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ACIDITY AND ALKALINITY IN MINE DRAINAGE: THEORETICAL CONSIDERATIONS

机译:矿井排水中的酸度和碱度:理论考虑

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Acidity, net acidity, and net alkalinity are widely used parameters for the characterization of mine drainage, but these terms are not well defined and are often misunderstood. Incorrect interpretation of acidity, alkalinity, and derivative terms can lead to inadequate treatment design or poor regulatory decisions. We briefly explain derivations of theoretical expressions of three types of alkalinities (caustic, phenolphthalein, and total) and acidities (mineral, CO_2, and total). Theoretically defined total alkalinity is closely analogous to measured alkalinity and presents few practical interpretation problems. Theoretically defined "CO_2- acidity" is closely related to most standard titration methods used for mine drainage with an endpoint pH of 8.3, but it presents numerous interpretation problems, and it is unfortunately named because CO_2 is intentionally driven off during titration of mine-drainage samples. Using the proton condition/massaction approach and employing graphs for visualization, we explore the concept of principal components and how to assign acidity contributions to solution species, including aqueous complexes, commonly found in mine drainage. We define a comprehensive theoretical definition of acidity in mine drainage on the basis of aqueous speciation at the sample pH and the capacity of these species to undergo hydrolysis to pH 8.3. This definition indicates the computed acidity in milligrams per liter (mg L-1) as CaCO_3 (based on pH and analytical concentrations of dissolved Fe~(III), Fe~(II), Mn, and Al in mg L~(-1)): Acidity_(computed) = 50.(10~((3-pH)) + 3 centre dot C_(FeIII)/55.8 + 2 centre dot C_(FeII)/55.8 + 2 centre dot C_(Mn)/54.9 + 3 centre dot C_(Al)/27.0) underestimates contributions from HSO_4~- and H~+, but overestimates the acidity due to Fe~(3+). These errors tend to approximately cancel each other. We demonstrate that "net alkalinity" is a valid mathematical construction based on theoretical definitions of alkalinity and acidity. We demonstrate that, for most mine-drainage solutions, a useful net alkalinity value can be derived from: 1) alkalinity and acidity values based on aqueous speciation, 2) measured alkalinity - computed acidity, or 3) taking the negative of the value obtained in a standard method "hot peroxide" acidity titration, provided that labs report negative values. We recommend the third approach; i.e., Net alkalinity = -Hot Acidity.
机译:酸度,净酸度,和净碱度被广泛使用的参数为矿井排水的特性,但这些条款没有明确定义,并经常被误解。酸度,碱度,以及导数项不正确的解释可能会导致治疗设计不足或低劣的监管决定。我们简单介绍一下三种类型的碱度(烧碱,酚酞和总)和酸度(矿物,CO_2和总)的理论表达式的推导。理论上定义的总碱度是密切类似于测量的碱度,并提出一些实用的解释问题。理论上定义的“CO_2-酸度”密切相关,用于矿井排水与8.3的终点PH值最标准的滴定法,但它提出了许多解释问题,以及这家饭店命名,是因为CO_2是滴定矿井排水过程中有意赶走样本。使用质子条件/ massaction方法,并采用图形可视化,我们探讨的主要成分对解决种分配酸度的贡献,包括水复合物,在矿山排水中常见的概念,以及如何。我们定义水溶液形态的样品pH值的基础和这些物质的进行水解至pH 8.3的能力上在矿山排水酸度的综合理论定义。此定义表示毫克每升计算酸度(毫克L-1)作为碳酸钙(基于pH值和溶解的Fe〜(III),铁〜(II),锰和Al的分析浓度以mg L〜(-1 )):Acidity_(计算)= 50(10〜((3- pH值))+ 3中心点C_(FeIII)/55.8 + 2中心点C_(FeII)/55.8 + 2中心点C_(Mn)的/54.9 + 3中心点C_(Al)的/27.0)低估从HSO_4〜捐款 - 和H +,但高估了酸度由于铁〜(3+)。这些错误往往大约相互抵消。我们证明,“净碱度”是基于碱性和酸性的理论定义一个有效的数学结构。我们证明,对于大多数矿山排水的解决方案中,有用的净碱度值可衍生自:1)碱度和酸度值基于含水形态,2)测定碱度 - 计算的酸度,或3)取的值的负获得在标准方法的“热过氧化物”酸度滴定,条件是实验室报告负值。我们建议第三种方法;即,净碱度= - 热酸度。

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