首页> 外文会议>West Virginia Surface Mine Drainage Task Force Symposium >THE USE OF MEASURED AND CALCULATED ACIDITY VALUES TO IMPROVE THE QUALITY OF MINE DRAINAGE DATASETS
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THE USE OF MEASURED AND CALCULATED ACIDITY VALUES TO IMPROVE THE QUALITY OF MINE DRAINAGE DATASETS

机译:使用测量和计算的酸度值来提高矿井排水数据集的质量

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The net acidity of a water sample can be measured directly by titration with a standardized base solution or calculated from the measured concentrations of the acidic and basic components. For coal mine drainage, the acidic components are primarily accounted for by free protons and dissolved ferrous iron, ferric iron, aluminum, and manganese. The base component is primarily accounted for by bicarbonate. A standard calculation is: Acid~(calc) =50*(2*Fe~(2+)/56 + 3*Fe~(3+)/56 + 3*Al/27 + 2*Mn/55 + 1000*10~(-pH)) -Alkalinity, where acidity and alkalinity are measured as mg/L CaCO_3 and the metals are mg/L. Because these methods of estimating acidity are derived by independent laboratory procedures, their comparison can provide a valuable QA/QC for AMD datasets. The relationship between measured and calculated acidities was evaluated for fourteen datasets containing 1,484 sample analyses. All datasets consisted of samples collected from mine drainage discharges or polluted receiving streams. The datasets were variable in nature, ranging from watersheds where most of the discharges contained alkalinity to ones where all of the discharges were acidic. Good relationships were found to exist between measured and calculated acidities. The average acidity measurement was 239 mg/L CaCO_3 and the average acidity calculation was 226 mg/L CaCO_3. Linear regressions were calculated for individual datasets and for the entire dataset. The linear regression for the entire dataset was: Acid~(calc) = 0.98 * Acid~(meas) - 8, r~2 = 0.98. The good correlation between calculated and measured acidity is the basis for an easy and inexpensive QA/QC for AMD data. Substantial variation between measured and calculated acidities can be used to infer sampling or analytical problems and allow data corrections, when appropriate.
机译:水样的净酸度可以通过用标准化的基础溶液滴定直接测量,或者由测量的酸性和碱性组分的浓度计算。对于煤矿排水,酸性成分主要由自由质子和溶解的亚铁,铁,铝和锰占。基本组分主要由碳酸氢盐占。标准计算是:酸〜(钙)= 50 *(2 * Fe〜(2 +)/ 56 + 3 * Fe〜(3 +)/ 56 + 3 * Al / 27 + 2 * Mn / 55 + 1000 * 10〜(-Fh)) - 列,其中酸性和碱度被测量为Mg / L CaCO_3,金属是Mg / L.因为这些估计酸度的方法是由独立的实验室程序导出的,所以它们的比较可以为AMD数据集提供有价值的QA / QC。评价测量和计算酸度之间的关系,用于含有1,484个样品分析的十四个数据集。所有数据集包括从矿山排水排放或污染的接收流中收集的样本。数据集本质上是可变的,从流域范围内,其中大部分放电都包含碱度,所有放电都是酸性的。发现在测量和计算的酸度之间存在良好的关系。平均酸度测量为239mg / L CaCO_3,平均酸度计算为226mg / L CaCO_3。针对各个数据集和整个数据集计算线性回归。整个数据集的线性回归是:酸〜(钙)= 0.98 *酸〜(MEAS) - 8,R〜2 = 0.98。计算和测量酸度之间的良好相关性是AMD数据的简单且廉价的QA / QC的基础。测量和计算酸之间的大量变化可用于推断采样或分析问题并在适当时允许数据校正。

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