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汞的形态及通过南加州沿海泻湖系统的海底地下水排放进行的迁移。

Mercury speciation and transport via submarine groundwater discharge at a southern California coastal lagoon system.

机构信息

Earth and Planetary Sciences, University of California, Santa Cruz, California, United States.

出版信息

Environ Sci Technol. 2012 Feb 7;46(3):1480-8. doi: 10.1021/es202783u. Epub 2012 Jan 27.

Abstract

We measured total mercury (Hg(T)) and monomethylmercury (MMHg) concentrations in coastal groundwater and seawater over a range of tidal conditions near Malibu Lagoon, California, and used (222)Rn-derived estimates of submarine groundwater discharge (SGD) to assess the flux of mercury species to nearshore seawater. We infer a groundwater-seawater mixing scenario based on salinity and temperature trends and suggest that increased groundwater discharge to the ocean during low tide transported mercury offshore. Unfiltered Hg(T) (U-Hg(T)) concentrations in groundwater (2.2-5.9 pM) and seawater (3.3-5.2 pM) decreased during a falling tide, with groundwater U-Hg(T) concentrations typically lower than seawater concentrations. Despite the low Hg(T) in groundwater, bioaccumulative MMHg was produced in onshore sediment as evidenced by elevated MMHg concentrations in groundwater (0.2-1 pM) relative to seawater (∼0.1 pM) throughout most of the tidal cycle. During low tide, groundwater appeared to transport MMHg to the coast, resulting in a 5-fold increase in seawater MMHg (from 0.1 to 0.5 pM). Similarly, filtered Hg(T) (F-Hg(T)) concentrations in seawater increased approximately 7-fold during low tide (from 0.5 to 3.6 pM). These elevated seawater F-Hg(T) concentrations exceeded those in filtered and unfiltered groundwater during low tide, but were similar to seawater U-Hg(T) concentrations, suggesting that enhanced SGD altered mercury partitioning and/or solubilization dynamics in coastal waters. Finally, we estimate that the SGD Hg(T) and MMHg fluxes to seawater were 0.41 and 0.15 nmol m(-2) d(-1), respectively - comparable in magnitude to atmospheric and benthic fluxes in similar environments.

摘要

我们在加利福尼亚马里布泻湖附近的一系列潮汐条件下测量了沿海地下水和海水中的总汞 (Hg(T)) 和一甲基汞 (MMHg) 浓度,并利用 (222)Rn 衍生的地下水排泄 (SGD) 估算值来评估汞种向近岸海水的通量。我们根据盐度和温度趋势推断了一个地下水-海水混合场景,并提出在低潮期间增加向海洋的地下水排放会将汞运出近海。地下水 (2.2-5.9 pM) 和海水 (3.3-5.2 pM) 中的未过滤 Hg(T) (U-Hg(T)) 浓度在退潮期间下降,地下水 U-Hg(T) 浓度通常低于海水浓度。尽管地下水的 Hg(T) 含量较低,但由于内陆沉积物中产生了生物累积性的 MMHg,因此内陆沉积物中的 MMHg 浓度升高,与海水 (∼0.1 pM) 相比,地下水 (0.2-1 pM) 的 MMHg 浓度升高。在低潮期间,地下水似乎将 MMHg 输送到海岸,导致海水 MMHg 浓度增加了 5 倍 (从 0.1 增加到 0.5 pM)。同样,在低潮期间,海水的过滤 Hg(T) (F-Hg(T)) 浓度增加了约 7 倍 (从 0.5 增加到 3.6 pM)。这些升高的海水 F-Hg(T) 浓度在低潮时超过了过滤和未过滤地下水的浓度,但与海水 U-Hg(T) 浓度相似,这表明增强的 SGD 改变了沿海水域的汞分配和/或溶解动力学。最后,我们估计 SGD 向海水输送的 Hg(T) 和 MMHg 通量分别为 0.41 和 0.15 nmol m(-2) d(-1),与类似环境中的大气和海底通量相当。

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