阿特拉津降解菌株的分离和鉴定

从农药厂废水中分离到6株能以除草剂阿特拉津为唯一氮源生长的细菌,即假单胞菌（Pseudomonas spp,.)AD1,AD2和AD6,土壤杆菌（Agrobacterium sp.)AD4,黄单胞菌（Xanthomonas sp.)AD5,欧氏菌（Erwinia sp.)AD7,AD1菌株能使无机盐培养基中的0．3g/L阿特拉津在72h内降解99．9％,当以AD1,AD2,AD4,AD5,AD6和AD7菌株的总DNA为模板进行PCR扩增时,除AD2菌株以外,均得到了与献报道的假单胞菌ADP菌株的阿特拉津氯水解酶基因（atzA)同源的PCR产物。     

一株联苯降解菌的筛选及其降解条件研究

通过选择性富集培养,从济南市南部山区所取的土样中分离得到1株联苯降解菌,实验证明该菌株能以联苯作为惟一的碳源和能源生长,初步命名为LB07,经形态学、生理生化鉴定和16SrRNA基因序列对比分析,确定该菌属于巨大芽胞杆菌。分别研究pH、温度、底物浓度、装液量和培养时间各个单因素对联苯降解率的影响。然后设计正交实验确定菌株降解联苯的最佳优化条件,最佳培养条件为联苯初始质量浓度150mg／L,温度35℃,pH=6．5,装液量为250mL三角瓶装50mL,培养时间10d,菌株LB07降解联苯的性能最好,降解率达到94％。     

氯酚类化合物的微生物降解研究进展

综述了近年在具有降解氯酚类化合物能力的微生物的筛选、氯酚类化合物的好氧和厌氧降解机制以及现代生物技术的开发利用研究．阐述了氯酚类化合物在不同条件下的降解路径．在好氧条件下,单氯酚和二氯酚在氧化酶的攻击下形成氯代邻二酚,邻二酚开环生成相应的氯代粘康酸或半醛,粘康酸内酯化过程中释放氯离子;高度氯代的化合物则是在氢氧化酶作用下生成氯代醌,并逐步脱去所有的氯原子生成苯酚后才开环．在厌氧或缺氧条件下,氯酚进行还原脱氯,在得到电子的同时去掉一个氯取代基．     

阿特拉津降解菌株的分离和鉴定*

从农药厂废水中分离到６株能以除草剂阿特拉津为唯一氮源生长的细菌,即假单胞菌（Ｐｓｅｕ－ｄｏｍｏｎａｓ ｓｐｐ．）ＡＤ１、ＡＤ２和 ＡＤ６,土壤杆菌（Ａｇｒｏｂａｃｔｅｒｉｕｍ　ｓｐ．）ＡＤ４,黄单胞菌（Ｘａｎｔｈｏｍｏｎａｓ ｓｐ．）ＡＤＳ,欧文氏菌（Ｅｒｗｉｎｉａ ｓｐ．）ＡＤ７。ＡＤ１菌株能使无机盐培养基中的 ０．３ｇ／Ｌ阿特拉津在７２ｈ内降解９９,９％。当以ＡＤ１、ＡＤ２、ＡＤ４、ＡＤ５、ＡＤ６和ＡＤ７菌株的总ＤＮＡ为模板进行ＰＣＲ扩增时,除Ａ     

一株高效广谱莠去津降解菌SB5的生长和降解特性

本研究采用富集培养技术自莠去津污染的活性污泥中分离筛选到一株具有降解三嗪类除草剂功能的菌株SB5,经形态学和16S rRNA基因分析将其初步鉴定为类节杆菌属细菌.其具有已知莠去津降解相关基因trzN、atzB及atzC.在培养基中添加葡萄糖、蔗糖、柠檬酸钠、酵母浸粉和蛋白胨可显著提高菌株SB5的生物量和对莠去津的降解效...     

溴氨酸降解菌株的分离和特性

从化工厂污泥中中分离到4个对蒽醌染料中间体溴氨酸有显降解和脱色作用的菌株。经鉴定,4株菌均为假单胞菌属（Pseudomonas sp.）。脱色效果最好的N1菌株能以溴酸为唯一碳源生长,其脱色效果受温度和pH影响较大,最佳生长条件是30℃,pH7.2。     

高效降解棉酚菌株的选育及脱毒条件的研究

From mildewed cottonseed cake and stock cultUres of mold and yeast We select more than ten strains of yeastS and molds which can degrade cotton Phenol. At last we got four strains which can degrade cotton phenol highly effeted after mutagenized by physical and chemical factors and induced by cotton Phenol. They belong to Candida tropicalis, Torulopsis candida, Aspergillus flavus and ASPergillus niger. By small and medium size fermenfations, the content of dissociated cottom Phenol all reach safe criterion (…     

真菌降解木质素研究进展及在好氧堆肥中的研究展望

综述了近十年来真菌降解木质素的研究进展,包括木质素的存在与结构,真菌降解木质素生物学、酶系及作用机理、生理学以及在环境工程中应用方面的研究进展,并对好氧堆肥处理城市垃圾中木质素生物降解的研究作了展望 。     

裂褶菌cfcc7252菌株对孔雀石绿染料的高效降解

【目的】评价裂褶菌cfcc7252菌株降解孔雀石绿(Malachite Green,MG)的能力及其潜在的应用价值。【方法】采用单因子液体培养实验,研究了通气、p H、温度、碳源和氮源种类及浓度、金属离子、盐度、染料浓度对该菌降解效果的影响;采用平皿培养实验,利用植物种子萌发和微生物抑菌实验对降解产物进行毒性测试。【结果】研究结果表明,裂褶菌cfcc7252菌株在好氧和厌氧条件下均能高效降解MG。该菌在10.0 g/L葡萄糖,5.0 g/L酵母浸粉,0.01 mmol/L Zn2+,p H为4.0的液体培养基中培养36 h,对350 mg/L的MG降解率达67.8%;连续降解7次后,其降解率还能保持在95.4%以上。此外,该菌在盐度低于10.20%时,其对MG的降解率均达到98%以上。对植物、微生物的毒性测试结果表明,MG降解产物对红豆、豌豆等植物、金黄色葡萄球菌、枯草芽孢杆菌和铜绿假单胞杆菌等微生物基本没有毒性。【结论】裂褶菌cfcc7252菌株在处理以MG为主的染料废水时具有很强的应用潜力。     

高效降解棉酚菌株的分离鉴定及诱变选育

作为一种蛋白资源, 棉籽粕因其含有毒素——游离棉酚限制了其在饲料工业中的应用。为获得能高效降解棉籽粕中棉酚的菌株, 以醋酸棉酚为唯一碳源培养基从16份样品中筛选出一株高效降解棉酚菌株(Y-2), 经生理生化及18S rDNA鉴定为Pichia guilliermondii, 此菌种为非致病酵母, 且首次报道用于棉酚的降解, 在工业生产中具有潜在的应用前景。通过紫外诱变获得一株棉酚降解率更高的突变株YUV-51。通过对突变株YUV-51发酵温度、时间及接种量的初步优化, 获得其固态发酵优化条件: 30 °C培养48 h, 接种量0.025 g湿菌体/g棉籽粕, 初始水分含量50%。为避免游离棉酚在前处理中大量降解棉籽粕, 不进行湿热处理, 经接种发酵后脱毒率可达到58%。这使微生物脱毒在实际生产中应用成为可能。     

TNT Biotransformation and Detoxification by a Pseudomonas Aeruginosa Strain

Successful microbial-mediated remediation requires transformationpathways that maximize metabolism and minimize the accumulation of toxic products. Pseudomonas aeruginosa strain MX, isolated from munitions-contaminated soil, degraded 100 mg TNT L^-1 in culture medium within 10 h under aerobic conditions. The major TNT products were 2-amino-4,6-dinitrotoluene (2ADNT, primarily in the supernatant) and 2,2'-azoxytoluene (2,2'AZT, primarily in the cell fraction), which accumulated as major products via the intermediate2-hydroxylamino-4,6-dinitrotoluene (2HADNT). The 2HADNT and2,2'AZT were relatively less toxic to the strain than TNT and 2ADNT. Aminodinitrotoluene (ADNT) production increased when yeast extract was added to the medium. While TNT transformation rate was not affected by pH, more HADNTs accumulated at pH 5.0 than at pH 8.0 and AZTs did not accumulate at the lower pH. The appearance of 2,6-diamino-4-nitrotoluene (2,6DANT) and 2,4-diamino-6-nitrotoluene (2,4DANT); dinitrotoluene (DNT) and nitrotoluene (NT); and 3,5-dinitroaniline (3,5DNA) indicated various routes of TNT metabolism and detoxification by P. aeruginosa strain MX.     

三硝基甲苯致白内障机理及其在晶状体内代谢的研究

在建立TNT大鼠白内障的基础上,用HPLC分析了晶状体内TNT及其代谢产物,并用ESR及NBT方法检测了TNT在晶状体内的代谢过程所产生的自由基。结果表明,慢性染毒24个月的大鼠白内障晶状体内含有TNT原形和4氨基2,6二硝基甲苯代谢产物,以及在体外与正常晶状体微粒体孵育可产生TNT硝基阴离子自由基和超氧阴离子自由基。上述结果提示,TNT可进入晶状体内,在其还原代谢过程中产生硝基阴离子自由基中间产物,在有氧条件下进而产生超氧阴离子自由基,这可能是TNT导致白内障的启动因素。     

三硝基甲苯中毒性白内障动物模型的建立及其发病机理的初步研究

反复多次给大鼠皮下注射20％三硝基甲苯(TNT)甘油:水混悬液,染毒15个月后21％动物发生白内障,其裂隙灯检查结果与人TNT性白内障基本相似,同时注射甘油:水溶剂的对照组大鼠无一例发生白内障。染毒10个月的大鼠,其晶状体LPO增高,GSH-P_X及GST活性降低,GR活性无变化,而GSH含量明显增加;注射TNT后肝脏LPO值、GSH含量、GSH-P_X、GR及GST活性均明显增高。本文结果提示,TNT中毒性白内障的形成可能系TNT及其代谢产物直接作用于晶状体,造成昌状体氧化损伤所致。TNT白内障大鼠模型的建立亦为深入探讨其发病机理及防治奠定了基础。     

A Transient Study of Formation of Conjugates during TNT Metabolism by Plant Tissues

The formation of TNT-derived conjugates was investigated in hairy root tissue cultures of Catharanthus roseus and in aquatic plant systems of Myriophyllum aquaticum. The temporal profiles of four TNT-derived conjugates, TNT-1, 2A-1, TNT-2 and 4A-1, were determined over 3 to 16-day exposure durations. When axenic C. roseus roots were exposed separately to 2,4,6 trinitrotoluene, 2-amino-4,6-dinitrotoluene and 4-amino-2,6-dinitrotoluene, the array and levels of conjugates varied. Exposure of axenic roots to either 4-amino-2,6-dinitrotoluene or 2-amino-4,6-dinitrotoluene resulted in the formation of only 4A-1 and 2A-1, respectively, and not TNT-1 and TNT-2. However, amendment of previously unexposed roots with TNT produced all four conjugates. The conjugates were preferentially accumulated within the biomass phase of root cultures. Significantly, conjugates TNT-1 and TNT-2 were observed in the biomass phase of intact M. aquaticum plants exposed to TNT. The results clearly indicate the presence of common TNT transformation products in two diverse plants species and tissue type. The distribution of conjugates formed via monoamine derivatives of TNT, however, may be a function of several factors, including the starting xenobiotic type and/or level. Initial bulk rate constants for disappearance of 2,4,6 trinitrotoluene, 2-amino-4,6-dinitrotoluene, and 4-amino-2,6-dinitrotoluene were also determined. Their magnitude followed the order: TNT >> 4-A-2,6-DNT > 2-A-4,6-DNT.     

Biodegradation of Chloromethane by Pseudomonas aeruginosa Strain NB1 under Nitrate-Reducing and Aerobic Conditions

Pseudomonas aeruginosa strain NB1 uses chloromethane (CM) as its sole source of carbon and energy under nitrate-reducing and aerobic conditions. The observed yield of NB1 was 0.20 (±0.06) (mean ± standard deviation) and 0.28 (±0.01) mg of total suspended solids (TSS) mg of CM⁻¹ under anoxic and aerobic conditions, respectively. The stoichiometry of nitrate consumption was 0.75 (±0.10) electron equivalents (eeq) of NO₃⁻ per eeq of CM, which is consistent with the yield when it is expressed on an eeq basis. Nitrate was stoichiometrically converted to dinitrogen (0.51 ± 0.05 mol of N₂ per mol of NO₃⁻). The stoichiometry of oxygen use with CM (0.85 ± 0.21 eeq of O₂ per eeq of CM) was also consistent with the aerobic yield. Stoichiometric release of chloride and minimal accumulation of soluble metabolic products (measured as chemical oxygen demand) following CM consumption, under anoxic and aerobic conditions, indicated complete biodegradation of CM. Acetylene did not inhibit CM use under aerobic conditions, implying that a monooxygenase was not involved in initiating aerobic CM metabolism. Under anoxic conditions, the maximum specific CM utilization rate (k) for NB1 was 5.01 (±0.06) μmol of CM mg of TSS⁻¹ day⁻¹, the maximum specific growth rate (μ_max) was 0.0506 day⁻¹, and the Monod half-saturation coefficient (K_s) was 0.067 (±0.004) μM. Under aerobic conditions, the values for k, μ_max, and K_s were 10.7 (±0.11) μmol of CM mg of TSS⁻¹ day⁻¹, 0.145 day⁻¹, and 0.93 (±0.042) μM, respectively, indicating that NB1 used CM faster under aerobic conditions. Strain NB1 also grew on methanol, ethanol, and acetate under denitrifying and aerobic conditions, but not on methane, formate, or dichloromethane.     

Biotransformation of 2,4,6-trinitrotoluene (TNT) by the fungus Fusarium oxysporum

The fungus Fusarium oxysporum was isolated and identified from the aquatic plant M. aquaticum. The capability of this fungus to transform 2,4,6-trinitrotoluene (TNT) in liquid cultures was investigated TNT was added to shake flask cultures and transformed into 2-amino-4,6-dinitrotoluene (2-A-DNT), 4-amino-2,6-dinitrotoluene (4-A-DNT), and 2,4-diamino-6-nitrotoluene (2,4-DAT) via 2- and 4-hydroxylamino-dinitrotoluene derivatives, which could be detected as intermediate metabolites. Transformation of TNT, 2-A-DNT, and 4-A-DNT was observed by whole cultures and with isolated mycelium. Cell-free protein extracts from the extracellular, soluble, and membrane-bound fractions were prepared from this fungus and tested for TNT-reducing activity. The concentrated extracellular culture medium was unable to transform TNT; however, low levels of TNT transformation were observed by the membrane fraction in the presence of nicotinamide adenine dinucleotide phosphate in an argon atmosphere. A concentrated extract of soluble enzymes also transformed TNT, but to a lesser extent. When TNT toxicity was studied with this fungus, a 50% decrease in the growth of F. oxysporum mycelium was observed when exposed to 20 mg/L TNT.     

酰胺生物降解机制的分子模拟研究

为探索酰胺生物降解酶的微观降解机制,用分子对接的方法模拟了酰胺与酰胺酶的相互作用,得到其复合物结构的理论模型,根据打分函数最低原则筛选出的RhAmidase与L-Methioninamide之间最佳构象打分函数为-86.741 9,二次打分函数为-76.022 4。同时,应用LPC/CSU Server研究了最佳构象的相互作用情况,结果表明,酰胺与酰胺酶之间以疏水作用数量最多,酰胺酶的ARG256 A、LEU353 A、TYR346 A、ARG225 A、THR218 A和PRO222 A在催化过程中起到了重要作用。     

Transformation of 2,4,6-trinitrotoluene (TNT) by immobilized Phanerochaete chrysosporium under fed-batch and continuous TNT feeding conditions

The cometabolic transformation of 2,4,6-trinitrotoluene (TNT) by an immobilized Phanerochaete chrysosporium culture was investigated under different TNT and/or glycerol feeding conditions in a 5-L reactor. In the fed-batch feeding mode, as a result of four spiking events at an average feeding rate of 20 mg TNT L(-1) d(-1) and 250 mg glycerol L(-1) d(-1), the initial TNT transformation rate and the glycerol uptake rate of the 7-day-old immobilized cell culture were 2.41 mg L(-1) h(-1) and 16.6 mg L(-1) h(-1), respectively. Thereafter, the TNT fed into the reactor depicted a negative effect on the cell physiology of P. chrysosporium, i.e., both rates decreased constantly. At 32 mg TNT L(-1) d(-1) feeding rate, also in the presence of glycerol (200 mg L(-1) d(-1)), this effect on the fungal cell metabolism was even more significant. When TNT was fed alone at 3.7 mg L(-1) d(-1), it showed an initial 0.75 mg L(-1) h(-1) rate of TNT transformation, i.e., one-third the initial level observed in the presence of glycerol. In contrast, in the continuous feeding mode (dilution rate, D = 0.11 d(-1)), at 5.5 mg TNT L(-1) d(-1) and 220 mg glycerol L(-1) d(-1), the immobilized cell culture exhibited a constant TNT transformation rate for cultivation periods of 50 and 61 days, under uncontrolled and controlled pH conditions, respectively. Thereafter, during the latter experiment, 100% TNT biotransformation was achieved at 1,100 mg L(-1) d(-1) glycerol feeding rate. Immobilized cells (115-day-old), sampled from a continuous TNT feeding experiment, mineralized [(14)C]-TNT to a level of 15.3% following a 41-day incubation period in a microcosm.     

Biodegradation of TNT (2,4,6-trinitrotoluene) by Phanerochaete chrysosporium

Extensive biodegradation of TNT (2,4,6-trinitrotoluene) by the white rot fungus Phanerochaete chrysosporium was observed. At an initial concentration of 1.3 mg/liter, 35.4 +/- 3.6% of the [14C]TNT was degraded to 14CO2 in 18 days. The addition of glucose 12 days after the addition of TNT did not stimulate mineralization, and, after 18 days of incubation with TNT only, about 3.3% of the initial TNT could be recovered. Mineralization of [14C]TNT adsorbed on soil was also examined. Ground corncobs served as the nutrient for slow but sustained degradation of [14C]TNT to 14CO2 such that 6.3 +/- 0.6% of the [14C]TNT initially present was converted to 14CO2 during the 30-day incubation period. Mass balance analysis of liquid cultures and of soil-corncob cultures revealed that polar [14C]TNT metabolites are formed in both systems, and high-performance liquid chromatography analyses revealed that less than 5% of the radioactivity remained as undegraded [14C]TNT following incubation with the fungus in soil or liquid cultures. When the concentration of TNT in cultures (both liquid and soil) was adjusted to contamination levels that might be found in the environment, i.e., 10,000 mg/kg in soil and 100 mg/liter in water, mineralization studies showed that 18.4 +/- 2.9% and 19.6 +/- 3.5% of the initial TNT was converted to 14CO2 in 90 days in soil and liquid cultures, respectively. In both cases (90 days in water at 100 mg/liter and in soil at 10,000 mg/kg) approximately 85% of the TNT was degraded. These results suggest that this fungus may be useful for the decontamination of sites in the environment contaminated with TNT.     

TNT在大鼠晶状体内的代谢及其对晶状体中抗氧化相关酶活性的影响

大鼠皮下注射ＴＮＴ,以ＨＰＬＣ分析其在晶状体内的代谢过程,并检测晶状体谷胱甘肽过氧化物酶、谷胱甘肽还原酶及超氧化物歧化酶的活性变化。发现在注射ＴＮＴ后２ｈ即可在晶状体内检测到为量极少的ＴＮＴ及其代谢产物,第１２ｈ一氨基二硝基甲苯含量达最高峰。鼠龄较小的大鼠晶状体内ＴＮＴ及其代谢产物高于鼠龄较大的大鼠．多剂量注射ＴＮＴ时大鼠晶状体内一氨基二硝基甲苯于第２天达到高峰,ＴＮＴ于第５天达饱和状态,第１８天一氨基二硝基甲苯含量与ＴＮＴ含量相近。谷胱甘肽过氧化物酶、谷胱甘肽还原酶及超氧化物歧化酶活性在注射ＴＮＴ的第２天均有不同程度的升高,在第５天和第１８天维持在低活性状态。实验表明ＴＮＴ在晶状体内是通过硝基还原而代谢的．ＴＮＴ进入晶状体后初期可诱发晶状体抗氧化相关酶活性的增高,后期则导致晶状体抗氧化相关酶活性的降低。