Rudel Ruthann A, Perovich Laura J
Silent Spring Institute, 29 Crafts Street, Newton, MA 02458.
Atmos Environ (1994). 2009 Jan 1;43(1):170-181. doi: 10.1016/j.atmosenv.2008.09.025.
The past 50 years have seen rapid development of new building materials, furnishings, and consumer products and a corresponding explosion in new chemicals in the built environment. While exposure levels are largely undocumented, they are likely to have increased as a wider variety of chemicals came into use, people began spending more time indoors, and air exchange rates decreased to improve energy efficiency. As a result of weak regulatory requirements for chemical safety testing, only limited toxicity data are available for these chemicals. Over the past 15 years, some chemical classes commonly used in building materials, furnishings, and consumer products have been shown to be endocrine disrupting chemicals-that is they interfere with the action of endogenous hormones. These include PCBs, used in electrical equipment, caulking, paints and surface coatings; chlorinated and brominated flame retardants, used in electronics, furniture, and textiles; pesticides, used to control insects, weeds, and other pests in agriculture, lawn maintenance, and the built environment; phthalates, used in vinyl, plastics, fragrances, and other products; alkylphenols, used in detergents, pesticide formulations, and polystyrene plastics; and parabens, used to preserve products like lotions and sunscreens. This paper summarizes reported indoor and outdoor air concentrations, chemical use and sources, and toxicity data for each of these chemical classes. While industrial and transportation-related pollutants have been shown to migrate indoors from outdoor sources, it is expected that indoor sources predominate for these consumer product chemicals; and some studies have identified indoor sources as the predominant factor influencing outdoor ambient air concentrations in densely populated areas. Mechanisms of action, adverse effects, and dose-response relationships for many of these chemicals are poorly understood and no systematic screening of common chemicals for endocrine disrupting effects is currently underway, so questions remain as to the health impacts of these exposures.
在过去的50年里,新型建筑材料、家具和消费品迅速发展,建筑环境中的新化学品也相应激增。虽然接触水平大多没有记录,但随着更多种类的化学品投入使用、人们开始在室内花费更多时间以及空气交换率降低以提高能源效率,接触水平可能有所增加。由于对化学品安全测试的监管要求薄弱,这些化学品仅有有限的毒性数据。在过去15年中,一些常用于建筑材料、家具和消费品的化学类别已被证明是内分泌干扰化学物质,即它们会干扰内源激素的作用。这些化学物质包括用于电气设备、填缝、油漆和表面涂层的多氯联苯;用于电子产品、家具和纺织品的氯化和溴化阻燃剂;用于农业、草坪维护和建筑环境中控制昆虫、杂草及其他害虫的杀虫剂;用于乙烯基、塑料、香料和其他产品的邻苯二甲酸盐;用于洗涤剂、农药配方和聚苯乙烯塑料的烷基酚;以及用于保存乳液和防晒霜等产品的对羟基苯甲酸酯。本文总结了这些化学类别各自报告的室内和室外空气浓度、化学用途和来源以及毒性数据。虽然工业和交通相关污染物已被证明会从室外来源迁移到室内,但预计这些消费品化学品的室内来源占主导地位;一些研究已确定室内来源是影响人口密集地区室外环境空气浓度的主要因素。许多此类化学品的作用机制、不良影响和剂量反应关系尚不清楚,目前也没有对常见化学品进行内分泌干扰效应的系统筛查,因此这些接触对健康的影响仍存在疑问。