Stern Alan H
Division of Science, Research, and Technology, New Jersey Department of Environmental Protection, P.O. 409, 401 E. State, St. Trenton, NJ 08625, USA.
Environ Res. 2005 May;98(1):133-42. doi: 10.1016/j.envres.2004.07.016.
In the 2000 report of the National Research Council's Committee on the Toxicological Effects of Methylmercury (MeHg), various adverse health effects potentially associated with MeHg exposure including cardiovascular effects were considered. At that time, the committee concluded that neurodevelopmental toxicity was the most sensitive endpoint but recognized emerging evidence of potential cardiovascular effects at low levels of exposure. The committee recommended that these potential effects be addressed through the uncertainty factors applied to the development of the neurodevelopmental reference dose (RfD). This approach was adopted by the US EPA in its derivation of the methylmercury RfD. Since that time, additional studies have become available. The available studies addressing the broad categories of heart disease (including myocardial infarction (MI) and ischemic heart disease), hypertension, and heart rate variability are critically reviewed here. Overall, the evidence linking realistic rates of MeHg exposure from fish consumption to cardiovascular disease suggests an association with heart disease, particularly MI. The apparent antagonistic interaction of MeHg and n-3 fatty acids contained in fish suggests a causal mechanism. As different individuals and populations characteristically consume different species of fish, the risk of cardiovascular effects may not be a simple function of MeHg exposure but its assessment may well need to take n-3 fatty acid intake into account also. The case for significant adverse effects of MeHg on blood pressure at current levels of exposure is weaker. This effect, observed in childhood, does not appear to persist into adolescence, and animal studies are difficult to interpret given the high doses employed. The decrease in heart rate variability related to fetal exposure to MeHg in the same cohort appears to persist into early adolescence and may reflect developmental neurophysiological alterations that are consistent with the developmental neuropsychological effects also observed in that cohort. However, the cardiovascular significance of this effect with regard to its direct effect on health or its ability to predict other, more direct, health effects is unclear. At present, the studies of the Finnish cohort relating MeHg exposure to acute MI and coronary heart disease appear to provide the strongest basis for a formal quantitative risk assessment of the cardiovascular effects of MeHg.
在国家研究委员会甲基汞(MeHg)毒理学效应委员会2000年的报告中,考虑了各种可能与甲基汞暴露相关的不良健康影响,包括心血管影响。当时,委员会得出结论,神经发育毒性是最敏感的终点,但认识到在低暴露水平下有潜在心血管影响的新出现证据。委员会建议通过应用于神经发育参考剂量(RfD)制定的不确定因素来解决这些潜在影响。美国环境保护局(EPA)在推导甲基汞RfD时采用了这种方法。自那时以来,已有更多研究可供参考。本文对有关心脏病(包括心肌梗死(MI)和缺血性心脏病)、高血压和心率变异性等广泛类别问题的现有研究进行了严格审查。总体而言,将因食用鱼类而接触甲基汞的实际发生率与心血管疾病联系起来的证据表明,其与心脏病,尤其是心肌梗死存在关联。甲基汞与鱼类中含有的n-3脂肪酸之间明显的拮抗相互作用提示了一种因果机制。由于不同个体和人群通常食用不同种类的鱼类,心血管影响的风险可能不是甲基汞暴露的简单函数,但其评估很可能还需要考虑n-3脂肪酸的摄入量。在当前暴露水平下,甲基汞对血压产生重大不良影响的证据较弱。这种在儿童期观察到的影响似乎不会持续到青春期,而且鉴于所使用的高剂量,动物研究难以解释。在同一队列中,与胎儿接触甲基汞相关的心率变异性降低似乎会持续到青春期早期,这可能反映了发育神经生理改变,与该队列中也观察到的发育神经心理影响一致。然而,这种影响对健康的直接作用或其预测其他更直接健康影响的能力在心血管方面的意义尚不清楚。目前,芬兰队列中关于甲基汞暴露与急性心肌梗死和冠心病关系的研究似乎为甲基汞心血管影响的正式定量风险评估提供了最有力的依据。