石油生物脱硫菌Pseudomonas stutzeri UP-1的筛选*

以二苯并噻吩(DBT)为模型化合物,筛选到一株能有效降解DBT的菌株,根据其菌落的形态特征、生理生化特征和分子生物学鉴定方法,确定其为Pseudomonas stutzeri UP-1。该菌株对DBT具有较强的降解能力,降解终产物为水溶性物质。通过对降解产物的分析,初步推断DBT的降解符合Kodama机理。     

石油生物催化脱硫菌Agrobacterium tumefaciens UP3的分离筛选

从胜利油田被原油污染的土壤中筛选到一株能有效降解模型化合物二苯并噻吩(DBT)的菌株.根据常规的形态分析、生理生化性状及16S rDNA序列分析,将其鉴定为根癌土壤杆菌(Agrobacterium tumefaciens UP3).该菌不能以十二烷、十六烷、液体石蜡和萘作为唯一碳源和能源生长,具有工业应用的潜力.对该菌株DBT降解能力的初步研究表明,54h内可将500mg/L的DBT降解至150mg/L.对降解产物的分析表明,根癌土壤杆菌降解DBT的途径与Kodama路线及4-S路线不同.     

石油生物催化脱硫菌Agrobacterium tumefaciens UP3的分离筛选

从胜利油田被原油污染的土壤中筛选到一株能有效降解模型化合物二苯并噻吩（DBT）的菌株。根据常规的形态分析、生理生化性状及16S rDNA序列分析,将其鉴定为根癌土壤杆菌（Agrobacterium tumefaciens UP3）。该菌不能以十二烷、十六烷、液体石蜡和萘作为唯一碳源和能源生长,具有工业应用的潜力。对该菌株DBT降解能力的初步研究表明,54h内可将500mg/L的DBT降解至150mg/L。对降解产物的分析表明,根癌土壤杆菌降解DBT的途径与Kodama路线及4_S路线不同。     

二苯并噻吩分解菌的分离及特性研究

目的利用二苯并噻吩(DBT)分解菌的分离培养基从昆明捞鱼河的污泥中分离得到一株分解DBT的细菌HWXFJ2。方法通过形态观察、生理生化特征和16S rRNA基因序列分析,表明该菌属于革兰阳性菌、杆状、有荚膜,将其初步鉴定为黄色杆菌属的一株菌株;同时利用该菌株进行DBT分解能力的检测和研究。结果该菌株对DBT有较强的分解能力,在7 d和14 d对DBT分解的量分别是红球菌(Rhodococcus sp.HNCS21)的6.04倍和2.07倍。结论煤炭中的有机硫模式化合物为DBT,本研究可以为脱除煤炭中的有机硫提供理论依据,为进一步的应用提供菌种资源。     

专一性脱硫菌的鉴定及高DBT降解力菌株的选育

从大庆油田土壤中分离得到1株可降解二苯并噻吩(DBT)的脱硫微生物HDBS-1,对该微生物的种属地位进行了鉴定并通过诱变手段提高了该菌株的脱硫能力。经过形态观察、生理生化特征分析及16S rDNA序列测定发现该微生物为坂崎肠杆菌(Enterobacter sakazakii),该菌种可以按特异性脱硫途径(简称4S途径)将DBT转化为2-羟基联苯(2-HBP)。利用紫外线(UV)、硫酸二乙酯(DES)和UV+DES对该菌株复合诱变后,得到菌株HDBS-4,其降解DBT生成2-HBP的能力得到了极大的提高,发酵液中2-HBP生成含量(2.574 mg/L)较原始菌株(0.434 mg/L)提高了5.93倍。     

红球菌SDUZAWQ对有机硫和无机硫的耐受性研究及脱硫基因的克隆

以筛选得到的红球菌SDUZAWQ为对象,研究其在不同浓度的有机硫化合物二苯并噻吩(DBT)存在下的脱硫能力,以及在0.2mmolLDBT和不同浓度Na2SO4同时存在下的脱硫情况。当DBT浓度高达6mmolL时,菌株仍能生长,而且检测出产物2-羟基联苯(2-HBP)的存在,说明该菌株具有耐受较高浓度DBT的能力。当DBT和Na2SO4同时存在时,DBT为菌株SDUZAWQ所利用,并且也检测出2-HBP,并非如文献所报道的红球菌在无机硫存在下不代谢DBT,表明该菌株能够耐受一定浓度的无机硫酸盐。对相关脱硫基因的克隆和测序结果显示,完整脱硫基因dszABC、其上游调控序列和dszD的序列与模式菌株RhodococcuserythropolisIGTS8的同源性分别是99%、100%和100%。     

脱硫菌Fds-1的分离鉴定及其对柴油脱硫特性的研究

从含硫土壤中分离筛选出一株专一性脱硫菌Fds-1,经生理生化指标和16S rRNA序列分析鉴定其属于枯草芽孢杆菌(Bacillus subtilis)。用Gibb’s试剂显色和气相色谱-质谱联用分析表明,该菌株通过“4S”途径脱除有机硫。实验发现Fds-1的最佳脱硫活性在30℃,在此温度下72h内能脱除约0.5mmol/L DBT中的有机硫。Fds-1菌株对有机硫化合物的利用情况和柴油脱硫前后烃组分比较都进一步证明该菌株适合于柴油生物脱硫。利用休止细胞对不同组分柴油的脱硫研究表明,脱硫菌株Fds-1对精制柴油中的DBT类化合物的降解能力强。因此,该菌株对精制低硫柴油的深度脱硫具有应用意义。     

一株柴油脱硫菌的分离与鉴定

由最终产物为邻苯基苯酚（2-HBP）的二苯并噻吩（DBT）的4-S代谢途径出发,从被高硫原油污染的土样中分离,纯化得到一株能高效降解DBT的菌株,通过形态学,生理生化试验及16SrDNA基因测序,归类为Mycobacteriumsp．对细菌的培养条件进行研究,初步确定较为适宜的培养条件：温度为40℃,pH值为7．0,转速为200r／min．在此培养条件下,利用该菌株处理含有5mmol／LDBT的正十二烷模拟相,24h以后,DBT减少到3．36mmol／L,平均比脱硫率为8．34mmol DBTh^-1kg^-1 DCW（干细胞重）。     

石油生物脱硫菌Agrobacterium tumefaciens UP-3的固定化研究

对能降解二苯并噻吩(DBT)的根癌土壤杆菌AgrobacteriumtumefaciensUP3菌株进行了固定化研究,以聚乙烯醇(PVA)和海藻酸钠(SA)混合物为包埋法固定化载体,固定化最佳操作条件为4℃交联,PVA和SA混合物总浓度7%,两者最佳浓度比为6,细胞浓度为0.05g/mL。当DBT加入量为2.7mmol/L时,UP-3的静息细胞最高脱硫率为13%,而固定化细胞的脱硫效率超过了60%;固定化细胞的最佳使用条件为降解5d,温度28℃～32℃。     

石油生物脱硫菌Agrobacterium tumefaciens UP-3的固定化研究*

对能降解二苯并噻吩(DBT)的根癌土壤杆菌AgrobacteriumtumefaciensUP3菌株进行了固定化研究,以聚乙烯醇(PVA)和海藻酸钠(SA)混合物为包埋法固定化载体,固定化最佳操作条件为4℃交联,PVA和SA混合物总浓度7%,两者最佳浓度比为6,细胞浓度为0.05g/mL。当DBT加入量为2.7mmol/L时,UP-3的静息细胞最高脱硫率为13%,而固定化细胞的脱硫效率超过了60%;固定化细胞的最佳使用条件为降解5d,温度28℃～32℃。     

Selective Desulfurization of Dibenzothiophene by Rhodococcus erythropolis D-1

A dibenzothiophene (DBT)-degrading bacterium, Rhodococcus erythropolis D-1, which utilized DBT as a sole source of sulfur, was isolated from soil. DBT was metabolized to 2-hydroxybiphenyl (2-HBP) by the strain, and 2-HBP was almost stoichiometrically accumulated as the dead-end metabolite of DBT degradation. DBT degradation by this strain was shown to proceed as DBT → DBT sulfone → 2-HBP. DBT at an initial concentration of 0.125 mM was completely degraded within 2 days of cultivation. DBT at up to 2.2 mM was rapidly degraded by resting cells within only 150 min. It was thought this strain had a higher DBT-desulfurizing ability than other microorganisms reported previously.     

Sequential Growth of Bacteria on Crude Oil

By modification of the enrichment culture procedure three bacterial strains capable of degrading crude oil in sea water were isolated in pure culture, UP-2, UP-3, and UP-4. Strain UP-2 appears to be highly specialized for growth on crude oil in sea water since it showed strong preference for oil or oil degradation products as substrates for growth, converted 66% of the oil into a form no longer extractable by organic solvents, quantitatively degraded the paraffinic fraction (gas chromatographic analysis), emulsified the oil during exponential growth, and produced 1.6 × 10⁸ cells per mg of oil. After exhaustive growth of UP-2 on crude oil the residual oil supported the growth of UP-3 and UP-4, but not a previously isolated oil-degrading bacterium, RAG-1. Strains UP-2, UP-3, and UP-4 grew on RAG-1-degraded oil (specifically depleted of n-alkanes). The growth of UP-3 and UP-4 on UP-2 and RAG-1-degraded oil resulted in the production of new paraffinic compounds as revealed by gas chromatography. When the four strains were grown either together in a mixed culture or sequentially, there was over 75% oil conversion. By plating on selective media, growth of the individual strains was measured kinetically in the reconstituted mixed culture, revealing competition for common growth substances (UP-2 and RAG-1), enhanced die-off (UP-2), and stabilization (UP-4) during the stationary phase.     

Microbial desulfurization of dibenzothiophene in the presence of hydrocarbon

The bacterium, Rhodococcus erythropolis H-2, which can utilize dibenzothiophene (DBT) as a sole source of sulfur in the presence of hydrocarbon, was isolated from soil samples. When this strain was cultivated in a medium containing 0.27 mM DBT and 40% n-tetradecane, DBT was metabolized stoichiometrically to 2-hydroxybiphenyl within 1 day. This strain grew in the presence of n-octane and longer-carbonchain hydrocarbons, but not with n-hexane, styrene, p-xylene, cyclooctane or toluene. DBT degradation proceeded in the resting cell system with lyophilized cells of this strain. The addition of n-tetradecane enhanced the reaction rate, the optimal concentration being 40%. DBT degradation occurred in the reaction mixture even in the presence of 70% n-tetradecane, whereas at concentrations above 80% n-tetradecane suppressed the degradation.     

Expression of dibenzothiophene-degradative genes in two Pseudomonas species

The genes encoding dibenzothiophene (DBT) degradation in Pseudomonas alcaligenes strain DBT2 were cloned into plasmid pC1 by other workers. This plasmid was conjugally transferred into a spontaneous variant of Pseudomonas sp. HL7b (designated HL7bR) incapable of oxidizing DBT (Dbt- phenotype). Acquisition of plasmid pC1 simultaneously restored oxidation of DBT and naphthalene to the transconjugant, although the primary DBT metabolite produced by transconjugant HL7bR(pC1) corresponded to that produced by wild-type strain DBT2 rather than that from wild-type strain HL7b. Inducers of the naphthalene pathway (naphthalene, salicylic acid, and 2-aminobenzoate) stimulated DBT oxidation in transconjugant HL7bR(pC1) when present at 0.1 mM concentrations but had no effect on wild-type strain HL7b. Higher concentrations (5 mM) of salicylic acid and naphthalene were inhibitory to DBT oxidation in all strains. DNA-DNA hybridization was not observed between plasmid pC1 and genomic DNA from strains HL7b or HL7bR, nor between authentic naphthalene-degradative genes (plasmid NAH2) and either plasmid pC1 or strain HL7b, despite the observation that the degradative genes encoded on plasmid pC1 functionally resembled broad-specificity naphthalene-degradative genes. Transconjugant HL7bR(pC1) is a mosaic of the parental types regarding DBT metabolite production, regulation, and use of carbon sources.     

Degradation of dibenzothiophene and its metabolite 3-hydroxy-2-formylbenzothiophene by an environmental isolate

Microbial degradation of dibenzothiophene (DBT) beyond 3-hydroxy-2-formylbenzothiophene (HFBT), a commonly detected metabolite of the Kodama pathway for DBT metabolism, and the catabolic intermediates leading to its mineralization are not fully understood. The enrichment cultures cultivated from crude oil contaminated soil led to isolation of ERI-11; a natural mixed culture, selected for its ability to deplete DBT in basal salt medium (BSM). A bacterial strain isolated from ERI-11, and tentatively named A₁₁, degraded more than 90 % of the initial DBT (270 µM), present as the sole carbon and sulfur source, in 72 h. Gas chromatography–mass spectrophotometry (GC–MS) analyses of the DBT degrading A₁₁ culture medium extracts led to detection of HFBT. The metabolite HFBT, produced using A₁₁, was used in degradation assays to evaluate its metabolism by the bacteria isolated in this study. Ultra violet–visible spectrophotometry and high-performance liquid chromatography analyses established the ability of the strain A₁₁ to deplete HFBT, present as the sole sulfur and carbon source in BSM. GC–MS analyses showed the presence of 2-mercaptobenzoic acid in the HFBT degrading A₁₁ culture extracts. The findings in this study establish that the environmental isolate A₁₁ possesses the metabolic capacity to degrade DBT beyond the metabolite HFBT. The compound 2-mercaptobenzoic acid is an intermediate formed on HFBT degradation by A₁₁.     

Influence of incubation period on the plasmid content of proliferating Nocardioides sp.

S. SANDHYA. 1996. Nocardioides sp., isolated for organic sulphur degradation, harbours catabolic plasmid pSB1 of molecular weight 34.2 kb. A correlation was noticed between the plasmid content and degradation of the organic sulphur compound dibenzothiophene (DBT). The maximum oxidation of DBT was only after 64 h, during which the content of plasmid DNA was also optimum.     

Cloning and expressing DBT (dibenzothiophene) monooxygenase gene (dszC) from Rhodococcus sp. DS-3 in Escherichia coli

Dibenzothiophene (DBT) monooxygenase (DszC)catalysis,the first and also the key step in the microbial DBT desulfurization,is the conversion of DBT to DBT sulfone (DBTO2).In this study,dszC of a DBT-desulfiaizing bacterium Rhodococcus sp.DS-3 was cloned by PCR.The sequence cloned was 99% homologous to Rhodococcus erythropolis IGTS8 that was reported in the Genebank.The gene dszC could be overexpressed effectively after being inserted into plasmid pET28a and transformed into E.coli BL21 strain.The expression amount of DszC was about 20% of total supernatant at low temperature.The soluble DszC in the supematant was purified by Ni2+ chelating His-Tag resin column and sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) to electronics purity.Only one band was detected by Western-blotting,which is for the antibody released in mouse against purified DszC in the expression product of BL21 (DE3,paC5) and Rhodococcus sp.DS-3.The activity of purified DszC was 0.36 U.DszC can utilize the organic compound such as DBT and methyl-DBT,hut not DBT derivates such as DBF,which has no sulfur or inorganic sulfur.     

Biodesulfurization of benzothiophene and dibenzothiophene by a newly isolated Rhodococcus strain

Rhodococcus sp. KT462, which can grow on either benzothiophene (BT) or dibenzothiophene (DBT) as the sole source of sulfur, was newly isolated and characterized. GC and GC-MS analyses revealed that strain KT462 has the same BT desulfurization pathway as that reported for Paenibacillus sp. A11-2 and Sinorhizobium sp. KT55. The desulfurized product of DBT produced by this strain, as well as other DBT-desulfurizing bacteria such as R. erythropolis KA2-5-1 and R. erythropolis IGTS8, was 2-hydroxybiphenyl. A resting cells study indicated that this strain was also able to degrade various alkyl derivatives of BT and DBT.