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Acid- and base-neutralization capacity in mine water and brines

机译:矿井水和盐水中的酸和碱中和能力

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Acidimetric and alkalimetric titration to the endpoint of pH 4.2 and 8.3 is commonly used in water chemistry to determine the amount of inorganic carbon species in water [1]. However, in mine water and brines the determination of inorganic carbon species should not be based on this method because buffering components such as polyvalent metals (e.g. iron, copper, manganese), non-carbonic acids (hydrogen sulfide, sulfuric acid, phosphoric acid, boric acid, silicic acid, organic acids, etc.), and the acid-base behavior of metals (aluminum, manganese, zinc, nickel, etc.) may be dominant and lead to completely wrong results with respect to the carbon species. As a kind of go around the hot peroxide acidity procedure is widely used for measuring the acidity of mine drainage. In this context, the poorly defined terms "net alkalinity" and "net acidity" are commonly used in particular in the mine-water community [2].
机译:将酸化和碱化滴定至pH 4.2和8.3的终点通常用于水化学以确定水中无机碳物种的量[1]。然而,在矿井水中和盐水中,无机碳物种的测定不应基于该方法,因为缓冲组分如多价金属(例如铁,铜,锰),非碳酸(硫化氢,硫酸,磷酸,硼酸,硅酸,有机酸等)和金属的酸碱行为(铝,锰,锌,镍等)可能是显性的,并导致碳物种的完全错误的结果。作为一种散热的臭氧酸度程序,广泛用于测量矿井排水的酸度。在这种情况下,定义的术语“净碱度”和“净酸度”尤其在矿井水域中使用[2]。

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