簡易檢索 / 詳目顯示

研究生: 巫得麗
Putri, Dyah Wulandari
論文名稱: 探討光電產業廢水生物處理程序中dimethyl sulfoxide 與 dimethyl sulfide對微生物族群之影響
Microbial community responses to dimethyl sulfoxide and dimethyl sulfide in TFT-LCD wastewater treatment process
指導教授: 黃良銘
Whang, Liang-Ming
學位類別: 碩士
Master
系所名稱: 工學院 - 環境工程學系
Department of Environmental Engineering
論文出版年: 2011
畢業學年度: 99
語文別: 英文
論文頁數: 145
中文關鍵詞: TFT-LCDDMSODMSNitrificationHyphomicrobium sp.Thiobacillus sp.ammonia oxidizing bacteria
外文關鍵詞: TFT-LCD, DMSO, DMS, Nitrification, Hyphomicrobium sp., Thiobacillus sp., ammonia oxidizing bacteria
相關次數: 點閱:103下載:0
分享至:
查詢本校圖書館目錄 查詢臺灣博碩士論文知識加值系統 勘誤回報
  • 二甲基亞楓(Dimethyl sulfoxide, DMSO)為TFT-LCD工業廢水中主要成分之一,其生物降解之過程中,DMS為主要的中間代謝產物,普遍被認為會造成環境惡臭,且同時抑制硝化作用(Nitrification),使廢水中另外兩種汙染物,乙醇胺(Monoethanolamine, MEA)和氫氧化四甲基銨(Tetramethyl-ammonium hydroxide, TMAH)無法被完全降解。因此,本研究主要探討DMSO的降解以及DMS抑制硝化作用的機制,。在能有效降解TFT-LCD工業廢水的二個連續批次反應器(Sequencing batch reactor, SBR)中,DMSO與DMS之主要降解菌群為Hyphomicrobium sp與Thiobacillus sp,此外藉由t-RFLP(terminal restriction fragment length polymorphism)的監測,發現在消長過程中此二菌群於在不同條件下各別為優勢族群。
    在本研究中,使用SYBR Green進行real-time PCR,定量Hyphomicrobium sp與Thiobacillus sp於SBR與廢水處理實場中之變化。在四組批次中,其中三組可發現Hyphomicrobium sp與Thiobacillus sp的競爭與硝化作用有顯著影響。當硝化作用不佳時,Thiobacillus sp為主要優勢菌群,反之,Hyphomicrobium sp則在良好硝化作用時成為優勢菌群。造成此現象的可能原因推測是,在系統中缺乏硝酸時DMSO取代硝酸成為主要電子接受者,改變DMS與DMSO間之比例,進而導致優勢族群的變化。在批次實驗中,當DMS或DMSO做為唯一基質時,兩菌群的rRNA表現量有相對減少的趨勢,且只有Hyphomicrobium sp能在第二或第三次加入基質時,仍持續釋出rRNA;推測廢水中其他物質,如TMAH及MEA可能提供微生物生長額外的條件,而廢水中複雜的微生物族群亦可能使對特定菌群(DMSO/DMS降解菌)的監測更加困難。
    而在DMS抑制硝化作用的批次實驗中,結合RT-PCR(Reverse transcription polymerase chain reaction)與t-RFLP的分子生物技術,用以監測硝化族群的功能性基因表現(amo subunit A, amoA)之變化。當DMS存在時,amoA基因的表現量會受到影響,且因不同硝化菌有不同影響:Nitrosomonas europeae (T-RF 491)會完全受到抑制,而Nitrosomonas europeae (T-RF 270)雖然有基因的表現,表現量仍少於無DMS抑制時之amoA基因表現量。

    Dimethylsulfide (DMS) is the main intermediates in dimethyl sulfoxide (DMSO) biodegradation. DMS is known as odor compound and suspected as inhibitor in nitrification process. Nitrification process is one of requirement to get complete degradation process for other two major compounds in TFT-LCD wastewater, monoethanolamine (MEA) and tetramethyl-ammonium hydroxide (TMAH). Because of this issue, DMSO degradation becomes the main concern in this study. The mechanisms of nitrification inhibition by DMS is also one of the main topic that was being studied.
    From two sequencing batch reactor, anoxic/oxic SBR and aerobic SBR which can reach complete degradation of TFT-LCD wastewater, Hyphomicrobium sp and Thiobacillus sp were found as DMSO/DMS degrading bacteria in the system process. By T-RFLP analysis for monitoring total bacteria from SBR time by time, the dynamics of Hyphomicrobium sp and Thiobacillus sp were detected.
    In this research, real time PCR with SYBR Green I methods is developed to quantify Hyphomicrobium sp and Thiobacillus sp in the system and applied to monitor two laboratory scale sequencing batch reactors (SBRs) and two full-scale wastewater treatment plants. From monitoring works, correlation of nitrification with Hyphomicrobium sp and Thiobacillus sp competition was found in three of four monitored treatment system. Thiobacillus sp was dominated while bad nitrification appears and Hyphomicrobium sp was dominated when good nitrification reached. Hypothesis was developed that domination of Hyphomicrobium sp and Thiobacillus sp is related to dominant sulfur compound (DMSO or DMS) in the system. This hypothesis built from the fact that nitrate concentration in the system affected amount of DMS in the system based on the roles of DMSO as main electron acceptor in the system while nitrate was not present in the system.
    Batch experiment using SBRs sludge was performed to get understanding about DMSO and DMS effect to Hyphomicrobium sp and Thiobacillus sp, From this batch experiment, TFT-LCD wastewater treatment system was found as complex system. While only DMS or DMSO as substrate, only Hyphomicrobium sp that can express rRNA. By applying second or third time feeding of DMS/DMSO, amount of rRNA expression from both of Hyphomicrobium sp and Thiobacillus sp was decreasing. DMSO or DMS alone as a substrate compound was not enough to maintain the growth of Hyphomicrobium sp and Thiobacillus sp. TMAH or MEA might be the other important substance for their growth, so the presence of TMAH or MEA in treatment system was necessary. Complex microbial community was also important factor that make difficulties to examine specific community response, in this case only DMSO/DMS degrading bacteria.
    The study of inhibition of nitrification by DMS was performed using batch experiments with sludges and pure culture. From sludge batch test, by monitoring amo subunit A (amoA) mRNA using real-time reverse transcription polymerase chain reaction and terminal restriction fragment length polymorphism (T-RFLP), while DMS present, the amount of amoA expression was inhibited. Inhibition effect of DMS was found different between different ammonia oxidizing bacteri (AOB) strains. Nitrosomonas europeae (T-RF 491) completely lost the ability to express amoA mRNA when DMS was present in the system, while Nitrosomonas europeae (T-RF 270) still had ability to express amoA mRNA although the expression level was much lower than that in the batch without DMS.. Nitrosomonas europeae (T-RF 491) and Nitrosomonas europeae (T-RF 270) was the same species but different strain of bacteria.

    Table of Content 摘要 II Abstract IV Acknowledgement VI Table of Content VIII List of Figures XII List of Tables XIX Chapter 1 Introduction 1 Chapter 2 Literature Review 4 2.1 Characteristic of TFT LCD wastewater 4 2.1.1 General characteristic 4 2.1.2 Characteristic of Dimethylsulfoxide (DMSO) 6 2.1.3 Characteristic of Monoethanolamine (MEA) 7 2.1.4 Characteristic of Tetramethylammonium hydroxide 7 2.2 Biodegradation Mechanisms and Microbial Community of TFT-LCD Wastewater Treatment 7 2.2.1 Biodegradation mechanisms of DMSO by DMSO/DMS degrading bacteria 8 2.2.2 Biodegradation of MEA 13 2.2.3 Biodegradation of TMAH 14 2.2.4 Nitrification by Nitrifying Bacteria 15 2.2.5 Microbial Community in TFT-LCD Wastewater Treatment Process 17 2.3 Sequencing Batch Reactor (SBR) 20 2.4 Application of molecular biology methods in biological process 21 2.4.1 Terminal Restriction Fragment Length Polymorphism (T-RFLP) 21 2.4.2 Real Time PCR 23 Chapter 3 Materials and Methods 27 3.1 Configuration and Operation of Sequencing Batch Reactors (Laboratory Scale) 27 3.2 Configuration of the full-scale TFT-LCD wastewater treatment 30 3.2.1 F6 wastewater treatment configuration 30 3.2.2 F5 wastewater treatment configuration 31 3.3 Batch Experiment 33 3.3.1 Sludge Batch Experiment 33 3.3.2 Pure culture study 35 3.4 Chemical Analytical Methods 38 3.4.1 General Analysis 38 3.4.2 Instrumental Analysis 38 3.4.2.1 DMSO (dimethyl sulphoxide) (Park et al., 2001) 38 3.4.2.2 Volatile sulfur compounds (VSCs) - DMS (dimethyl sulfide) 39 3.4.2.3 Oxygen and Carbon Dioxide 39 3.4.2.4 MEA, TMAH, and Ammonium (Mrklas et al., 2003) 39 3.4.2.5 Inorganic anion 40 3.5 Molecular Biology Analytical Methods 40 3.5.1 DNA Extraction 40 3.5.2 RNA Extraction and Reverse Transcription Reaction 41 3.5.2.1 RNA Extraction 41 3.5.2.2 Reverse Transcription Reaction 43 3.5.3 DNA and RNA concentration measurement 44 3.5.4 Polymerase Chain Reaction (PCR) 45 3.5.5 Terminal Restriction Fragment Length Polymorphism (T-RFLP) 48 3.5.6 Real Time Polymerase Chain Reaction (Real time PCR) 49 Chapter 4 Results and Discussion 52 4.1 Developing Real Time PCR methods to monitor Hyphomicrobium sp and Thiobacillus sp 52 4.2 Laboratory Scale - Sequencing Batch Reactor 56 4.2.1 Anoxic/Oxic SBR 56 4.2.1.1 Chemical Analysis Data 57 4.2.1.2 Biological Analysis Data 62 4.2.1.3 Summary 64 4.2.2 Aerobic SBR 65 4.2.2.1 Chemical Analysis Data 65 4.2.2.2 Biological Analysis Data 68 4.2.2.3 Summary 68 4.3 Full Scale TFT-LCD Wastewater Treatment Plant 68 4.3.1 F6 Wastewater Treatment Plant 70 4.3.1.1 Chemical Analysis Data 70 4.3.1.2 Biological Analysis Data 73 4.3.1.3 Summary 73 4.3.2 F5 Wastewater Treatment Plant 74 4.3.2.1 Chemical Analysis Data 75 4.3.2.2 Biological Analysis Data 79 4.3.2.3 Summary 81 4.4 General Discussion of DMSO/DMS Degrading Bacteria Monitoring 82 4.5 Batch Experiments 84 4.5.1 DMSO/DMS Degrading Bacteria Dynamics 84 4.5.1.1 Effect of DMSO or DMS as Main Sulfur Compound in the System with Aerobic and Anoxic Experimental Condition 84 4.5.1.1.1 Dimethylsulfide (DMS) as substrate 85 4.5.1.1.2 Dimethyl sulfoxide (DMSO) as substrate 88 4.5.1.1.3 Summary 91 4.5.1.2 A/O and O sludge long term batch experiment 92 4.5.1.2.1 A/O sludge with DMS as substrate 92 4.5.1.2.2 O sludge with DMS as substrate 94 4.5.1.2.3 AO sludge with DMSO as substrate 96 4.5.1.2.4 O sludge with DMSO as substrate 98 4.5.1.2.5 Summary 100 4.5.2 DMS as inhibitor compound for AOB activity 101 4.5.2.1 Sludge Batch Experiment 101 4.5.2.2 Nitrosomonas europeae Pure Culture Study 110 4.5.2.3 Summary 113 Chapter 5 Conclusions and Suggestions 114 5.1 Conclusions 114 5.2 Suggestions 115 References 117 Appendix A Comparison of T-RFLP and real time PCR methods 123 Appendix B Hyphomicrobium sp and Thiobacillus sp Pure Culture Study 127 Appendix C Figure of T-RFLP Results 132 Appendix D Copy Number Data of Real Time PCR 141

    References

    Alef, K. and D. Kleiner (1989). "Rapid and sensitive determination of microbial activity in soils and in soil aggregates by dimethylsulfoxide reduction." Biology and Fertility of Soils 8(4): 349-355.
    Andreae, M. (1980). "Dimethylsulfoxide in marine and freshwaters." Limnology and Oceanography 25(6): 1054-1063.
    Anthony, C. (1982). “The Biochemistry of Methylotrophs”, Academic press, London.
    APHA (1995). “Standard Methods for the Examination of Water and Wastewater Nineteenth Edition”. Washington D.C., USA.
    Balows, A. (1992). “The Prokaryotes: a handbook on the biology of bacteria: ecophysiology, isolation, identification, applications”, Springer-Verlag.
    Baytshtok, V., Lu, H. et al. (2008). “Impact of Varying Electron Donors on the Molecular Microbial Ecology and Biokinetics of Methylotrophic Denitrifying Bacteria” Wiley InterScience.
    Bellin, T., Pulz., M., Matussek, A., Hempen, H., Gunzer, F., (2001). “Rapid detection of enterohemmorhagic Escherichia coli by real time PCR with fluorescent hybridization probes”. J. Clin. Microbiol. 39 (1), 370-374.
    Bentley, R. and T. G. Chasteen (2004). "Environmental VOSCs--formation and degradation of dimethyl sulfide, methanethiol and related materials." Chemosphere 55(3): 291-317.
    Charlson, R., J. Lovelock, et al. (1987). "Oceanic phytoplankton, atmospheric sulphur, cloud albedo and climate." Month: 655-661.
    Chen, P. C. (2010). “Study of Biodegradation Mechanism and Microbial Ecology of TFT-LCD Wastewater Treatment (Master Thesis)”. National Cheng Kung University, Taiwan.

    Chen, T. K., C. H. Ni, et al. (2003). "Nitrification–Denitrification of Opto-electronic Industrial Wastewater by Anoxic/Aerobic Process." Journal of Environmental Science and Health, Part A: Toxic/Hazardous Substances and Environmental Engineering 38(10): 2157 - 2167.
    Cho, K.-S., M. Hirai, et al. (1991). "Degradation characteristics of hydrogen sulfide, methanethiol, dimethyl sulfide and dimethyl disulfide by Thiobacillus thioparus DW44 isolated from peat biofilter." Journal of Fermentation and Bioengineering 71(6): 384-389.
    Cole JR, Chai B, Marsh TL, Farris RJ, Wang Q, et al. (2003) “The ribosomal database project (RDP-II) : Previewing a new autoaligner that allows regular updates and the new prokaryotic taxonomy”. Nucleic Acids Res 31.
    De Bont, J. A. M., J. P. Van Dijken, et al. (1981). "Dimethyl Sulphoxide and Dimethyl Sulphide as a Carbon, Sulphur and Energy Source for Growth of Hyphomicrobium S." J Gen Microbiol 127(2): 315-323.
    De Zwart, J. M. M. a. K., J.G. (1992). "C1-cycle of sulfur compounds." Biodegradation 3(37-59).
    Ferre, D., (1992). “Quantitative or semi-quantitavive PCR: reality versus myth. PCR Meth. Appl. 2 1-9.
    Fittipaldi, M., Codony, F., Morato, J., (2010), “Comparison of conventional culture and real-time quantitative PCR using SYBR Green for detection of Lenionella pneumophilia in water samples”. Water SA. Vol. 36 No.4
    Garrity, G. M. (2005), “Bergey’s Manual of Systematic Bacteriology Second Edition : Volume Two The Proteobacteria Part C The Alpha-, Beta-, Delta- and Epsilonproteobacteria”, Springer.
    Gilomen, S. (2007). “Identifying ammonia and nitrite oxidizing bacteria responsible for nitrification in opto-electronic wastewater”, Southern Illinois Univerdity, Carbondale, USA.
    Goerke, C., Bayer, M., Wolz, C., 2001. “Quantification of bacterial transcript during infection using competitive reverse transcription-PCR and Lightcycler RT-PCR. Clin. Diagn. Lab. Immunol. 8 (2), 279-282.
    Grady, C., G. Daigger, et al. (1999). “Biological wastewater treatment”, Marcel Dekker Inc.
    Griebler, C. (1997). "Dimethylsulfoxide (DMSO) reduction: a new approach to determine microbial activity in freshwater sediments." Journal of Microbiological Methods 29(1): 31-40.
    Hayes, A. C., Lin, S. N., Allen, D. G. (2010). “Growth Kinetics of Hyphomicrobium and Thiobacillus spp. In Mixed Cultures Degrading Dimethyl Sulfide and Methanol” Appl. Environ. Microbiol. AEM.0076-10.
    Hein, I., Lehner, A., Rieck, P., Klein, K., Brandl, E., Wagner, M. (2001). “Comparison of different approaches to quantify Stcphylococcus aureus cells by real time quantittive PCR and application of this technique for examination of cheese”. Appl. Environ. Microbiol. 67 (7), 3122-3126.
    Hirano, K., J. Okamura, et al. (2001). "An efficient treatment technique for TMAH wastewater by catalyticoxidation." IEEE transactions on semiconductor manufacturing 14(3): 202-206.
    Huang, S. (2006). "Bioprocess study and ecological dynamics of non-woven membrane bioreactor treating TFT-LCD wastewater. (Master Thesis)" National Cheng Kung University, Taiwan.
    Jewell, T., S. L. Huston, et al. (2008). "Methylotrophy in freshwater Beggiatoa alba strains." Appl. Environ. Microbiol.: AEM.00379-00308.
    Juliastuti, S.R, Bayens, J., et al. (2003). “The inhibitory effects of heavy metals and organic compounds on the next maximum specific growth rate of the autotrophic biomass in activated sludge”. Journal of Hazardours Materials B100 271-281.
    Juliette, L. Y., M. R. Hyman, et al. (1993). "Inhibition of Ammonia Oxidation in Nitrosomonas europaea by Sulfur Compounds: Thioethers Are Oxidized to Sulfoxides by Ammonia Monooxygenase." Appl. Environ. Microbiol. 59(11): 3718-3727.
    Kane, S. R., A. Y. Chakicherla, et al. (2007). "Whole-Genome Analysis of the Methyl tert-Butyl Ether-Degrading Beta-Proteobacterium Methylibium petroleiphilum PM1." Journal of Bacteriology 189(5): 1931-1945.
    Klein, D., (2002). “Quantification using real-time PCR technology: applications and limitations”. Trends Mol. Med. 8, 257-260.
    Knapp, J., N. Jenkey, et al. (1989). "The anaerobic biodegradation of diethanolamine by a nitrate reducing bacterium." Biodegradation 7(3): 183-189.
    Koito, T., M. Tekawa, et al. (1998). "A novel treatment technique for DMSO wastewater." IEEE transactions on semiconductor manufacturing 11(1): 3-8.
    Lai, B. and W. K. Shieh (1996). "Batch monoethylamine degradation via nitrate respiration." Water Research 30(10): 2530-2534.
    Lee, C., Kim, J., Shin, S. G., Hwang, S., (2006) “Absolure and relative QPCR quantification of plasmid copy number in Escherichia coli” Journal of Biothecnology 123, 273-280
    Lee, D., M. Lee, et al. (2004). Strain for decomposing TMAH, and method of wastewater treatment using the same, Google Patents.
    Lei, C. N. (2008). "Study of the degradation mechanism of TFT-LCD organic wastewater under aerobic, anoxic and anaerobic conditions (Master thesis)." National Cheng Kung University, Taiwan.
    Lin, H. L. (2006). "Study on reaction kinetics characteristics of Thin-film Transistor Liquid Crystal Display Wastewater by SBR reactor." National Cheng Kung University.
    Liu, W., T. Marsh, et al. (1997). "Characterization of microbial diversity by determining terminal restriction fragment length polymorphisms of genes encoding 16S rRNA." Appl. Environ. Microbiol. 63(11): 4516-4522.
    Lomans, B. P., C. van der Drift, et al. (2002). "Microbial cycling of volatile organic sulfur compounds." Cellular and Molecular Life Sciences 59(4): 575-588.
    Lukow, T., P. Dunfield, et al. (2006). "Use of the T-RFLP technique to assess spatial and temporal changes in the bacterial community structure within an agricultural soil planted with transgenic and non-transgenic potato plants." FEMS Microbiology Ecology 32(3): 241-247.
    Mohan, S., N. Rao, et al. (2005). "Treatment of complex chemical wastewater in a sequencing batch reactor (SBR) with an aerobic suspended growth configuration." Process Biochemistry 40(5): 1501-1508.
    Mrklas, O., A. Chu, et al. (2003). "Determination of ethanolamine, ethylene glycol and triethylene glycol by ion chromatography for laboratory and field biodegradation studies." Journal of Environmental Monitoring 5(2): 336-340
    Murakami-Nitta, T., H. Kurimura, et al. (2002). "Continuous degradation of dimethyl sulfoxide to sulfate ion by Hyphomicrobium denitrificans WU-K217." J Biosci Bioeng 94(1): 52-56.
    Ndegwa, A., R. Wong, et al. (2004). "Degradation of monoethanolamine in soil." Journal of Environmental Engineering and Science 3(2): 137-145.
    O’Mahony, J., Hill, C. (2002). “A real time PCR assay for the detection and quantitation of Mycobacterium avium subsp paratuberculosis using SYBR Green and the Light Cycler”. Journal of Microbiological Methods 51:283-293
    Park, H. (2005). Effect of dissolved oxygen on ammonia-oxidizing bacterial communities in activated sludge, The University of Wusconsin, Madison.
    Park, H. and D. Noguera (2004). "Evaluating the effect of dissolved oxygen on ammonia-oxidizing bacterial communities in activated sludge." Water Research 38(14-15): 3275-3286.
    Park, S., T. Yoon, et al. (2001). "Biological treatment of wastewater containing dimethyl sulphoxide from the semi-conductor industry." Process Biochemistry 36(6): 579-589.
    Regan, J., G. Harrington, et al. (2002). "Ammonia-and nitrite-oxidizing bacterial communities in a pilot-scale chloraminated drinking water distribution system." Applied and Environmental Microbiology 68(1): 73.
    Rotthauwe, J.H., Witzel, K.P. and Liesack, W. (1997) “The ammonia monooxygenase structural gene amoA as a functional marker: molecular fine-scale analysis of natural ammonia-oxidizing populations”. Appl Environ Microbiol 63(12), 4704-4712
    Schafer, H., Myronova, N., Boden, R., (2010). “Microbial degradation of dimethylsulphide and related C1-sulphur compounds: organisms and pathways controlling fluxes of sulphur in the biosphere”. J Exp Bot , 61, (2), 315-34.
    Suylen, G. and J. Kuenen (1986). "Chemostat enrichment and isolation of Hyphomicrobium EG." Antonie Van Leeuwenhoek 52(4): 281-293.
    Taylor, M.J., Hughes, M., Skuce, R., Neill, S., (2001). “Detection of Mycobacterium bovis in bovine clinical specimens using real time fluorescence and fluorescence resonance enerdy transfer probe rapid-cycle PCR. J. Clin. Microbio. 39 (4), 1272-1278/
    Urakami, T., H. Araki, et al. (1990). "Isolation and identification of tetramethylammonium-biodegrading bacteria." Journal of Fermentation and Bioengineering 70(1): 41-44.
    USEPA (1999). "Wastewater technology fact sheet sequencing batch reactors." EPA 832-F-99-073.
    Wellinghausen, N., Frost, C., Marre, R., (2001). “Detection of Legionellae in hospital water samples by quantitative real time LC PCR”. Appl. Environ. Microbio. 67 (9) 2985-2993.
    Zinder, S. and T. Brock (1978). "Dimethyl sulfoxide as an electron acceptor for anaerobic growth." Archives of Microbiology 116(1): 35-40.

    無法下載圖示 校內:2016-08-02公開
    校外:不公開
    電子論文尚未授權公開,紙本請查館藏目錄
    QR CODE