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一种用于估算汞目标水平的特定流域水生食物网生物放大模型。

A basin-specific aquatic food web biomagnification model for estimation of mercury target levels.

作者信息

Hope Bruce

机构信息

Land Quality Division, Oregon Department of Environmental Quality, 811 SW Sixth Avenue, Portland, Oregon 97209, USA.

出版信息

Environ Toxicol Chem. 2003 Oct;22(10):2525-37. doi: 10.1897/02-395.

Abstract

In the Willamette River Basin (WRB, Oregon, USA), health advisories currently limit consumption of fish that have accumulated methylmercury (MeHg) to levels posing a potential health risk for humans. Under the Clean Water Act, these advisories create the requirement for a total maximum daily load (TMDL) for mercury in the WRB. A TMDL is a calculation of the maximum amount of a pollutant that a body of water can receive and still meet water-quality standards. Because MeHg is known to biomagnify in aquatic food webs, a basin-specific biomagnification factor can be used, given a protective fish tissue criterion, to estimate total mercury concentrations in surface waters required to lower advisory mercury concentrations currently in fish in the WRB. This paper presents an aquatic food web biomagnification model that simulates inorganic mercury (Hg(II)) and MeHg accumulation in fish tissue and estimates WRB-specific biomagnification factors for resident fish species of concern to stakeholders. Probabilistic (two-dimensional Monte Carlo) techniques propagate parameter variability and uncertainty throughout the model, providing decision makers with credible range information and increased flexibility in establishing a specific mercury target level. The model predicts the probability of tissue mercury concentrations in eight fish species within the range of concentrations measured in these species over 20 years of water-quality monitoring. Estimated mean biomagnification factor values range from 1.12 x 10(6) to 7.66 x 10(6) and are within the range of U.S. Environmental Protection Agency national values. Several WRB-specific mercury target levels are generated, which very by their probability of affording human health protection relative to the federal MeHg tissue criterion of 0.30 mg/kg. Establishing a specific numeric target level is, however, a public policy decision, and one that will require further discussions among WRB stakeholders.

摘要

在美国俄勒冈州的威拉米特河流域(WRB),健康建议目前限制食用已积累甲基汞(MeHg)至对人类构成潜在健康风险水平的鱼类。根据《清洁水法》,这些建议要求确定WRB中汞的总最大日负荷(TMDL)。TMDL是对水体能够接收且仍能达到水质标准的污染物最大量的计算。由于已知MeHg在水生食物网中会生物放大,给定一个保护性鱼类组织标准,可使用流域特定的生物放大因子来估算降低WRB中鱼类当前建议汞浓度所需的地表水中总汞浓度。本文提出了一个水生食物网生物放大模型,该模型模拟鱼类组织中无机汞(Hg(II))和MeHg的积累,并估算利益相关者关注的流域常驻鱼类物种的WRB特定生物放大因子。概率性(二维蒙特卡洛)技术在整个模型中传播参数变异性和不确定性,为决策者提供可靠的范围信息,并在确定特定汞目标水平时增加灵活性。该模型预测了在20年水质监测中这些物种测量浓度范围内的8种鱼类组织汞浓度的概率。估计的平均生物放大因子值范围为1.12×10⁶至7.66×10⁶,且在美国环境保护局的国家值范围内。生成了几个WRB特定的汞目标水平,相对于0.30毫克/千克的联邦MeHg组织标准,它们提供人类健康保护的概率各不相同。然而,确定一个特定的数值目标水平是一项公共政策决策,并且需要WRB利益相关者之间进一步讨论。

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