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An F1-Extended One-Generation Reproductive Toxicity Study in Crl:CD(SD) Rats With 24-Dichlorophenoxyacetic Acid

机译:F1扩展的Crl:CD(SD)大鼠用24-二氯苯氧基乙酸的单代生殖毒性研究

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摘要

2,4-Dichlorophenoxyacetic acid (2,4-D) was assessed for systemic toxicity, reproductive toxicity, developmental neurotoxicity (DNT), developmental immunotoxicity (DIT), and endocrine toxicity. CD rats (27/sex/dose) were exposed to 0, 100, 300, 600 (female), or 800 (male) ppm 2,4-D in diet. Nonlinear toxicokinetic behavior was shown at high doses; the renal clearance saturation threshold for 2,4-D was exceeded markedly in females and slightly exceeded in males. Exposure was 4 weeks premating, 7 weeks postmating for P1 males and through lactation for P1 females. F1 offspring were examined for survival and development, and at weaning, pups were divided in cohorts, by sex and dose, and by systemic toxicity (10), DNT (10), DIT (20), and reproductive toxicity (≥ 23). Remaining weanlings were evaluated for systemic toxicity and neuropathology (10–12). Body weight decreased during lactation in high-dose P1 females and in F1 pups. Kidney was the primary target organ, with slight degeneration of proximal convoluted tubules observed in high-dose P1 males and in high-dose F1 males and females. A slight intergenerational difference in kidney toxicity was attributed to increased intake of 2,4-D in F1 offspring. Decreased weanling testes weights and delayed preputial separation in F1 males were attributed to decreased body weights. Endocrine-related effects were limited to slight thyroid hormone changes and adaptive histopathology in high-dose GD 17 dams seen only at a nonlinear toxicokinetic dose. 2,4-D did not cause reproductive toxicity, DNT, or DIT. The “No Observed Adverse Effect Level” for systemic toxicity was 300 ppm in both males (16.6mg/kg/day) and females (20.6mg/kg/day), which is approximately 6700- to 93 000-fold higher than that reported for 2,4-D exposures in human biomonitoring studies.
机译:评估了2,4-二氯苯氧基乙酸(2,4-D)的全身毒性,生殖毒性,发育神经毒性(DNT),发育免疫毒性(DIT)和内分泌毒性。 CD大鼠(27 /性别/剂量)在饮食中暴露于0、100、300、600(雌性)或800(雄性)ppm 2,4-D。高剂量时表现出非线性的毒代动力学行为。女性明显超过了2,4-D的肾清除率饱和阈值,而男性则略有超过。 P1雄性的暴露时间为早产4周,孕后7周,而P1雌性则为哺乳期。检查F1子代的存活和发育,在断奶时,按性别,剂量,系统毒性(10),DNT(10),DIT(20)和生殖毒性(≥23)将幼崽按队列进行分组。评估其余的断奶的全身毒性和神经病理学(10-12)。高剂量的P1雌性和F1幼崽的泌乳期体重下降。肾脏是主要的靶器官,在大剂量的P1雄性和大剂量的F1雄性和雌性中观察到近端的曲折小管轻微退化。肾脏毒性的几代人之间的细微差别归因于F1后代中2,4-D的摄入增加。 F1雄性的断奶睾丸重量减少和前齿分离延迟归因于体重下降。内分泌相关的影响仅限于仅在非线性毒代动力学剂量下观察到的高剂量GD 17大坝中的甲状腺激素轻微变化和适应性组织病理学。 2,4-D不会引起生殖毒性,DNT或DIT。男性(16.6mg / kg /天)和女性(20.6mg / kg /天)的全身毒性“未观察到不良反应水平”均为300 ppm,比报道的高出约6700-9.3倍人类生物监测研究中的2,4-D暴露。

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