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一种评估退役海上石油和天然气基础设施潜在环境汞释放、食物网生物累积以及人类膳食甲基汞摄入情况的方法。

An approach to assess potential environmental mercury release, food web bioaccumulation, and human dietary methylmercury uptake from decommissioning offshore oil and gas infrastructure.

作者信息

von Hellfeld Rebecca, Gade Christoph, Koppel Darren J, Walters William J, Kho Fenny, Hastings Astley

机构信息

School of Biological Sciences, University of Aberdeen, School of Biological Sciences, Aberdeen, UK; National Decommissioning Centre, Ellon, UK.

School of Biological Sciences, University of Aberdeen, School of Biological Sciences, Aberdeen, UK; National Decommissioning Centre, Ellon, UK.

出版信息

J Hazard Mater. 2023 Jun 15;452:131298. doi: 10.1016/j.jhazmat.2023.131298. Epub 2023 Mar 27.

Abstract

Subsea pipelines carrying well fluids from hydrocarbon fields accumulate mercury. If the pipelines (after cleaning and flushing) are abandoned in situ, their degradation may release residual mercury into the environment. To justify pipeline abandonment, decommissioning plans include environmental risk assessments to determine the potential risk of environmental mercury. These risks are informed by environmental quality guideline values (EQGVs) governing concentrations in sediment or water above which mercury toxicity may occur. However, these guidelines may not consider e.g., the bioaccumulation potential of methylated mercury. Therefore, EQGVs may not protect humans from exposure if applied as the sole basis for risk assessments. This paper outlines a process to assess the EQGVs' protectiveness from mercury bioaccumulation, providing preliminary insights to questions including how to (1) determine pipeline threshold concentrations, (2) model marine mercury bioaccumulation, and (3) determine exceedance of the methylmercury tolerable weekly intake (TWI) for humans. The approach is demonstrated with a generic example using simplifications to describe mercury behaviour and a model food web. In this example, release scenarios equivalent to the EQGVs resulted in increased marine organism mercury tissue concentrations by 0-33 %, with human dietary methylmercury intake increasing 0-21 %. This suggests that existing guidelines may not be protective of biomagnification in all circumstances. The outlined approach could inform environmental risk assessments for asset-specific release scenarios but must be parameterised to reflect local environmental conditions when tailored to local factors.

摘要

输送来自油气田井液的海底管道会积累汞。如果这些管道(在清洗和冲洗后)原地弃置,其降解可能会将残留汞释放到环境中。为证明管道弃置的合理性,退役计划包括环境风险评估,以确定环境汞的潜在风险。这些风险由环境质量指导值(EQGVs)告知,该指导值规定了沉积物或水中可能发生汞毒性的浓度上限。然而,这些指导方针可能未考虑例如甲基汞的生物累积潜力。因此,如果仅将EQGVs作为风险评估的唯一依据,可能无法保护人类免受汞暴露。本文概述了一个评估EQGVs对汞生物累积保护作用的过程,为以下问题提供了初步见解:如何(1)确定管道阈值浓度,(2)模拟海洋汞生物累积,以及(3)确定人类甲基汞每周耐受摄入量(TWI)的超标情况。该方法通过一个通用示例进行了演示,该示例使用简化方法来描述汞的行为和一个模型食物网。在这个示例中,与EQGVs等效的释放情景导致海洋生物体内汞组织浓度增加了0 - 33%,人类膳食甲基汞摄入量增加了0 - 21%。这表明现有指导方针在所有情况下可能无法保护生物放大作用。所概述的方法可为特定资产释放情景的环境风险评估提供参考,但在根据当地因素进行调整时,必须进行参数化以反映当地环境条件。

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