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戊二醛的毒理学、医学及工业卫生方面,特别提及它在冷消毒程序中的杀菌用途。

Toxicological, medical and industrial hygiene aspects of glutaraldehyde with particular reference to its biocidal use in cold sterilization procedures.

作者信息

Ballantyne B, Jordan S L

机构信息

Applied Toxicology Group, Union Carbide Corporation, 39 Old Ridgebury Road, Danbury, CT 06817-0001, USA.

出版信息

J Appl Toxicol. 2001 Mar-Apr;21(2):131-51. doi: 10.1002/jat.741.

DOI:10.1002/jat.741
PMID:11288136
Abstract

Aqueous solutions of > or =5% glutaraldehyde (GA) are of moderate acute peroral toxicity and those of < or =2% are of slight toxicity. By single sustained skin contact, aqueous GA solutions of > or =45% are of moderate acute percutaneous toxicity, those of 25% are of slight toxicity and those of </=15% do not present an acute percutaneous hazard. Vapor generated at ambient temperature may cause sensory irritant effects to the eye and respiratory tract, but not acute respiratory tract injury. The 50% decrease in respiratory rate (rd(50)) is 13.86 ppm. A 0.1% solution of GA is not irritating to the eye; the threshold for conjunctival irritation is 0.2% and for corneal injury it is 1.0%. Eye injury is moderate at 2% and severe at > or =5%. Primary skin irritation depends on the duration and contact site, occlusion and solvent. By sustained contact, the threshold for skin irritation is 1%, above which erythema and edema are dose related. With 45% and higher, skin corrosion may occur. There is a low incidence of skin sensitizing reactions, with an eliciting threshold of 0.5% aqueous GA. However, GA is neither phototoxic nor photosensitizing. Subchronic repeated exposure studies by the peroral route show only renal physiological compensatory effects, secondary to reduced water consumption. Repeated skin contact shows only minor skin irritant effects without systemic toxicity. By subchronic vapor exposure, effects are limited to the nasal mucosa at 1.0 ppm, with a no-effect concentration generally at 0.1 ppm. There is no evidence for systemic target organ or tissue toxicity by subchronic repeated exposure by any route. A chronic drinking water study showed an apparent increase, in females only, of large granular cell lymphocytic leukemia but this was not dosage related. This is most likely the result of a modifying effect on the factor(s) responsible for the expression of this commonly occurring rat neoplasm. A chronic (2-year) inhalation toxicity/oncogenicity study showed inflammatory changes in the anterior nasal cavity but no neoplasms or systemic toxicity. In vitro genotoxicity studies--bacterial mutagenicity, forward gene mutation (HGPRT and TK loci), sister chromatid exchange, chromosome aberration, UDS and DNA repair tests--have given variable results, ranging from no effect through to weak positive. In vivo genotoxicity studies--micronucleus, chromosome aberration, dominant lethal and Drosophila tests--generally have shown no activity but one mouse intraperitoneal study showed bone marrow cell chromosome aberrations. Developmental toxicity studies show GA not to be teratogenic, and a two-generation study showed no adverse reproductive effects. Percutaneous pharmacokinetic studies showed low skin penetration, with lowest values measured in vitro in rats and human skin. Overexposure of humans produces typical sensory irritant effects on the eye, skin and respiratory tract. Some reports have described an asthmatic-like reaction by overexposure to GA vapor. In most cases this resembles reactive airways dysfunction syndrome, and the role of immune mechanisms is uncertain. Local mucosal effects may occur if medical instruments or endoscopes are not adequately decontaminated. Protection of individuals from the potential adverse effects of GA exposure requires that there be adequate protection of the skin, eyes and respiratory tract. The airborne concentration of GA vapor should be kept below the recommended safe exposure level (e.g. the threshold limit value) by the use of engineering controls. Those who work with GA should, through a training program, be aware of the properties of GA, its potential adverse effects, how to handle the material safely and how to deal with accidental situations involving GA. If effects develop in exposed workers, the reasons should be determined immediately and corrective methods initiated. (c) 2001 John Wiley & Sons, Ltd.

摘要

浓度大于或等于5%的戊二醛(GA)水溶液具有中等程度的急性经口毒性,而浓度小于或等于2%的则具有轻微毒性。通过单次持续性皮肤接触,浓度大于或等于45%的GA水溶液具有中等程度的急性经皮毒性,25%的具有轻微毒性,而浓度小于或等于15%的不存在急性经皮危害。在环境温度下产生的蒸汽可能会对眼睛和呼吸道造成感觉刺激,但不会造成急性呼吸道损伤。呼吸速率降低50%(rd(50))为13.86 ppm。0.1%的GA溶液对眼睛无刺激性;结膜刺激阈值为0.2%,角膜损伤阈值为1.0%。2%时眼睛损伤为中度,大于或等于5%时为重度。原发性皮肤刺激取决于接触持续时间、接触部位、封闭情况和溶剂。通过持续性接触,皮肤刺激阈值为1%,超过该浓度时红斑和水肿与剂量相关。浓度为45%及更高时,可能会发生皮肤腐蚀。皮肤致敏反应发生率较低,GA水溶液的激发阈值为0.5%。然而,GA既无光毒性也无光敏性。经口途径的亚慢性重复暴露研究仅显示肾脏生理代偿效应,这是由于饮水量减少所致。重复皮肤接触仅显示轻微的皮肤刺激作用,无全身毒性。通过亚慢性蒸汽暴露,在1.0 ppm时影响仅限于鼻粘膜,无效应浓度一般为0.1 ppm。没有证据表明通过任何途径进行亚慢性重复暴露会对全身靶器官或组织产生毒性。一项慢性饮用水研究表明,仅在雌性大鼠中,大颗粒细胞淋巴细胞白血病明显增加,但这与剂量无关。这很可能是对负责这种常见大鼠肿瘤表达的因素产生修饰作用的结果。一项慢性(2年)吸入毒性/致癌性研究表明,前鼻腔有炎症变化,但无肿瘤或全身毒性。体外遗传毒性研究——细菌诱变性、正向基因突变(HGPRT和TK位点)、姐妹染色单体交换、染色体畸变、UDS和DNA修复试验——结果各异,从无影响到弱阳性。体内遗传毒性研究——微核、染色体畸变、显性致死和果蝇试验——一般显示无活性,但一项小鼠腹腔内研究显示骨髓细胞染色体畸变。发育毒性研究表明GA无致畸性,一项两代研究表明无不良生殖影响。经皮药代动力学研究表明皮肤渗透率低,在大鼠和人皮肤的体外测量值最低。人体过度暴露会对眼睛、皮肤和呼吸道产生典型的感觉刺激作用。一些报告描述了过度暴露于GA蒸汽会引发类似哮喘的反应。在大多数情况下,这类似于反应性气道功能障碍综合征,免疫机制的作用尚不确定。如果医疗器械或内窥镜未得到充分消毒,可能会发生局部粘膜效应。保护个人免受GA暴露的潜在不利影响需要对皮肤、眼睛和呼吸道进行充分保护。通过工程控制,应将GA蒸汽的空气传播浓度保持在推荐的安全暴露水平以下(例如阈限值)。接触GA的人员应通过培训计划了解GA的特性、其潜在的不利影响、如何安全处理该物质以及如何应对涉及GA的意外情况。如果接触GA的工人出现症状,应立即确定原因并采取纠正措施。(c)2001约翰·威利父子有限公司

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