Williams Gary M, Iatropoulos Michael J
New York Medical College, Department of Pathology, Chemical Safety Laboratory, Valhalla, NY 10595, USA.
Regul Toxicol Pharmacol. 2009 Feb;53(1):6-15. doi: 10.1016/j.yrtph.2008.09.005. Epub 2008 Oct 5.
Ethyl acrylate (EA) is an acrylic monomer used in the manufacture of a variety of polymers and copolymers as components of many commercially important products. Human exposure to EA occurs primarily in the workplace via inhalation or dermal contact. In F344 rat and B6C3F(1) mouse studies of EA carcinogenicity conducted by the National Toxicology Program [National Toxicology Program, NTP, 1986. Carcinogenesis Studies of Ethyl Acrylate (CAS No. 140-88-5) in F344/N Rats and B6C3F(1) Mice (Gavage Studies) (Tech. Rep. Ser. No. 259; NIH Publication No. 87-2515), Research Triangle Park, NC, USA], the only increased tumor incidences was in squamous cell papillomas and carcinomas of the forestomach, when EA was administered by gavage in corn oil at 100 or 200mg/kg/day (high dose; HD). The neoplasms were preceded by forestomach irritation, inflammation, hyperkeratosis and hyperplasia of the forestomach mucosa. In studies in which rats and mice were exposed at comparable doses to EA in drinking water, by inhalation, or by dermal application, no neoplasms in the forestomach or in any other tissue were reported. EA exhibited clastogenicity and related mutagenicity in vitro, but was non-genotoxic in vivo, including in the forestomach of treated rats. The in vitro clastogenicity response correlates well with cellular toxicity, mediated by non-protein sulfhydryl depletion and mitochondrial impairment. Thus, the carcinogenicity in the forestomach can be ascribed to a non-genotoxic mode of action (MOA). The forestomach mucosal hyperplastic and even dysplastic changes, observed chronically, were reversible, provided the HD exposure was not longer than 6months. This again supports a non-genotoxic MOA. In addition, the route and rate of EA exposure in rodents for forestomach neoplasia are irrelevant to potential human exposure, since humans do not have forestomach and are not exposed to EA by oral bolus. Thus, the weight of evidence indicates that the tumors produced in the rodent carcinogenicity studies arise from conditions that are irrelevant for human risk assessment.
丙烯酸乙酯(EA)是一种丙烯酸单体,用于制造各种聚合物和共聚物,是许多商业上重要产品的组成成分。人类接触EA主要通过工作场所的吸入或皮肤接触。在美国国家毒理学计划(National Toxicology Program, NTP, 1986. Carcinogenesis Studies of Ethyl Acrylate (CAS No. 140-88-5) in F344/N Rats and B6C3F(1) Mice (Gavage Studies) (Tech. Rep. Ser. No. 259; NIH Publication No. 87-2515), Research Triangle Park, NC, USA)对F344大鼠和B6C3F(1)小鼠进行的EA致癌性研究中,仅在以100或200mg/kg/天(高剂量;HD)的玉米油灌胃方式给予EA时,前胃鳞状细胞乳头瘤和癌的肿瘤发生率有所增加。这些肿瘤之前存在前胃刺激、炎症、角化过度和前胃黏膜增生。在大鼠和小鼠通过饮用水、吸入或皮肤涂抹接触相当剂量EA的研究中,未报告前胃或任何其他组织出现肿瘤。EA在体外表现出致断裂性和相关的诱变性,但在体内无遗传毒性,包括在接受治疗的大鼠前胃中。体外致断裂性反应与由非蛋白质巯基耗竭和线粒体损伤介导的细胞毒性密切相关。因此,前胃的致癌性可归因于非遗传毒性作用模式(MOA)。长期观察到的前胃黏膜增生甚至发育异常变化在HD暴露不超过6个月的情况下是可逆的。这再次支持了非遗传毒性MOA。此外,啮齿动物前胃癌变中EA暴露的途径和速率与潜在的人类暴露无关,因为人类没有前胃且不会通过口服大剂量接触EA。因此,证据权重表明,啮齿动物致癌性研究中产生的肿瘤源于与人类风险评估无关的条件。