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美国南达科他州夏延河流域受采矿影响沉积物中砷释放的碳酸氢盐和磷酸盐的影响。

Effect of bicarbonate and phosphate on arsenic release from mining-impacted sediments in the Cheyenne River watershed, South Dakota, USA.

机构信息

Department of Civil Engineering, University of New Mexico, MSC01 1070, Albuquerque, New Mexico 87131, USA.

出版信息

Environ Sci Process Impacts. 2019 Mar 20;21(3):456-468. doi: 10.1039/c8em00461g.

Abstract

The mobilization of arsenic (As) from riverbank sediments affected by the gold mining legacy in north-central South Dakota was examined using aqueous speciation chemistry, spectroscopy, and diffraction analyses. Gold mining resulted in the discharge of approximately 109 metric tons of mine waste into Whitewood Creek (WW) near the Homestake Mine and Cheyenne River at Deal Ranch (DR), 241 km downstream. The highest concentrations of acid-extractable As measured from solid samples was 2020 mg kg-1 at WW and 385 mg kg-1 at DR. Similar sediment mineralogy between WW and DR was identified using XRD, with the predominance of alumino-silicate and iron-bearing minerals. Alkalinity measured in surface water at both sites ranged from 1000 to 2450 mg L-1 as CaCO3 (10-20 mM HCO3- at pH 7). Batch laboratory experiments were conducted under oxidizing conditions to evaluate the effects of NaHCO3 (0.2 mM and 20 mM) and NaH2PO3 (0.1 and 10 mM) on the mobilization of As. These ions are relevant for the site due to the alkaline nature of the river and nutrient mobilization from the ranch. The range of As(v) release with the NaHCO3 treatment was 17-240 μg L-1. However, the highest release (6234 μg L-1) occurred with 10 mM NaH2PO3, suggesting that As release is favored by competitive ion displacement with PO43- compared to HCO3-. Although higher total As was detected in WW solids, the As(v) present in DR solids was labile when reacted with NaHCO3 and NaH2PO3, which is a relevant finding for communities living close to the river bank. The results from this study aid in a better understanding of As mobility in surface water sites affected by the mining legacy.

摘要

本研究采用水相形态化学、光谱和衍射分析方法,考察了北达科他州中北部受金矿遗留物影响的河岸沉积物中砷的迁移情况。金矿开采导致约 109 公吨的矿渣排入霍姆斯特克矿附近的怀特伍德溪(WW)和切延河的迪尔牧场(DR),距离源头 241 公里。WW 和 DR 的固体样品中可萃取酸的砷浓度最高,分别为 2020 毫克/千克和 385 毫克/千克。WW 和 DR 之间的沉积物矿物学相似,使用 XRD 确定,主要为铝硅酸盐和含铁矿物。两处地表水中的碱度均在 1000 至 2450 毫克/升(pH7 时为 10-20 毫摩尔/升 HCO3-)。在氧化条件下进行了批量实验室实验,以评估 NaHCO3(0.2 毫米和 20 毫米)和 NaH2PO3(0.1 和 10 毫米)对砷迁移的影响。由于河流的碱性和牧场养分的释放,这些离子与该地点有关。用 NaHCO3 处理时,As(v)的释放范围为 17-240μg/L。然而,当使用 10 mM NaH2PO3 时,释放量最高(6234μg/L),这表明与 HCO3-相比,PO43-的竞争离子置换有利于 As 的释放。尽管 WW 固体中检测到的总砷含量较高,但当与 NaHCO3 和 NaH2PO3 反应时,DR 固体中的 As(v)是不稳定的,这一发现对生活在河岸附近的社区具有重要意义。本研究的结果有助于更好地了解受采矿业遗留物影响的地表水站点中砷的迁移。

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