基于生物聚合物改性粉质黏土的覆盖屏障建造与土体气态污染物阻隔性能研究

    Construction of Biopolymer-amended Silty Clay Based Cover Barriers and Evaluation of Barrier Performance of Controlling Migration of Volatile Organic Compounds Gases in Soils

    • 摘要: 针对某有机-重金属复合污染土的非正规填埋污染地块,开展了覆盖阻隔现场试验研究。以低碳生物聚合物黄原胶为改性剂,采用两种工艺改性场地内原有覆土(粉质黏土):①湿法工艺。将黄原胶干粉水化为溶液,并将溶液喷洒在松铺的粉质黏土上方,待溶液渗透浸入松铺土层后碾压成型压实粉质黏土;②干法工艺。将黄原胶干粉与原有覆土混拌后碾压成型为压实黏土。覆盖阻隔屏障由保护土层和防渗阻气层构成,防渗阻气层类型包括:改性压实土、改性压实土-黄原胶改性膨润土防水毯复合层、未改性压实土-土工膜复合层,以及未改性压实土。针对压实土层和保护层的取芯试样,开展了压实度、含水率、液塑限测定,进行了气体渗透和扩散以及柔性壁水力渗透实验,评价压实土的均质性和黄原胶的分布均匀性,研究压实土层试样的防渗阻气性能。结果表明,湿法和干法工艺所形成压实土的体积含水率、压实度、孔隙比的数值相近。在饱和度77% ~ 90%时,改性压实土与未改性土相比,气体渗透率从8×10-13 m2 ~ 3.3 ×10-12 m2 降低至4.7×10-14 m2 ~ 4.2×10-13 m2(降低了约10倍),气体扩散系数从1.2 ×10-8 m2/s ~ 6.9 ×10-8 m2/s降低至4.9×10-9 m2/s ~ 1.7×10-8 m2/s(降低了约4倍)。未改性压实土的饱和水力渗透系数为8.8 ×10-8 m/s,两种改性工艺下的压实土层饱和水力渗透系数均低于1×10-9 m/s。82天原位监测结果表明,改性压实土在降雨前后含水率的相对变化幅度小于1%,而未改性压实土的含水率相对变化幅度为33%;改性压实土层上方保护土层内VOC气体浓度均低于0.2 mg/m3,是未改性压实土层上方保护层内VOC气体浓度(2 mg/m3)1/6、 污染土内VOC气体浓度(12.5 mg/m3)1/60,表明改性压实土层防渗阻气性能良好。

       

      Abstract: Field tests were conducted to evaluate the performance of cover barrier for legacy organic-contaminated soil resulting from informal landfilling at a chemical plant site. Xanthan gum (XG), a low-carbon biopolymer, was used as a soil amendment to amend the existing on-site cover soil (silty clay) through two treatment methods: (1) a wet mixing method, in which the XG was pre-hydrated into a solution and sprayed onto loosely placed silty clay, followed by infiltration and compaction to form an amended silty clay; and (2) a dry mixing method, where the XG powder was directly mixed with the soil. The cover barrier consisted of a protective layer and compacted soil layer (gas/hydraulic barrier). Four types of barrier configurations were constructed: XG-amended compacted soil, a composite layer of amended soil and XG-amended geosynthetic clay liner (GCL), a composite layer of unamended soil and geomembrane, and unamended compacted soil. Core samples were collected from the compacted soil layer and protection layer. Laboratory tests were conducted to evaluate the homogeneity of the compacted soil, the distribution uniformity of XG, and the gas/hydraulic barrier performance of the compacted soil specimens. These tests included measurements of degree of compaction, moisture content, Atterberg limits, gas permeability, gas diffusion, and flexible-wall hydraulic conductivity tests. Results showed that both unamended and amended compacted soil had similar volumetric water content, degree of compaction, and void ratio values. At saturation levels of 77% - 90%, the gas permeability of amended compacted soil significantly reduced from 8×10-13 to 3.3×10-12 m2 for unamended soils to 4.7×10-14 to 4.2×10-13 m2(approximately a tenfold decrease). The gas diffusion coefficient also decreased from 1.2×10-8 to 6.9×10-7 m2/s (unamended) to 4.9×10-9 to 1.7×10-8 m2/s (amended) representing about a fourfold reduction. The saturated hydraulic conductivity of unamended soil was 8.8×10⁻⁸ m/s, whereas amended soils exhibited hydraulic conductivity below 1×10-9 m/s. After 82 days of field monitoring, the volumetric water content of the amended CCL varied by less than 1% before and after rainfall, while the unamended soil showed a 33% relative variation. Moreover, the VOC concentration within the protection layer above the amended compacted soil remained below 0.2 mg/m3, which is one-sixth of the value observed above the unamended compacted soil (2 mg/m3), and just 1/60 of the VOC concentration measured in the contaminated soil layer (12.5 mg/m³), indicating superior gas and fluid isolation performance of the biopolymer-modified compacted barrier.

       

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