposed indirectly via lactation (maternal treatment). BW of litters exposed to 2.5 mg DBTC/kg BW was 10-20% lower (por = 0.05) relative to other groups from PND14 (males) or PND17 (females) through PND37. Delayed-type hypersensitivity (DTH), antibody synthesis, and natural killer (NK) cell activity were evaluated in immunologically mature offspring (N = 6/sex/group). DTH responses and antibody synthesis did not differ by dose, sex, or exposure. NK cell activity in the 10 mg DBTC/L maternal only group was greater in male offspring than in female. In female offspring from the maternal + direct group, cytotoxicity increased by dose at the 25:1 effector:target cell ratio. Our data suggest that developmental immunotoxicity from DBTC-tainted drinking water is unlikely as the concentrations we used were several orders of magnitude higher than concentrations expected to leach from PVC pipes.