文章摘要
张雪娜,贾海滨,李橙,王伟,张丽秀,冯圣东,杨志新.添加淀粉和通气对固定化Fusarium.sp修复煤矿区老化污染土壤HMW-PAHs的影响[J].农业环境科学学报,2016,35(9):1709-1716.
添加淀粉和通气对固定化Fusarium.sp修复煤矿区老化污染土壤HMW-PAHs的影响
Effect of starch and aeration addition on degradation of HMW-PAHs by immobilized Fusarium.sp in a polluted and aged soil of a coal mining area
投稿时间:2016-04-28  
DOI:10.11654/jaes.2016-0596
中文关键词: 典型煤矿区  HMW-PAHs  固定化Fusarium.sp  淀粉  通气  土壤酶活性
英文关键词: a coal mining area  HMW-PAHs  immobilized Fusarium.sp  starch  aeration  soil enzyme activity
基金项目:河北省教育厅项目(Z2013058);863专项(2012AA101403-3)
作者单位E-mail
张雪娜 河北农业大学资源与环境科学学院, 河北 保定 071000  
贾海滨 河北农业大学资源与环境科学学院, 河北 保定 071000  
李橙 河北省环境科学研究院, 石家庄 050000  
王伟 河北农业大学资源与环境科学学院, 河北 保定 071000  
张丽秀 河北农业大学资源与环境科学学院, 河北 保定 071000  
冯圣东 河北农业大学资源与环境科学学院, 河北 保定 071000 fengshengdong@126.com 
杨志新 河北农业大学资源与环境科学学院, 河北 保定 071000
河北省农田生态环境重点实验室, 河北 保定 071000 
yangzhixin@126.com 
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中文摘要:
      为了提高Fusarium.sp对PAHs的修复效果,在典型煤矿区老化污染土壤中添加淀粉和通气,经为期60 d的土壤培养试验,研究玉米秸秆固定化Fusarium.sp对土壤10种HMW-PAHs的修复效果及不同处理下土壤中酶活性变化规律。结果表明:HMW-PAHs(High molecular weight-PAHs)总量去除率表现为固定化菌剂+淀粉+通气处理(J+D+O,29.19%)≈固定化菌剂+淀粉处理(J+D,25.89%)>固定化菌剂处理(J,16.54%);4环、5环和6环PAHs去除率在J+D+O和J+D两组处理间的差异均不显著,且与J处理相比均有显著提高(P<0.05);三组处理对单个HMW-PAH的去除率分别为9.12%~21.73%、17.93%~43.12%、24.34%~35.79%,J+D+O和J+D处理对单个HMW-PAH的修复效果均有显著促进作用,其中,对BkF的去除增幅最大,分别增加了68.09%、63.78%。从酶活性规律看,土壤过氧化氢酶活性呈CK > J > J+D > J+D+O(P<0.05)的规律,且与10种PAHs单体的去除率呈显著或极显著负相关;土壤木质素过氧化物酶活性却与Chry、BkF、InP、DbA、BghiP去除率呈显著正相关。综上认为,不同处理对单个PAHs的去除具有其选择性,且添加淀粉的两处理均显著提高了土壤中HMW-PAHs的修复效果。
英文摘要:
      The soil incubation experiment was performed to study the effect of starch and aeration addition on HMW-PAHs degradation by Fusarium.sp in polluted and aged soil of a coal mining area. After 60 days incubation, the degradation rate of 10 HMW-PAHs as well as the change rule of soil enzyme activities were analyzed. The results showed that the treatments were in the following order in terms of ∑10 HMW-PAHs degradation rate:immobilized Fusarium.sp+starch+aeration(J+D+O, 29.19%)≈immobilized Fusarium.sp+starch(J+D, 25.89%)>immobilized Fusarium.sp(J, 16.54%). There was no significant difference between J+D+O and J+D for the degradation of ∑4-rings, ∑5-ring and ∑6-ring PAHs, but their degradation rates were higher than J significantly(P<0.05). The degradation range of 10 individual HMW-PAHs were 9.12%~21.73%, 17.93%~43.12%, 24.34%~35.79% in J, J+D and J+D+O treatments respectively. The results demonstrated that far higher degradation rates of the 10 individual HMW PAHs were achieved in J+D+O and J+D treatments than those in J treatment, but there was no significant difference between J+D+O and J+D. The removal rates of BkF presented the highest increase extent in the two treatments and increased 68.09%, 63.78% respectively. In addition, the treatments were in the following order in terms of catalase enzyme activities:CK > J > J+D > J+D+O(P<0.05). We found that there were significant(P<0.05) linear negative correlation between the removal rates of the 10 individual HMW-PAHs and catalase activity in soil. However, the degradation rate of Chry, BkF, InP, DbA, BghiP had significant(P<0.05) linear positive correlation with lignin peroxidase activity. In conclusion, the individual PAH was removed by different treatments selectively, and the degradation rate were significantly improved by adding starch.
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