高效石油降解菌群的构建及其固定化研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
随着石油污染的日益加重,高效无污染的生物修复技术逐渐成为治理石油污染的重要方法之一,受到广泛关注。石油是由饱和烃、芳香烃类化合物和少量的沥青质、树脂类等组成的复杂混合物,而单菌株所能代谢的石油组分通常十分有限,难以将石油从环境中彻底去除。混合菌群之间的协同作用有助于提高微生物对石油的降解能力。因此如何利用不同菌种间的相互作用,优化组合出合理、高效的降解菌群是目前的研究热点。固定化微生物技术可以使微生物高度密集并保持其生物活性,强化对石油的降解效果。
     本研究把实验室已筛选得到的烷烃降解菌GS3C、菲降解菌GY2B和芘降解菌(GP3A和GP3B)进行驯化,结果表明这些菌能以原油为唯一碳源进行良好的生长繁殖,并对原油有一定的降解效果,去除率都在30%以上。经过GC-MS分析,GS3C能基本去除原油中的直链烷烃化合物, GY2B对芳烃类化合物有很好的降解效果,GP3A对C<20的中短链烷烃化合物和芳烃类化合物有一定的降解作用,GP3B对烷烃类和芳烃类化合物的降解效果一般。
     利用这四种菌构建高效混合菌群,筛选出最优混合菌G8,对石油的去除率达到68.76%,比单菌株提高了近30%。经GC-MS分析, G8保留了单菌株GS3C和GY2B的降解特性,能基本去除原油中的烷烃类化合物,同时对芳烃类化合物表现出较强的降解能力,通过三种菌的共同作用增强了对原油的完全去除能力。
     对混合菌G8的降解性能进行研究发现混合菌G8的最佳混合比例为1:1:1,其最适生长条件为:温度为30℃,初始pH值为7.0,接种量为4%,石油浓度为2000 mg/L,在最佳环境条件下降解5d后使石油去除率达到69.20%。
     采用稻草秸秆和玉米秸秆2种载体对混合菌G8进行表面吸附固定,结果表明固定化菌对原油的去除效果比游离菌或者载体与菌液的混合物好,不灭菌的秸秆对原油的去除效果都比灭菌的好。其中稻草秸秆固定化菌的去除率达到90%~95%,玉米秸秆固定化菌的去除率为95%~98%,都比单纯的游离菌G8提高了近40%。选择不灭菌的玉米秸秆为最佳载体固定混合菌G8,对原油的去除率达到98.19%,效果最佳。
With the oil pollution becoming more and more serious, biodegradation has become an important method for controlling the oil pollution, because it is efficient and pollution-free. Oil is a complex mixture which composed of saturated hydrocarbon, aromatic compounds, some asphaltene and resin. Single strains have limited ability of metabolizing oil components, so it is difficult to completely remove the oil from the environment. The synergies of mixed strains help to improve the ability of degradation. Therefore, the research focus is how to use the interaction between different strains to build a reasonable and efficient degradation flora. Immobilized microorganism technology can enhance oil degradation by keeping high density micro-organisms and biological activity.
     In this study, the alkane degrading bacteria GS3C, phenanthrene degrading bacteria GY2B and pyrene degrading bacteria (GP3A and GP3B) were domesticated by crude oil. The results show that these strains can grow and metabolize by using crude oil as sole carbon source. So they can degrade crude oil and the removal ratio reaches 30%. GC-MS analysis shows that GS3C can basically remove the straight-chain alkane compounds in crude oil. GY2B has a good degradation of the aromatic compounds. GP3A can remove the short-chain alkanes and aromatic compounds and GP3B have less degradation of alkanes and aromatic compounds.
     Efficient mixed strains were constructed by using these four strains. The optimal mixed strains G8 was selected and its oil removal ratio is 68.76%, nearly 30% higher than the single strains. The GC-MS analysis indicated that G8 retained the degradation characteristics of GS3C and GY2B. It can basically remove the alkane compounds in crude oil and has a good degradation on the aromatic compounds. Through the joint of three kinds of strains, mixed strains G8 have more capacity of degrading the crude oil.
     The results show the best mixing ratio of mixed bacteria G8 is GS3C:GY2B:GP3B= 1:1:1. The removal efficiency of combination G8 reached 69.20% in 5 days when the initial crude oil concentration was 2000 mg/L, which was 30% higher than that of individual bacterial strain. The optimum conditions for G8 growth were 30℃,initial pH 7, and 4% inoculation volume.
     The mixed strains G8 was adsorbed and immobilized by rice straw and corn stalks. The results showed that the immobilized strains have better removal of oil than free strain or the mixture of carrier and strains and the no-sterilized straw have better removal of the oil than sterilization one. The mixed strains G8 which immobilized by rice straw was removed 90%~95% of oil. The one immobilized by corn stalk was removed 95%~98% of oil, nearly 40% higher than the one by non-immobilized G8 . The non-sterile corn stalks as the best carrier, the removal of crude oil reached 98.19 %.
引文
[1] Pawl T.K., Edward J.C. Hydrocarbon contaminated and ground water[J]. Lewis Publishers, INC, 1991:187-253.
    [2] Pritehard P.H., Costa C.F. EPA’s Alaska oil spill bioremediation project[J]. Environ Sci Technol,1991,25(3): 372-379.
    [3] Farinazleen M.G., Raja N.Z.A.R., Abu B.S., et al. Mahiran Basri.Biodegradation of hydrocarbons in soil by microbial consortium [J]. International Biodeterioration & Biodegradation, 2004, 54: 61-67.
    [4]谢丹平,尹华,彭辉,等.混合菌对石油的降解[J].应用与环境生物学报, 2004,10(2): 210-214.
    [5]赵晴.疏水性石油烃降解菌强化降解系统的构建及其降解能力研究[D].武汉大学, 2005.
    [6]胡凌燕,孙东平,邵涛,等.混合菌群的筛选及其与白腐真菌串联降解石油的效果初探[J].化学与生物工程, 2007, 24(5):34-37
    [7] Supaphol S, Panichsakpatana S, Trakulnaleamsai S, et al. The selection of mixed microbial inocula in environmental biotechnology: Example using petroleum contaminated tropical soils[J]. Journal of Microbiological Methods, 2006, 65: 432-441
    [8]司友斌,彭军.固定化微生物技术及其在污染土壤修复中的应用[J].土壤, 2007, 39 (5): 673-676
    [9]袁红莉,杨金水,王占生,等.降解石油微生物菌种的筛选及降解特性[J].中国环境科学, 2003, 23(2): 157-161.
    [10] Truax D.D., Brittu R., Sherrard J.H. Bench-scalt studies of reactor-based treatment of fuel-contaminated soil[J].Waste Management, 1995,15(5-6), :351-357
    [11]何良菊,魏德州,张维庆.土壤微生物处理石油污染的研究[J].环境科学进展,1999,7(3):110-115
    [12]陈尧.中国近海石油污染现状及防治[J].工业安全与环保,2003,29(11):20-24
    [13]高廷耀,顾国维.水污染控制工程(上册) [M].北京:高等教育出版社,1999.
    [14] Madsen E.L. Determining in situ biodegradation: Facts and Challenges [J]. Envrion. Sci. Technol. , 1991,25 (10):1663-1672
    [15]陈燕,李寅等.环境和营养条件对煤油生物降解的影响[J].应用与环境生物学报,2002,8(2):184-189.
    [16] Bragg J.R. Effectiveness of biodegradation for the exxon valdez oil spill [J]. Nature, 1994,368 :413-418.
    [17]姜昌亮.石油污染土壤长料堆式移位生物修复技术研究[J].应用生态学报,2001,12(2):279-282.
    [18]任华峰,单德臣,李淑芹.石油污染土壤生物修复技术的研究进展[J].东北农业大学学报, 2004, 35(3):373-376
    [19]李丽,张利平,张元亮.石油烃类化合物降解菌的研究概况[J].微生物学通报,2001, 28(5):89-92.
    [20]姚伟静,高效除油微生物菌株的筛选及表面活性剂增强生物降解石油烃的研究[D].重庆大学,2007.
    [21] Ijah U.J. Studies on relative capabilities of bacterial and yeast isolates from tropical soil in degrading crude oil [J]. Waste Management, 1998, 18(5):293-299
    [22]丁明宇,黄健,李永祺.海洋微生物降解石油的研究[J].环境科学学报,2001, 21(1): 85-88.
    [23] Pinholt Y, Struwe S, Kjoller A. Microbial Changes During Oil Decomposition in Soil [J]. Holartic Ecol., 1979, 2: 195-200.
    [24]廖有贵.高效石油降解菌去除石油污染土壤中的油[D].湘潭大学, 2007.
    [25] Kiesele L.U. Efficient and cost-effective purification of groundwater polluted by polycyclic aromatic hydroearbons experience with a cokeplant hazardous waste site. Altlasten Spektrum, 1997, 6(5):214-217.
    [26] Sidorov D.G., Borzenkov I.A., Ibatullin R.R. A field experiment on decontamination of oil polluted soil employing hydrocarbon-oxidizing microorganisms[J]. Prikl Biokhim Mikrobiol, 1997, 33(5):497-502.
    [27]陈国华.水体油污染治理[M].化学工业出版社,2001,1-27
    [28]李习武,刘志培.石油烃类的微生物降解[J].微生物学报,2002,42(6):764-767
    [29] Anders R.J., Lukas Y.W., Hauke H.Principles of microbial PAHs degradation in soil[J].Environmental Pollution,2005,133(1):71-84
    [30] Van Beilen J.B.,Wubbolts M.G. Genetics of alkane oxidation by pseudomonasoleovorans[J]. Biodegradation, 1994,5(3-4):161-174
    [31]孙铁珩,周启星,李培军.污染生态学[M].北京:科学出版社,2001:309-368.
    [32]郑金秀.高效石油烃降解菌群的构建及其在生物修复中的强化作用研究[D].武汉大学,2005
    [33]夏北成.环境污染物生物降解[M].化学工业出版社,2002,123-135
    [34] Chaineau C., Morel J., Oudot J. Microbial Degradation in Soil Microcosms of Fuel oil Hydrocarbons from Drilling Cuttings [J]. Environ Sci . Technol . , 1995, 29: 1615-1621.
    [35] Atlas R., Bartha R. Microbial Ecology [M].Third Edition The Enjam in/ Cummings Publishing Co. 1993.
    [36]苏荣国,牟伯中,王修林,等.微生物对石油烃的降解机理及影响因素[J].化工环保,2001,21(4):205-208.
    [37] Del’Arco J.P., de Franca F.P. Influence of oil contamination levels on hydrocarbon biodegradation in sandy sediment. Environmental Pollution,2001,110:515-519。
    [38]金文标,末莉辉,董晓利,等.油污土壤微生物治理的影响因素[J].污染防治技术, 1998, 10:27-28
    [39] Margesin R. Potential of cold-adapted microorganisms for bioremediation of oil-polluted Alpine soils[J]. International Biodeterioration and Biodegradation, 2000, 46(1):3-10.
    [40] Ward D.M., Atlas R.M., Boehm P.D., et al . Microbial biodegradation and the chemical evolution of Amoco Cadiz oil pollutants [J]. Ambio. , 1980, (9): 277 - 283.
    [41] Salmon C., Crabos J.L., Sambuco J.R., et al. Artificial wetland performances in the purification effciency of hydroearbon wastewater[J].Wate,Air,and Soil Pollution, 1998,104(3-4):313-329.
    [42]齐永强,王红旗,刘敬奇.土壤石油微生物降解影响因子的正交实验分析[J].地球学报, 2003, 24(3): 279-284
    [43] Rahman S.M.K., Rahman-Thahira J.,Kourkoutas Y.,et al. Enhanced bioremediation of n-alkane in petroleum sludge using bacterial consortium amended with rhamnolipid and micronutrients[J]. Bioresource Technology, 2003,90(2):159-168.。
    [44] Rahman S.M.K.,Rahman-Thahira J.,Lakshmanaperumalsamy P.,et al. Towards efficient crude oil degradation by a mixed bacterial consortium[J]. Bioresource Technology, 2002,85(3):257-261.
    [45]魏德洲,秦煌民. H2O2在石油污染土壤微生物治理过程中的作用[J].中国环境科学, 1997, 17(5): 429-432
    [46]李文利,王忠彦,胡永松.土壤和地下水石油污染的生物治理[J].重庆环境科学,1999, 21(2):35-37
    [47] Churchill P.F., Dudley R.J., Churchill S.A. Surfactant-enhanced bioremediation[J]. Waste Management, 1995,15(5/6) : 371-377.
    [48]魏德洲,秦煜民.表面活性剂对石油污染物生物降解的影响[J].东北大学学报(自然科学版) , 1998.19 (2):125-127.
    [49] Grimberg S.J., Stringfellow W.T., Altken M.D. The biodegradation of phenanthrene by Pseudomonas stutzeri P16 in the presence of a nonionic surfactant[J].Applied Environmental Microbiology,1996,62(7):2387-2392.
    [50] Yuan S.Y., Wei S.H., Chang B.V. Biodegradation of polycyclic aromatic hydrocarbons by a mixed culture[J].Chemosphere,2000,41(9):1463-1468.
    [51]阿特拉斯R.M.,黄第藩,谭实等.石油微生物学[M].北京:石油工业出版社.1991:302.
    [52]沈德中.污染环境的生物修复[M].北京:化学工业出版社. 2002: 268-279.
    [53] Oudot J., Merlin F.X., Pinvidic P. Weathering rates of oil components in a bioremediation experiment in estuarine sediments[J]. Marine Environmental Research, 1998, 45(2): 113-125
    [54]张甲耀,李静,夏威林,等.生物修复技术研究进展[J].应用与环境生物学报, 1996, 2(2):193-199
    [55]丁克强,骆永明.生物修复石油污染土壤[J].土壤,2001,4:179-184.
    [56]郭清根.海洋石油污染的生物强化修复[J].当代经理人,2006,21:1410-1411.
    [57] Groser R.J., Warshewsky D, Robie V.J. Indigenous and enhanced mineralization of pyrene, benzo(a)pyrene and carbazole in soil[J]. Applied and Environmental Microbiology, 1991, 57: 3462-3469
    [58] Trindade P.V.O., Sobral L.G., Rizzo A.C.L., et al. Bioremediation of a weathered and a recently oil-contaminated soils from Brazil: a comparison study[J]. Chemosphere, 2005, 58(4): 515-522
    [59] Coulon F., Pelletier E., Gourhant L., et al. Effects of nutrient and temperature on degradation of petroleum hydrocarbons in contaminated sub-Antarctic soil[J].Chemosphere, 2005, 58(10): 1439–1448
    [60] Atlas R.M. Microbial degradation of petroleum hydrocarbons:an environmental perspective[J]. Microbiological Review,1981,45:180-209
    [61] Lal B., Khanna S. Degradation of crude oil by Acinetobacter calcoaceticus and Aicaligenes Odorans [J]. Appl. Bacterial, 1996, 81 (4):355-362
    [62]赵荫薇,王世明,张建法.微生物在油污地下水生物处理中的应用研究[J].应用生态学报,1998,9(2):209-212.
    [63]管亚军,梁凤来,张心平,等.混合菌群对原油的降解作用[J].南开大学学报(自然科学), 2001, 34(4): 82-90
    [64]邢新会,刘则华.环境生物修复技术的研究进展[J] .化工进展,2004 ,23 (6) :579-581.
    [65] Westmeier F., Rehm H.J. Degradation of 4-chlorophenol in municipal wastewater by adsorptive immobilized Alcaligenes sp. A7- 2[J]. Appl. Microbiol. Biotechnol.,1987, 26 :78-83.
    [66] Meriem B., Nevenka A., Cesar P., et al . Degradation of sodium anthraquinone sulphonate by free and immobilized bacterial cultures[J]. Appl. Microbiol. Biotechnol., 1994 , 41 : 110-116.
    [67]王建龙.生物固定化技术与水污染控制[M],北京:科学出版社, 2002
    [68]高宝玉,岳钦艳,程小东.固定化细胞在废水处理中的应用[J].山东环境, 1999, 89(2): 3-5
    [69]崔明超,陈繁忠,傅家谟,等.固定化微生物技术在废水处理中的研究进展[J].化工环保,2003 ,23 (5) :261-264。
    [70]曹亚莉,田沈,赵军,等.固定化微生物细胞技术在废水处理中的应用[J].微生物学通报, 2003, 30(3): 77-81
    [71]王新,李培军,宋守志,等.固定化微生物技术在环境工程中的应用研究进展[J].环境污染与治理, 2005,27(7):535-537
    [72]齐水冰,罗建中,乔庆霞,等.固定化微生物技术处理废水[J].上海环境科学, 2002, 21(3):185-188
    [73] Li P.J., Wang X., Stagnitti F., et al. Degradation of phenanthrene and pyrene in slurry reactors with immobilized bacteria Zoogloea sp. [J]. Environmental Engineering Science ,2005 , 22 (3) : 390-399.
    [74]王孔星,谢裕敏.用无机载体固定脱色混合菌处理印染废水的模拟试验[J].环境科学与技术, 1989,(4):26-29.
    [75] Durham D.R., Leda C., Marshall, et al. New composite biocarriers engineered to contain adsorptive and ion-exchange properties improve immobilized-cell bioreaor process depend ability [J]. Appl Environ Microbial, 1994,60:4178-4181.
    [76] Pai S.L. Continuous degradation of phenol by R. hodoccus sp. Immobilized on granular activeated carbon and incaccium alginate[J].Bioresource Technol,1995,51:37-42
    [77]王新,李培军,巩宗强,等.固定化细胞技术的研究与进展[J].农业环境保护, 2001, 20(2): 120-122
    [78]沈耀良,黄勇,赵单,等.固定化微生物污水处理技术[M].北京:化学工业出版社,2002
    [79]刘和,王晓云,陈英旭.固定化微生物技术处理含酚废水[J].中国给水排水,2003,19(5) :53-55.
    [80]郭静仪,尹华,彭辉,等.木屑固定除油菌处理含油废水的研究[J].生态科学, 2005, 24(2): 154-157
    [81]邵娟,尹华,彭辉,等.秸秆固定化石油降解菌降解原油的初步研究[J].环境污染与治理, 2006, 28(8):565-568
    [82] Quek E., Ting Y.P., Tan H.M. Rhodococcus sp. F92 immobilized on polyurethane foam Shows ability to degrade various petroleum products[J]. Bioresource Technology , 2006 , 97 : 32-38.
    [83]张辉,李培军,王桂燕,等.固定化混合菌修复油污染地表水的研究[J].环境工程学报, 2008,(12):1613-1617
    [84]张秀霞,耿春香,房苗苗,等.固定化微生物应用于生物修复石油污染土壤.石油学报,2008,24(4):409-414
    [85]吴仁人,党志,易筱筠,等.氨基酸对烷烃降解菌GS3C降解性能的影响[J].环境科学研究, 2009, 22(6): 702-706
    [86]陶雪琴,卢桂宁,党志,等.菲降解菌株GY2B的分离鉴定及其降解特性[J] .中国环境科学, 2006, 26(4): 478-481.
    [87]陈晓鹏,易筱筠,陶雪琴,等.石油污染土壤中芘高效降解菌群的筛选及降解特性研究[J].环境工程学报, 2008, 2(3): 413-417
    [88] Tao X.Q., Lu G.N., Dang Z., et al. Aphenanthrene-degradingstrain Sphingomonas sp.GY2B isolated from contaminated soils[J]. Process Biochemistry, 2007, 42: 401—408
    [89]武金装,刘红玉,曾光明,等.柴油降解菌的筛选及其降解特性研究[J].农业环境科学学报, 2008,27(5): 1742-1746 [90 ]奚立旦,孙裕生,刘秀英.环境监测[M] .北京:高等教育出版社,2004 :581-585.
    [91]郑晓红,郑晓霖.水中油类监测分析方法研究[J].仪器仪表与分析监测, 2001,(01):1-3
    [92] Watson J.S., Jones D.M., Swannell R.P.J., et al. Formation of carboxylic acids during aerobic biodegradation of crude oil and evidence of microbial oxidation of hopanes[J]. Organic Geochemistry,2002,33:1153-1169
    [93]田贞乐,朱丽华,吴映辉,等.气相色谱与紫外分光光度法评价石油烃类污染物的微生物降解过程[J].分析化学, 2006, 3(36):343-346
    [94]徐恒刚,姚秀清,李倩,等.两种高效原油降解菌降解率测定方法的对比研究[J].化学与生物工程, 2006, 23 (9): 43-44,53
    [95]水质分析大全编写组.水质分析大全[M] .北京:科学技术出版社,1990:339-347.
    [96] Tirso G.O., Joan O.G., Marc L., et al. Microcosm experiments of oil degradation by microbial mats [J]. Science of the Total Environment, 2006, 357:12– 24
    [97]龚利萍,张甲耀,罗宇煊.土壤微生物降解石油污染物[J].上海环境科学,2001,(20)4:201-203
    [98]李广贺,张旭,黄巍.石油污染包气带中降解微生物的分布特性[J].环境科学, 2000, 21(4): 61-64
    [99] Galin T., McDowell C., Yaron B. The effect of volatilization on the mass of a non-aqueous pollutant liquid mixture in an inert porous medium[J]. Journal of Soil Science, 1990, 41: 6331-6341
    [100]齐永强,王红旗,刘敬奇,等.土壤中石油污染物微生物降解过程中各石油烃组分的演变规律[J].环境科学学报, 2003, 23(6): 834-836
    [101]Shan J.Y., Jia Y., Liu J., et al. Two pseudomonas act on hydrocarbon and their synergistic effect[J]. Microbiology, 2002, 29(4): 55-58
    [102]Wang Z.D., Fingas M., Blenkinsopp S., et al. Comparison of oil composition changesdue to biodegradation and physical weathering in different oils[J]. Journal of comatography A, 1998,809(1-2): 89-107
    [103]Leahy J.G., Colwell R.R. Microbial Degradation of Hydrocarbons in Environment [J]. Microbiol Rev, 1990, 54(9): 305-315
    [104]Margesin R., Schinner F. Effect of temperature on oil degradation by a psychrotrophic yeast in liquid culture and in oil[J]. FEMS Microbiology Ecology, 1997,24(3):243-249
    [105]陈熹兮,李堃宝,李道棠.低温微生物及其在生物修复领域中的应用[J].自然杂志, 2001, 23(3): 163~167
    [106]Ayotamuno M.J., Kogbara R.B., et al. 2006. Bioremediation of a crude-oil polluted agricultural soil at Port Harcourt, Nigeria[J]. Applied Energy, 83(11): 1249-1257
    [107]徐金兰,黄延林,唐智新,等.高效石油降解菌的筛选及石油污染土壤生物修复特性的研究[J].环境科学学报, 2007, 27(4 ):622-628
    [108]朱文芳,李伟光,吕炳南,等.固定化除油工程菌处理含油废水研究[J].中国给水排水,2003,19(11):39-40
    [109]张红莲,张锐.农作物秸秆饲料处理技术研究进展[J].饲料与畜牧, 2004,(03)18-22
    [110]陈卫民.作物秸秆主要处理技术的研究[J].宁夏农林科技, 2003,(06):86-87
    [111] Zhang M.L.,Fan Y.T.,Lay J.J. Enhanced biohydrogen production from cornstalk wastes with acidification pretreatment by mixed anaerobic cultures[J]. Biomass Bioenergy, 2007, 31(4): 250-254

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700