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1.
阿特拉津降解菌株的分离和鉴定   总被引:28,自引:0,他引:28  
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。  相似文献   

2.
邱并生 《微生物学通报》2009,36(7):1098-1098
阿特拉津(Atrazine)是一种三嗪类除草剂,商品名莠去津,主要用于玉米、高粱和甘蔗地的杂草防除.研究表明,阿特拉津是一种内分泌干扰剂,它能干扰激素的调节功能,引起人和两栖动物的生殖缺陷,诱发肿瘤和癌症,其生态毒理风险不容忽视[1-3].  相似文献   

3.
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  相似文献   

4.
阿特拉津降解菌株的分离、鉴定和工业废水生物处理试验   总被引:1,自引:0,他引:1  
用液体无机盐培养基富集培养法和无机盐平板直接分离法, 从生产阿特拉津的农药厂的废水和污泥混合物中分离到13个能以阿特拉津为唯一氮源生长的细菌菌株。通过16S rRNA基因序列分析, 11个菌株被鉴定为Arthrobacter spp., 2个菌株被鉴定为Pseudomonas spp.。对阿特拉津降解活力最高的Arthrobacter sp. AD30和Pseudomonas sp. AD39的降解基因组成和降解特性进行了详细研究。降解基因的PCR扩增表明, AD30和AD39都含有trzN-atzBC基因, 能将有毒的阿特拉津降解成无毒的氰尿酸。降解实验表明, 向阿特拉津浓度为200 mg/L的无机盐培养基中分别接种等量的AD30、AD39和这两个菌株的混合菌液, 30°C振荡培养48 h以后, 阿特拉津去除率分别为92.5%、97.9%和99.6%, 表明混合菌的降解效果好于单菌。用AD30和AD39的混合菌液接种阿特拉津浓度为176 mg/L的工业废水, 30°C振荡培养72 h以后, 99.1%的阿特拉津被去除, 表明混合菌株在阿特拉津工业废水的生物处理中有很好的应用潜力。  相似文献   

5.
【背景】玉豆轮作过程中,玉米田中长残留除草剂阿特拉津易对下茬大豆作物产生不良影响。【目的】从黑龙江省安达市的农田土筛选一株能适应该土壤环境生长的阿特拉津降解菌并研究其降解特性。【方法】利用富集培养法,分离、筛选一株阿特拉津高效降解菌并结合外观形态、生理生化及16SrRNA基因序列测定对其进行鉴定,通过单一变量法设置不同的碳源、pH、温度和阿特拉津浓度,研究降解菌株最佳发酵及降解条件。【结果】得到一株在BSM-G中能够以阿特拉津为唯一氮源生长的高效阿特拉津降解菌AD111,鉴定为马德普拉塔无色小杆菌(Achromobacter marplatensis)。菌株AD111降解阿特拉津的最适温度为35℃,最适pH为8.0,最佳碳源为蔗糖,24 h内对浓度为50 mg/L的阿特拉津降解率达到99.7%,对300 mg/L的阿特拉津降解率达到81.9%。【结论】降解菌AD111具有较好的环境适应及阿特拉津降解能力,为解决黑龙江偏碱土壤中阿特拉津残留提供了良好的候选菌株。  相似文献   

6.
一株阿特拉津降解菌的分离鉴定及降解特性   总被引:2,自引:0,他引:2  
从农药厂废水处理池的活性污泥中分离到一株阿特拉津降解菌X-4, 根据其生理生化特性和16S rRNA基因序列相似性分析, 将其初步鉴定为节杆菌属(Arthrobacter sp.)。该菌能以阿特拉津为唯一碳氮源生长, 42 h内对100 mg/L的阿特拉津降解效果为95.7%, 降解阿特拉津的最适温度为30 °C, pH为7.0。该菌对多种重金属离子都存在抗性, 显示了其在去除阿特拉津和重金属复合污染方面的应用潜力。对其降解基因的初步研究显示, 该菌含有trzN、atzB和atzC 3个阿特拉津降解相关基因。  相似文献   

7.
阿特拉津降解菌SA1的分离鉴定及其降解特性研究   总被引:4,自引:0,他引:4  
为进行阿特拉津(AT)污染的生物修复,从AT降解混合菌群中,经长期的交替液体摇瓶培养和平板划线分离,筛选到一株能完全降解AT的菌株SA1。经生理生化特征及16S rDNA序列分析,将该菌鉴定为假单胞菌属(Pseudomonas sp.)。与已报道的AT降解菌Pseudomonas sp.ADP不同,SA1能以AT为唯一碳源、氮源和能源生长,培养基中添加铵盐不抑制SA1的降解功能,而添加葡萄糖时,累积的氰尿酸会被快速降解。SA1生长的最适温度为37℃,最适pH值为7.0。SA1的静息细胞在10℃~40℃或pH值4~11时均能高效降解AT,比ADP降解具有更广的pH和温度范围,表明SA1降解菌株具有广阔的应用前景。SA1中AT降解基因为保守的atzABCD,并含有IS1071的tnpA基因片段,传代过程中降解基因会以一定频率丢失。  相似文献   

8.
【目的】研究阿特拉津降解菌株DNS32的菌种分类、降解特性及降解途径,丰富阿特拉津降解菌菌种资源。【方法】在长期施用阿特拉津的东北地区寒地黑土中筛选出一株以阿特拉津为唯一氮源生长的降解菌株DNS32,测定其基本降解特性,通过16S rRNA序列分析进行分类鉴定,并利用阿特拉津降解基因PCR扩增技术及降解产物生成量的测定,进一步揭示其降解途径。【结果】实验结果发现DNS32菌株具有较好的降解能力,且在相对较低温度下也具有一定的降解能力。16S rRNA序列分析结果表明DNS32与鲁氏不动杆菌(Acinetobacter lwoffii)16S rRNA序列同源性高达99%。成功地扩增降解基因trzN、atzB及atzC,实验结果表明DNS32遵循Arthrobacter aurescens TC1的降解模式,可将阿特拉津降解为氰尿酸,降解产物的生成量测定也证明了这一点。【结论】实验结果丰富了阿特拉津降解菌菌种资源,为不动杆菌属的阿特拉津降解菌研究提供了参考。  相似文献   

9.
阿特拉津降解菌SYSA的分离筛选和鉴定   总被引:2,自引:0,他引:2  
从长期施用阿特拉津的土壤中筛选到1株能够以阿特拉津为惟一碳源生长的菌株SYSA,经生理生化特性鉴定和16S rDNA序列分析,该菌为阴沟肠杆菌(Enterobacter cloacae).对SYSA菌的生物学特性研究表明,pH 7-8,30℃时,在以阿特拉津(20 mg/L)为惟一碳源的培养基上经146 h培养,降解率为87%.  相似文献   

10.
阿特拉津及其降解菌的使用对土壤微生物群落的影响   总被引:4,自引:0,他引:4  
比较了阿特拉津及降解菌株BTAH1的使用对土壤微生物的影响.结果表明,在实验周期内阿特拉津对土壤微生物的代谢作用有较明显的刺激作用,与空白土壤(未施用阿特拉津和降解菌)相比,对照土壤(施用50mg·kg-1土阿特拉津)呼吸强度显著增加,且土壤中的阿特拉津浓度对土壤NH4+-N和NO3--N浓度的影响显著.降解菌BTAH1可在1周内降解土壤中98%以上的阿特拉津,从而使土壤呼吸强度有所下降,土壤中NH4+-N和NO3--N的浓度基本与空白土壤持平,对微生物量C和微生物量N影响不显著;放线菌和真菌数量也基本与空白持平,细菌数量较高.对土壤细菌的16SrDNA文库的ARDRA分析发现,阿特拉津及其降解菌的使用对土壤细菌群落结构有一定程度的影响,阿特拉津的使用会降低细菌群落的多样性,而降解菌的使用会恢复土壤细菌的多样性.  相似文献   

11.
Twenty numerically dominant 4-chlorobenzoate (4-CBA)-degrading bacteria were isolated from agricultural soils. The isolates were able to utilize 4-CBA as a sole source of carbon and energy. A total of 65% of the isolates was identified to the species level by fatty acid methyl ester (FAME) analysis, and the isolates were strains of Micrococcus, Pseudomonas, Oerskovia, Cellulomonas, and Arthrobacter species. The chromosomal DNA patterns of the isolates obtained by polymerase chain reaction (PCR) amplification of repetitive extragenic palindromic (REP) sequences were distinct from each other. Most of the isolates grew rapidly in 4-CBA medium, but their substrate utilization capabilities were generally restricted. Plasmid DNAs were detected from 55% of the isolates, and one strain, HR7, was shown to have self-transmissible, 4-CBA degradative plasmids. 4-CBA degradative enzymes were inducible by the presence of 4-CBA and most of the isolates appeared to mineralize it through 4-hydroxybenzoate rather than 4-chlorocatechol.  相似文献   

12.
The community structure of sulfate-reducing bacteria in littoral and profundal sediments of the oligotrophic Lake Stechlin (Germany) was investigated. A collection of 32 strains was isolated from the highest positive dilutions of most-probable-number series, and their partial 16S rRNA gene sequences and genomic fingerprints based on ERIC (enterobacterial repetitive intergenic consensus)-PCR were analyzed. The strains fell into eight distinct phylogenetic lineages, and the majority (70%) showed a close affiliation to the genus Desulfovibrio. Most of the remaining strains (22%) were related to the gram-positive Sporomusa and Desulfotomaculum groups. A high redundancy of 16S rRNA gene sequences was found within several of the phylogenetic lineages. This low phylogenetic diversity was most pronounced for the subset of strains isolated from oxic sediment layers. ERIC-PCR revealed that most of the strains with identical 16S rRNA gene sequences were genetically different. Since strains with identical 16S rRNA gene sequences but different genomic fingerprints also differed considerably with respect to their physiological capabilities, the high diversity detected in the present work is very likely of ecological relevance. Our results indicate that a high diversity of sulfate-reducing bacterial strains can be recovered from the natural environment using the established cultivation media. Received: 20 April 1998 / Accepted: 12 June 1998  相似文献   

13.
14.
Atrazine degradation previously has been shown to be carried out by individual bacterial species or by relatively simple consortia that have been isolated using enrichment cultures. Here, the degradative pathway for atrazine was examined for a complex 8-membered enrichment culture. The species composition of the culture was determined by PCR-DGGE. The bacterial species included Agrobacterium tumefaciens, Caulobacter crescentus, Pseudomonas putida, Sphingomonas yaniokuyae, Nocardia sp., Rhizobium sp., Flavobacterium oryzihabitans, and Variovorax paradoxus. All of the isolates were screened for the presence of known genes that function for atrazine degradation including atzA,-B,-C,-D,-E,-F and trzD,-N. Dechlorination of atrazine, which was obligatory for complete mineralization, was carried out exclusively by Nocardia sp., which contained the trzN gene. Following dechlorination, the resulting product, hydroxyatrazine was further degraded via two separate pathways. In one pathway Nocardia converted hydroxyatrazine to N-ethylammelide via an unidentified gene product. In the second pathway, hydroxyatrazine generated by Nocardia sp. was hydrolyzed to N-isopropylammelide by Rhizobium sp., which contained the atzB gene. Each member of the enrichment culture contained atzC, which is responsible for ring cleavage, but none of the isolates carried the atzD,-E, or -F genes. Each member further contained either trzD or exhibited urease activity. The enrichment culture was destabilized by loss of Nocardia sp. when grown on ethylamine, ethylammelide, and cyanuric acid, after which the consortium was no longer able to degrade atrazine. The analysis of this enrichment culture highlights the broad level bacterial community interactions that may be involved in atrazine degradation in nature.  相似文献   

15.
This study investigated the aerobic and anoxic biodegradation of four estrogens [estrone (E1), estradiol (E2), estriol (E3), and the synthetic 17α-ethinylestradiol (EE2)] in microcosms constructed with marine sand and ulftrafiltered (UF) secondary effluent. Three estrogen-degrading bacteria, LHJ1, LHJ3, and CYH, were isolated. Based on gram-stain morphology and 16S rRNA sequence homology, LHJ1 and LHJ3 belong to the genus Acinetobacter and Agromyces, respectively; CYH matched to 95% with the genus Sphingomonas. Aerobically LHJ3 degrades E3, CYH degrades E1, and all three isolates oxidize E2 to E1. Under anoxic conditions, CYH degrades E1 and LHJ3 degrades E2, whereas E3 and EE2 were not degraded by the three isolates; EE2 was transformed in microcosms incubated with site ground water. The degradation kinetics of E1 and E2 by CYH and E2 by LHJ3 under aerobic conditions was linearly correlated with the initial concentration, which ranged from 50 to 2,000 μg/l. The degradation of E1 by CYH under anoxic conditions followed Michaelis–Menten kinetics. 16α-Hydroxyestrone was found to be a transient transformation product of E3 under aerobic conditions.  相似文献   

16.
AIMS: To isolate and characterize atrazine-degrading bacteria in order to identify suitable candidates for potential use in bioremediation of atrazine contamination. METHODS AND RESULTS: A high efficiency atrazine-degrading bacterium, strain AD1, which was capable of utilizing atrazine as a sole nitrogen source for growth, was isolated from industrial wastewater. 16S rDNA sequencing identified AD1 as an Arthrobacter sp. The atrazine chlorohydrolase gene (atzA) isolated from strain AD1 differed from that found in the Pseudomonas sp. ADP by only one nucleotide. However, it was found located on the bacterial chromosome rather than on plasmids as previously reported for other bacteria. CONCLUSIONS: Atrazine chlorohydrolase gene, atzA, either encoded by chromosome or plasmid, is highly conserved. SIGNIFICANCE AND IMPACT OF THE STUDY: Comparison analysis of atrazine degradation gene structure and arrangement in this and other bacteria provides insight into our understanding of the ecology and evolution of atrazine-degrading bacteria.  相似文献   

17.
We report the characterisation of Nocardioides sp. SP12, an atrazine-degrading bacteria isolated from atrazine-treated bulk- and maize rhizosphere soil. Based on 16S rDNA alignment, strain SP12 showed close phylogenic relationships with Nocardioides sp. C157 and Nocardioides simplex. Internal transcribed spacer (ITS) sequences of strain SP12 were longer than those of other Nocardioides sp. and present Ala- and Ile-tRNA unlike Actinomycetales. Nocardioides sp. SP12 presents a novel atrazine catabolic pathway combining trzN with atzB and atzC. Atrazine biodegradation ends in a metabolite that co-eluted in HPLC with cyanuric acid. This metabolite shows an absorption spectrum identical to that of cyanuric acid with a maximal absorption at 214.6 nm. The mass of the atrazine metabolite is in concordance with that of cyanuric acid according to mass spectrometry analysis. Quantitative PCR revealed that the ITS sequence of Nocardioides sp. SP12 was at a lower number than the one of trzN in atrazine-treated soil samples. It suggests that trzN could also be present in other atrazine degrading bacteria. The numbers of trzN and ITS sequences of Nocardioides sp. SP12 were higher in the maize rhizosphere than in bulk soil.  相似文献   

18.
19.
Thirty-seven carbofuran-degrading bacteria were isolated from agricultural soils, and their genetic and phenotypic characteristics were investigated. The isolates were able to utilize carbofuran as a sole source of carbon and energy. Analysis of the 16S rRNA gene sequence indicated that the isolates were related to members of the genera Rhodococcus, Sphingomonas, and Sphingobium, including new types of carbofuran-degrading bacteria, Bosea and Microbacterium. Among the 37 isolates, 15 different chromosomal DNA patterns were obtained by polymerase chain reaction (PCR) amplification of repetitive extragenic palindromic (REP) sequences. Five of the 15 representative isolates were able to degrade carbofuran phenol, fenoxycarb, and carbaryl, in addition to carbofuran. Ten of the 15 representative isolates had 1 to 8 plasmids. Among the 10 plasmid-containing isolates, plasmid-cured strains were obtained from 5 strains. The cured strains could not degrade carbofuran and other pesticides anymore, suggesting that the carbofuran degradative genes were on the plasmid DNAs in these strains. When analyzed with PCR amplification and dot-blot hybridization using the primers targeting for the previously reported carbofuran hydrolase gene (mcd), all of the isolates did not show any positive signals, suggesting that their carbofuran hydrolase genes had no significant sequence homology with the mcd gene.  相似文献   

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