• Title/Summary/Keyword: reproduction toxicity

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Assessment on combined repeated dose and reproduction/developmental toxicity of benzoyl peroxide

  • Sanghwan Song;Kim, Su-Hyon;Heekyung Bae;Lee, Moon-Soon;Park, Kwangsik
    • Proceedings of the Korean Society of Toxicology Conference
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    • 2002.11b
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    • pp.171-171
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    • 2002
  • This study was carried out by an Korean GLP laboratory to assess the combined repeated dose, reproduction and developmental toxicity of benzoyl peroxide for OECD SIDS(Screening Information Data Set) program. Male and female Sprague Dawley rats were exposed to benzoyl peroxide at levels of 0, 250, 500 and 1,000 mg/kg/day for 29 days for male and for 41-51 days for female.(omitted)

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Toxicological Study on Nonylphenol using the Soil Nematode, Caenorhabditis elegans (토양선충 Caenorhabditis elegans를 이용한 Nonylphenol의 독성 영향 연구)

  • Roh, Ji-Yeon;Choi, Jin-Hee
    • Environmental Analysis Health and Toxicology
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    • v.21 no.4 s.55
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    • pp.323-330
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    • 2006
  • The aim of current study was to evaluate the toxicity of nonylphenol(NP) on soil nematode, Caenorhabditi elegans. The stress-related gene expression, growth, reproduction and development have been employed to monitor soil toxicity. The 24-h median effect concentrations $(LC_{50s})$ of NP was $0.15mg/L$. The expressions of vitellogenin-6, vitellogenin-2, cytochrome P450 family protein 35a2 and apoptosis enhancer-1 genes were upregulated in C. elegans by NP exposure. Alterations in growth, reproduction and development were also observed in NP-exposed group and especially hatching failure was observed. The overall results indicate that C. elegans has considerable potential as sensitive markers for NP toxicity monitoring.

Arsenic Toxicity in Male Reproduction and Development

  • Kim, Yoon-Jae;Kim, Jong-Min
    • Development and Reproduction
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    • v.19 no.4
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    • pp.167-180
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    • 2015
  • Arsenic is a toxic metalloid that exists ubiquitously in the environment, and affects global health problems due to its carcinogenicity. In most populations, the main source of arsenic exposure is the drinking water. In drinking water, chronic exposure to arsenic is associated with increased risks of various cancers including those of skin, lung, bladder, and liver, as well as numerous other non-cancer diseases including gastrointestinal and cardiovascular diseases, diabetes, and neurologic and cognitive problems. Recent emerging evidences suggest that arsenic exposure affects the reproductive and developmental toxicity. Prenatal exposure to inorganic arsenic causes adverse pregnancy outcomes and children's health problems. Some epidemiological studies have reported that arsenic exposure induces premature delivery, spontaneous abortion, and stillbirth. In animal studies, inorganic arsenic also causes fetal malformation, growth retardation, and fetal death. These toxic effects depend on dose, route and gestation periods of arsenic exposure. In males, inorganic arsenic causes reproductive dysfunctions including reductions of the testis weights, accessory sex organs weights, and epididymal sperm counts. In addition, inorganic arsenic exposure also induces alterations of spermatogenesis, reductions of testosterone and gonadotrophins, and disruptions of steroidogenesis. However, the reproductive and developmental problems following arsenic exposure are poorly understood, and the molecular mechanism of arsenic-induced reproductive toxicity remains unclear. Thus, we further investigated several possible mechanisms underlying arsenic-induced reproductive toxicity.

Isoprocarb induces acute toxicity in developing zebrafish embryos through vascular malformation

  • Park, Hahyun;Song, Gwonhwa;Lim, Whasun
    • Journal of Animal Reproduction and Biotechnology
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    • v.36 no.1
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    • pp.17-24
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    • 2021
  • In this study, the potential toxicity of isoprocarb was demonstrated using zebrafish embryos. We treated isoprocarb (0, 29, and 58 mg/L) to the zebrafish embryos for 72 h then, we estimated morphological changes and apoptotic cell numbers. The increasing extent of apoptosis from the anterior to posterior region of developing zebrafish larvae was correlated with toxicity in the overall development process, including growth and normal organ formation. The appearance of abnormalities in the isoprocarb-treated groups in comparison to normal developing zebrafish larvae was verified using quantitative image analysis based on ImageJ software program. The vascular system comprising a complex interconnection of blood vessels was visualized in vessel-fluorescent transgenic zebrafish (fli1:eGFP). The main vasculature was malformed on isoprocarb treatment, and this was also related to cardiac defects. Taken together, normal embryonic development in zebrafish was interrupted owing to the acute toxicity of isoprocarb.

EVALUATION OF GENETIC TOXICITY FROM ENVIRONMENTAL POLLUTANTS IN DAPHNIA MAGNA AND CHIRONOMUS TENTANS FOR APPLICATION IN ECOLOGICAL RISK ASSESSMENT

  • Park, Sun-Young;Lee, Si-Won;Choi, Jin-Hee
    • Environmental Engineering Research
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    • v.11 no.5
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    • pp.277-284
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    • 2006
  • The genetic toxicity of environmental pollutants, namely, nonylphenol (NP), bisphenol A (BPA) and chloropyriphos (CP) was investigated in aquatic sentinel species, freshwater crustacean, Daphnia magna, and larva of aquatic midge, Chironomus tentans, using Comet assay. Physiological effect of such pollutants was also investigated by studying the specimens' rates of reproduction, growth and survival. Acute toxicity results showed that, as expected, Daphnia was more sensitive than Chironomus to chemical exposure. The order of acute toxicity was CP > NP > BPA in D. magna and NP > CP > BPA in C. tentans. BPA may exert a genotoxic effect on D. magna and C. tentans, given that DNA strand breaks increased in both species exposed to this compound, whereas NP- and CP-induced DNA damage occurred only in C. tentans. In vivo genotoxic data obtained in aquatic sentinel species could provide valuable information for freshwater quality monitoring. The experiments with NP-exposed D. magna showed that the pollutant has long-term effects on reproduction, whereas no short-term effect on DNA integrity was found, being an example of a false-negative result from the biomarkers perspective. This result could be interpreted that other mechanism than genetic alteration might be involved in NP-induced reproduction failure in D. magna. False-positive results from the genotoxic biomarker obtained in BPA-exposed D. magna and in NP-exposed C. tentans make it difficult to use DNA integrity as an early warning biomarker. However, as the mere presence of genotoxic compounds, which are potentially carcinogenic, is of high concern to human and ecosystem health, it could also be important to rapidly and effectively detect genotoxic compounds in the aquatic system in ways that do not necessarily accompany a higher level of alteration. Considering the potential of D. magna and C. tentans as bioindicator species, and the importance of genotoxic biomarkers in ecotoxicity monitoring, DNA damage in these species could provide useful information for environmental risk assessment.

Toxicity Assessment of Titanium (IV) Oxide Nanoparticles Using Daphnia magna (Water Flea)

  • Bang, Seung-Hyuck;Le, Thai-Hoang;Lee, Sung-Kyu;Kim, Pil;Kim, Jong-Soo;Min, Ji-Ho
    • Environmental Analysis Health and Toxicology
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    • v.26
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    • pp.3.1-3.6
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    • 2011
  • Objectives: Titanium dioxide ($TiO_2$), a common nanoparticle widely used in industrial production, is one of nano-sized materials. The purpose of this study was to determine the acute and chronic toxicity of $TiO_2$ using different size and various concentrations on Daphnia magna. Methods: In the acute toxicity test, four concentrations (0, 0.5, 4, and 8 mM) for $TiO_2$ with 250 or 500 nm and five concentrations (0, 0.25, 0.5, 0.75, and 1 mM) for $TiO_2$ with 21 nm were selected to analyze the toxic effect to three groups of ten daphnia neonates over 96 hours. In addition, to better understand their toxicity, chronic toxicity was examined over 21 days using 0, 1, and 10 mM for each type of $TiO_2$. Results: Our results showed that all organisms died before the reproduction time at a concentration of 10 mM of $TiO_2$. In addition, the exposure of anatase (21 nm) particles were more toxic to D. magna, comparing with that of anatase (250 nm) and rutile (500 nm) particles. Conclusions: This study indicated that $TiO_2$ had adverse impacts on the survival, growth and reproduction of D. magna after the 21days exposure. In addition, the number of test organisms that were able to reproduce neonates gradually were reduced as the size of $TiO_2$ tested was decreased.

The Acute and Chronic Toxicity Studies of Herbicide, Molinate to Waterfleas (Molinate의 물벼룩에 대한 급성 및 만성독성 연구)

  • Shin, On-Sup;Kim, Byung-Seok;Park, Yeon-Ki;Park, Kyung-Hoon;Lee, Je-Bong;Kyung, Kee-Sung;Ahn, Young-Joon
    • The Korean Journal of Pesticide Science
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    • v.12 no.3
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    • pp.215-221
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    • 2008
  • To assess the impact of molinate on freshwater aquatic organisms, acute and chronic toxicity studies for waterfleas were conducted. In acute toxicity studies for Daphnia magna, and Moina macrocopa, the 48-h $EC_{50}$ values were 11.4 and 8.3 mg/L respectively. And in reproduction toxicity studies for the same species, the NOEC's were 2.5 and 2.0 mg/L respectively. These results suggest that waterfleas have simillar sensitivity to molinate. On the other hand, the NOEC for 3-generation toxicity of moina macrocopa 0.16 mg/L, was much lower than those of acute values. This studies concludes that molinate has minimal risk to waterfleas in river.

A Study of Ecotoxicity Test for Byproducts of Ozone in the Ballast Water Treatment System with Ozonation

  • Park, Sung-Jin;Ha, Shin-Young;Kim, In-Soo
    • Journal of Navigation and Port Research
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    • v.35 no.9
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    • pp.741-747
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    • 2011
  • Ecological toxicity testing of the whole-effluent from the ozone ballast water treatment system was conducted as specified in the quality assurance project plans (QAPP). The growth inhibition test with microalgae, acute aquatic toxicity test with the Rotifer reproduction, toxicity test (or population growth) with the Rotifer, survival and growth toxicity test with larval fish and sediment toxicity test with amphipod were carried out to evaluate ecological toxicity on the movile test barge.