Int J Toxicol. 2005;24 Suppl 2:21-50. doi: 10.1080/10915810590953842.
Polyacrylamide is a polymer of controllable molecular weight formed by the polymerization of acrylamide monomers available in one of three forms: solid (powder or micro beads), aqueous solution, or inverse emulsions (in water droplets coated with surfactant and suspended in mineral oil). Residual acrylamide monomer is likely an impurity in most Polyacrylamide preparations, ranging from <1 ppm to 600 ppm. Higher levels of acrylamide monomers are present in the solid form compared to the other two forms. Polyacrylamide is reportedly used in 110 cosmetic formulations, at concentrations ranging from 0.05% to 2.8%. Residual levels of acrylamide in Polyacrylamide can range from <.01% to 0.1%, although representative levels were reported at 0.02% to 0.03%. Because of the large sizes of Polyacrylamide polymers, they do not penetrate the skin. Polyacrylamide itself is not significantly toxic. For example, an acute oral toxicity study of Polyacrylamide in rats reported that a single maximum oral dose of 4.0 g/kg body weight was tolerated. In subchronic oral toxicity studies, rats and dogs treated with Polyacrylamide at doses up to 464 mg/kg body weight showed no signs of toxicity. Several 2-year chronic oral toxicity studies in rats and dogs fed diets containing up to 5% Polyacrylamide had no significant adverse effects. Polyacrylamide was not an ocular irritant in animal tests. No compound-related lesions were noted in a three-generation reproductive study in which rats were fed 500 or 2000 ppm Polyacrylamide in their diet. Polyacrylamide was not carcinogenic in several chronic animal studies. Human cutaneous tolerance tests performed to evaluate the irritation of 5% (w/w) Polyacrylamide indicated that the compound was well tolerated. Acrylamide monomer residues do penetrate the skin. Acrylamide tested in a two-generation reproductive study at concentrations up to 5 mg/kg day(- 1) in drinking water, was associated with prenatal lethality at the highest dose, with evidence of parental toxicity. The no adverse effects level was close to the 0.5 mg/kg day(- 1) dose. Acrylamide tested in a National Toxicology Program (NTP) reproductive and neurotoxicity study at 3, 10, and 30 ppm produced no developmental or female reproductive toxicity. However, impaired fertility in males was observed, as well as minimal neurotoxic effects. Acrylamide neurotoxicity occurs in both the central and peripheral nervous systems, likely through microtubule disruption, which has been suggested as a possible mechanism for genotoxic effects of acrylamide in mammalian systems. Acrylamide was genotoxic in mammalian in vitro and in vivo assays. Acrylamide was a tumor initiator, but not an initiator/promoter, in two different mouse strains at a total dose of 300 mg/kg (6 doses over 2 weeks) resulting in increased lung adenomas and carcinomas without promotion. Acrylamide was tested in two chronic bioassays using rats. In one study, increased incidence of mammary gland tumors, glial cell tumors, thyroid gland follicular tumors, oral tissue tumors, uterine tumors and clitoral gland tumors were noted in female rats. In male rats, the number of tumors in the central nervous system (CNS), thyroid gland, and scrotum were increased with acrylamide exposure. In the second study, using higher doses and a larger number of female rats, glial cell tumors were not increased, nor was there an increase in mammary gland, oral tissue, clitoral gland, or uterine tumors. Tumors of the scrotum in male rats were confirmed, as were the thyroid gland follicular tumors in males and females. Taken together, there was a dose-dependent, but not statistically significant, increase in the number of astrocytomas. Different human lifetime cancer risk predictions have resulted, varying over three orders of magnitude from 2 x 10(- 3) to 1.9 x 10(- 6). In the European Union, acrylamide has been limited to 0.1 ppm for leave-on cosmetic products and 0.5 ppm for other cosmetic products. An Australian risk assessment suggested negligible health risks from acrylamide in cosmetics. The Cosmetic Ingredient Review (CIR) Expert Panel acknowledged that acrylamide is a demonstrated neurotoxin in humans and a carcinogen in animal tests, but that neurotoxic levels could not be attained by use of cosmetics. Although there are mechanisms of action of acrylamide that have been proposed for tumor types seen in rat studies that suggest they may be unique to the rat, the Panel was not convinced that these results could be disregarded as a species-specific finding with no relevance to human health and safety. Based on the genotoxicity and carcinogenicity data, the Panel does not believe that acrylamide is a genotoxic carcinogen in the usual manner and that several of the risk assessment approaches have overestimated the human cancer risk. The Panel did conclude, however, that it was appropriate to limit acrylamide levels to 5 ppm in cosmetic formulations.
聚丙烯酰胺是一种分子量可控的聚合物,由丙烯酰胺单体聚合而成,有三种形式:固体(粉末或微珠)、水溶液或反相乳液(包裹在表面活性剂中并悬浮在矿物油中的水滴)。在大多数聚丙烯酰胺制剂中,残留的丙烯酰胺单体可能是一种杂质,含量从<1 ppm到600 ppm不等。与其他两种形式相比,固体形式中丙烯酰胺单体的含量更高。据报道,聚丙烯酰胺用于110种化妆品配方中,浓度范围为0.05%至2.8%。聚丙烯酰胺中丙烯酰胺的残留水平可从<0.01%至0.1%,不过据报道典型水平为0.02%至0.03%。由于聚丙烯酰胺聚合物体积较大,它们不会穿透皮肤。聚丙烯酰胺本身毒性并不显著。例如,一项对大鼠进行的聚丙烯酰胺急性口服毒性研究报告称,单次最大口服剂量为4.0 g/kg体重时,大鼠可以耐受。在亚慢性口服毒性研究中,用高达464 mg/kg体重的剂量处理大鼠和狗,未显示出毒性迹象。在几项对大鼠和狗进行的为期两年的慢性口服毒性研究中,给它们喂食含高达5%聚丙烯酰胺的饮食,未产生明显的不良影响。在动物试验中,聚丙烯酰胺不是眼部刺激物。在一项三代生殖研究中,给大鼠喂食饮食中含有500或2000 ppm聚丙烯酰胺,未发现与化合物相关的损伤。在几项慢性动物研究中,聚丙烯酰胺没有致癌性。进行人体皮肤耐受性试验以评估5%(w/w)聚丙烯酰胺的刺激性,结果表明该化合物耐受性良好。丙烯酰胺单体残留物确实会穿透皮肤。在一项两代生殖研究中,饮用水中丙烯酰胺浓度高达5 mg/kg·天⁻¹,在最高剂量下与产前致死率相关,并伴有母体毒性证据。无不良影响水平接近0.5 mg/kg·天⁻¹剂量。在国家毒理学计划(NTP)的一项生殖和神经毒性研究中,对丙烯酰胺在3、10和30 ppm剂量下进行测试,未产生发育毒性或雌性生殖毒性。然而,观察到雄性生育能力受损以及轻微的神经毒性作用。丙烯酰胺的神经毒性发生在中枢神经系统和周围神经系统,可能是通过微管破坏,这被认为是丙烯酰胺在哺乳动物系统中产生遗传毒性作用的一种可能机制。丙烯酰胺在哺乳动物的体外和体内试验中具有遗传毒性。在两种不同的小鼠品系中,丙烯酰胺在总剂量为300 mg/kg(2周内6剂)时是一种肿瘤引发剂,但不是引发剂/促进剂,导致肺腺瘤和癌增加而无促进作用。在两项使用大鼠的慢性生物测定中对丙烯酰胺进行了测试。在一项研究中,雌性大鼠乳腺肿瘤、神经胶质细胞瘤、甲状腺滤泡肿瘤、口腔组织肿瘤、子宫肿瘤和阴蒂腺肿瘤的发生率增加。在雄性大鼠中,中枢神经系统(CNS)、甲状腺和阴囊中的肿瘤数量因接触丙烯酰胺而增加。在第二项研究中,使用更高剂量和更多雌性大鼠,神经胶质细胞瘤没有增加,乳腺、口腔组织、阴蒂腺或子宫肿瘤也没有增加。雄性大鼠阴囊肿瘤以及雄性和雌性大鼠的甲状腺滤泡肿瘤得到证实。总体而言,星形细胞瘤的数量有剂量依赖性增加,但无统计学意义。不同的人类终生癌症风险预测结果各不相同,相差三个数量级,从2×10⁻³到1.9×10⁻⁶。在欧盟,丙烯酰胺在免洗化妆品中的限量为0.1 ppm,在其他化妆品中的限量为0.5 ppm。澳大利亚的一项风险评估表明,化妆品中的丙烯酰胺对健康的风险可忽略不计。化妆品成分审查(CIR)专家小组承认,丙烯酰胺在人体中是一种已证实的神经毒素,在动物试验中是一种致癌物,但使用化妆品不会达到神经毒性水平。尽管在大鼠研究中观察到的肿瘤类型存在丙烯酰胺的作用机制,表明它们可能是大鼠特有的,但专家小组不相信这些结果可以作为与人类健康和安全无关的物种特异性发现而被忽视。基于遗传毒性和致癌性数据,专家小组认为丙烯酰胺并非通常意义上的遗传毒性致癌物,并且几种风险评估方法高估了人类癌症风险。然而,专家小组确实得出结论,在化妆品配方中将丙烯酰胺水平限制在5 ppm是合适的。