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Estimation of Sequential Biodegradation Product Rate Constants

机译:估计顺序生物降解产品率常数

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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:使用单种分析溶质传输建模方法(例如,Buscheck和Alcantar方法)可以导致无低估的生物降解产品速率常数值,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。为了改善女儿产品生物降解率常数的估计,推导出三种物种的一阶链反应的点源的一维平面分散方程的稳态解。该解决方案可以校准为父母和女儿产品的近似稳态羽常数的浓度与距离数据,以估计其现场级速率常数。对分析解决方案的分析还表明交叉点(父母和女儿集中与距离数据相交)和最大点(发生最高浓度水平的距离)的下降位置可用于直接解释现场数据和估计女儿产品速率常数。作为应用,这种一维的多数分析解决方案被校准到棕榈湾的地方的准稳态三氯乙烯(TCE),CIS-L,2-二氯乙烯(DCE)和氯乙烯(VC)羽流条件, FL,为了估计其现场规模,一阶生物降解率常数。通过分析溶液的稳态羽流的估计的一阶速率恒定值为0.88yr〜(-1),0.82yr〜(-1),0.87yr〜(-1),用于TCE,DCE和VC , 分别。这些速率常数值是上限估计,因为假设具有可忽略的横向分散率的点源释放导致具有较高计算的羽流率浓度,以伴随较高的校准速率常数,以便与观察到的数据匹配。尽管源宽度和横向分散性值通常在该字段中通常很好地定义,但是可以在合理的情况下应用两个或三维模型以减少这些估计速率常数的不确定性。

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