Jin Lei, Sun Xiumei, Zhang Xiaojun, Guo Yuanming, Shi Hui
Marine Fishery Research Institute of Zhejiang Province, Zhejiang Province Key Lab of Mariculture & Enhancement, Zhoushan, 316100, Zhejiang Province, China,
Curr Microbiol. 2014 Jun;68(6):708-16. doi: 10.1007/s00284-014-0533-8. Epub 2014 Feb 7.
Two di-n-butyl phthalate (DBP)-degrading strains, designated as S-3 and H-2, were isolated from DBP-polluted soil and both identified as Paenibacillus sp. When DBP was provided as the sole carbon source, about 45.5 and 71.7 % of DBP (100 mg/L) were degraded by strain S-3 and H-2, respectively, after incubation for 48 h. However, DBP (100 mg/L) was degraded completely by co-culture of strain S-3 and H-2 after incubation for 60 h. Four phthalic acid (PA) esters could be utilized by co-metabolism in the study and the degradation rates followed the order of dimethyl phthalate > diethyl phthalate > DBP > dioctyl phthalate. The metabolic pathway of DBP was elucidated based on the results of metabolites identification and enzyme assays. For strain S-3, DBP was degraded into butyl hydrogen phthalate which was degraded to PA by carboxyesterase further. But PA could be not hydrolyzed further because strain S-3 lacked 3,4-phthalate dioxygenase. Different with S-3, strain H-2 could hydrolyze PA into 3,4-dihydroxy-PA by 3,4-phthalate dioxygenase. Then 3,4-dihydroxy-PA was converted to protocatechuate and benzoic acid. Finally, the aromatic ring was cleavage and mineralized to CO2 and H2O. Above all, co-metabolism could increase the activity of 3,4-phthalate dioxygenase and accelerated the degradation of DBP. This study highlights an important potential use of co-metabolic biodegradation for the in situ bioremediation of DBP and its metabolites-contaminated environment.
从邻苯二甲酸二丁酯(DBP)污染土壤中分离出两株DBP降解菌,分别命名为S-3和H-2,二者均鉴定为芽孢杆菌属。以DBP作为唯一碳源时,培养48 h后,菌株S-3和H-2分别降解了约45.5%和71.7%的DBP(100 mg/L)。然而,菌株S-3和H-2共培养60 h后可将100 mg/L的DBP完全降解。研究发现,4种邻苯二甲酸(PA)酯可通过共代谢被利用,降解率顺序为邻苯二甲酸二甲酯>邻苯二甲酸二乙酯>DBP>邻苯二甲酸二辛酯。基于代谢产物鉴定和酶活性测定结果阐明了DBP的代谢途径。对于菌株S-3,DBP先降解为邻苯二甲酸氢丁酯,后者再被羧酸酯酶进一步降解为PA。但由于菌株S-3缺乏3,4-邻苯二甲酸双加氧酶,PA无法进一步水解。与S-3不同,菌株H-2可通过3,4-邻苯二甲酸双加氧酶将PA水解为3,4-二羟基-PA。然后3,4-二羟基-PA转化为原儿茶酸和苯甲酸。最后,芳香环被裂解并矿化为CO2和H2O。综上所述,共代谢可提高3,4-邻苯二甲酸双加氧酶的活性,加速DBP的降解。本研究突出了共代谢生物降解在原位修复DBP及其代谢产物污染环境方面的重要潜在应用。