3-苯氧基苯甲酸降解菌的分离及降解特性研究

从农药厂污泥中分离到一株3-苯氧基苯甲酸（3-Phenoxybenzoic acid,3-PBA）降解菌PBM11。经生理生化试验和16S rDNA测定初步鉴定为假单胞菌属（Pseudomonas sp．）。PBM11能以3-PBA为唯一碳源生长,降解试验表明：在基础盐培养基中,初始pH7．0,3＆C,160r／rain,装瓶量为100mL／250mL的条件下,PBM11经过24h可完全降解200mg／L的3-PBA;添加低浓度的外源营养物质能够在一定程度上促进降解;Cu^2＋和Co^2＋等对其降解性能有抑制作用,而Fe^3＋有明显的促进作用;通过分析底物利用情况,初步推断3-PBA降解的中间产物能为原儿茶酸和苯酚。经过7d的处理,PBM11对土壤中100mg／L3-PBA的降解率为66．25％。从PBM11中检测到一个质粒。     

3-苯氧基苯甲酸降解菌的分离及降解特性研究*

从农药厂污泥中分离到一株3-苯氧基苯甲酸(3-Phenoxybenzoicacid,3-PBA)降解菌PBM11。经生理生化试验和16SrDNA测定初步鉴定为假单胞菌属(Pseudomonassp·)。PBM11能以3-PBA为唯一碳源生长,降解试验表明:在基础盐培养基中,初始pH7·0,30℃,160r/min,装瓶量为100mL/250mL的条件下,PBM11经过24h可完全降解200mg/L的3-PBA;添加低浓度的外源营养物质能够在一定程度上促进降解;Cu²⁺和     

一株3-苯氧基苯甲酸降解菌的筛选及其协同Bacillus licheniformis G-04降解高效氯氰菊酯的研究

【目的】从长期受拟除虫菊酯类农药污染的白菜根系土壤分离1株3-苯氧基苯甲酸(3-phenoxybenzoic acid, 3-PBA)降解菌,并探究其与Bacillus licheniformis G-04协同作用对高效氯氰菊酯(beta-cypermethrin,Beta-CP)的降解及污染土壤的生物修复,为土壤农药残留危害处理提供优良菌种。【方法】采用富集驯化、筛选纯化方法,筛选3-PBA降解菌,并通过形态和生理生化特征以及16S rRNA序列分析进行鉴定。利用Origin 8.0分析3-PBA降解菌与B. licheniformis G-04的生长降解动力学过程。同时,采用高效液相色谱法评估两菌株协同降解Beta-CP的能力及其对受Beta-CP污染土壤的修复作用。【结果】筛选得到1株3-PBA高效降解菌HA516,48 h对3-PBA (100 mg/L)的降解率达到87.73%,经鉴定为皮特不动杆菌(Acinetobacter pittii);构建了该菌株和B. licheniformis G-04的生长降解动力学方程,结果表明模型与实验数据能较好拟合;以6.7∶3.3的接种比例先接种B. licheniformis G-04,24 h后再接入A. pittii HA516协同作用,在48 h,Beta-CP (50 mg/L)的降解率达78.37%,较单菌株(B. licheniformisG-04)的降解率(40.47%)提高了37.90%,半衰期从58.39h缩短为24.51h。土壤修复实验表明,第7天协同组对Beta-CP(30mg/kg)的降解率较单菌株提高了33.26%,达到79.27%。【结论】A.pittiiHA516是1株3-PBA高效降解菌,能与B. licheniformis G-04协同增效降解Beta-CP,可作为修复3-PBA或拟除虫菊酯类农药污染的优良微生物资源。     

一株路德维希肠杆菌的筛选及其对3-苯氧基苯甲酸的降解特性分析

【目的】3-苯氧基苯甲酸(3-phenoxybenzoic acid,3-PBA)的消除是解决拟除虫菊酯类农药污染的关键,目的是从受拟除虫菊酯类农药污染植物根系土壤中分离出3-PBA高效降解菌株。【方法】采用富集驯化、筛选纯化方法,以3-PBA为唯一碳源、能源筛选3-PBA降解菌株;菌株鉴定采用形态、生理生化和16S r RNA序列分析法;并研究其生长降解动力学特性,最后采用Box-Behnken响应面分析确定最佳降解条件。【结果】从川北地区大豆根系土壤中筛选得到1株高效降解菌BPBA031,经鉴定为路德维希肠杆菌(Enterobacter ludwigii);该菌株耐3-PBA浓度达1600 mg/L,其生长降解过程分别符合Logistic生长动力学(μm=0.09149 h~(–1),X_m=1.1145)和一级降解动力学模型(k=0.02085,t_(1/2)=33.24 h);对3-PBA降解的最适条件为34–37°C、3-PBA浓度25–200 mg/L和p H 7.5–8.5;在35.19°C、30.0 mg/L 3-PBA和p H 7.58条件下,该菌株48 h对3-PBA的降解率达83.75%。【结论】路德维希肠杆菌BPBA031是1株高效3-PBA降解菌,可作为生物修复受3-PBA或拟除虫菊酯类农药污染环境的潜在菌株资源。     

食源米曲霉菌株的分离及其降解高效氯氰菊酯和3-苯氧基苯甲酸的特性研究

【目的】通过研究不同食源米曲霉菌株对高效氯氰菊酯(beta-cypermethrin,β-CP)及其必经代谢产物3-苯氧基苯甲酸(3-phenoxybenzoic acid,3-PBA)的降解特性,了解不同菌株的降解共性及差异性,为农副产品和发酵食品的农残减除提供理论基础和食品用安全微生物资源。【方法】以发酵食品为菌源,通过形态学鉴定、ITS测序和菌株产黄曲霉毒素B1 (AFB1)的测定筛选鉴定米曲霉菌株,采用高效液相色谱法(HPLC)、气相色谱-质谱法(GC-MS)、液相色谱-质谱法(LC-MS)对米曲霉模式菌株RIB40 (保藏编号:ATCC 42149)、米曲霉M4 (保藏编号:CGMCC 11645)和鉴定获得的米曲霉菌株的β-CP和3-PBA降解特性进行研究。【结果】鉴定获得15株不产AFB1的食源米曲霉,17株米曲霉在马铃薯液体培养基(PD)中振荡培养5d,对50mg/L的β-CP降解率为19.33%-50.29%不等,检测到降解产物3-PBA,对50 mg/L的3-PBA降解率为45.59%-99.67%不等;分别在添加50 mg/Lβ-CP和3-PBA的无机盐培养基(MM)中振荡培养5 d,米曲霉菌株均未生长,对β-CP和3-PBA无降解;在富集培养基(GM)中振荡培养2 d,对100 mg/L的3-PBA转化或降解率为69.28%-99.58%不等,检测到3-苯氧基苄醇(3-PBlc)和羟基-3-苯氧基苯甲酸(HO-3-PBA)。【结论】食源米曲霉具有共代谢降解β-CP和3-PBA的共性,3-PBA为β-CP降解中间产物,米曲霉对3-PBA普遍具有较高的降解率。在3-PBA降解初期,米曲霉可将其短暂还原生成毒性相对较低的3-PBlc,同时,3-PBA逐渐羟基化生成水溶性更强的HO-3-PBA参与下游降解。     

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。     

高环多环芳烃降解菌的筛选及其降解特性

通过富集培养及平板升华法从本溪钢铁公司周边多环芳烃(PAHs)污染土壤中分离出7株PAHs降解菌。以芘和苯并[a]芘为底物进行摇瓶降解实验,结果表明:G1、G2和G3菌株对高环PAHs芘和苯并[a]芘均具有较强的降解能力。进一步研究此3株菌及混合菌对原状污染土壤中PAHs的降解能力,发现80 d时对总PAHs的降解顺序依次为:混合菌G2G1G3,其中混合菌对PAHs降解率较单菌分别提高了9.17%、11.49%和16.11%;4个处理对4~6环PAHs的降解率较对照组相比提高的倍数随着环数增加而增大;总PAHs的降解率与脱氢酶的活性呈正相关。电场影响G1、G2和G3菌株对PAHs降解,在1.0 V·cm~(-1)电场条件下,4环、5环及6环PAHs降解率较单纯微生物修复提高12.13%、13.35%和14.52%,说明3株菌具有较强的电场适应能力,可在高环PAHs污染土壤的电动-微生物修复中应用。形态学观察及16S rRNA序列比对分析表明,G1、G2、G3菌株分别为鞘氨醇单胞菌属(Sphingomonas sp.)、苍白杆菌属(Ochrobactrum sp.)和无色杆菌属(Achromobacter sp.)。     

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)。     

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。     

聚乙烯醇高效降解菌的筛选及降解特性研究

以聚乙烯醇为唯一碳源从环境中筛选获得了高效降解聚乙烯醇的微生物菌株XT11, 初步鉴定为假单胞菌属(Pseudomonas sp.)。对菌株Pseudomonas XT11的生长过程及PVA降解过程进行了研究, 发现该菌株在54 h内可将1 g/L的聚乙烯醇(PVA)降解。同时研究了温度、pH值及酵母膏浓度对该菌株降解PVA的影响, 结果表明其最适温度、pH值和酵母膏浓度分别为30℃、7.0和0.5 g/L。研究了PVA浓度对PVA降解率的影响, 发现随着PVA浓度的增大, PVA的降解率降低。     

Co-Metabolic Biodegradation of DBP by Paenibacillus sp. S-3 and H-2

Two di-n-butyl phthalate (DBP)-degrading strains, designated as S-3 and H-2, were isolated from DBP-polluted soil and both identified as Paenibacillus sp. When DBP was provided as the sole carbon source, about 45.5 and 71.7 % of DBP (100 mg/L) were degraded by strain S-3 and H-2, respectively, after incubation for 48 h. However, DBP (100 mg/L) was degraded completely by co-culture of strain S-3 and H-2 after incubation for 60 h. Four phthalic acid (PA) esters could be utilized by co-metabolism in the study and the degradation rates followed the order of dimethyl phthalate > diethyl phthalate > DBP > dioctyl phthalate. The metabolic pathway of DBP was elucidated based on the results of metabolites identification and enzyme assays. For strain S-3, DBP was degraded into butyl hydrogen phthalate which was degraded to PA by carboxyesterase further. But PA could be not hydrolyzed further because strain S-3 lacked 3,4-phthalate dioxygenase. Different with S-3, strain H-2 could hydrolyze PA into 3,4-dihydroxy-PA by 3,4-phthalate dioxygenase. Then 3,4-dihydroxy-PA was converted to protocatechuate and benzoic acid. Finally, the aromatic ring was cleavage and mineralized to CO₂ and H₂O. Above all, co-metabolism could increase the activity of 3,4-phthalate dioxygenase and accelerated the degradation of DBP. This study highlights an important potential use of co-metabolic biodegradation for the in situ bioremediation of DBP and its metabolites-contaminated environment.     

Screening of a beta-cypermethrin-degrading bacterial strain <Emphasis Type="Italic">Brevibacillus parabrevis</Emphasis> BCP-09 and its biochemical degradation pathway

A novel beta-cypermethrin (Beta-CP)-degrading strain isolated from activated sludge was identified as Brevibacillus parabrevis BCP-09 based on its morphological and physio-biochemical characteristics, and 16S rRNA gene analysis. Strain BCP-09 could effectively degrade Beta-CP at pH 5.0–9.0, 20–40 °C, and 10–500 mg L^?1 Beta-CP. Under optimal conditions (pH 7.41, 38.9 °C, 30.9 mg L^?1 Beta-CP), 75.87% Beta-CP was degraded within 3 days. Beta-CP degradation (half-life, 33.45 h) and strain BCP-09 growth were respectively described using first-order-kinetic and logistic-kinetic models. Seven metabolites were detected by high-performance liquid chromatography and gas chromatography-mass spectrometry- methyl salicylate, catechol, phthalic acid, salicylic acid, 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid, 3-phenoxybenzaldehyde, and 3-phenoxybenzoic acid (3-PBA). The major Beta-CP metabolite, 3-PBA was further degraded into phenol, benzoic acid, and 4-methylhexanoic acid. BCP-09 also degraded aromatic compounds such as phenol, catechol, and protocatechuic acid. Beta-CP appears to be mainly degraded into 3-PBA, which is continuously degraded into smaller benzene or chain compounds. Thus, strain BCP-09 could form a complete degradation system for Beta-CP and might be considered a promising strain for application in the bioremediation of environments and agricultural products polluted by Beta-CP.     

氯氰菊酯降解菌株L12的分离鉴定及降解特性

[目的]通过分离纯化氯氰菊酯降解菌,研究降解特性为实际应用提供理论依据.[方法]利用富集驯化培养技术分离菌株,通过形态、生理生化特征及16S rRNA基因序列分析鉴定菌株.测定培养液中氯氰菊酯的浓度和代谢产物以及菌体细胞的密度和细胞表面疏水性,研究菌株的降解特性.[结果]从生产氯氰菊酯的农药厂污水曝气池中,分离到1株能...     

Degradation of 3-Phenoxybenzoic Acid by a Bacillus sp

3-Phenoxybenzoic acid (3-PBA) is of great environmental concern with regards to endocrine disrupting activity and widespread occurrence in water and soil, yet little is known about microbial degradation in contaminated regions. We report here that a new bacterial strain isolated from soil, designated DG-02, was shown to degrade 95.6% of 50 mg·L⁻¹ 3-PBA within 72 h in mineral salt medium (MSM). Strain DG-02 was identified as Bacillus sp. based on the morphology, physio-biochemical tests and 16S rRNA sequence. The optimum conditions for 3-PBA degradation were determined to be 30.9°C and pH 7.7 using response surface methodology (RSM). The isolate converted 3-PBA to produce 3-(2-methoxyphenoxy) benzoic acid, protocatechuate, phenol, and 3,4-dihydroxy phenol, and subsequently transformed these compounds with a q _max, K _s and K _i of 0.8615 h⁻¹, 626.7842 mg·L⁻¹ and 6.7586 mg·L⁻¹, respectively. A novel microbial metabolic pathway for 3-PBA was proposed on the basis of these metabolites. Inoculation of strain DG-02 resulted in a higher degradation rate on 3-PBA than that observed in the non-inoculated soil. Moreover, the degradation process followed the first-order kinetics, and the half-life (t _1/2) for 3-PBA was greatly reduced as compared to the non-inoculated control. This study highlights an important potential application of strain DG-02 for the in situ bioremediation of 3-PBA contaminated environments.     

Biodegradation of fenvalerate and 3-phenoxybenzoic acid by a novel Stenotrophomonas sp. strain ZS-S-01 and its use in bioremediation of contaminated soils

A bacterial strain ZS-S-01, newly isolated from activated sludge, could effectively degrade fenvalerate and its hydrolysis product 3-phenoxybenzoic acid (3-PBA). Based on the morphology, physiological biochemical characteristics, and 16 S rDNA sequence, strain ZS-S-01 was identified as Stenotrophomonas sp. Strain ZS-S-01 could also degrade and utilize deltamethrin, beta-cypermethrin, beta-cyfluthrin, and cyhalothrin as substrates for growth. Strain ZS-S-01 was capable of degrading fenvalerate rapidly without a lag phase over a wide range of pH and temperature, even in the presence of other carbon sources, and metabolized it to yield 3-PBA, then completely degraded it. No persistent accumulative product was detected by HPLC and GC/MS analysis. Studies on biodegradation in various soils showed that strain ZS-S-01 demonstrated efficient degradation of fenvalerate and 3-PBA (both 50 mg·kg⁻¹) with a rate constant of 0.1418–0.3073 d⁻¹, and half-lives ranged from 2.3 to 4.9 days. Compared with the controls, the half-lives for fenvalerate and 3-PBA reduced by 16.9–156.3 days. These results highlight strain ZS-S-01 may have potential for use in bioremediation of pyrethroid-contaminated environment.     

硝基苯类化合物微生物降解研究进展

硝基苯类化合物是一类具有稳定化学性质、高毒性和易在生物体内积累的优先污染物.微生物降解在硝基苯类化合物废水废气治理和污染环境修复方面具有明显优势.从降解菌的驯化筛选、降解途径、降解机理、共代谢、趋化性和分子遗传学角度,阐述了硝基苯类化合物微生物降解研究的最新进展,指出应进一步加强工程菌的构建及其应用开发研究.在硝基苯类化合物污染环境的微生物修复方面,共代谢和混合菌株的协同作用具有重要的应用前景.     

Co-metabolic degradation of tribenuron methyl,a sulfonylurea herbicide,by Pseudomonas sp. strain NyZ42

A co-metabolic degradation of tribenuron methyl bacterial strain NyZ42 was isolated from polluted agricultural soil and classified as genus Pseudomonas by its 16S rRNA gene sequencing. The degradation efficiency of tribenuron methyl was about 80% of the originally supplemented 200 mg l⁻¹ tribenuron methyl in liquid minimal medium within four days, when either glucose or succinate was used as a supplemental carbon source. Three intermediates formed during the degradation of tribenuron methyl mediated by strain NyZ42 were captured by LC-MS, and two alternative pathways were proposed for the microbial mediated tribenuron methyl degradation, via either cleavage of the sulfonylurea bridge or saponification of alkyl-group. Furthermore, inoculation of strain NyZ42 enhanced the degradation of tribenuron methyl in the sterilized soil samples, although the biodegradation/co-metabolism ability of NyZ42 was not obvious in the nonsterilized soil samples when compared with the indigenous microbial consortium under current laboratory conditions.     

Secretory production of biologically active rat interleukin-2 by Clostridium acetobutylicum DSM792 as a tool for anti-tumor treatment

A bacterium, isolated from contaminated soils around a chemical factory and named strain DSP3 was capable of biodegrading both chlorpyrifos and 3,5,6-trichloro-2-pyridinol. Based on the results of phenotypic features, phylogenetic similarity of 16S rRNA gene sequences, DNA G+C content, and DNA homology between strain DSP3 and reference strains, strain DSP3 was identified as Alcaligenes faecalis. Chlorpyrifos was utilized as the sole source of carbon and phosphorus by strain DSP3. We examined the role of strain DSP3 in the degradation of chlorpyrifos and 3,5,6-trichloro-2-pyridinol under different culture conditions. Parathion and diazinon could also be degraded by strain DSP3 when provided as the sole sources of carbon and phosphorus. An addition of strain DSP3 (10(8)cells g(-1)) to soil with chlorpyrifos (100 mg kg(-1)) resulted in a higher degradation rate than the one obtained from non-inoculated soils. Different degradation rates of chlorpyrifos in six types of treated soils suggested that soils used for cabbage growing in combination with inoculation of strain DSP3 showed enhanced microbial degradation of chlorpyrifos.