国家毒理学计划(NTP)对F344/N大鼠和B6C3F1小鼠灌胃给予过苯甲酸丁酯(CAS No. 614-45-9)毒性研究的技术报告。

Toxicity report series Pub Date : 1992-07-01
H.B. Matthews
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引用次数: 0

摘要

过苯甲酸丁酯(t-BP)是一种相对稳定的脂溶性有机过氧化物,广泛应用于聚合物工业。研究旨在确定t-BP在各种生物介质中的稳定性,其在完整动物体内的皮肤吸收和分布,以及t-BP在大鼠和小鼠两性口服14天或13周时的毒性。在遗传毒性研究中,发现t-BP对鼠伤寒沙门氏菌菌株TA100、TA1537和TA98具有诱变作用,无论是否具有代谢激活作用。t- bp在体外诱导中国仓鼠卵巢细胞的姐妹染色单体交换和染色体畸变,但在13周的研究中未诱导小鼠外周血形成微核。稳定性研究表明,t-BP在剂量配方中足够稳定,可以通过灌胃、静脉注射或皮肤给药。然而,t-BP在血液、胃内容物、肝脏匀浆或谷胱甘肽存在时降解迅速。t-BP的初始降解产物为苯甲酸和丁醇。对t-BP处置的研究确定,给大鼠皮肤剂量的约16%被吸收并迅速消除,没有组织积累。同样,静脉给药的t-BP被迅速降解和消除,主要在尿液中,在任何组织中没有明显的积累。由于认为皮肤吸收不足以给予毒性剂量,因此采用灌胃方式进行t-BP毒性研究。大鼠、小鼠各性别5只动物14天的毒性研究结果表明,玉米油灌胃给药剂量为70 ~ 1112 mg/kg的t-PB未产生明显的全身毒性。t- BP对小鼠的毒性主要局限于接受最高剂量的雄性和雌性小鼠胃重的增加。这种毒性的特征是前胃上皮增生、溃疡和急性炎症。在为期14天的研究中,还给予等量剂量的t-BP降解产物(丁醇和苯甲酸),以确定t-BP毒性是否可归因于母体化合物或其化学降解和/或代谢的产物。这些研究结果表明,等摩尔剂量的丁醇对两性和物种都没有毒性。在接受最高剂量(642 mg/kg)的小鼠中,两性均观察到苯甲酸的一些全身毒性,但在大鼠中没有。在研究的第一周内,给药动物的不良状况和几例死亡证明了毒性。显微镜下未观察到病变,推测这种毒性可能是由于酸中毒。在为期13周的研究中,t-BP通过水灌胃给予10只大鼠和10只雌雄小鼠,剂量高达500 mg/kg。剂量导致最高剂量组的体重增加受到抑制,前胃重量呈剂量依赖性增加。多数给药组大鼠前胃粘膜均出现增生,且增生程度随剂量增加而加重。增生的特征是鳞状上皮细胞增多和嗜碱性细胞增多,并伴有不同程度的角化过度。在小鼠中观察到的t-BP毒性仅限于大多数剂量组的前胃重量增加,而在接受最高剂量的小鼠中,腺胃重量的增加幅度较小。除低剂量组外,所有小鼠的前胃毒性表现为鳞状上皮增生呈剂量依赖性增加。根据本报告的结果,我们认为t-BP诱导大鼠和小鼠前胃病变的未观察到不良反应水平(NOAEL)约为30 mg/kg。口服剂量高达1112 mg/kg时,两种物种均未观察到全身毒性。苯碳过氧酸;1、1-dimethylester;Esperox 10;Trigonox C;t-BP。
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NTP technical report on the toxicity studies of t-Butyl Perbenzoate (CAS No. 614-45-9) Administered By Gavage To F344/N Rats And B6C3F1 Mice.

t-Butyl perbenzoate (t-BP) is a relatively stable, lipid-soluble, organic peroxide widely used in the polymer industry. Studies were designed to determine the stability of t-BP in various biological media, its dermal absorption and distribution in intact animals, and the toxicity of t-BP when administered orally to both sexes of rats and mice for 14 days or 13 weeks. In genetic toxicity studies, t-BP was found to be mutagenic in Salmonella typhimurium strains TA100, TA1537, and TA98, with and without metabolic activation. t-BP-induced sister-chromatid exchange and chromosomal aberrations in Chinese hamster ovary cells in vitro but did not induce formation of micronuclei in peripheral blood in mice in the 13-week studies. Stability studies indicated t-BP was sufficiently stable in dose formulations to permit administration by gavage, intravenous injection, or dermally. However, t-BP degraded rapidly in blood, stomach contents, and liver homogenates, or in the presence of glutathione. Initial degradation products of t-BP are benzoic acid and t-butanol. Studies of t-BP disposition determined that approximately 16% of dermal doses administered to rats was absorbed and rapidly eliminated without tissue accumulation. Similarly, t-BP given intravenously was rapidly degraded and eliminated, primarily in urine, with no apparent accumulation in any tissue. Because dermal absorption was considered insufficient to administer a toxic dose, studies of t-BP toxicity were performed using gavage administration. Results of 14-day toxicity studies with 5 animals of each sex of rats and mice indicated that t-PB, administered by gavage in corn oil in doses ranging from 70 to 1112 mg/kg, produced no marked signs of systemic toxicity. Toxicity in mice, attributable to t- BP, was limited largely to increased stomach weights in males and females receiving the highest doses. This toxicity was characterized by forestomach epithelial hyperplasia, ulceration, and acute inflammation. Equimolar doses of the degradation products of t-BP (t-butanol and benzoic acid) also were administered in the 14-day studies to determine if t-BP toxicity could be attributed to the parent compound or products of its chemical degradation and/or metabolism. Results of these studies indicated that equimolar doses of t-butanol were not toxic in either sex or species. Some systemic toxicity of benzoic acid was observed in both sexes of mice, but not rats, receiving the highest dose (642 mg/kg). Toxicity was evidenced by the poor condition of dosed animals and in several deaths during the first week of the study. No lesions were observed microscopically, and it is speculated that this toxicity may have been due to acidosis. In the 13-week studies, t-BP was administered by gavage in water to 10 rats and 10 mice of each sex, at doses up to 500 mg/kg. The doses resulted in depressed body-weight gains in the highest dose groups and in dose-dependent increases in forestomach weights. Hyperplasia of the forestomach mucosa was observed in most groups of dosed rats and increased in severity with dose. Hyperplasia was characterized by increased cellularity and basophilia of the squamous epithelium with variable degrees of hyperkeratosis. t-BP toxicity observed in mice was limited to increased forestomach weight in most dose groups and to less dramatic increases in glandular stomach weight in mice receiving the highest doses. Forestomach toxicity was characterized by dose-dependent increases in hyperplasia of the squamous epithelium in all mice except those in the low dose group. Based on the results presented in this report, it is concluded that the no-observed-adverse-effect-level (NOAEL) for t-BP to induce forestomach lesions in rats and mice is approximately 30 mg/kg. Systemic toxicity was not observed in either species with oral doses as high as 1112 mg/kg. Synonyms: Benzenecarboperoxoic acid; 1,1-dimethylester; Esperox 10; Trigonox C; t-BP.

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