Centro de Investigaciones en Ciencias de la Tierra (CICTERRA), CONICET, and FCEFyN Universidad Nacional de Córdoba, Córdoba, Argentina, Avda Velez Sarsfield 1611, 5016, Ciudad Universitaria, Córdoba, Argentina.
Centro de Investigaciones en Ciencias de la Tierra (CICTERRA), CONICET, and FCEFyN Universidad Nacional de Córdoba, Córdoba, Argentina, Avda Velez Sarsfield 1611, 5016, Ciudad Universitaria, Córdoba, Argentina.
Environ Pollut. 2018 Nov;242(Pt A):264-276. doi: 10.1016/j.envpol.2018.06.067. Epub 2018 Jun 28.
The sulphide-rich mine wastes accumulated in tailing dumps of La Concordia Mine (Puna of Argentina) have been exposed to the weathering action for more than 30 years. Since then, a series of redox reactions have triggered the generation of a highly acidic drainage -rich in dissolved metals-that drains into the La Concordia creek. The extent of metal and acid release in the site was analysed through field surveys and laboratory experiments. Static tests were conducted in order to predict the potential of the sulphidic wastes to produce acid, while Cu-, Zn-, Fe- and Pb-bearing phases present in the wastes were identified by XRD, SEM/EDS analysis and sequential extraction procedures. Finally, the release of these metals during sediment-water interaction was assessed in batch experiments carried out in a period of nearly two years. Field surveys indicate that the prolonged alteration of the mine wastes led to elevated electrical conductivity, pH values lower than 4 and metal concentrations that exceed the guide values for drinking water in the La Concordia stream regardless of the dominating hydrological conditions. The highly soluble Fe and Mg (hydrous)sulphates that form salt crusts on the tailings surfaces and the riverbed sediments play an important role in the control of metal mobility, as they rapidly dissolve in contact with water releasing Fe, but also Cu and Zn which are scavenged by such minerals. Another important proportion of the analysed metals is adsorbed onto Fe (hydr)oxides or form less soluble hydroxysulfates. Metals present in these phases are released to water more slowly, thus representing a potential long term source of heavy metal pollution. The obtained results are a contribution to the understanding of long term metal transformations and mobility in mine waste-impacted sites.
拉孔科迪亚矿(阿根廷普纳)尾矿堆中富含硫化物的矿渣已经暴露在风化作用下超过 30 年。从那时起,一系列氧化还原反应引发了具有高溶解金属含量的强酸性排水的产生,这些排水流入拉孔科迪亚溪。通过野外调查和实验室实验分析了该地点金属和酸的释放程度。进行了静态测试,以预测硫化物废物产生酸的潜力,同时通过 XRD、SEM/EDS 分析和顺序提取程序确定了废物中存在的 Cu、Zn、Fe 和 Pb 赋存相。最后,在近两年的时间里,通过批实验评估了这些金属在泥沙水相互作用过程中的释放情况。野外调查表明,矿渣的长期变化导致电导率升高、pH 值低于 4 以及金属浓度超过拉孔科迪亚溪饮用水指导值,无论主导水文条件如何。在尾矿表面和河床沉积物上形成盐壳的高可溶性 Fe 和 Mg(含水)硫酸盐对金属迁移性的控制起着重要作用,因为它们与水接触时会迅速溶解,释放出 Fe,但也会释放出被这些矿物吸附的 Cu 和 Zn。分析的金属中还有另一重要比例被吸附到 Fe(氢)氧化物上或形成较少可溶性的羟硫酸盐。这些相中存在的金属向水中的释放速度较慢,因此代表了重金属污染的潜在长期来源。获得的结果有助于理解矿山废物影响区中长期金属转化和迁移。