Cooper R L, Kavlock R J
Reproductive Toxicology Division, National Health and Environmental Effects Research Laboratory, US Environmental Protection Agency, Research Triangle Park, North Carolina 27711, USA.
J Endocrinol. 1997 Feb;152(2):159-66. doi: 10.1677/joe.0.1520159.
It is clear that the endocrine system presents a number of target sites for the induction of adverse effects by environmental agents (Fig. 1). There are numerous examples demonstrating that reproductive and developmental processes may be exquisitely sensitive to exposure and there are clear effects induced by presumed endocrine-disrupting chemicals in a variety of species. The concerns raised by studies of wildlife and humans place added significance on a better understanding of the myriad of effects attributed to endocrine disruptors. But there remains a large void between the study of relatively high exposure levels used in laboratory settings versus the relatively low levels found in the general environment. It is also equally clear that the term "endocrine disruption' has been applied to situations where the biological basis is far from conclusive. This may be a moot point in situations where populations are experiencing adverse effects on reproduction, but as scientists we must be vigilant of the appropriate use of descriptive terminology, particularly in cases where public awareness and concern are as great as this. Not only is there a need for better test procedures (both in vivo and in vitro) to characterize the potential of environmental agents to disrupt endocrine function in laboratory species, but there is also a need for a more comprehensive understanding of the normal physiological processes associated with reproduction and development in those wildlife species studied. At the same time, obtaining better information on the transport, fate and bioavailability of chemicals released into the environment remains an important but imposing task. The goals of risk characterization are to carefully delineate cause-and-effect relationships, define the dose-response relationships, and determine whether environmental exposures exceed acceptable levels. A concerted research effort is needed to fill the voids in our knowledge and reduce the large uncertainties that exist today. Only then can regulatory actions take place within the confines of legislative mandates, remediation strategies and considerations of international use and transport. Towards this end, the US Environmental Protection Agency (EPA) sponsored two workshops in 1995 (Ankley et al. 1996, Kavlock et al. 1996) at which groups of international scientists began the process of identifying research needs. Similar efforts also took place in several European countries at about the same time (Danish Environmental Protection Agency 1995, Medical Research Council 1995, Umweltbundesamt 1995). More recently, a Working Group on Endocrine Disruptors has been established within the Committee on the Environment and Natural Resources of the US Government's National Science and Technology Council. The objectives of this Working Group are to (1) formulate a framework for identifying research needs related to the health and ecological effects of endocrine-disrupting chemicals; (2) conduct an inventory of on-going federal research programs; and (3) identify research gaps and facilitate a co-ordinated research plan to address them. These efforts were largely completed in the Fall of 1996 and the information will be made available via the Internet (http;@www.cpa.gov/endocrine). The group also plans to work more broadly with other governments and private industry and public interest groups conducting research on this tissue to co-ordinate research and disseminate scientific information. Persons wishing to know more about this effort should contact the authors. The issue of endocrine disruption has raised the consciousness of many researchers, both within and outside the toxicology community, and has attracted considerable public and political interest. We now have the beginnings of international co-operation to identify the most important scientific uncertainties and to dedicate resources to address the critical gaps. (ABSTRACT TRUNCATED)
显然,内分泌系统为环境因素诱导不良反应提供了许多靶点(图1)。有大量实例表明,生殖和发育过程可能对暴露极为敏感,而且各种物种中,假定的内分泌干扰化学物质会引发明显的效应。对野生动物和人类的研究引发的担忧,凸显了更好地理解内分泌干扰物所造成的各种效应的重要性。但实验室环境中使用的相对高暴露水平的研究与一般环境中发现的相对低水平之间,仍存在很大空白。同样明显的是,“内分泌干扰”一词已被用于生物学基础远未确凿的情况。在人群生殖受到不利影响的情况下,这可能是个有争议的问题,但作为科学家,我们必须警惕描述性术语的恰当使用,尤其是在公众意识和关注度如此之高的情况下。不仅需要更好的测试程序(体内和体外)来表征环境因素在实验物种中干扰内分泌功能的潜力,还需要更全面地了解所研究的野生动物物种中与生殖和发育相关的正常生理过程。与此同时,获取有关释放到环境中的化学物质的迁移、归宿和生物可利用性的更好信息,仍然是一项重要但艰巨的任务。风险表征的目标是仔细描绘因果关系、确定剂量反应关系,并确定环境暴露是否超过可接受水平。需要协同研究努力来填补我们知识中的空白,减少目前存在的巨大不确定性。只有这样,监管行动才能在立法授权、补救策略以及国际使用和运输考虑的范围内进行。为此,美国环境保护局(EPA)在1995年主办了两次研讨会(安克利等人,1996年;卡夫洛克等人,1996年),国际科学家小组在会上开始了确定研究需求的进程。大约在同一时间,几个欧洲国家也开展了类似的工作(丹麦环境保护局,1995年;医学研究理事会,1995年;联邦环境局,1995年)。最近,在美国政府国家科学技术委员会的环境与自然资源委员会内成立了一个内分泌干扰物工作组。该工作组的目标是:(1)制定一个框架,以确定与内分泌干扰化学物质的健康和生态效应相关的研究需求;(2)对正在进行的联邦研究项目进行清查;(3)确定研究差距,并推动制定协调一致的研究计划来解决这些差距。这些工作在1996年秋季基本完成,相关信息将通过互联网提供(http;@www.cpa.gov/endocrine)。该小组还计划与其他政府、私营企业以及对该领域进行研究的公共利益团体更广泛地合作,以协调研究并传播科学信息。希望了解更多此项工作的人应与作者联系。内分泌干扰问题已经提高了毒理学界内外许多研究人员的认识,并引起了公众和政治的极大关注。我们现在已经开始了国际合作,以确定最重要的科学不确定性,并投入资源填补关键空白。(摘要截选)