Land Remediation and Pollution Control Division, US EPA Office of Research and Development, National Risk Management Research Laboratory, 26 W. Martin Luther King Drive, Cincinnati, OH 45268, USA.
Water Res. 2011 Jan;45(1):328-36. doi: 10.1016/j.watres.2010.07.077. Epub 2010 Aug 4.
Remediation of streams influenced by mine-drainage may require removal and burial of metal-containing bed sediments. Burial of aerobic sediments into an anaerobic environment may release metals, such as through reductive dissolution of metal oxyhydroxides. Mining-impacted aerobic streambed sediments collected from North Fork Clear Creek, Colorado were held under anaerobic conditions for four months. Eh, pH, and concentrations of Cd, Cu, Fe, Mn, and Zn (filtered at 1.5 μm, 0.45 μm, and 0.2 μm), sulfate, and dissolved organic carbon (DOC) were monitored in stream water/sediment slurries. Two sediment size fractions were examined (2 mm-63 μm and <63 μm). Sequential extractions evaluated the mineral phase with which metals were associated in the aerobic sediment. Released Cu was re-sequestered within 5 weeks, while Fe and Mn still were present at 16 weeks. Mn concentration was lower than in the initial stream water at and beyond 14 weeks for the smaller sized sediment. Cd was not released from either sediment size fraction. Zn was released at early times, but concentrations never exceeded those present in the initial stream water and all was re-sequestered over time. The greatest concentrations of Cu, Fe, Mn, and Zn were associated with the Fe/Mn reducible fraction. Sulfate and Fe were strongly correlated (r = 0.90), seeming to indicate anaerobic dissolution of iron oxy-hydroxy-sulfate minerals. DOC and sulfate were strongly correlated (r = 0.81), with iron having a moderately strong correlation with DOC (r = 0.71). Overall concentrations of DOC, sulfate, Cu, Fe, and Zn and pH were significantly higher (p < 0.05) in the water overlying the small sized sediment samples, while the concentrations of Mn released from the larger sized sediment samples were greater.
受矿山排水影响的溪流的修复可能需要去除和埋藏含金属的河床沉积物。将好氧沉积物埋藏在厌氧环境中可能会释放金属,例如通过金属氢氧化物的还原溶解。从科罗拉多州北叉克里克采集的受采矿影响的好氧河床沉积物在厌氧条件下保持了四个月。Eh、pH 值以及 Cd、Cu、Fe、Mn 和 Zn(经 1.5μm、0.45μm 和 0.2μm 过滤)、硫酸盐和溶解有机碳(DOC)的浓度在溪流水/沉积物悬浮液中进行了监测。检查了两个沉积物粒径(2mm-63μm 和 <63μm)。顺序提取评估了金属在好氧沉积物中与之结合的矿物相。释放的 Cu 在 5 周内重新被固定,而 Fe 和 Mn 在 16 周时仍存在。在较小粒径的沉积物中,Mn 浓度在 14 周及以后低于初始溪流水中的浓度。Cd 没有从任何沉积物粒径中释放出来。Zn 最初很快释放出来,但浓度从未超过初始溪流水中的浓度,并且随着时间的推移被重新固定。Cu、Fe、Mn 和 Zn 的最大浓度与 Fe/Mn 可还原部分有关。硫酸盐和 Fe 呈强相关性(r = 0.90),似乎表明铁的缺氧溶解-羟基-硫酸盐矿物。DOC 和硫酸盐呈强相关性(r = 0.81),铁与 DOC 呈中度强相关性(r = 0.71)。在小粒径沉积物样品上方的水中,DOC、硫酸盐、Cu、Fe 和 Zn 的总浓度以及 pH 值明显更高(p <0.05),而较大粒径沉积物样品释放的 Mn 浓度更高。