Velimirovic Milica, Tosco Tiziana, Uyttebroek Maarten, Luna Michela, Gastone Francesca, De Boer Cjestmir, Klaas Norbert, Sapion Hans, Eisenmann Heinrich, Larsson Per-Olof, Braun Juergen, Sethi Rajandrea, Bastiaens Leen
VITO, Boeretang 200, 2400 Mol, Belgium; University of Antwerp, Department of Bio-Engineering, Groenenborgerlaan 171, 2020 Antwerp, Belgium; Department of Environmental Geosciences, University of Vienna, Althanstrasse 14, 1090 Vienna, Austria.
Dipartimento di Ingegneria dell'Ambiente, del Territorio e delle Infrastrutture - Politecnico di Torino, corso Duca degli Abruzzi 24, 10129 Torino, Italy.
J Contam Hydrol. 2014 Aug;164:88-99. doi: 10.1016/j.jconhyd.2014.05.009. Epub 2014 Jun 4.
A pilot injection test with guar gum stabilized microscale zerovalent iron (mZVI) particles was performed at test site V (Belgium) where different chlorinated aliphatic hydrocarbons (CAHs) were present as pollutants in the subsurface. One hundred kilograms of 56μm-diameter mZVI (70gL(-1)) was suspended in 1.5m(3) of guar gum (7gL(-1)) solution and injected into the test area. In order to deliver the guar gum stabilized mZVI slurry, one direct push bottom-up injection (Geoprobe) was performed with injections at 5 depths between 10.5 and 8.5m bgs. The direct push technique was preferred above others (e.g. injection at low flow rate via screened wells) because of the limited hydraulic conductivity of the aquifer, and to the large size of the mZVI particles. A final heterogeneous distribution of the mZVI in the porous medium was observed explicable by preferential flow paths created during the high pressure injection. The maximum observed delivery distance was 2.5m. A significant decrease in 1,1,1-TCA concentrations was observed in close vicinity of spots where the highest concentration of mZVI was observed. Carbon stable isotope analysis (CSIA) yielded information on the success of the abiotic degradation of 1,1,1-TCA and indicated a heterogeneous spatio-temporal pattern of degradation. Finally, the obtained results show that mZVI slurries stabilized by guar gum can be prepared at pilot scale and directly injected into low permeable aquifers, indicating a significant removal of 1,1,1-TCA.
在比利时的试验场地V进行了一项瓜尔胶稳定化的微尺度零价铁(mZVI)颗粒的先导注入试验,该场地的地下存在不同的氯代脂肪烃(CAHs)作为污染物。将100千克直径为56μm的mZVI(约70gL(-1))悬浮于1.5立方米的瓜尔胶(约7gL(-1))溶液中,并注入试验区。为了输送瓜尔胶稳定化的mZVI浆液,采用了一次直接推注自下而上的注入方式(地质探测仪),在地下10.5米至8.5米之间的5个深度进行注入。由于含水层的水力传导率有限以及mZVI颗粒尺寸较大,所以相较于其他方法(例如通过筛管井以低流速注入),直接推注技术更为可取。在高压注入过程中形成的优先流路径可以解释在多孔介质中观察到的mZVI最终的非均匀分布。观察到的最大输送距离为2.5米。在观察到mZVI浓度最高的点附近,观察到1,1,1-TCA浓度显著降低。碳稳定同位素分析(CSIA)提供了关于1,1,1-TCA非生物降解成功与否的信息,并表明了降解的非均匀时空模式。最后,所获得的结果表明,瓜尔胶稳定化的mZVI浆液可以在先导规模下制备并直接注入低渗透含水层,这表明1,1,1-TCA有显著去除。