环境科技
環境科技
배경과기
Environmental Science and Technology
2015年
5期
38-41
,共4页
土壤修复%微生物降解%厌氧-好氧工艺
土壤脩複%微生物降解%厭氧-好氧工藝
토양수복%미생물강해%염양-호양공예
Soil remediation%Microbial degradation%Anaerobic-aerobic process
针对好氧工艺与厌氧工艺单一修复污染土壤的不足, 设计组合工艺, 考察了不同污染物在该工艺下的降解率,对微生物土壤修复具有重要意义. 采用本组合工艺,分别以被二氯联苯;邻(对)硝基氯苯;滴滴涕(DDTs);六六六(HCHs)污染的4种污染土壤为对象,研究了各污染土壤在对应的厌氧与好氧菌共同作用下污染物的降解程度. 结果表明:最终污染物的降解率均达到95%以上,说明本工艺可以有效地对难降解有机污染土壤进行修复.铝加入量为硫化砷渣质量的15%时,砷的浸出质量浓度为1.25 mg/L,达到了危险废物填埋污染控制标准.
針對好氧工藝與厭氧工藝單一脩複汙染土壤的不足, 設計組閤工藝, 攷察瞭不同汙染物在該工藝下的降解率,對微生物土壤脩複具有重要意義. 採用本組閤工藝,分彆以被二氯聯苯;鄰(對)硝基氯苯;滴滴涕(DDTs);六六六(HCHs)汙染的4種汙染土壤為對象,研究瞭各汙染土壤在對應的厭氧與好氧菌共同作用下汙染物的降解程度. 結果錶明:最終汙染物的降解率均達到95%以上,說明本工藝可以有效地對難降解有機汙染土壤進行脩複.鋁加入量為硫化砷渣質量的15%時,砷的浸齣質量濃度為1.25 mg/L,達到瞭危險廢物填埋汙染控製標準.
침대호양공예여염양공예단일수복오염토양적불족, 설계조합공예, 고찰료불동오염물재해공예하적강해솔,대미생물토양수복구유중요의의. 채용본조합공예,분별이피이록련분;린(대)초기록분;적적체(DDTs);륙륙륙(HCHs)오염적4충오염토양위대상,연구료각오염토양재대응적염양여호양균공동작용하오염물적강해정도. 결과표명:최종오염물적강해솔균체도95%이상,설명본공예가이유효지대난강해유궤오염토양진행수복.려가입량위류화신사질량적15%시,신적침출질량농도위1.25 mg/L,체도료위험폐물전매오염공제표준.
As efficiency of single soil rem ediation process is limited,the combination of aerobic and anaerobic process was studied. The soil samples, polluted by dichlorobenzene,ortho-nitrochlorobenzene,DDTs and HCHs respectively, were collected. The pollutants degradation of those samples was studied by the bio-degradation of anaerobic and aerobic bacteria. The results show that pollutants degradation rate is above 95%, which means that the combination of aerobic-anaerobic process is effective.