地下水循环井技术修复硝基苯污染含水层效果模拟

实验在二维模拟槽中进行,以曝气前后地下水水位高度变化表征地下水循环强度,分析了地下水初始水位,曝气量和地下水初始流速对循环井运行的影响,并以得到的最佳运行参数进行硝基苯污染地下水修复效果模拟.结果表明,地下水初始水位45 cm,曝气量0.7 m3·h-1,地下水初始流速低于1.0 m·d-1时,循环井可以达到良好运行状态.硝基苯在地下水中的纵向迁移距离明显大于横向,泄漏第50 d时,平均浓度达到246.97 mg·L-1.循环井修复过程中,逐渐形成一个以循环井为中心的有机物高效修复区域.该区域内有机物被优先去除,浓度持续下降.高效修复区域外,存在过渡区域,该区域内有机物的浓度受有机物吸附/解吸和迁移性共同作用影响.整个修复过程中,硝基苯的浓度经历了快速下降-缓慢下降-浓度拖尾3个阶段,累计曝气14 h后,硝基苯的平均浓度下降至71.19 mg·L-1,残留的硝基苯分布在远离循环井的区域.由此可见,地下水循环井技术能够较好地修复硝基苯污染的地下水,修复过程存在最佳运行条件及最适修复时间.

Laboratory Evaluation of Remediation of Nitrobenzene Contaminated Aquifer by Using Groundwater Circulation Well

A two-dimension simulated sand box was set up to investigate the influencing factors, such as the initial groundwater level, aeration rate and the initial groundwater rate, that affect groundwater circulation well (GCW) by determining the intensity of groundwater circulation which was characterized by the variation of groundwater level before and after aeration. The optimal operating parameters were used to remediate nitrobenzene contaminated aquifer. The results demonstrated that: GCW could be well operated under the conditions of 45 cm groundwater level, 0.7 m³ ·h^-1 aeration rate. The effects of groundwater velocity less than 1.0 m ·d^-1 could be ignored. The lateral mobility rate of nitrobenzene was faster than that of longitudinal. The average concentration of nitrobenzene was 246.97 mg ·L^-1 on day 50 of leakage. During the remediation of circulation well, an efficient organics remediation region was gradually formed around the circulation well. The organics in this region was removed preferentially, and the concentration decreased continuously. Besides the efficient remediation region, there was a transient region, where the concentration of organics was influenced by the combined effects of adsorption/desorption and migration potential of organics. During the whole remediation process, the concentration of nitrobenzene went through three stages described as rapid removal, slow removal. After 14h aeration, the nitrobenzene average concentration was reduced to 71.19 mg ·L^-1. The residual nitrobenzene was distributed in regions far away from GCW. Therefore, nitrobenzene contaminated aquifer could be well remediated by GCW, and there were optimal operation conditions and appropriate remediation time which guaranteed the best remediation effect.