There is no doubt that TCDD is capable of inducing effects on a variety of components and functions of the immune system in a variety of species. In fact, such changes seem to belong to the most sensitive variables affected by TCDD. Some of the biological effects, induced at rather high doses of TCDD exhibiting general toxicity (> 3 micrograms TCDD/kg body wt), may be considered unspecific or the result of the pronounced thymus involution. However, other effects (such as that on lymphocyte subtype patterns in marmosets or a reduced resistance of mice to influenza viruses) have been reported to occur at dose levels far from those leading to thymic involution or general toxicity. It should be remembered that the pathognomonic relevance for man of subtle modifications in the pattern of lymphocyte surface receptors is largely unknown. Until now, such deviations are considered rather as biological phenomena than indications or causes of specific diseases. Nevertheless, such changes represent clear-cut biological effects induced by TCDD. Since effects of TCDD on components and defined functions of the immune system have been revealed in several species, it would be surprising if humans were largely resistant to such effects, but reliable data in humans with high exposures to defined dioxins verified by an appropriate quantification of the exposure are scarce as of now. Data published so far have not revealed pronounced alterations of such variables. However, no studies of well-defined human populations with quantified body burdens have been performed with modern methods (such as flow cytometry) analyzing a wide variety of surface receptors. Performance of such studies is essential for a better and reliable risk assessment, and the technology is available. Some of the effects observed (such as the changes in the pattern of lymphocyte subpopulations) must certainly be considered as biological effects induced by TCDD, and the situation is similar to the induction of hepatic monooxygenases, which are also observable in this dose range. However, the relevance of such changes with respect to adverse health effects in humans is presently difficult to judge in the absence of clear-cut functional deficits demonstrated so far either in vivo or in vitro.

Aciclovir (synonym: acyclovir) causes abnormal thymus development in rats. After treatment on day 10 of gestation a weight reduction of the organ is obvious in 21-day-old fetuses which persists postnatally. Adult male rats exposed in utero to one or three injections of 100 mg aciclovir/kg body wt given to the dam on day 10 of pregnancy showed a reduction of the thymus weight to 333 +/- 158 mg and 276 +/- 61 mg (control: 428 +/- 92 mg; n = 10). Corresponding alterations were detectable in female offspring. Liver weight was also decreased and spleen weight (in relation to body wt) was significantly increased in the offspring after the three exposures. In a host resistance model with Trichinella spiralis the function of the immune system of rats prenatally exposed to aciclovir was examined. Six weeks postnatally 10-12 randomly selected male rat offspring of one control and two treatment groups (1 or 3 injections of 100 mg aciclovir/kg body wt on day 10 of gestation) were infected orally with 500 Trichinella spiralis muscle larvae. Before and several times after the infection blood was taken from a tail vein or obtained by decapitation for examination of the antibody titers (IgM, IgG, IgA, IgE) to antigens of T. spiralis. Six weeks after the infection the weight of relevant organs was determined and tongue preparations were used for T. spiralis muscle larvae counting. Aciclovir exposed animals showed a different immune response than control rats. IgM titers in both treatment groups were higher than in controls two weeks after the infection but not different by the end of the experiment.(ABSTRACT TRUNCATED AT 250 WORDS)

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