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The assessment and remediation of mercury contaminated sites: A review of current approaches

机译:汞污染场地的评估和补救:当前方法的回顾

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Remediation of mercury (Hg) contaminated sites has long relied on traditional approaches, such as removal and containment/capping. Here we review contemporary practices in the assessment and remediation of industrial-scale Hg contaminated sites and discuss recent advances. Significant improvements have been made in site assessment, including the use of XRF to rapidly identify the spatial extent of contamination, Hg stable isotope fractionation to identify sources and transformation processes, and solid-phase characterization (XAFS) to evaluate Hg forms. The understanding of Hg bioavailability for methylation has been improved by methods such as sequential chemical extractions and porewater measurements, including the use of diffuse gradient in thin-film (DGT) samplers. These approaches have shown varying success in identifying bioavailable Hg fractions and further study and field applications are needed. The downstream accumulation of methylmercury (MeHg) in biota is a concern at many contaminated sites. Identifying the variables limiting/controlling MeHg production—such as bioavailable inorganic Hg, organic carbon, and/or terminal electron acceptors (e.g. sulfate, iron) is critical. Mercury can be released from contaminated sites to the air and water, both of which are influenced by meteorological and hydrological conditions. Mercury mobilized from contaminated sites is predominantly bound to particles, highly correlated with total sediment solids (TSS), and elevated during stormflow. Remediation techniques to address Hg contamination can include the removal or containment of Hg contaminated materials, the application of amendments to reduce mobility and bioavailability, landscape/waterbody manipulations to reduce MeHg production, and food web manipulations through stocking or extirpation to reduce MeHg accumulated in desired species. These approaches often rely on knowledge of the Hg forms/speciation at the site, and utilize physical, chemical, thermal and biological methods to achieve remediation goals. Overall, the complexity of Hg cycling allows many different opportunities to reduce/mitigate impacts, which creates flexibility in determining suitable and logistically feasible remedies.
机译:长期以来,汞(Hg)污染场所的修复一直依靠传统方法,例如去除和围堵/封顶。在这里,我们回顾了评估和修复工业规模汞污染场地的当代实践,并讨论了最新进展。现场评估已取得重大进步,包括使用XRF快速识别污染的空间范围,使用汞稳定同位素分级法来识别来源和转化过程,以及使用固相表征(XAFS)来评估汞形式。对汞甲基化甲基化生物利用度的了解已通过诸如顺序化学提取和孔隙水测量等方法得到了改善,包括在薄膜(DGT)采样器中使用扩散梯度。这些方法在鉴定生物可利用的汞组分方面显示出不同的成功,需要进一步的研究和现场应用。甲基汞(MeHg)在生物区系中的下游积累是许多受污染场所的关注点。确定限制/控制MeHg产生的变量(例如生物可利用的无机Hg,有机碳和/或末端电子受体(例如硫酸盐,铁))至关重要。汞可以从受污染的地方释放到空气和水中,这两者都受气象和水文条件的影响。从受污染场所迁移出来的汞主要与颗粒结合,与总沉积物固体(TSS)高度相关,并在暴风雨期间升高。解决汞污染的补救技术可包括去除或控制汞污染的材料,应用修正案以减少迁移率和生物利用度,对景观/水体进行处理以减少MeHg的产生以及对食物网的处理,例如通过放养或消灭以减少所需的累积的MeHg种类。这些方法通常依赖于现场对汞形式/形态的了解,并利用物理,化学,热学和生物方法来达到修复目标。总体而言,汞循环的复杂性为减少/减轻影响提供了许多不同的机会,这为确定合适的和在逻辑上可行的补救措施创造了灵活性。

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