采用温室盆栽试验,在种植紫花苜蓿的同时,分别施加木霉菌剂、根瘤菌菌剂以及木霉与根瘤菌复合菌剂,并采用离心分级法将处理后土壤分为4个粒径团聚体,即细黏粒(0.1~1μm)、粗黏粒(1~5gm)、粉粒(5~50μm)以及细砂粒(50~250μm),分析了植物域生物联合作用对不同粒径土壤中PAHs的去除效应。研究结果表明:紫花苜蓿一根瘤菌联合作用对PAHs污染土壤的修复效果最优,其降解率达60%以上。不同粒径组分中PAHs含量的分布表现为细砂粒〉粉粒〉粗黏粒〉细黏粒,且PAHs在不同粒径团聚体中去除率差异性较大。低环(2、3环)PAHs在各粒径组分中去除率较低(20%以下),并在不同粒径组分间呈非均衡分配状态;4环PAHs的去除主要集中在粉粒和细砂粒中,而5环PAHs的去除主要发生在细黏粒上。可见,PAHs在土壤不同粒径组分中分布特征及降解效应为进一步阐明PAHs污染土壤的生物修复机制提供了科学依据。
A pot experiment was conducted to explore the combined remediation of microorganisms (Trichoderma reesei and Rhizobium meliloti) and alfalfa stimulated the degradation of PAHs by rhizosphere microflora in different particle-size fractions of soil aggregates. Soil aggregates were partitioned into 4 particle-size fractions (clay: 0.1 - 1 μm, fine silt: 1 - 5 μm, silt: 5 - 50 μm and fine sand: 50 - 250μm) by using the method of centrifugation in five treatments. The results showed that the degradation rate of PAHs in soil treated with Rhizobiurn meliloti with alfalfa was 60%. The distribution of 16 PAHs concentrations in different soil particle size composition was in the order of fine sand 〉 silt 〉 fine sand 〉 clay, besides, low-molecular (2, 3-ring) PAHs was not degraded and but transferred in different size of particles (degradation rate less than 20%). The degradation of 4-ring PAHs occurred mainly on silt and fine sand soil particles and 5-ring PAHs degradation on the clay. Ilence, the distribution and degradation of PAils in different size of particles has a great significance on remediation ofPAHs polluted soil.