Effects of selected therapeutic agents on urolithiasis induced by terephthalic acid in the male weanling Fischer 344 rat.

Exposure of male weanling Fischer 344 rats to 4.0% terephthalic acid (TPA) in the diet (positive controls) for two weeks (postnatal days 28-42) resulted in a 50% incidence of bladder calculi, aciduria, elevated urinary excretion of calcium (Ca) and magnesium (Mg), and slightly elevated serum levels of Ca and Mg relative to negative controls. Possible mechanisms of TPA-induced urolithiasis were examined by daily oral administration of allopurinol, chlorothiazide, or neutral phosphates, at their recommended therapeutic doses during exposure to dietary 4.0% TPA. An additional group was fed 4.0% TPA and 4.0% sodium bicarbonate in the diet for two weeks. Chlorothiazide or dietary bicarbonate abolished TPA-induced urolithiasis, but allopurinol and neutral phosphates had no effect. Bicarbonate increased water intake above that of positive controls and ameliorated the TPA-induced aciduria. It also increased urinary Mg and TPA above positive control values. Chlorothiazide reduced urinary Ca and TPA levels below those of positive controls. Treatment with chlorothiazide, neutral phosphates or bicarbonate slightly reduced serum Ca below the levels in either positive or negative controls. Drug treatment did not alter TPA-induced elevated serum Mg levels, but bicarbonate reduced serum Mg levels to negative control values. In conclusion, TPA-induced urolithiasis in male weanling rats was abolished by therapeutic agents which reduced urinary Ca and TPA excretion (chlorothiazide), or which enhanced water intake, urinary Mg and TPA excretion, and ameliorated TPA-induced aciduria (dietary bicarbonate). These factors appear to be critical for TPA-induced urolithiasis.

The interaction of cadmium-binding proteins (Cd-bp) and progesterone in cadmium-induced tissue and embryo toxicity.

Previous work indicates that a dimer of Cd-thionein (Cd-bp-D, 19,000 MW) is involved in the hereditary resistance to Cd-embryotoxicity seen in the inbred NAW/Pr (NAW) mouse strain. Cd-bp-D is not detected in virgin females after Cd exposure and is detected only after the first 24 hours of exposure to Cd in an inbred strain (C57BL/10ChPr) susceptible to Cd-induced embryotoxicity (Wolkowski, '74; Wolkowski-Tyl, '78). Since progesterone (P) is critical for maintenance of pregnancy in mice, we have studied the possible relationship between this hormone and Cd-bp-D production. As a model system, was examined effects of Cd treatment on Cd-bp synthesis in NAW males. It was anticipated that this model could provide information bearing not only on the relationship between P and Cd-bp-D production, but also on that between Cd-bp-D and Cd toxicity, since a single sc injection of CdCl2 causes typical testicular hemorrhagic necrosis in NAW males, and these animals make only metallothionein and not Cd-bp-D. NAW males were, therefore, given P (0.1 g/Kg bw) and then exposed to Cd. Sephadex gel chromatography (G-200) of liver cytosol from animals killed 24 hours later detected only Cd-bp-D. Testes of these males did not show hemorrhagic necrosis. Since the adrenals of male mammals release P in response to stress, NAW males were stressed by repeated sesame oil or propylene glycol injections (5 ml/Kg bw), or the adrenal was stimulated directly with injections of ACTH (100 IU/Kg bw) for seven days prior to Cd exposure. All methods tested which significantly elevated serum P levels (as confirmed by radioimmunoassay), also resulted in production of Cd-bp-D and absence of testicular hemorrhage in Cd-treated NAW males. Suppression of P release by injection of dexamethazone or corticosterone or by adrenalectomy resulted in testicular hemorrhage and production of only metalicthionein after Cd exposure. The relevance of the interaction between P, Cd-bp-D and protection against Cd-induced toxicity seen in the model system was supported by analysis of serum P levels in pregnant females; elevated levels were seen in resistant (NAW dams on day 10 of gestation and significantly lower levels seen in dams from a Cd-sensitive strain.

Structural teratogenicity evaluation of methyl chloride in rats and mice after inhalation exposure.

One hundred bred Fischer-344 female rats were exposed daily for 6 hours to atmospheres containing 0, 100, 500, or 1,500 ppm methyl chloride, 25 females per exposure concentration, from gestation day (gd) 7 through gd 19. On gd 20, the females were sacrificed for evaluation of maternal reproductive and fetal parameters. Maternal and fetal toxicity was apparent at the highest exposure concentration. There were no methyl chloride-induced external, skeletal, or visceral abnormalities seen in the fetuses. One hundred thirty-two C57BL/6 female mice bred to C3H males to produce B6C3F1 offspring were exposed daily for 6 hours to atmospheres containing 0, 100, 500, or 1,500 ppm methyl chloride, 33 females per exposure concentration, from gd 6 through gd 17. Exposure to the entire 1,500-ppm group was terminated on gd 10-14, with the animals killed in extremis. Selective necrosis of neurons in the internal granular layer of the cerebellum, ranging from individual cell involvement to focal areas comprising large numbers of neurons, was found in all females. On gd 18, the females from the other treatment groups, all of which survived, were killed for evaluation of maternal reproductive and fetal parameters. No evidence was seen of maternal or fetal toxicity in these exposure groups. There were no significant alterations in external appearance in fetuses from any of the exposure groups. Visceral examination of mouse fetuses revealed a small, but statistically significant, incidence of heart defects in litters of the 500-ppm group. The anomaly, a reduction or absence of the atrioventricular valve, chordae tendineae, and papillary muscle, was observed on the left side (bicuspid valve) in three fetuses and the right side (tricuspid valve) in six fetuses: three males and six females. It is concluded that methyl chloride inhalation exposure in pregnant rats, during critical periods of embryo and fetal development, is not teratogenic at concentrations which elicit maternal and fetal toxicity. In pregnant mice, methyl chloride was severely toxic to dams following 4 days or more of exposure to 1,500 ppm in air. Methyl chloride, at 500, but not 100 ppm, was teratogenic in mice, leading to a malformation in the heart. No embryo-fetal toxicity or teratogenicity was associated with exposure of mice, during critical periods of embryo and fetal development, to 100 ppm of ethyl chloride.

Evaluation of heart malformations in B6C3F1 mouse fetuses induced by in utero exposure to methyl chloride.

C57BL/6 female mice impregnated by C3H males mice to produce B6C3F1 fetuses were exposed daily for six hr to atmospheres containing 0, 250, 500, or 750 ppm methyl chloride, from gestation day 6 to gestation day 18. There were 74 to 77 females with copulation plugs per exposure concentration. Females exposed to 750 ppm ethyl chloride exhibited ataxia commencing on the seventh day of exposure (gestation day 12). They also showed hypersensitivity to touch or sound, tremors and convulsions. Six females in the 750 ppm group died and one was euthanized in extremis prior to scheduled sacrifice. On gestation day 18, all other females were euthanized for evaluation. Only dams exposed to 750 ppm exhibited significant decrease in body weight by gestation day 18, weight gain during the gestation period, and absolute weight gain (weight gain minus gravid uterine weight) versus controls. There were no treatment related-effects on these parameters in the other exposure groups. None of the groups exhibited exposure-related differences in pregnancy rate, gravid uterine weight, or maternal liver weight. There were no differences in the numbers of implantations, resorption, dead fetuses, nonlive (dead plus resorbed) fetuses, live fetuses, sex-ratio, or mean fetal body weight per litter. There was a significant exposure-related increase in the number and percentage of affected (nonlive plus malformed) fetuses per litter with the incidence of affected fetuses in the 750 ppm group significantly higher than controls. There was a statistically significant increase in the incidence of heart defects in the 500 and 750 ppm group relative to controls. Of the 37 fetuses in the study with heart defects, 23 were females, 14 were males. The heart defects observed included: absent or abnormal tricuspid valve, reduced number of papillary muscles and/or chordae tendineae on the right side, small right ventricle, globular heart, and white spots in the left ventricular wall. Multiple malformations were observed in one fetus from the 500 ppm group and in three fetuses in the 750 ppm group. It is concluded that methyl chloride inhalation exposure to pregnant C57BL/6 mice from gestation day 6 through gestation day 17 resulted in maternal toxicity only at the 750 ppm exposure concentration and was teratogenic to B6C3F1 conceptuses at exposure concentrations of 750 and 500 ppm, leading to fetal heart malformations. No evidence of embryo or fetotoxicity other than teratogenicity was seen at any of the exposure concentrations employed. No maternal, embryo or fetotoxicity or teratogenicity was associated with exposure of mice, during critical periods of embryo and fetal development, to 250 ppm of methyl chloride.

Chemical urolithiasis. III. Pharmacokinetics and transplacental transport of terephthalic acid in Fischer-344 rats.

The pharmacokinetics of [14C]terephthalic acid ([14C]TPA) were determined in Fischer-344 rats after intravenous and oral administration. After iv injection, the plasma concentration-time data were fitted using a three-compartment pharmacokinetic model. The average terminal half-life in three rats was 1.2 +/- 0.4 hr, and the average volume of distribution in the terminal phase was 1.3 +/- 0.3 liters/kg. Following administration by gavage, a longer terminal half-life was obtained, indicating that dissolution of [14C]TPA or absorption from the gut may be partially rate-limiting. Recovery of [14C]TPA in the urine following a bolus iv dose was 101 +/- 8%, indicating essentially complete urinary excretion of the compound. No evidence of metabolism of [14C]TPA was obtained by analysis of urine by high-performance liquid chromatography. [14C]TPA was transported to the fetus after administration of the compound to pregnant rats; however, the concentrations in fetal tissues were low relative to the corresponding maternal tissues. Neonatal rats exposed to 5% TPA in the diet of their dams did not develop calculi until the onset of self-feeding. These results demonstrate that TPA is rapidly excreted into urine after administration to rats, and that excretory mechanisms in the dam provide an effective mechanism of defense against TPA-induced urolithiasis in neonatal rats.

Reproduction in Fischer-344 rats exposed to methyl chloride by inhalation for two generations.

Male and female Fischer-344 rats were exposed to methyl chloride by inhalation (0, 150, 475, or 1500 ppm, 6 hr/day, 5 days/week, 40 males and 80 females per group). The only treatment-related clinical signs were a 10 to 20% body weight gain depression (BWGD) in both males and females exposed to 1500 ppm at all weekly weighings after 2 weeks of exposure and a 5-7% BWGD in 475-ppm exposed animals after Day 57. After 10 weeks the exposure schedule was changed to 6 hr/day, 7 days/week and each male was mated to two exposed females. The mating period was ended after 2 weeks, at which point 10 males/group were necropsied. The only treatment-related lesions found were severe bilateral testicular degeneration (10/10) and granulomas in the epididymis (3/10) in the 1500-ppm males. The remaining 30 males per group were then removed from exposure and mated during a 2-week period with 60 unexposed females. The exposed females were continued on exposure from the start of mating to Postnatal Day 28 (6 hr/day, 7 days/week). The females were not exposed from Gestation Day 18 to Postnatal Day 4, and the pups were never directly exposed prior to weaning. There were no significant differences between groups in the number of exposed or unexposed females that mated, as evidenced by copulation plugs. No litters were born to exposed or unexposed females mated to the 1500-ppm males. There was no significant difference in the number of litters produced by the 150-ppm groups when compared to the control groups. Fewer litters were born in the 475-ppm groups than in the control groups. No differences in litter size, sex ratio, pup viability, or pup growth were found among the 475-ppm, 150-ppm, or control F0 groups. When bred 10 weeks after the cessation of exposures, 5 to 20 1500-ppm F0 males had regained the ability to sire normal litters. The same number of 475-ppm F0 males proved as fertile (15/20) as control F0 males (13/20). After weaning, F1 pups from the 475-, 150-, and 0-ppm groups were exposed to the same concentrations of methyl chloride for 10 weeks and then mated. A trend toward decreased fertility was found in the 475-ppm F1 group.