两株丁草胺高效降解菌复配菌剂降解特性研究

LYC-1(Acinetobacter sp.)与LYC-2(Ancylobacter sp.)为两株从长期受农药污染的土壤中分离得到的丁草胺高效降解菌。本研究考察此两株降解菌复配菌剂对丁草胺降解特性,结果表明,菌株LYC-1和LYC-2的菌悬液以3:1的比例混合时,其降解率最高,且高于两个单菌株的降解率。当丁草胺浓度为100 mg·L-1和200 mg·L-1时,混合菌达到最大降解率和生长量,分别为97.8%与1.26(OD600mn)。     

厌氧丁草胺降解菌BAD-20的分离鉴定及降解特性研究

【目的】分离并鉴定能够降解除草剂丁草胺的厌氧微生物菌株,研究其厌氧降解丁草胺的特性和代谢途径,为深入研究丁草胺厌氧降解机制提供依据。【方法】以丁草胺为碳源作为选择压力从水稻田土壤中富集驯化丁草胺降解菌,利用16S rRNA基因系统发育分析结合菌株培养特征对降解菌株进行初步鉴定,利用液相色谱-时间飞行质谱(LC-TOF-MS)检测菌株降解丁草胺的代谢产物。【结果】筛选到一株降解丁草胺的厌氧细菌,命名为BAD-20,初步鉴定为嗜蛋白质菌属(Proteiniphilum),菌株BAD-20降解丁草胺的最适条件为温度30–35℃、pH 7.5–8.0和0–0.5%NaCl,在有氧条件下该菌不能降解丁草胺。最适条件下,菌株BAD-20在10d降解90%的20mg/L丁草胺。菌株BAD-20还能降解甲草胺、乙草胺、丙草胺,降解效率从高到低依次为甲草胺乙草胺丙草胺丁草胺,对这些氯乙酰胺除草剂的降解动力学符合一级动力学方程。鉴定到2个丁草胺降解代谢产物,分别是N-(2,6-二乙基苯基)-N-(丁氧甲基)乙酰胺(DEPBMA)和N-(2,6-二乙基苯基)乙酰胺(DEPA),表明菌株BAD-20降解丁草胺的起始步骤为脱氯,随后脱去N-丁氧甲基。【结论】本研究富集分离到一株降解丁草胺的厌氧细菌嗜蛋白质菌属(Proteiniphilum) BAD-20,为深入研究丁草胺厌氧降解机制及研发含丁草胺废水厌氧生物处理技术提供依据。     

丁草胺降解菌的分离优化

通过富集、驯化培养及平板划线等微生物分离技术,从长期生产丁草胺的山东省某农药厂附近的土壤中分离得到了三株以丁草胺为唯一碳源或氮源的降解菌株,分别标记为SD-1、SD-2和SD-3。通过革兰氏染色可以判断,SD-1被染成蓝紫色为革兰氏阳性球菌,SD-2被染成蓝紫色为革兰氏阳性杆菌,SD-3被染成红色为革兰氏阴性杆菌.随后,通过糖发酵及IMVIC等生理生化实验对菌株的基本生理生化特征进行了鉴定.同时,通过单因子优化实验确定了三株丁草胺降解菌的最适生长温度均为28℃,最适p H均为7.0,所需的最适丁草胺浓度SD-1为100 mmol/L,SD-2和SD-3均为300 mmol/L.     

氯苯降解菌的筛选及降解条件研究

从活性污泥中筛选到一株具有降解氯苯功能的菌株JH02,依据菌落特征形态和生理生化反应鉴定该菌株属于链球菌属(Streptococcus)。分别考察培养温度、培养时间、氯苯浓度、pH值、菌悬液接种量及摇床转速等因素对菌株降解性能的影响。确定菌株StreptococcusJH02的对氯苯的最适降解条件为:培养温度为37℃,培养时间24 h,菌悬液接种量体积分数为4%,pH8.0,摇床转速140 r.min-1,此条件下氯苯的降解率可达94.7%。     

一株高分子量多环芳烃降解菌的筛选、鉴定及降解特性研究

采用富集培养方法从多环芳烃污染土壤中筛选分离得到1株能以苯并[a]芘(B[a]P)为唯一碳源和能源生长的菌株.形态特征观察和16S rDNA序列分析结果表明,该菌株为副球菌属(Paracoccus sp.),编号为HPD-2.HPD-2在3.0 mg/L的B[a]P液体培养基中生长较慢,培养5 d后B[a]P的降解率为89.7%.同时,该菌株对四环的芘和荧蒽也具有较好的降解能力,培养7 d后芘和荧蒽的降解率分别达到47.2%和84.5%.可见,该菌株对高分子量PAHs具有很好的降解潜力.     

1株甲苯降解真菌的筛选鉴定及其降解甲苯的特性

从实验室保存的7株真菌筛选到1株能高效降解甲苯的菌株H1,基于形态特征、ITS序列系统学分析,将H1菌株鉴定为毛栓菌（Trametes hirsuta）。利用正交设计实验方法研究了温度、pH值、甲苯浓度和吐温80浓度对H1菌株降解甲苯的影响,研究得出该菌株降解甲苯的最适条件为30℃、pH 5.0、甲苯浓度300mg/L、吐温80浓度0.05%,在该条件下H1对甲苯的最大降解率为85.3%,降解率比未优化之前有了显著提高。比较了H1菌株在3种培养基产生漆酶的能力,H1在土豆葡萄糖培养基产酶能力最强,在第7天达到酶活高峰16 500 U/L。H1在甲苯为唯一碳源的培养基中,漆酶酶活最低,培养7 d时漆酶酶活为589 U/L。     

油脂降解菌种的鉴定及降解条件优化

从学校食堂排放的废水中筛选出1株油脂降解菌株,经形态特征、生理生化特征、16S rDNA同源性序列分析,鉴定为克雷伯氏菌属,暂命名为Klebsiella sp.X-1。并利用正交实验进一步考察了pH、培养温度、摇床转速对油脂降解率的影响。实验结果表明,在高含油废水培养基中,pH 7.0、转速为140 r/min、培养温度为30 ℃时,72 h内该菌的油脂降解率最高达68.2%。     

聚丁二酸丁二醇酯降解菌株的筛选及其降解性能研究

从石油污染土壤中筛选到1株具有聚丁二酸丁二醇酯降解能力的菌株PBS1302,经菌体形态特征、菌落培养特征、生理生化鉴定和16S r DNA基因序列分析,初步鉴定为铜绿假单胞菌(Pseudomonas aeruginosa)。该菌株在培养温度37℃,培养基起始p H 6.8的条件下经6 d的培养,对聚丁二酸丁二醇酯薄膜的降解率可达36.9%。经电子显微镜观察,与降解前相比,聚丁二酸丁二醇酯薄膜表面变得粗糙,出现明显的蚀刻痕迹。     

二氯喹啉酸降解菌MC-10的筛选、鉴定及其降解特性

【目的】为治理稻-烟轮作田块上茬土壤中二氯喹啉酸残留问题,筛选高效降解细菌菌株。【方法】通过富集培养和选择培养,从常年施用二氯喹啉酸的水稻田中筛选可以降解二氯喹啉酸的细菌;对其进行形态学观察、生理生化特征测定和16S r DNA序列系统发育鉴定。【结果】分离的降解菌株MC-10被鉴定为节杆属菌株(Arthrobacter sp.)。菌株MC-10在5%接种量p H 7、28℃时,对初始浓度为20 mg/L二氯喹啉酸7 d可降解90%以上。该降解菌的最佳降解条件为p H 7、30℃,二氯喹啉酸初始浓度在1-100mg/L间均有良好的降解效果;菌株MC-10在土壤中对二氯喹啉酸同样有良好的降解效果,温室内7 d对二氯喹啉酸污染土壤的修复率可达70%。【结论】菌株MC-10在二氯喹啉酸污染土壤和水质治理中具有潜在的应用前景。     

敌敌畏降解菌的分离鉴定及降解特性研究

目的:从受有机磷农药污染的土壤中分离能降解DDVP的菌株,对其进行鉴定和降解特性研究.方法:采用DDVP为惟一碳源和能源的无机盐培养基,通过富集培养、平板划线分离得到一株优势菌,编号为DDW-1,采用形态学、生理生化和16S-rDNA序列分析对其进行鉴定,采用气相色谱测定菌株DDW-1对DDVP的降解能力,并进行底物广谱性测试和降解酶定位实验.结果:该菌株鉴定为甲基杆菌属(Methylobacterium sp.).降解特性试验结果表明,其最佳生长条件为温度28℃,初始pH为7.0,在该条件下,500mg·L-> DDVP经过DDW-1菌株代谢3d后,降解率达63.7%.结论:菌株DDW-1能降解DDVP,该菌株产胞内酶.     

Construction and analysis of an intergeneric fusant able to degrade bensulfuron-methyl and butachlor

Rhodococcus sp. BX2 degrades bensulfuron-methyl but not butachlor, and Acinetobacter sp. LYC-1 degrades butachlor but not bensulfuron-methyl. Functional strains were constructed through protoplast fusion of Rhodococcus sp. BX2 and Acinetobacter sp. LYC-1 to generate fusants with an improved ability to simultaneously degrade bensulfuron-methyl and butachlor. Initial identification and stability tests of the fusants were performed. Three fusants with eighth transfer on plates containing two antibiotics and two herbicides were obtained. F1 also grew well in an inorganic salt solution containing bensulfuron-methyl and butachlor. F1 was characterized by its parents’ morphological and physio-biochemical features. F1 not only had bands in common with BX2 and LYC-1, but also had its own specific bands analyzed by Random Amplified Polymorphic DNA. The genetic similarity indices between F1 and BX2 and F1 and LYC-1 were 0.507 and 0.470, respectively. The percentages bensulfuron-methyl and butachlor degradation by F1 in an inorganic salt solution supplemented with 100 mg/L bensulfuron-methyl and 100 mg/L butachlor were 65.35 and 62.41 %, respectively, and the percentages in soil contaminated with 10 mg/kg bensulfuron-methyl and 10 mg/kg butachlor with an inoculum size of 5 % at 34 °C and at a pH of 7.5 after 35 days were 63.74 and 61.53 %, respectively. It was demonstrated that F1 could simultaneously degrade bensulfuron-methyl and butachlor.     

Isolation and characterization of butachlor‐catabolizing bacterial strain Stenotrophomonas acidaminiphila JS‐1 from soil and assessment of its biodegradation potential

Aims: Isolation, characterization and assessment of butachlor‐degrading potential of bacterial strain JS‐1 in soil. Methods and Results: Butachlor‐degrading bacteria were isolated using enrichment culture technique. The morphological, biochemical and genetic characteristics based on 16S rDNA sequence homology and phylogenetic analysis confirmed the isolate as Stenotrophomonas acidaminiphila strain JS‐1. The strain JS‐1 exhibited substantial growth in M9 mineral salt medium supplemented with 3·2 mmol l^?1 butachlor, as a sole source of carbon and energy. The HPLC analysis revealed almost complete disappearance of butachlor within 20 days in soil at a rate constant of 0·17 day^?1 and half‐life (t_½) of 4·0 days, following the first‐order rate kinetics. The strain JS‐1 in stationary phase of culture also produced 21·0 μg ml^?1 of growth hormone indole acetic acid (IAA) in the presence of 500 μg ml^?1 of tryptophan. The IAA production was stimulated at lower concentrations of butachlor, whereas higher concentrations above 0·8 mmol l^?1 were found inhibitory. Conclusions: The isolate JS‐1 characterized as Stenotrophomonas acidaminiphila was capable of utilizing butachlor as sole source of carbon and energy. Besides being an efficient butachlor degrader, it substantially produces IAA. Significance and Impact of the Study: The bacterial strain JS‐1 has a potential for butachlor remediation with a distinctive auxiliary attribute of plant growth stimulation.     

Cyanobacterial diversity shifts induced by butachlor in selected Indian rice fields in Eastern Uttar Pradesh and Western Bihar analyzed with PCR and DGGE

The present study examines the effects of 30 mg/kg butachlor on the cyanobacterial diversity of rice fields in Eastern Uttar Pradesh and Western Bihar in India. A total of 40 samples were grouped into three classes [(i) acidic, (ii) neutral, and (iii) alkaline soils], based on physicochemical and principle component analyses. Acidic soils mainly harbored Westillopsis, Trichormus, Anabaenopsis, and unicellular cyanobacteria; whereas Nostoc, Anabaena, Calothrix, Tolypothrix, and Aulosira were found in neutral and alkaline soils. Molecular characterization using 16S rRNA PCR and DGGE revealed the presence of 13 different phylotypes of cyanobacteria in these samples. Butachlor treatment of the soil samples led to the disappearance of 5 and the emergence of 2 additional phylotypes. A total of 40 DGGE bands showed significant reproducible changes upon treatment with butachlor. Phylogenetic analyses divided the phylotypes into five major clusters exhibiting interesting links with soil pH. Aulosira, Anabaena, Trichormus, and Anabaenopsis were sensitive to butachlor treatment, whereas uncultured cyanobacteria, a chroococcalean member, Westillopsis, Nostoc, Calothrix, Tolypothrix, Rivularia, Gloeotrichia, Fischerella, Leptolyngbya, and Cylindrospermum, appeared to be tolerant against butachlor at their native soil pH. Butachlor-induced inhibition of nitrogen fixation was found to be 65% (maximum) and 33% (minimum) in the soil samples of pH 9.23 and 5.20, respectively. In conclusion, low butachlor doses may prove beneficial in paddy fields having a neutral to alkaline soil pH.     

Butachlor inhibits production and oxidation of methane in tropical rice soils under flooded condition

In laboratory incubation experiments, application of a commercial formulation of the herbicide butachlor (N-butoxymethyl-2-chloro-2',6'-diethyl acetanilide) to three tropical rice soils, widely differing in their physicochemical characteristics, under flooded condition inhibited methane (CH4) production. The inhibitory effect was concentration dependent and most remarkable in the alluvial soil. Thus, following application of butachlor at 5, 10, 50 and 100 microg g(-1) soil, respectively, cumulative CH4 production in the alluvial soil was inhibited by 15%, 31%, 91% and 98% over unamended control. Since CH4 production was less pronounced in the sandy loam and acid sulfate soil, the impact of amendment with butchalor, albeit inhibitory, was less extensive than the alluvial soil. Inhibition of CH4 production in butachlor-amended alluvial soil was related to the prevention in the drop in redox potential as well as low methanogenic bacterial population especially at high concentrations of butachlor. CH4 oxidation was also inhibited in butachlor-amended alluvial soil with the inhibitory effect being more prevalent under flooded condition. Inhibition in CH4 oxidation was related to a reduction in the population of soluble methane monooxygenase producing methanotrophs. Results demonstrate that butachlor, a commonly used herbicide in rice cultivation, even at very low concentrations can affect CH4 production and its oxidation, thereby influencing the biogeochemical cycle of CH4 in flooded rice soils.     

凝结芽胞杆菌G1及其抑菌物质的研究

目的获得具有良好性状的产细菌素菌株。方法测定菌株形态学和生理生化学特性以进行菌种鉴定;采用牛津杯法测定抑菌谱及细菌素的理化特性。结果经鉴定实验菌株为凝结芽胞杆菌,所产细菌素在100℃加热60min后,残余活力为90％;在pH5～9范围内,抗菌活力稳定。结论凝结芽胞杆菌G1可产性能良好的抑制革兰阳性菌生长的细菌素。     

Butachlor is cytotoxic and clastogenic and induces apoptosis in mammalian cells

The ability of butachlor to induce cytotoxicity, clastogenicity and DNA damage was assessed using Chinese hamster ovary cells (CHO), Swiss mouse embryo fibroblasts (MEF) and human peripheral blood lymphocytes. A dose and time dependent loss of viability was evident upon treatment of CHO cells with butachlor. Cell killing to an extent of 50% was observed when cells were treated with 16.2 micrograms/ml of butachlor for 24 hr or with 11.5 micrograms/ml for 48 hr. The herbicide induced micronuclei significantly in cultured lymphocytes at 24 and 48 hr of treatment suggesting that it is clastogenic. To understand the mechanism of cell death caused by butachlor, its effect on DNA strand breaks was studied in MEF. A concomitant decrease in cell viability was observed with increase in DNA strand breaks. Agarose gel electrophoresis of DNA from herbicide treated CHO cells and cytochemical staining indicate the induction of apoptosis by butachlor.     

不同浓度下四种除草剂对福寿螺和坑螺的生态毒理效应

以化学除草剂应用为前提的水稻免耕抛秧栽培技术是近年来推广的节本栽培新技术。为更好地评价除草剂的环境风险,为防治除草剂的负效应提供科学依据,采用室内静水模拟实验研究了4种免耕稻田除草剂丁草胺、苄嘧磺隆、丁苄混剂和氯酸钾的3种浓度梯度下对典型水生动物福寿螺、坑螺的影响。结果表明,各除草剂对水生动物的代谢都有不同程度的影响, 氯酸钾和苄嘧磺隆对2种水生动物的呼吸作用影响不大,而丁草胺和丁苄混剂对3种水生动物的呼吸作用的影响有显著的抑制作用,且呈现一定的剂量效应;在本实验染毒剂量下, 丁草胺和丁苄混剂对2种水生动物的存活率影响很大,而氯酸钾和苄嘧磺隆对其存活率影响较小。丁草胺和丁苄混剂处理对福寿螺的氮代谢影响远远大于氯酸钾和苄嘧磺隆处理,而从水体总氮和总磷含量的影响来看,4种除草剂对其影响都较大。总之,从4种除草剂对实验用螺存活率和主要代谢生理指标的综合影响大小来看,丁草胺>丁苄混剂>苄嘧磺隆>氯酸钾。     

丁草胺对水稻土甲烷释放和厌氧细菌的影响

近年来,我国水稻田的化除面积增加很快,除草剂的使用已成为一种必不可少的手段。因而除草剂大量使用的环境污染问题日益突出,对生态系统的平衡产生威胁性影响,引起农产品农药含量超标,或者即使不超标也由于食物链的生物富集最终进入人体危害健康。除草剂致癌、致突变和致畸胎的事实不胜枚举。除草剂在水稻田使用,至少有70％进入土壤,直接影响土壤微生物的生长和代谢。     

农药污染对水稻田土壤反硝化细菌种群数量及其活性的影响

在实验室条件下,研究了农药污染对水稻田土壤反硝化细菌(Denitrfying bacteria,DNB)种群数量及其反硝化活性的影响。结果表明,紫色稻田土壤、黄松稻田土壤和红壤稻田土的DNB种群数量范围分别为59．04×10⁴～157．59×10⁴、42．89×10⁴～108．97×10⁴和32．14×10⁴～75．30×10⁴cfu·g^-1,稻田土DNB种群数量和土壤NO3^-的消耗量之间具有正相关性。在1kg干土中加入1mg丁草胺或呋喃丹,能刺激DNB的生长及其反硝化活性,在1kg干土中加入5mg多菌灵、10mg丁草胺或呋喃丹,对DNB的生长及其反硝化活性有明显的抑制作用,丁草胺和呋喃丹施后7d,多菌灵施后14d,对水稻田土壤的DNB种群数量和反硝化活性抑制作用达到最大,然后逐渐减轻,最后呈现一定的促进作用。     

A Novel Aldo-Keto Reductase (AKR17A1) of Anabaena sp. PCC 7120 Degrades the Rice Field Herbicide Butachlor and Confers Tolerance to Abiotic Stresses in E. coli

Present study deals with the identification of a novel aldo/keto reductase, AKR17A1 from Anabaena sp. PCC7120 and adds on as 17^th family of AKR superfamily drawn from a wide variety of organisms. AKR17A1 shares many characteristics of a typical AKR such as— (i) conferring tolerance to multiple stresses like heat, UV-B, and cadmium, (ii) excellent activity towards known AKR substrates (isatin and 2-nitrobenzaldehyde), and (iii) obligate dependence on NADPH as a cofactor for enzyme activity. The most novel attribute of AKR17A1, first reported in this study, is its capability to metabolize butachlor, a persistent rice field herbicide that adversely affects agro-ecosystem and non-target organisms. The AKR17A1 catalyzed- degradation of butachlor resulted into formation of 1,2-benzene dicarboxylic acid and 2,6 bis (1,1, dimethylethyl) 4,-methyl phenol as the major products confirmed by GC-MS analysis.