Identification of three novel salicylate 1-hydroxylases involved in the phenanthrene degradation of Sphingobium sp. strain P2

Five sets of large and small subunits of terminal oxygenase (ahdA1[a-e] and ahdA2[a-e]) and a single gene set encoding ferredoxin (ahdA3) and ferredoxin reductase (ahdA4) were found to be scattered through 15.8- and 14-kb DNA fragments of phenanthrene-degrading Sphingobium sp. strain P2. RT-PCR analysis indicated the inducible and specific expression of ahdA3, ahdA4, and three sets of genes for terminal oxygenase (ahdA1[c-e] and ahdA2[c-e]) in this strain grown on phenanthrene. The biotransformation experiments with resting cells of Escherichia coli JM109 harboring recombinant ahd genes revealed that AhdA2cA1c, AhdA1dA2d, and AhdA1eA2e can all function as a salicylate 1-hydroxylase which converts salicylate, a metabolic intermediate of phenanthrene, to catechol in cooperation with the electron transport proteins AhdA3A4. The first two oxygenases exhibited a broad range of substrate specificities such that they also catalyzed the hydroxylation of methyl- and chloro-substituted salicylates to produce their corresponding substituted catechols.     

Biodegradaon of phenanthrene in soil microcosms stimulated by an introduced Alcaligenes sp.

Abstract A phenanthrene degrading strain of Alcaligenes sp. was isolated from oil polluted soil. Addition of Alcaligenes sp. to soil microcosms supplemented with phenanthrene (1 mg/g dry soil) resulted in degradation of the added phenanthrene within 11 days. The phenanthrene concentration declined only 12% in uninoculated soil during 42 days. The total phenanthrene degradation potential of Alcaligenes sp. was 2.3 mg/g dry soil during a period of 22 days. The amount of CO₂ evolved during 22 days corresponded to the conversion of 91% of the degraded phenanthrene to CO₂. The Alcaligenes sp. were not able to degrade phenanthrene in sterile soil.     

好氧条件下Sphingomonas sp．XJ1降解DBP途径的研究

在三角瓶中采用Sphingomonas sp．XJ1对邻苯二甲酸丁酯（DBP）进行好氧降解,以考察DBP的降解途径。分别对降解16h、32h和40h的DBP样品进行代谢产物分析,可判定保留时间为4．79min和5．11min所对应的代谢产物分别为原儿茶酸和邻苯二甲酸。由此可知,菌株Sphingomonassp．XJ1对DBP的降解遵循DBP好氧生物降解途径的一般途径。即在菌株XJI的作用下,DBP首先水解为MBP,继而水解为PA,经由PCA最终完全降解为CO2和H2O。     

好氧条件下Sphingomonassp.XJ1降解DBP途径的研究

在三角瓶中采用Sphingomonas sp.XJ1对邻苯二甲酸丁酯(DBP)进行好氧降解,以考察DBP的降解途径。分别对降解16h、32h和40h的DBP样品进行代谢产物分析,可判定保留时间为4.79min和5.11min所对应的代谢产物分别为原儿茶酸和邻苯二甲酸。由此可知,菌株Sphingomonas sp.XJ1对DBP的降解遵循DBP好氧生物降解途径的一般途径。即在菌株XJ1的作用下,DBP首先水解为MBP,继而水解为PA,经由PCA最终完全降解为CO2和H2O。     

3-苯氧基苯甲酸降解菌Sphingomonas sp. SC-1降解苯酚环境条件及其降解中间产物的研究

【目的】探究高效降解3-苯氧基苯甲酸(3-Phenoxybenzoic acid,3-PBA)的鞘氨醇单胞菌(Sphingomonas sp.) SC-1对苯酚的降解特性。【方法】采用HPLC测定微生物降解体系中苯酚残留量,考察环境条件对菌株SC-1降解苯酚的影响;分析不同培养时间苯酚降解体系混合样品的HPLC谱图,确定其降解中间产物。【结果】菌株SC-1能在基础盐培养基中以苯酚为唯一碳源和能源生长,在初始pH 7.0、30 °C条件下,24 h可完全降解100 mg/L苯酚;Cu2+、Ba2+、Mn2+等对其降解苯酚有不同程度的抑制作用;HPLC谱图分析,初步确定邻苯二酚是菌株SC-1降解苯酚的中间产物,且该菌株可在48 h内完全降解100 mg/L邻苯二酚。【结论】菌株SC-1对苯酚及邻苯二酚均有较强的降解能力,为完善3-PBA的降解途径及污染3-PBA或含酚废水或含酚农药残留的降解提供了数据参考。     

Degradation of polyvinyl alcohol by <Emphasis Type="Italic">Sphingomonas</Emphasis> sp. SA3 and its symbiote

A total of 800 samples was taken from Taegu province, Korea, where many textile factories provide a source of polyvinyl alcohol (PVA) waste. These samples were screened for PVA-degrading bacteria. A new strain, SA3, was discovered which formed yellow colonies and used PVA as the sole carbon and energy source. Strain SA3 was identified as a Sphingomonas sp., based on the partial nucleotide sequence analysis of 16S ribosomal RNA, the presence of 2-hydroxymyristic acid (14:O 2-OH) and sphingolipids with d-17:0, d-18:0, d-19:1, and d-20:1 as the main dihydrosphingosines. This genus has not previously been reported as a PVA-degrading bacterium. Sphingomonas sp. SA3 needs a symbiote strain, SA2, for PVA degradation as a growth factor producer. In mixed cultures of these strains, the optimum temperature for PVA biodegradation ranged from 30 °C to 35 °C. The optimum pH was 8.0 and the most effective nitrogen source was NH₄ ⁺. Electronic Publication     

Sphingomonas sp. strain KA1, carrying a carbazole dioxygenase gene homologue,degrades chlorinated dibenzo-p-dioxins in soil

Hybridization analysis showed that a newly isolated carbazole (CAR)-degrading bacterium Sphingomonas sp. strain KA1 did not possess the gene encoding the terminal oxygenase component (carAa) of CAR 1,9a-dioxygenase at high homology (more than 90% identity) to that of another CAR-degrader, Pseudomonas resinovorans strain CA10. However, PCR experiments using the primers for amplifying the internal fragment of the carAa gene (810 bp for strain CA10) showed that a PCR product of unexpected size (1100 bp) was amplified. Sequence analysis revealed that this DNA region contained the portion of two possible ORFs, which showed moderate homology to CarAa and CarBa from strain CA10 (61% and 40% identities at the amino acid level, respectively). Inoculation of strain KA1 into dioxin-contaminated model soil resulted in 96% and 70% degradation of 2-mono- and 2,3-dichlorinated dibenzo-p-dioxin, respectively, after 7-day incubation.     

呋喃丹降解菌CDS-1的双标记菌株的构建

用Sau3AI消化呋喃丹降解菌Sphingomonassp.CDS-1的基因组DNA,将所得DNA片段与BamHⅠ酶切的启动子探针载体pRobe-GFP酶连后转化E.coliDH5α感受态细胞,在选择性平板上培养,从大约1×104个菌落中筛选到50个含启动子片段的阳性克隆。挑选其中一个发光强度最强的阳性克隆F7,将它的重组质粒pF7用EcoRⅠ和HindⅢ双酶切后得到包含Sphingomonassp.CDS-1启动子和gfp基因的DNA片段,将该片段克隆到广宿主载体pPZP201上,得到pPZP201-gfp质粒。将pPZP201-gfp通过三亲接合转移至Sphingomonassp.CDS-1中得到GFP标记菌株CDS-gfp,经荧光显微镜观察,gfp基因在CDS-gfp中表达量很高。对标记菌株进行连续传代10次(48h/次),发现pPZP201-gfp依然存在,而且发光明显。通过NotⅠ酶切位点把linA基因连接到pUT/mini-Tn5上构建新的转座子载体pUT/mini-Tn5-linA。以pRK600为辅助质粒将pUT/mini-Tn5-linA引入到CDS-1中,linA基因通过转座作用,插入到CDS-gfp的染色体中,得到双标记菌株CDS-GFP-LinA。该菌株是一株能同时降解γ-六六六和呋喃丹的基因工程菌,本研究的结果为研究Sphingomonassp.CDS-1的生态学行为奠定了基础。     

Isolation and characterization of genes encoding polycyclic aromatic hydrocarbon dioxygenase from acenaphthene and acenaphthylene degrading Sphingomonas sp. strain A4

Sphingomonas sp. strain A4 is capable of utilizing acenaphthene and acenaphthylene as sole carbon and energy sources, but it is unable to grow on other polycyclic aromatic hydrocarbons (PAHs). The genes encoding terminal oxygenase components of ring-hydroxylating dioxygenase (arhA1 and arhA2) were isolated from this strain by means of the ability to oxidize indole to indigo of the Escherichia coli clone containing electron transport proteins from phenanthrene-degrading Sphingobium sp. strain P2. The translated products of arhA1 and arhA2 exhibited moderate sequence identity (less than 56%) to large and small subunits of dioxygenase of other ring-hydroxylating dioxygenases. Biotransformation with recombinant E. coli clone revealed the broad substrate specificity of this oxygenase toward several PAHs including acenaphthene, acenaphthylene, naphthalene, phenanthrene, anthracene and fluoranthene. Southern hybridization analysis revealed the presence of a putative arhA1 homologue on a locus different from that of the arhA1 gene. Insertion inactivation of the arhA1 gene in strain A4 suggested that the gene but not the putative homologue one was involved in the degradation of acenaphthene and acenaphthylene in this strain.     

Biodegradation of phenanthrene by Pseudomonas sp. BZ-3, isolated from crude oil contaminated soil

A phenanthrene (PHE) degrading bacterium strain BZ-3 was isolated from the crude oil contaminated soil in Binzhou, China. The isolate was identified as Pseudomonas sp. BZ-3 on the basis of 16S rRNA gene sequence. Various experiments were conducted to investigate the effect of pH, salinity and PHE concentration on the degradation efficiency of PHE. The degradation efficiency and degradation metabolites of PHE were detected by using GC–MS and HPLC-MS analyses. The strain BZ-3 could degrade 75% of PHE at an initial concentration of 50 mg/L under 20 g/L salinity in 7 days. PHE degradation kinetics was estimated in a first-order degradation rate model and the rate coefficient was calculated as 0.108 d⁻¹. On the basis of the identified degradation metabolites, the strain BZ-3 could degrade PHE in the salicylate metabolic pathway. In a mixture system consisting of PHE and other PAHs including naphthalene (NA), anthracene (ANTH), and pyrene (PYR), the strain BZ-3 showed an efficiently degradation capability. Further study showed that the strain BZ-3 could also use NA, ANTH, PYR, xylene, 1-hydroxy-2-naphthoic acid, and hexane as the sole carbon and energy source, but did not grow on nitrobenzene-containing medium.     

鞘氨醇单胞菌TP-3合成新型生物聚合物Ss的发酵条件优化

鞘氨醇单胞菌(Sphingomonas sp.)TP-3能合成一种具有增稠性、假塑性、成凝胶特性和乳化性能的新型生物聚合物Ss。运用单因素实验和均匀设计法对菌株TP-3合成聚合物Ss的发酵条件进行优化, 实验结果表明, 培养基组成为葡萄糖41.2 g/L, 豆饼粉2.0 g/L, NaCl 0.85 g/L, K2HPO4 1.46 g/L, MgSO4 0.12 g/L, MnCl2 0.0075 g/L, FeSO4 0.002 g/L, 初始pH为7.0, 在27°C, 180 r/min的条件下摇床培养60 h, 聚合物Ss的产量达到21.5 g/L。该聚合物生产成本低, 在油田开发中极具应用前景。     

Degradation of azo dyes containing aminonaphthol by Sphingomonas sp strain 1CX

Sphingomonas sp strain 1CX was isolated from a wastewater treatment plant and is capable of aerobically degrading a suite of azo dyes, using them as a sole source of carbon and nitrogen. All azo dyes known to be decolorized by strain 1CX (Orange II, Acid Orange 8, Acid Orange 10, Acid Red 4, and Acid Red 88) have in their structure either 1-amino-2-naphthol or 2-amino-1-naphthol. In addition, an analysis of the structures of the dyes degraded suggests that there are certain positions and types of substituents on the azo dye which determine if degradation will occur. Growth and dye decolorization occurs only aerobically and does not occur under fermentative or denitrification conditions. The mechanism by which 1CX decolorizes azo dyes appears to be through reductive cleavage of the azo bond. In the case of Orange II, the initial degradation products were sulfanilic acid and 1-amino-2-naphthol. Sulfanilic acid, however, was not used by 1CX as a growth substrate. The addition of glucose or inorganic nitrogen inhibited growth and decoloration of azo dyes by 1CX. Attempts to grow the organism on chemically defined media containing several different amino acids and sugars as sources of nitrogen and carbon were not successful. Phylogenetic analysis of Sphingomonas sp strain 1CX shows it to be related to, but distinct from, other azo dye-decolorizing Sphingomonas spp strains isolated previously from the same wastewater treatment facility. Received 19 May 1999/ Accepted in revised form 11 August 1999     

合成生物聚合物的重要微生物资源-鞘氨醇单胞菌

摘要：鞘氨醇单胞菌属的许多菌株能够合成结冷胶、沃仑胶、迪特胶等多种结构相似,物理性能多样的生物聚合物,统称为鞘氨醇胶。目前,结冷胶已经大规模的生产和应用,由于鞘氨醇单胞菌属的提出仅有十几年的历史,其他种类鞘氨醇胶的研究和开发才刚刚起步。本文综述了鞘氨醇单胞菌属分类研究的最新进展,以及鞘氨醇胶的结构、特性、生物合成途径、分子遗传学和基因工程的研究现状,并对今后的研究重点和方向进行了展望。     

Isolation of hexachlorocyclohexane-degrading Sphingomonas sp. by dehalogenase assay and characterization of genes involved in gamma-HCH degradation

Aim: To screen and identify bacteria from contaminated soil samples which can degrade hexachlorocyclohexane (HCH)‐isomers based on dechlorinase enzyme activity and characterize genes and metabolites. Methods and Results: Dechlorinase activity assays were used to screen bacteria from contaminated soil samples for HCH‐degrading activity. A bacterium able to grow on α‐, β‐, γ‐ and δ‐HCH as the sole carbon and energy source was identified. This bacterium was a novel species belonging to the Sphingomonas and harbour linABCDE genes similar to those found in other HCH degraders. γ‐Pentachlorocyclohexene 1,2,4‐trichlorobenzene and chlorohydroquinone were identified as metabolites. Conclusions: The study demonstrates that HCH‐degrading bacteria can be identified from large environmental sample‐based dehalogenase enzyme assay. This kind of screening is more advantageous compared to selective enrichment as it is specific and rapid and can be performed in a high‐throughput manner to screen bacteria for chlorinated compounds. Significance and Impact of the Study: The chlorinated pesticide HCH is a persistent and toxic environmental pollutant which needs to be remediated. Isolation of diverse bacterial species capable of degrading all the isomers of HCH will help in large‐scale bioremediation in various parts of the world.     

The role of the Sphingomonas species UG30 pentachlorophenol-4-monooxygenase in p-nitrophenol degradation

Pentachlorophenol-4-monooxygenase is an aromatic flavoprotein monooxygenase which hydroxylates pentachlorophenol and a wide range of polyhalogenated phenols at their para position. The PCP-degrading Sphingomonas species UG30 was recently shown to mineralize p-nitrophenol. In this study, the UG30 pcpB gene encoding the pentachlorophenol-4-monooxygenase gene was cloned for use to study its potential role in p-nitrophenol degradation. The UG30 pcpB gene consists of 1614 bp with a predicted translational product of 538 amino acids and a molecular mass of 59,933 Da. The primary sequence of pentachlorophenol-4-monooxygenase contained a highly conserved FAD binding site at its N-terminus associated with a beta alpha beta fold. UG30 has been shown previously to convert p-nitrophenol to 4-nitrocatechol. We observed that pentachlorophenol-4-monooxygenase catalyzed the hydroxylation of 4-nitrocatechol to 1,2,4-benzenetriol. About 31.2% of the nitro substituent of 4-nitrocatechol (initial concentration of 200 microM) was cleaved to yield nitrite over 2 h, indicating that the enzyme may be involved in the second step of p-nitrophenol degradation. The enzyme also hydroxylated p-nitrophenol at the para position, but only to a very slight extent. Our results confirm that pentachlorophenol-4-monooxygenase is not the primary enzyme in the initial step of p-nitrophenol metabolism by UG30.     

Isolation and identification of a carbazole degradation gene cluster from Sphingomonas sp.JS1

The carbazole degrading bacterium JS1 was isolated from carbazole polluted soil and identified as Sphingomonas sp. bacterium based on its 16S rDNA gene. The car gene cluster located in the genome of JS1 was isolated by PCR and its presence verified by Southern hybridization. Sequence analysis of the car gene cluster showed that the arrangement of elements in JS1 was different from that of Pseudomons sp. CA10 and Nocardioides aromaticivorans IC177, but car gene cluster and neighboring regions were nearly identical to that of Sphingomonas sp. KA1 and Sphingomonas sp.GTIN11. Each element of the car gene cluster was expressed in E. coli upon IPTG induction. The amount of CaBb protein expressed was higher than CarBa and the ratio of these two proteins was 1:1.5. CarC expression level was detected using anti-CarC antibody. The result showed that carbazole degrading proteins were induced by the substrate carbazole. The quantity of CarC at 0.5 mg/ml carbazole was five times more than that at 0.1 mg/ml. Meiying Yang and Wenming Li have the equal contribution for this work.