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Sastri, V. S. (1975). Reverse osmosis for the treatment of metal waste solutions. Canada Centre For Mineral And Energy Technology Scientific Bulletin, 75-07, 18.
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Mason, D. G., & Gupta, M. K. (1972). Reverse Osmosis Demineralization Of Acid Mine Drainage. Water Pollution Control Research Series, , 110.
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Kingham, N. W., Semenak, R., Powell, G., & Way, S. (2002). Reverse osmosis coupled with chemical precipitation treatment of acid mine leachate at the Basin-Luttrell Pit, Ten Mile Creek Site, Lewis and Clark County, Montana Hardrock mining 2002; issues shaping the industry..
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Carlson, L., & Kumpulainen, S. (2001). Retention of harmful elements by ochreous precipitates of iron. Tutkimusraportti Geologian Tutkimuskeskus, -(154), 30–33.
Abstract: The capability of soil fines to fix harmful elements, e.g. heavy metals and arsenic, depends on specific surface area and other characteristics, such as surface charge. In the pH-range typical of natural waters (pH 5,5-7,5), the surfaces of fine-grained silicate particles and manganese oxides are negatively charged; consequently cations, such as heavy metals, fix effectively to them. The iron oxide surfaces are usually positively charged and typically fix anions, such as sulphate and arsenate. Retention of anions is especially extensive to precipitates formed from acid mine drainage (pH 2,5-5,0). For example, precipitates found at Paroistenjarvi mine, Finland, contain more than 70 g/kg of arsenic (dry matter). Adsorbed anions, e.g. sulphate, enhance the capacity of precipitate to fix heavy metal cations in low-pH environments.
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Li, L., Jiang, Y., & Guo, Y. (1999). Research on a comprehensive industrialization technology for the treatment of mining water containing sulfate ions. Meitian Dizhi Yu Kantan = Coal Geology & Exploration, 27(6), 51–53.
Abstract: A method using a barium reagent was developed for the purification of the higher-sulphate mine water.
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