Department of Health Sciences of the University of Milan, International Centre for Rural Health of the Occupational Health Unit of the University Hospital San Paolo, and Laboratory for Analytical Toxicology and Metabolomics, Via San Vigilio 43, 20142, Milan, Italy.
Toxicology. 2013 May 10;307:74-88. doi: 10.1016/j.tox.2012.11.015. Epub 2012 Dec 3.
Persistent organic pollutants comprised of organic chemicals like polychlorinated biphenyls, dibenzo-p-dioxins, dibenzofurans and organochlorinated pesticides which have many characteristics in common. Once released in the environment they resist physical, biological, chemical and photochemical breakdown processes and thus persist in the environment. They are subject to long transboundary air pollution transport. They accumulate in the food chain due to their lipophilicity, bioaccumulation and biomagnification properties. Human exposure occurs through inhalation of air, ingestion of food and skin contact. Because most of them bioaccumulate and remain preferentially in fat, their long-term effects are still a matter of public health concern. They are condemned for health adverse effects such as cancer, reproductive defects, neurobehavioral abnormalities, endocrine and immunological toxicity. These effects can be elicited via a number of mechanisms among others include disruption of endocrine system, oxidation stress and epigenetic. However most of the mechanisms are not clear thus a number of studies are ongoing trying to elucidate them. In this review, the underlying possible mechanisms of action and their possible roles in adverse developmental and reproductive processes are discussed and where possible a linkage is made to some existing epidemiological data. Both genomic and nongenomic pathways are used to describe these effects. Understanding of these mechanisms will enable development of strategies to protect the public by reducing these adverse effects. This review is limited to persistent organochlorinated pesticides (OCPs) such as dichlorodiphenyltrichloroethane (DDT) and its metabolites, hexachlorobenzene (HCB), beta-hexachlorocyclohexane (β-HCH) and endosulfan.
持久性有机污染物由有机化学品组成,如多氯联苯、二恶英、呋喃和有机氯农药,它们具有许多共同特征。一旦释放到环境中,它们就会抵抗物理、生物、化学和光化学分解过程,因此在环境中持久存在。它们受到长距离跨界空气污染传输的影响。由于它们的亲脂性、生物积累和生物放大特性,它们会在食物链中积累。人类通过吸入空气、摄入食物和皮肤接触来接触这些污染物。由于它们大多数会生物积累并优先保留在脂肪中,因此它们的长期影响仍然是公共卫生关注的问题。它们因健康不良影响而受到谴责,如癌症、生殖缺陷、神经行为异常、内分泌和免疫毒性。这些影响可以通过多种机制引发,包括内分泌系统紊乱、氧化应激和表观遗传。然而,大多数机制尚不清楚,因此正在进行多项研究试图阐明这些机制。在这篇综述中,讨论了潜在的作用机制及其在不良发育和生殖过程中的可能作用,并在可能的情况下将其与一些现有的流行病学数据联系起来。基因组和非基因组途径都用于描述这些影响。对这些机制的理解将使我们能够制定战略,通过减少这些不利影响来保护公众。本综述仅限于持久性有机氯农药 (OCPs),如滴滴涕 (DDT) 及其代谢物、六氯苯 (HCB)、β-六氯环己烷 (β-HCH) 和硫丹。