盐碱土壤PAHs 降解菌的筛选鉴定及其降解特性

采用富集培养的方法,从天津大港油田PAHs污染盐碱化土壤中分离出一株能以菲、芘为唯一碳源和能源的优势菌TJB5。经形态观察和16S rDNA序列分析结果表明,该菌株为成团泛菌(Pantoea agglomerans)。采用液体培养的方法,研究了pH、盐度、菲芘的初始浓度对TJB5菌株降解菲芘效果的影响,确定了最佳降解条件。结果表明,该菌对菲、芘的降解具有较广泛的pH、盐度范围和良好的降解效果。在菲、芘浓度分别为50 mg/L、pH 6.8-9.5、盐度2%-3%、温度30°C条件下,接种15 d后菲降解率在93.3%以上,芘降解率在20%以上。     

高效芘降解菌N12的分离鉴定与降解特性

以芘为目标降解物,利用选择性富集培养方法,从沈抚灌区污染土壤中分离到一株高效芘降解菌N12,经生理生化试验和16S rDNA测序分析,该菌被鉴定为分枝杆菌属（Mycobacterium sp.）.菌株N12能以菲、苊、芴和芘为唯一碳源和能源生长,不能以蒽、萘和苯并芘为唯一碳源和能源生长.在菲和芘共同存在的情况下菌株N12可降解苯并芘,9 d内对苯并芘降解率可达79.0%.摇瓶降解试验表明,菌株N12可在7 d内将100 mg·L^-1的芘降解94.4%,14 d内将其完全降解;可将600 mg·L^-1的芘在7 d内降解56.1%,14 d内降解95.5%.添加葡萄糖可促进N12对芘的降解.菌株N12是一株优良的多环芳烃降解菌,可作为多环芳烃污染土壤生物修复的菌种资源.     

多环芳烃降解菌的筛选与降解能力测定

从本溪多环芳烃(PAHs)污染土壤中经富集培养筛选出8株PAHs降解菌,研究了8株菌及其等比例混合培养对菲、芘和苯并[a]芘的降解能力。结果表明,在28℃,培养基中菲、芘和苯并[a]芘的浓度分别为50、50和5mg·L-1的复合底物条件下,培养28d后,菌株B3的降解效果最好,对菲、芘和苯并[a]芘的降解率分别为88.4%、54.0%和68.4%,8株菌的混合培养对菲、芘和苯并[a]芘的降解率分别为87.7%、35.3%和42.0%;经生理生化实验和16SrRNA序列比对,初步鉴定B3菌为假单胞菌属(Pseudomonas sp.)。     

多环芳烃降解菌X20的鉴定及降解特性

从多环芳烃降解高效的混合菌群中分离筛选到1株多环芳烃降解菌X20,经形态观察和16SrRNA序列分析,属于假单胞菌(Pseudomonas sp.)。采用室内摇瓶培养的方法,研究了该菌在不同环境条件下对菲和芘的降解。结果表明:弱碱环境有利于菌株X20对菲和芘的降解,最适pH为8.0;葡萄糖对菲芘降解率的影响呈抛物线变化,当葡萄糖浓度为0.2%时,X20对菲和芘的降解达到最高;X20对菲和芘的降解率随其初始浓度的上升而降低,菲和芘在初始浓度为10、20和40mg.L-1时的7d降解率分别为56.3%、39.25%、29.75%和41.8%、29.55%、23.50%,芘对X20降解的抑制强度高于菲。本研究结果将为构建高效的多环芳烃降解菌群,提高多环芳烃原位污染土壤的生物修复效果奠定基础。     

多环芳烃降解菌的筛选、鉴定及降解特性

【目的】多环芳烃(PAHs)是一类普遍存在于环境中且具有高毒性的持久性有机污染物,高效降解菌的筛选对利用生物修复技术有效去除环境中的多环芳烃具有重要意义。研究拟从供试菌株中筛选多环芳烃高效降解菌,并分析其降解特性,为多环芳烃污染环境的微生物修复提供资源保障和科学依据。【方法】采用平板法从25株供试菌株中筛选出以菲和芘为唯一碳源和能源的高效降解菌,经16S rRNA基因序列进行初步鉴定,通过单因素实验法分析其在液体培养基中的降解特性。【结果】筛选出的3株多环芳烃高效降解菌SL-1、02173和02830经16S rRNA基因序列分析,02173和02830分别与假单胞菌属中的Pseudomonas alcaliphila和Pseudomonas corrugate同源性最近,SL-1为本课题组发表新类群Rhizobium petrolearium的模式菌株;降解实验表明,菌株SL-1 3 d内对单一多环芳烃菲(100 mg/L)和芘(50 mg/L)的降解率分别达到100%和48%,5 d后能够降解74%的芘;而其3 d内对混合PAHs中菲和芘的降解率分别为75.89%和81.98%。菌株02173和02830 3 d内对混合多环芳烃中萘(200 mg/L)、芴(50 mg/L)、菲(100 mg/L)和芘(50 mg/L)的降解率均分别超过97%。【结论】筛选出的3株PAHs降解菌SL-1、02173和02830不仅可以高效降解低分子量PAHs,还对高分子量PAHs具有很好的降解潜力。研究表明,由于共代谢作用低分子量多环芳烃可促进高分子量多环芳烃的降解,而此时低分子量多环芳烃的降解将受到抑制。     

芘高效降解菌的分离鉴定及其降解特性

以芘为唯一碳源,采用富集培养方法,从沈抚灌区石油污染土壤中分离得到一株芘降解菌ZQ5.根据形态学观察、生理生化鉴定和16S rDNA序列分析结果,将菌株ZQ₅鉴定为寡养单胞菌属（Stenotrophomonas sp.）.采用摇瓶振荡培养方法研究该菌株降解芘的特性及培养条件对降解效能的影响.结果表明：菌株ZQ₅在30 ℃振荡培养10 d后,对100 mg·L^-1的芘降解率为91.2%,加入水杨酸（100 mg·L^-1）作为共代谢底物可以提高菌株ZQ₅对芘的降解率.当培养基pH为7～8、盐浓度不高于2%时,有利于菌株ZQ₅降解效能的发挥.     

高分子量多环芳烃降解菌筛选及在土壤电动-生物修复中应用

采用富集培养和多环芳烃双加氧酶基因检测方法,从焦化场地多环芳烃污染土壤分离筛选出9株PAHs降解菌。以高分子量多环芳烃芘为唯一碳源进行摇瓶降解实验,结果表明,J6、S5、S4、S2和B4对芘具有较好的降解能力,21 d时芘降解率均达55%以上,其中B4处理芘的降解率最高,达到70.2%。进一步研究了该5株菌及其混合菌对土壤中芘的降解效果,发现混合菌的降解效果高于单菌的降解效果,其中混合菌H4和单菌B4的降解效果较好,49 d时混合菌H4和单菌B4处理土壤中芘的降解率达29.3%和18.3%。经过16S rRNA基因序列比对,鉴定J6菌株为赤红球菌(Rhodococcus ruber),S5为芽孢杆菌属(Bacillus sp.),S4和S2是鞘脂单胞菌属(Sphingopyxis sp.),B4为假单胞菌属(Pseudomonas sp.)。在电场条件下,混合菌H4和单菌B4处理微生物数量及活性均显著提高,芘的降解率较单独H4和B4处理提高33.0%和20.1%,说明筛选出的5株高分子量多环芳烃降解菌具有较强的电场适应能力,可在高分子量多环芳烃污染土壤电动-微生物修复中应用。     

盐渍化土壤翅碱蓬根际促生细菌的筛选及对多环芳烃的降解特性

为了强化多环芳烃污染盐渍化土壤的原位植物-微生物修复的应用,获得促进植物降解多环芳烃的高效菌种资源,本研究采用富集培养的方法,从多环芳烃污染的大港油田翅碱蓬根际分离到1株能以菲、芘为唯一碳源同时分泌1-氨基环丙烷~(-1)-脱氨酶的优势菌株B~(-1),通过形态观察和16S rRNA序列分析鉴定该菌株,并对其潜在的促生能力和菲、芘的降解特性进行分析。16S rRNA序列分析结果表明,该菌株为动性球菌属(Planococcus sp.),可产生3-吲哚乙酸,且具有溶磷能力。同时对菲、芘的降解具有较广泛的p H值和盐浓度范围,在菲和芘浓度均为50 mg·L~(-1),p H 8.0,盐度2%时,7 d对菲、芘的降解率为66.6%和52.0%。表面活性剂烷基糖苷的添加使菲、芘降解效率分别提高至94.2%和78.8%。     

一株高效降解芘的细菌分离、鉴定及其降解效果

摘要：【目的】获得高效降解高分子量多环芳烃的细菌,并研究其对多环芳烃的降解能力。【方法】利用富集培养和芘升华平板方法,从焦化厂污染土壤中分离多环芳烃降解细菌,对分离菌株通过形态特征、16S rRNA基因和gyrb基因序列相似性分析进行鉴定,并研究该菌对高分子量多环芳烃（HMW-PAHs）的降解效果。【结果】筛选到一株能以芘、苯并蒽、屈、苯并芘、茚并芘、苯并苝、荧恩为碳源和能源生长并降解这些底物的菌株HBS1,该菌株的16S rRNA基因和gyrb基因序列与Gordonia amicalis的相应基因的相似     

芘高效降解菌的分离鉴定及其降解特性的研究

以芘为惟一碳源.采用寓集培养方法,从沈抚灌区石油污染土壤中分离得到一株芘降解菌B05.根据形态学观察、生理牛化鉴定和16S rDNA序列分析结果.将菌株B05鉴定为Aminobacter ciceronei.在芘初始浓度为1mg/L的液体无机盐培养基中,培养10d,菌株B05对芘的降解率为51%;在芘初始浓度为1mg/kg的土壤培养基条件下,培养30d,菌株B05对芘的降解率可达51%;在芘初始浓度为50mg/L的乙醇液体培养基条件下,培养5d,菌株B05对芘的降解率可达25.9%.对菌株培养条件进行优化,经SlideWrite统计软件拟合,菌株B05在牛肉膏蛋白胨液体培养基上的最适生长pH值为7.3,最适生长温度为32.5℃,最适装液量为25.4mL(150mL三角瓶).     

芘在土壤中的共代谢降解研究

高分子量多环芳烃（PAHs)的降解通常以共代谢方式进行,研究比较了高分子量多环芳烃代表种类芘作为唯一C源和能源的降解过程和有共代谢底物存在下的降解过程,结果表明,25d后前者中芘的降解率57％,而后者中芘的降解率为80％,且有共代谢底物存在下,芘在降解过程中关衰期缩短;水扬酸,邻苯二甲酸,琥珀酸钠能作为共代谢底物提高芘的降解率,琥珀酸钠效果最好,芘和低要子量多环芳烃之间也有共代谢关系,菲促进了芘的降解,但萘未出现同样的结果,此外,这阐明了共代谢原理和适宜作高分子量多环芳烃共代谢底物的物质。     

共基质对10株细菌降解芘的作用

从石油污染的污泥中分离出10株细菌(SB01—SB10),研究了有(或无)共基质(葡萄糖Glu,或菲PHE)对细菌降解芘(PYR)的影响.结果表明：当以PYR为唯一碳源和能源时(MS₁),SB01的PYR降解率最高,5 d可降解30.4%;以Glu为共代谢基质时(MS₂),SB09的PYR降解率最高,可达37.7%;以PHE为共代谢基质时(MS₃),SB10的PYR降解率为50.2%.Glu抑制SB01、SB03对PYR的降解,对SB01抑制作用最明显,使SB01的PYR降解率降低7.9%;Glu对SB02、SB07、SB08、SB10降解率无明显促进或抑制作用.PHE对细菌降解PYR均有促进作用,对SB10的促进作用最明显,使其降解率提高298%.Glu与PHE对SB04和SB09降解PYR的促进作用无显著差异,而对其它各菌株而言,PHE对PYR降解的促进作用大于Glu.     

Phenanthrene stimulates the degradation of pyrene and fluoranthene by <Emphasis Type="Italic">Burkholderia</Emphasis> sp. VUN10013

Pyrene and fluoranthene, when supplied as the sole carbon source, were not degraded by Burkholderia sp. VUN10013. However, when added in a mixture with phenanthrene, both pyrene and fluoranthene were degraded in liquid broth and soil. The amounts of pyrene and fluoranthene in liquid media (initial concentrations of 50 mg l⁻¹ each) decreased to 42.1% and 41.1%, respectively, after 21 days. The amounts of pyrene and fluoranthene in soil (initial concentrations of 75 mg kg⁻¹ dry soil each) decreased to 25.8% and 12.1%, respectively, after 60 days. None of the high molecular weight (HMW) polycylic aromatic hydrocarbons (PAHs) tested adversely affected phenanthrene degradation by this bacterial strain and the amount of phenanthrene decreased rapidly within 3 and 15 days of incubation in liquid broth and soil, respectively. Anthracene also stimulated the degradation of pyrene or fluoranthene by Burkholderia sp. VUN10013, but to a lesser extent than phenanthrene. The extent of anthracene degradation decreased in the presence of these HMW PAHs.     

Production of metabolites in the biodegradation of phenanthrene, fluoranthene and pyrene by the mixed culture of Mycobacterium sp. and Sphingomonas sp

The effects of the mixed culture of Mycobacterium sp. strain A1-PYR and Sphingomonas sp. strain PheB4 on the degradation characteristics of single polycyclic aromatic hydrocarbon were investigated. In the mixed bacterial culture, phenanthrene, fluoranthene and pyrene were degraded by 100% at Day 3, 71.2% and 50% at Day 7, respectively. Compared to their respective pure cultures, the degradation of phenanthrene and fluoranthene decreased, but that of pyrene increased significantly. Based on GC-MS analysis, eight and six new metabolites were produced from the biodegradation of phenanthrene and fluoranthene, respectively, while only two new metabolites were formed from pyrene. To our knowledge, this is the first report that the mixed bacterial culture could increase the diversity of metabolites from PAH, but the diverse metabolite pattern was not necessarily beneficial to the degradation of the recalcitrant PAH. The enhancement on pyrene degradation was possibly attributed to the rapid growth of strain PheB4.     

PAH Degradation Capacity of Soil Microbial Communities—Does It Depend on PAH Exposure?

Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous pollutants of the environment. But is their microbial degradation equally wide in distribution? We estimated the PAH degradation capacity of 13 soils ranging from pristine locations (total PAHs ≈ 0.1 mg kg^?1) to heavily polluted industrial sites (total PAHs ≈ 400 mg kg^?1). The size of the pyrene- and phenanthrene-degrading bacterial populations was determined by most probable number (MPN) enumeration. Densities of phenanthrene degraders reflected previous PAH exposure, whereas pyrene degraders were detected only in the most polluted soils. The potentials for phenanthrene and pyrene degradation were measured as the mineralization of ¹⁴C-labeled spikes. The time to 10% mineralization of added ¹⁴C phenanthrene and ¹⁴C pyrene was inversely correlated with the PAH content of the soils. Substantial ¹⁴C phenanthrene mineralization in all soils tested, including seven unpolluted soils, demonstrated that phenanthrene is not a suitable model compound for predicting PAH degradation in soils. ¹⁴C pyrene was mineralized by all Danish soil samples tested, regardless of whether they were from contaminated sites or not, suggesting that in industrialized areas the background level of pyrene is sufficient to maintain pyrene degradation traits in the gene pool of soil microorganisms. In contrast, two pristine forest soils from northern Norway and Ghana mineralized little ¹⁴C pyrene within the 140-day test period. Mineralization of phenanthrene and pyrene by all Danish soils suggests that soil microbial communities of inhabited areas possess a sufficiently high PAH degradation capacity to question the value of bioaugmentation with specific PAH degraders for bioremediation.     

Effects of soil amendment with different carbon sources and other factors on the bioremediation of an aged PAH-contaminated soil

Carbon supplementation, soil moisture and soil aeration are believed to enhance in situ bioremediation of PAH-contaminated soils by stimulating the growth of indigenous microorganisms. However, the effects of added carbon and nitrogen together with soil moisture and soil aeration on the dissipation of PAHs and on associated microbial counts have yet to be fully assessed. In this study the effects on bioremediation of carbon source, carbon-to-nitrogen ratio, soil moisture and aeration on an aged PAH-contaminated agricultural soil were studied in microcosms over a 90-day period. Additions of starch, glucose and sodium succinate increased soil bacterial and fungal counts and accelerated the dissipation of phenanthrene and benzo(a)pyrene in soil. Decreases in phenanthrene and benzo(a)pyrene concentrations were effective in soil supplemented with glucose and sodium succinate (both 0.2 g C kg⁻¹ dry soil) and starch (1.0 g C kg⁻¹ dry soil). The bioremediation effect at a C/N ratio of 10:1 was significantly higher (P < 0.05) than at a C/N of either 25:1 or 40:1. Soil microbial counts and PAH dissipation were lower in the submerged soil but soil aeration increased bacterial and fungal counts, enhanced indigenous microbial metabolic activities, and accelerated the natural degradation of phenanthrene and benzo(a)pyrene. The results suggest that optimizing carbon source, C/N ratio, soil moisture and aeration conditions may be a feasible remediation strategy in certain PAH contaminated soils with large active microbial populations.     

Pyrene and Phenanthrene Influence on Soil Microbial Populations

Two studies were conducted to evaluate microbial populations in polycyclic aromatic hydrocarbon-contaminated soil. Captina silt loam was freshly exposed to (1) 0 or 2000 mg pyrene/kg and sampled after 10- and 61-wk incubation and (2) 0 or 505 mg pyrene + 445 mg phenanthrene/kg and sampled after a 21-wk incubation. Microbial numbers were determined by plate-count techniques. Isolated bacteria, selected degraders, and wholesoil extracts were analyzed by fatty acid methyl ester analysis (FAME). In the pyrene experiment, pyrene did not affect total bacterial or fungal numbers, but pyrene degraders increased from undetectable levels to 7.09 log₁₀ degraders/g in the contaminated soil. The FAME analysis of bacterial isolates detected no pyrene effect, but wholesoil FAME indicated an increase in the contaminated soil of a fatty acid characteristic of protozoa and a major fatty acid detected in isolated degraders. In the pyrene + phenanthrene experiment, the contaminants had no impact on bacterial, fungal, or actinomycete numbers but increased degrader numbers. No effect of pyrene + phenanthrene was detected by isolate FAME, but whole-soil FAME indicated an effect similar to that in the pyrene experiment. The results indicate that pyrene, although not impacting microbial numbers, may have altered the soil microbial composition and that Captina silt loam can develop an effective degrader population under tested conditions.     

Pyrene and Phenanthrene Influence on Soil Microbial Populations

Two studies were conducted to evaluate microbial populations in polycyclic aromatic hydrocarbon-contaminated soil. Captina silt loam was freshly exposed to (1) 0 or 2000?mg pyrene/kg and sampled after 10- and 61-wk incubation and (2) 0 or 505?mg pyrene + 445?mg phenanthrene/kg and sampled after a 21-wk incubation. Microbial numbers were determined by plate-count techniques. Isolated bacteria, selected degraders, and wholesoil extracts were analyzed by fatty acid methyl ester analysis (FAME). In the pyrene experiment, pyrene did not affect total bacterial or fungal numbers, but pyrene degraders increased from undetectable levels to 7.09 log₁₀ degraders/g in the contaminated soil. The FAME analysis of bacterial isolates detected no pyrene effect, but wholesoil FAME indicated an increase in the contaminated soil of a fatty acid characteristic of protozoa and a major fatty acid detected in isolated degraders. In the pyrene + phenanthrene experiment, the contaminants had no impact on bacterial, fungal, or actinomycete numbers but increased degrader numbers. No effect of pyrene + phenanthrene was detected by isolate FAME, but whole-soil FAME indicated an effect similar to that in the pyrene experiment. The results indicate that pyrene, although not impacting microbial numbers, may have altered the soil microbial composition and that Captina silt loam can develop an effective degrader population under tested conditions.