DTU Environment, Technical University of Denmark, Denmark.
J Contam Hydrol. 2012 Aug;136-137:1-9. doi: 10.1016/j.jconhyd.2012.04.007. Epub 2012 May 9.
Tracer experiments during clogging and de-clogging experiments in a 2D sand box were via an image analysis used to establish a data set on the relation between changes in hydraulic conductivity (K) and relative porosity (β). Clogging appears to create a finger-like tracer transport, which could be caused by an initial heterogeneous distribution of biomass in the sand box. De-clogging occurs at a slower rate possibly due to the presence of inert biomass that is not affected by the starvation conditions by sudden removal of the substrate source. The tracer front was observed to get disturbed closer and closer to the substrate source during the experiments suggesting that the zone of clogging moved upstream. Three clogging models, K(β), from the literature were tested for their ability to describe the temporal changes in clogging at the scale of the sand box; the model of Clement et al. (1996) that makes no assumption on biomass distribution, the plug formation model of Thullner et al. (2002a), and the biofilm-plug formation model of Vandevivere (1995). The plug formation and biofilm-plug formation models both match the observed changes between the hydraulic conductivity of the sand box and the relative porosity. Unfortunately our experiments did not reach low relative porosities where the two models predict different behaviors. The model by Clement et al. (1996) underestimates clogging.
在二维砂箱的堵塞和解堵实验中,通过图像分析建立了一个关于水力传导率(K)和相对孔隙率(β)变化之间关系的数据组。堵塞似乎会产生类似手指的示踪剂传输,这可能是由于生物质在砂箱中的初始非均匀分布造成的。解堵的速度可能较慢,这可能是由于存在惰性生物质,它们不受基质源突然去除引起的饥饿条件的影响。在实验过程中,示踪剂前沿在靠近基质源的地方被观察到越来越受到干扰,这表明堵塞区向上游移动。测试了来自文献的三种堵塞模型,K(β),以评估它们在砂箱尺度上描述堵塞时间变化的能力;Clement 等人的模型(1996 年)没有对生物质分布做出假设,Thullner 等人的堵塞形成模型(2002a),以及 Vandevivere(1995 年)的生物膜-堵塞形成模型。堵塞形成和生物膜-堵塞形成模型都与砂箱水力传导率和相对孔隙率之间的观察到的变化相匹配。不幸的是,我们的实验没有达到两个模型预测不同行为的低相对孔隙率。Clement 等人的模型(1996 年)低估了堵塞。