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高分子量多环芳烃降解菌LD29的筛选及降解特性研究
摘要点击 2725  全文点击 1912  投稿时间:2010-07-05  修订日期:2010-10-20
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中文关键词  高分子量  多环芳烃  生物降解  矢野口鞘氨醇菌
英文关键词  high molecular weight  polycyclic aromatic hydrocarbons(PAHs)  biodegradation  Sphingobium yanoikuyae
作者单位
刘芳 中国农业大学资源与环境学院北京100193 
梁金松 中国农业大学资源与环境学院北京100193中国科学院生态环境研究中心环境水质学国家重点实验室北京100085 
孙英 中国农业大学理学院北京100193 
郭岩彬 中国农业大学资源与环境学院北京100193 
李庆孝 美国夏威夷大学生物科学与生物工程系夏威夷96822 
李季 中国农业大学资源与环境学院北京100193 
中文摘要
      采用硅油-水双液相富集体系,以蒽为富集碳源,从原油污染土壤富集分离多环芳烃降解菌,分离出1株能降解菲、蒽、荧蒽、芘、苯并[a]芘的细菌,经形态特征、生理生化和16S rDNA鉴定为矢野口鞘氨醇菌(Sphingobium yanoikuyae),编号为LD29.采用高效液相色谱(HPLC)对LD29在无机盐培养基中对PAHs的降解特性做了研究.LD29能以唯一碳源与能源方式降解菲、蒽、荧蒽、芘(初浓度均为50 mg/L),4 d的降解率分别为92%、 87%、 28%、 7%,但未能降解苯并[a]芘.蒽能促进LD29对荧蒽/芘的降解,而荧蒽/芘则抑制LD29对蒽的降解.较高初始pH(pH=9)的培养基有利于LD29对混合多环芳烃的降解.外加营养可促进LD29对荧蒽的降解.外加碳源(葡萄糖,200 mg/L)或氮源(蛋白胨,50 mg/L)处理中荧蒽(100 mg/L)6 d的降解率分别为69%、 81%,而对照组只有34%.在含有5种多环芳烃(菲、蒽、荧蒽、芘、苯并[a]芘)的无机盐培养基溶液中,LD29在4 d的适应期之后开始快速降解高分子量多环芳烃,6 d芘和荧蒽的降解率(48%、 66%)比4 d分别增加40%、 56%,并且苯并[a]芘也被降解了17%.LD29具有降解高分子量PAHs的潜力.
英文摘要
      Two-liquid-phase (silicone oil-water) culture enrichment systems,with anthracene as carbon source,was used to enrichment PAHs-degrading strains from contaminated soil by crude oil.One strain,which can degrade phenanthrene,anthracene,fluoranthene,pyrene and benzo[a]pyrene,was isolated and identified as Sphingobium yanoikuyae based on 16S rDNA sequences,phenotypic characteristics and physio-biochemistry characteristics,and numbered as LD29.Degradation characteristics of LD29 in mineral salts medium (MSM) was measured by HPLC.After 4 days of growing in MSM with single PAH as carbon source,LD29 degraded phenanthrene,anthracene,fluoranthene,pyrene (initial concentration: 50 mg/L) by 92%, 87%, 28% and 7% respectively,but no benzo[a]pyrene was degraded.Anthracene enhanced the degradation of fluoranthene/pyrene by LD29,whereas fluoranthene/pyrene impeded anthracene degradation by LD29.MSM with high initial pH value (pH=9) favored the degradation of PAHs mixture in MSM by LD29.The degradation activity of LD29 can be improved by additional nutrition.Additional carbon source (glucose, 200 mg/L) or nitrogen source (peptone, 50 mg/L) accelerated fluoranthene (100 mg/L) degradation in MSM,with degradation rate 69%, 81% respectively(CK: 34%) within 6 days.LD29 started to significantly degrade HMW PAHs from the 4th day in MSM with 5 PAHs (phenanthrene,anthracene,fluoranthene,pyrene and benzo[a]pyrene),and the degradation rate of pyrene and fluoranthene at day 6 were 44% and 58% higher than those of day 4 respectively,and the degradation rate of benzo[a]pyrene also reached to 17% at day 6.LD29 has significant potential for PAHs degradation,including high molecular weight (HMW) PAHs.

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