• Toxicological Research
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• v.11 no.1
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• pp.69-75
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• 1995

The present study was carried out to establish several spermatotoxicity test methods. For this purpose we investigated following parameters in the fertility study of DA-125, a new anticancer agent, in rats: testicular spermatid counts, epididymal sperm counts, daily sperm production rate, sperm morphology, and serum testosterone concentration. Motility and velocity of sperms were also measured using non-treated rats. At 0.3 mg DA-125/kg, spermatids per 1g testis and daily sperm production rate per 1g testis were significantly decreased, when compared with those of control group. Several types of abnormal sperms, such as no head, pin head, double head, hook at wrong angle, no tail, and small sperm, were found in both treated and control groups at a low frequency. Serum testosterone concentration at 0.3 mg DA-125/kg was close to the control value. Sperm motility and velocity measured with non-treated rats were in a good agreement with the results of other investigators. In our study established spermatotoxicity test methods can be used as a tool not only for the close examination of the cause of drug- or chemical-induced infertility, but also for the effective evaluation of reproductive toxicity.

• Proceedings of the Korea Environmental Mutagen Society Conference
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• 2004.11a
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• pp.126-127
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• 2004

• Journal of Korean Society of Occupational and Environmental Hygiene
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• v.23 no.3
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• pp.273-286
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• 2013

Objectives: The present study was conducted in order to investigate the reproductive toxicity in rats exposed to 1,4-dichlorobutane. Methods: The test chemical was administered orally at 0, 8.3, 50 and 300 mg/kg/day. Males were administered daily for 10 weeks prior to the mating period. Females were administered from between two weeks before mating to the 21stday of lactation. Results: In both sexes, a decrease in body weight and an increase in the weights of the liver and kidneys were observed. In males, discoloration of the liver, hepatocyte hypertrophy and mineralization in the kidneys were observed. In females, animal deaths, dystocia and pup deaths due to maternal dysfunction were observed. In F1 animals of both sexes, a decrease in body weight was observed at 300 mg/kg/day. An increase in the weights of the liver in both sexes, mineralization in the kidneys of males, animal deaths, hepatocyte hypertrophy and pup deaths due to maternal dysfunction were observed at 50 mg/kg/day. Mineralization in the kidneys of males was observed at 8.3 mg/kg/day. Therefore, the no-observed-adverse-effect levels (NOAELs) of 1,4- dichlorobutane were considered to be under 8.3 mg/kg/day for males, 8.3 mg/kg/day for females, more than 300 mg/kg/day for fertility in both sexes, 8.3 mg/kg/day for maternal functions and 50 mg/kg/day for F1 offspring. The absolute toxic dose was believed to be 8.3 mg/kg/day for males, 50 mg/kg/day for females, 50 mg/kg/day for maternal functions and 300 mg/kg/day for F1 offspring. However NOAEL for fertility could not be determined since there were no treatment-related changes. Conclusions: Under the present experimental conditions, 1,4-dichlorobutane is a Category 1B Reproductive Toxicant (presumed human reproductive or developmental toxicant).