一株氯嘧磺隆降解菌分离鉴定及降解条件优化

为解决氯嘧磺隆残留对土壤、水体污染及后茬敏感作物药害问题,为污染土壤微生物修复提供降解菌种资源,文中采用富集培养、逐级驯化等方法,从氯嘧磺隆污染土壤中分离到1株高效氯嘧磺隆降解菌T9DB-01,经形态特征、生理生化及16S rDNA序列分析,鉴定为假单胞菌Pseudomonas sp.。采用单因素实验探究温度、pH值、底物浓度、装液量和接种量对菌株T9DB-01降解氯嘧磺隆的影响,采用正交试验及验证,优化菌株T9DB-01对氯嘧磺隆降解条件。结果表明,在30℃,pH 8.0,底物浓度200 mg/L,装液量100 mL/250 mL,接种量4%的条件下,5 d后降解率达到93.7%。该降解菌株对氯嘧磺隆污染土壤原位生物修复具有一定的应用潜力。     

高效氯氰菊酯降解菌CH7的分离鉴定及降解条件的优化

从农药厂活性污泥中,分离到一株能以高效氯氰菊酯为唯一碳源生长的细菌CH7。经生理生化试验和16S rD-NA分析,将菌株CH7鉴定为铜绿假单胞菌(Pseudomonas aeruginosa)。采用Box-behnken设计试验、响应面法(response surfacemethodology)优化菌株CH7的降解条件。在最优条件下(29.4°C,pH7.0,接种量0.15g/L),菌株CH7在12d内对100mg/L高效氯氰菊酯的降解率为90%。     

单甲脒降解菌的分离筛选

从土壤、水体和受单甲脒长期污染的样品中通过富集培养,从中分离筛选到一株单甲脒耐性较高的ＤＲ－８菌株。该菌株在牛肉汁培养基中对单甲脒的耐性可达１２５０ｍｇ／Ｌ,而在无机盐培养基中的耐性则为５００ｍｇ／Ｌ。该菌株可以利用单甲脒作为唯一氮源,但是不能以单甲脒作为碳源和能源而生长。降解单甲脒的最适温度为３７℃,最适ｐＨ为７．０,其完整细胞悬液对５５０ｍｇ／Ｌ左右单甲脒的降解率最高可达６４．８２％。经鉴定该菌株为门多萨假单胞菌（ＰｓｅｕｄｏｍｏｎａｓｍｅｎｄｏｃｉｎａＤＲ－８）。     

一株地塞米松磷酸钠降解菌的分离鉴定

目的为用微生物修复技术清除水环境中的地塞米松污染提供菌种。方法采集被地塞米松磷酸钠污染的医院废水,通过无机盐培养基和含地塞米松磷酸钠的缺碳培养基富集和分离地塞米松降解菌。将分离菌初步驯化后,用常规高效液相色谱法测定其对地塞米松和地塞米松磷酸钠的降解率。分离菌经形态、染色性、生化试验和16S r DNA鉴定。结果获得1株能以地塞米松磷酸钠为唯一碳源和能源的菌株,经生物学特性和16S r DNA分析鉴定为产碱假单胞菌(Pseudomonas alcaligenes)。分离菌对地塞米松磷酸钠的降解率为50.86%。其中,75.23%地塞米松磷酸钠被降解为地塞米松,23.63%被进一步降解率为其他他物质。结论成功地分离到1株地塞米松降解菌,为进一步研究用微生物修复技术清除水环境中的地塞米松污染提供了实验材料。     

氯氰菊酯降解菌GF31的分离鉴定及其降解特性

从受污染的土壤中分离得到1株以氯氰菊酯为唯一碳源生长的降解菌GF31, 通过形态观察、16S rDNA基因序列分析、生理生化实验, 鉴定该菌为铜绿假单胞菌(Pseudomonas aeruginosa)。菌株GF31降解氯氰菊酯的最佳pH值为7.0, 接种量为10%, 对浓度高达300 mg/L的菊酯仍可保持较高的降解活性。外加氮源对菌株的降解效能影响显著, 有机氮比无机氮更有利于农药降解。当以0.5 g/L蛋白胨作为氮源时, 降解速率明显提高, 对100 mg/L氯氰菊酯降解的平均速率为13.64 mg/(L·d), 是以硫酸铵为氮源时的2倍。初步分析认为降解产物及碱性pH环境对菌株的生长及活性具有一定的抑制作用。     

聚乙烯醇降解酶产生菌的分离和发酵条件

从工厂废水中分离到一株高效降解聚乙烯醇(PVA)的细菌D8株,四天能将培养基中0.5％的PVA(500,1700)完全降解,经鉴定为假单胞菌属类产碱假单胞菌(Pseudoraonospseudoalcaligenes)。对菌株的发酵条件进行了研究,结果表明,最适培养基成份为(％)：PVA1．5,(NH4),SO4 0．1,K2HPO4 0．24,KH2PO4 0．04, MgSO4·7H2O 0.035,NaCl 0.01,FeSO4 0.001,酵母膏0.15;起始pH 7.5;通气量在250ml三角瓶装30ml培养基为最逢,于30℃,160r／rain的旋转摇床振荡培养72h产酶活力最高。     

一株苯酚降解菌的鉴定及其降解特性

【目的】鉴定从某化工厂附近土样中分离到的一株耐高浓度苯酚的菌株T10,通过优化菌株的培养条件提高菌株对苯酚的降解率。【方法】根据菌株的形态、生理生化鉴定及16S rDNA测序分析确定其种属,以液体摇瓶培养菌株T10对苯酚的降解率为指标,对菌株的生长条件进行优化。【结果】菌株T10属恶臭假单胞菌(Pseudomonas putida)。添加葡萄糖、蛋白胨能有效缩短T10菌的生长周期,并使苯酚的降解率提高1.7倍。在菌体初始接种浓度为10%、温度为30°C、转速为180 r/min条件下,对初始苯酚浓度、pH和装液量的响应面优化结果如下:初始苯酚浓度3 000 mg/L、pH 7.5和装液量80 mL/250 mL,苯酚去除率最高可达到87.56%。【结论】T10菌能够耐受较高浓度的含酚废水,并且对苯酚有较强的降解能力,为下一步利用生物法处理含酚废水提供科学依据。     

一株可高效降解羽毛的铜绿假单胞菌的分离、鉴定、产酶条件优化及其酶活研究

【目的】筛选海洋环境产角蛋白酶菌株,研究其发酵条件及酶学性质,为后续开发和利用海洋微生物降解废弃羽毛提供菌种资源和理论依据。【方法】采集广西北部湾某海鸭养殖场淤泥,用酪蛋白平板初筛和角蛋白酶活复筛获得羽毛降解效果好的菌株,并进行形态学和分子生物学鉴定;利用单因素和正交试验对菌株产酶条件进行优化,最后对酶学性质及羽毛降解产物的游离氨基酸组成进行研究。【结果】筛选到1株可高效降解羽毛的菌株,经鉴定为铜绿假单胞菌(Pseudomonas aeruginosa Gxun-7)。最佳产酶条件为：羽毛25 g/L,Zn2+0.10 g/L、初始pH 8.0、发酵温度32.5°C、发酵时间48 h,酶活力达124.03 U/mL,较优化前提高了2.3倍;酶学性质分析表明,该角蛋白酶最适作用温度和pH分别为70°C和8.0,化学试剂巯基乙醇可使酶活提高6.16倍,而苯甲基磺酰氟(PMSF)使相对酶活降至15.00%,该酶耐盐性较好(20%NaCl中相对酶活为74.29%);羽毛降解产物中检测到16种氨基酸,7种为必需氨基酸,总的游离氨基酸含量高达2 329.80 mg/L,其中缬氨酸含量最高为575....     

一株苯酚高效降解菌的分离及其分解能力的初步研究

为了寻找能高效降解苯酚的微生物 ,从武汉市某化工厂周围的下水道污泥中 ,筛选分离出一种具有很高苯酚降解能力的菌株PheD1。通过生理生化及外观鉴定[1～ 3] ,将其初步鉴定为假单胞菌 (Pseudomonassp .)。经驯化后发现 ,该菌生长的迟缓期随苯酚浓度的增大而延长 ,但比同类报道的苯酚降解菌要短 ;在 35℃对数生长期时的苯酚降解率超过同类报道[6 ] ,6 0 0mg·L- 1 苯酚浓度的完全降解时间在 2 4h之内 ,比同类报道[4～ 6 ] 苯酚降解菌的分解能力要高。该菌为好氧菌 ,在空气充足的条件下可提高降解能力。对该菌的继续研究可使其在苯酚的生物降解及污水处理等实际运用中起到重要的作用。     

一株林可霉素降解菌的筛选鉴定及其降解机制

【背景】抗生素污染越来越引起人们的关注。利用微生物处理抗生素污染被认为是一种环境友好型的方法。【目的】筛选林可霉素高效降解菌并研究其降解机制。【方法】经形态学观察、生理生化鉴定和16S rRNA基因测序分析进行鉴定;通过PCR技术和质谱分析技术对该菌抗性基因和降解产物等进行分析。【结果】从林可霉素菌渣堆肥样本中获得一株高效降解林可霉素的假单胞菌(Pseudomonas RST-1),该菌在林可霉素浓度为3.0 g/L的牛肉膏蛋白胨培养基上培养40 h后,林可霉素降解率高达57.3%。该菌含有intI1、sul1、sul2等抗性基因,降解产物为去甲基林可霉素和2-丙基-N-甲基脯氨酸。【结论】菌株RST-1具有高效降解林可霉素的能力,推测可能的降解机制为去甲基化和酰胺键水解作用,该菌株降解特性及降解机制研究为林可霉素降解工程菌及其高效降解菌剂的研制奠定了基础。     

产脂肪酶菌株筛选及柠檬酸杆菌产酶条件优化

脂肪酶可以催化甘油三酯水解成脂肪酸和甘油,已广泛应用在工业领域,而获得产酶微生物是研究的基础。采用油脂平板法筛选出1株脂肪酶产生菌。经16S rRNA序列分析可知,该菌株属于柠檬酸杆菌(Citrobacter werkman and Gillen)。单因素试验对其进行产酶条件优化,优化后产酶条件（g/L）：淀粉2.0,KH₂PO₄ 1.0,K₂HPO₄·3H₂O 2.2,(NH₄)₂SO₄ 1.0,MgSO₄·7H₂O 0.1,牛肉膏2.0,橄榄油10.0 mL,pH 7.5,接种量1.5%(v/v),37 ℃培养43 h。获得最大酶活为384 U/mL,是优化前的13倍。可以利用该菌制备脂肪酶。     

Mapping of some genes involved in C-1 metabolism in the facultative methylotroph Methylobacterium sp strain AM1 (Pseudomonas AM1)

R68.45 mediated mobilisation of the chromosome of Methylobacterium sp strain AM1 has been investigated. High frequencies of cotransfer of four genes required for C-1 metabolism with the genes coding for streptomycin, phosphonomycin and cycloserine resistance were demonstrated. A preliminary map of this region has been constructed on the basis of the results of three and four factor crosses showing that not all the C-1 genes are contiguous.Abbreviations Str streptomycin - Pho phosphonomycin - Cyc cycloserine - Tc tetracycline - Km kanamycin - Cb carbenicillin - Ade adenine - Thi thiamine - Met methionine     

Short communication: Methylparathion degradation by Pseudomonas sp. A3 immobilized in sodium alginate beads

An organophosphate-degrading soil isolate of Pseudomonas sp. A3, immobilized at 5% (wet wt/v) cell mass in 3% (w/v) sodium alginate beads, detoxified 99% of 1 mm methylparathion in 48 h. The beads were re-usable for five batches, the sixth batch only giving 73% methylparathion removal.     

Maleylacetate reductase of Pseudomonas sp. strain B13: dechlorination of chloromaleylacetates,metabolites in the degradation of chloroaromatic compounds

The maleylacetate reductase of 3-chlorobenzoate-grown cells of Pseudomonas sp. strain B13 has been purified 50-fold. The enzyme converted 2-chloromaleylacetate to 3-oxoadipate with temporary occurrence of maleylacetate; 1 mol of chloride was eliminated during the conversion of 1 mol of 2-chloro- and 2,3-dichloromaleylacetate; 2 mol of NADH were consumed per mol of 2-chloro- and 2,3-dichloromaleylacetate while only 1 mol was necessary to catalyze the conversion of maleylacetate or 2-methylmaleylacetate. The maleylacetate reductase failed to use fumarylacetate as a substrate. The role of the enzyme in the chloroaromatics degradation is discussed.     

Degradation of chlorosubstituted aromatic compounds by Pseudomonas sp. strain B13: fate of 3,5-dichlorocatechol

The degradation of 3,5-dichlorocatechol by enzymes of 3-chlorobenzoate-grown cells of Pseudomonas sp. strain B13 was studied. The following compounds were formed from 3,5-dichlorocatechol: trans-2-chloro-4-carboxymethylenebut-2-en-4-olide, cis-2-chloro-4-carboxymethylenebut-2-en-4-olide, and chloroacetylacrylate as the decarboxylation product of 2-chloromaleylacetate. They were identified by chromatographic and spectroscopic methods (UV, MS, PMR). An enzyme activity converting trans-2-chloro-4-carboxymethylenebut-2-en-4-olide into the cis-isomer was observed.Abbreviations 3CB 3-chlorobenzoate - 4CB 4-chlorobenzoate - 3,5DCB 3,5-dichlorobenzoate - 2,4D 2,4-dichlorophenoxyacetate - NOE Nuclear-Overhauser-Effect     

17α-ethinylestradiol cometabolism by bacteria degrading estrone, 17β-estradiol and estriol

17alpha-ethinylestradiol (EE2), the active compound of the contraceptive pill, is a recalcitrant estrogen, which is encountered at ng/l levels in wastewater treatment plant (WWTP) effluents and rivers and can cause feminization of aquatic organisms. The aim of this study was to isolate micro-organisms that could remove such low EE2 concentrations. In this study, six bacterial strains were isolated from compost that cometabolize EE2 when metabolizing estrone (E1), 17beta-estradiol (E2) and estriol (E3). The strains belong to the alpha, beta and gamma-Proteobacteria. All six strains metabolize E2 over E1, at mug/l to ng/l concentrations. In 4 days, initial concentrations of 0.5 mug E2/l and 0.6 mug EE2/l were degraded to 1.8 +/- 0.4 ng E2/l and 85 +/- 16 ng EE2/l, respectively. No other metabolites besides E1, E2, E3 or EE2 were detected, suggesting that total degradation and cleavage of the aromatic ring occurred. This is the first study describing that bacteria able to metabolize E2, can subsequently cometabolize EE2 at low mug/l levels.     

Dehalogenation of 4-chlorobenzoate

Pseudomonas sp. CBS3 is capable of growing with 4-chlorobenzoate as sole source of carbon and energy. The removal of the chlorine of 4-chlorobenzoate is performed in the first degradation step by an enzyme system consisting of three proteins. A 4-halobenzoate-coenzyme A ligase activates 4-chlorobenzoate in a coenzyme A, ATP and Mg²⁺ dependent reaction to 4-chlorobenzoyl-coenzyme A. This thioester intermediate is dehalogenated by the 4-chlorobenzoyl-coenzyme A dehalogenase. Finally coenzyme A is split off by a 4-hydroxybenzoyl-CoA thioesterase to form 4-hydroxybenzoate. The involved 4-chlorobenzoyl-coenzyme A dehalogenase was purified to apparent homogeneity by a five-step purification procedure. The native enzyme had an apparent molecular mass of 120,000 and was composed of four identical polypeptide subunits of 31 kDa. The enzyme displayed an isoelectric point of 6.7. The maximal initial rate of catalysis was achieved at pH 10 at 60 °C. The apparent K_m value for 4-chlorobenzoyl-coenzyme A was 2.4–2.7 µM. V_max was 1.1 × 10^–7 M sec^–1 (2.2 µmol min^–1 mg^–1 of protein). The NH₂-terminal amino acid sequence was determined. All 4-halobenzoyl-coenzyme A thioesters, except 4-fluorobenzoyl-coenzyme A, were dehalogenated by the 4-chlorobenzoyl-CoA dehalogenase.Abbreviations CBA chlorobenzoate - CoA coenzyme A - HBA hydroxybenzoate - DTT dithiothreitol - HPLC high performance liquid chromatography - PAGE polyacrylamide gel electrophoresis     

Conversion of substituted naphthalenesulfonates by Pseudomonas sp. BN6

The range of substituted naphthalenesulfonates which are metabolized by Pseudomonas sp. BN6 were investigated. Resting cells from strain BN6 oxidized 1- and 2-naphthalenesulfonate, 1-hydroxynaphthalene-2-sulfonate, 2,6-naphthalenedisulfonate and all monosulfonated naphthalene-2-sulfonates which carry one or two substitutents in the positions 4-, 5-, 6-, 7- or 8- of the naphthalene ring-system. With the exception of (substituted) 4- or 5-amino- and 4-hydroxynaphthalene-2-sulfonates these compounds were converted to the corresponding salicylates. Strain BN6 did not oxidize substituted naphthalene-1-sulfonates, 3-substituted naphthalenesulfonates and substituted naphthalenedisulfonates. Turnover of 4-amino- or 4-hydroxynaphthalene-2-sulfonates resulted in the accumulation of the corresponding naphthoquinones in the culture medium. Thus, degradation of 4-amino- and 4-hydroxynaphthalenesulfonates was restricted by the rapid autoxidation of the substituted 1,2-dihydroxynaphthalenes formed as metabolites. Catabolic activities of strain BN6 for naphthalenesulfonates were induced by salicylate, 3- or 6-hydroxysalicylate, and 3-, 4- or 5-aminosalicylate but not by 4- and 5-hydroxysalicylate. All naphthalenesulfonates that were not converted into the corresponding salicylates, were found to be inefficient as effectors. It was therefore concluded that (substituted) salicylates are the inducers of the relevant enzymes. The degradation of 2-naphthalene-sulfonate by a pure culture of strain BN6 was prevented by the toxicity of the dead-end product salicylate. Substituted salicylates were less toxic and allowed growth of strain BN6 in axenic culture with various substituted naphthalenesulfonates.Abbreviations AB aminobenzoate - ANS aminonaphthalenesulfonate - DHN dihydroxynaphthalene - DHNC dihydroxynaphthalene-carboxylate - DHNDO 1,2-dihydroxynaphthalene dioxygenase - HBPA 2-hydroxybenzalpyruvate aldolase - HNS hydroxynaphthalenesulfonate - HS hydroxysalicylate - Ind-C indolecarboxylate - Ind-S indolesulfonate - MANS N-methylaminonaphthalenesulfonate - NC naphthalenecarboxylate - NDS naphthalenedisulfonate - NQ naphthoquinone - NS naphthalenesulfonate - NSDO naphthalenesulfonate dioxygenase - R_t retention time - SADH salicylaldehyde dehydrogenase - THN trihydroxynaphthalene (hydroxy-1,2-dihydroxynaphthalene)     

褐藻胶降解菌株S10鉴定及产酶条件优化

探讨了褐藻胶降解菌株S10的生长条件及其对产褐藻胶降解酶活力的影响。以分离自海参肠道的褐藻胶降解菌株S10为研究对象,采用形态学观察结合16S rDNA序列分析,对菌株S10进行菌种鉴定并对其生理生化特性进行测定。以降解酶活力为指标,利用单因素、Plackett-Burman(PB)和响应面法对培养基成分和培养条件进行优化;最后对优化前后的菌株生长量、产酶活力和粗酶液稳定性进行分析。结果表明,菌株S10属于溶藻孤菌(Vibrio algindyticus);当pH 7、接种量2%(体积分数)、装液量150 mL、温度26℃、转速150 r/min、NaCl 3%(质量分数,下同)、海藻酸钠含量1.12%、硫酸铵含量0.44%、培养时间35.95 h条件下,褐藻胶降解酶活力最大(188.18 U/min)。优化后产酶活力提高30%;4℃低温更有利于该酶保存。综上,优化后的菌株S10产褐藻胶降解酶活力较高,能更好地用于降解褐藻胶,可为提高褐藻胶的利用率和进一步发掘褐藻胶寡糖的利用价值提供参考。     

Physiological properties and substrate specificity of a pentachlorophenol-degradingPseudomonas species

A bacterial strain capable of utilizing pentachlorophenol (PCP) as sole source of carbon and energy for growth was isolated from enrichment cultures containing 100 mg/l PCP in a mineral salts medium inoculated with contaminated soil from a lumber treatment waste site. The isolate, designated strain SR3, was identified as a species ofPseudomonas by virtue of its physiological and biochemical characteristics. Mineralization of PCP byPseudomonas sp. strain SR3 was demonstrated by loss of detectable PCP from growth medium, stoichiometry of chloride release (5 equivalents of chloride per mole of PCP), and formation of biomass consistent with the concentration of PCP mineralized. PCP-induced cells of strain SR3 showed elevated rates of oxygen consumption in the presence of PCP, and with different chlorinated phenols, with complete degradation of 2,3,5,6-, 2,3,6-, 2,4,6-, 2,4-, and 2,6-chloro-substituted phenols. Concentrations of PCP up to 175 mg/liter supported growth of this organism, but maximal rates of PCP removal were observed at a PCP concentration of 100 mg/liter. Based on its degradative properties,Pseudomonas sp. strain SR3 appears to have utility in bioremediation of soil and water contaminated with PCP.Abbreviations DCP dichlorophenol - TCP trichlorophenol - TeCP tetrachlorophenolContribution No. 750 from the United States Environmental Protection Agency Environmental Research Laboratory, Gulf Breeze, FL32561, USA. A preliminary report of this work has appeared in abstract form (Resnick & Chapman 1990; Abstr. Annu Meet Amer Soc Microbiol Q-70, p. 300).