Miao Ziheng, Nihat Hakan, McMillan Andrew Lee, Brusseau Mark L
Department of Soil, Water and Environmental Science, School of Earth and Environmental Sciences, University of Arizona, 429 Shantz Building #38, P.O. Box 210038, Tucson, AZ, USA ; Department of Hydrology and Water Resources, School of Earth and Environmental Sciences, University of Arizona, 429 Shantz Building #38, P.O. Box 210038, Tucson, AZ, USA.
Department of Soil, Water and Environmental Science, School of Earth and Environmental Sciences, University of Arizona, 429 Shantz Building #38, P.O. Box 210038, Tucson, AZ, USA ; Department of Geological Engineering, University of Kocaeli, Umuttepe Kampüsü, TR-41380 Kocaeli, Turkey.
Appl Geochem. 2013 Nov;38. doi: 10.1016/j.apgeochem.2013.08.002.
The remediation of ammonium-containing groundwater discharged from uranium mill tailing sites is a difficult problem facing the mining industry. The Monument Valley site is a former uranium mining site in the southwest US with both ammonium and nitrate contamination of groundwater. In this study, samples collected from 14 selected wells were analyzed for major cations and anions, trace elements, and isotopic composition of ammonium and nitrate. In addition, geochemical data from the U.S. Department of Energy (DOE) database were analyzed. Results showing oxic redox conditions and correspondence of isotopic compositions of ammonium and nitrate confirmed the natural attenuation of ammonium via nitrification. Moreover, it was observed that ammonium concentration within the plume area is closely related to concentrations of uranium and a series of other trace elements including chromium, selenium, vanadium, iron, and manganese. It is hypothesized that ammonium-nitrate transformation processes influence the disposition of the trace elements through mediation of redox potential, pH, and possibly aqueous complexation and solid-phase sorption. Despite the generally relatively low concentrations of trace elements present in groundwater, their transport and fate may be influenced by remediation of ammonium or nitrate at the site.
铀矿尾矿场排放的含铵地下水的修复是采矿业面临的一个难题。纪念碑谷场地是美国西南部一个 former uranium mining site,地下水同时受到铵和硝酸盐的污染。在本研究中,对从 14 口选定井中采集的样本进行了主要阳离子和阴离子、微量元素以及铵和硝酸盐的同位素组成分析。此外,还分析了美国能源部(DOE)数据库中的地球化学数据。结果显示氧化还原条件以及铵和硝酸盐同位素组成的对应关系证实了铵通过硝化作用的自然衰减。此外,观察到羽流区域内的铵浓度与铀以及包括铬、硒、钒、铁和锰在内的一系列其他微量元素的浓度密切相关。据推测,铵 - 硝酸盐转化过程通过氧化还原电位、pH 值以及可能的水相络合和固相吸附作用来影响微量元素的分布。尽管地下水中微量元素的浓度通常相对较低,但它们的迁移和归宿可能会受到该场地铵或硝酸盐修复的影响。