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Estimation of Sequential Biodegradation Product Rate Constants

机译:顺序生物降解产物速率常数的估计

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The use of single-species analytical solute transport modeling approaches (e.g., Buscheck and Alcantar method) can lead to underestimated values of biodegradation product rate constants because these approaches do not include biodegradation product accumulation along the groundwater flow path. In order to improve estimates of daughter product biodegradation rate constants, the steady-state solution of the one-dimensional advection-dispersion equation for a point source with first-order chain reaction of three species was derived. This solution can be calibrated to concentration versus distance data of approximate steady-state plumes of both parent and daughter products in order to estimate their field-scale rate constants. An analysis of the analytical solution also indicates that the downgradient locations of both cross-over points (where parent and daughter concentration versus distance data intersect) and maximum points (distance where highest concentration levels occur) can be used to directly interpret field data and estimate daughter product rate constants. As an application, this one-dimensional, multispecies analytical solution was calibrated to quasi-steady state trichloroethene (TCE), cis-l,2-dichloroethene (DCE), and vinyl chloride (VC) plume conditions at a site in Palm Bay, FL, in order to estimate their field-scale, first-order biodegradation rate constants. The estimated first-order rate constant values for the steady-state plumes by the analytical solution were 0.88 yr~(-1), 0.82yr~(-1), and 0.87 yr~(-1) for TCE, DCE, and VC, respectively. These rate constant values are upper-bound estimates because the assumption of a point source release with negligible transverse dispersion leads to higher calculated plume centerline concentrations with concomitant higher calibrated rate constants in order to match the observed data. Although the source width and transverse dispersivity values are not typically well defined in the field, a two- or three-dimensional model could be applied when justifiable in order to reduce the uncertainty of these estimated rate constants.
机译:使用单种分析溶质运移建模方法(例如Buscheck和Alcantar方法)可能会导致生物降解产物速率常数的值被低估,因为这些方法不包括沿地下水流动路径的生物降解产物积累。为了提高子产物生物降解速率常数的估计值,推导了具有三种物种一阶链反应的点源的一维对流扩散方程的稳态解。可以针对母产品和子产品的近似稳态羽流的浓度与距离数据校准此解决方案,以估算其场比例速率常数。对分析解决方案的分析还表明,交叉点(父子浓度与子浓度之间的距离与距离数据相交)和最大点(发生最高浓度水平的距离)的降级位置均可用于直接解释田间数据和估算子产品速率常数。作为一种应用,此一维,多物种分析解决方案已在Palm Bay的某处校准为准稳态三氯乙烯(TCE),顺式1,2-二氯乙烯(DCE)和氯乙烯(VC)羽状条件。 FL,以估计其田间规模的一阶生物降解速率常数。对于TCE,DCE和VC,解析溶液估计的稳态羽流的一阶速率常数估计值为0.88 yr〜(-1),0.82yr〜(-1)和0.87 yr〜(-1)。 , 分别。这些速率常数值是上限估计值,因为假设点源释放具有可忽略的横向分散,会导致较高的计算羽流中心线浓度,并伴随较高的校准速率常数,以匹配观察到的数据。尽管在现场通常没有很好地定义光源的宽度和横向色散值,但是在合理的情况下可以使用二维或三维模型,以减少这些估计的速率常数的不确定性。

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