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Microbial Functional Roles In Eco-friendly Treatment for Tannery Wastewater Using a Microbial Consortium

DC Field Value Language
dc.contributor.author EkpeghereKaluIbe -
dc.date.accessioned 2017-02-22T02:24:09Z -
dc.date.available 2017-02-22T02:24:09Z -
dc.date.issued 2014 -
dc.date.submitted 2014-11-11 -
dc.identifier.uri http://kmou.dcollection.net/jsp/common/DcLoOrgPer.jsp?sItemId=000002174340 ko_KR
dc.identifier.uri http://repository.kmou.ac.kr/handle/2014.oak/8342 -
dc.description.abstract A novel microbial consortium (BM-S-1) enriched from the natural soils was successfully implemented to treat the tannery wastewater from leather manufacturing industries in Korea in a pilot scale and full scale system in China without chemical pretreatment. The full scale tannery system was built after the pilot system has been proven effective. Chemical oxygen demand (COD), total nitrogen (TN), total phosphorus (TP), chromium (Cr) and mixed liquor suspended solids (MLSS) were measured to monitor treated water quality and treatment efficiency. Microbial population dynamics were analyzed using pyrosequencing and denitrifying bacteria was quantified using real-time PCR (RT-PCR) of the nitrous oxide reductase gene (nosZ) in both systems. Removal efficiencies for COD, T-N and T-P were more than 91%, 79%, and 90%, respectively for the pilot system while the removal efficiencies of COD, TN, TP, and Cr were 98.3%, 98.6%, 93.6%, and 88.5% in the full scale system. In the pilot system, the dominant phyla in buffering tank (B), primary aeration (PA), secondary aeration (SA) and sludge digestion tank (SD), were Proteobacteria, Firmicutes, Bacteroidetes, Planctomycetes and Deionococcus-Thermus while the full scale system contained Proteobacteria, Firmicutes, Bacteroidetes, Chloroflexi and Deinococcus-Thermus. Cluster analysis based on unifrac distance of the species in the different stages showed that the microbial communities in PA is similar to SA while B is closer to SD in the pilot system, B is closely related to PA and SA to SD in the full scale. The qPCR of nosZ genes showed the highest abundance of denitrifiers in B increasing 734 folds compared to the influent (I) in the pilot system while the abundance of denitrifiers increased approximately 195 times in B, as compared to the influent of wastewater, and after the BM-S-1 consortium augmentation in the full scale treatment system. The pyrosequencing analysis of the pilot system showed AB430337_f_uc_s, Methyloversatilis_uc, AB430336_s, were the most abundant species while Brachymonas denitrificans was the most abundant in full scale especially in B (6-37.5%). Other polymeric substance degraders (Clostridia), sulfate reducers (Desulfuromonas palmitatis), and sulfur oxidizers (uncultured Thiobacillus) were dominant in the sludge digestion (SD) tank. Whole-metagenome sequencing analysis using Illumina MiSeq Sequencer was done to determine microbial community structures and functional genes associated with treatment of tannery wastewater in the full scale treatment system. The metagenome sequencing data demonstrated that four phyla were Proteobacteria, Bacteriodetes, Firmicutes and Actinobacteria were dominant in the treatment process. The genes involved in metabolisms of carbohydrates, protein and amino acids were more than 80% compared to the genes associated with metabolisms of lipids and fatty acid, nitrogen, sulfur and phosphorus that were less than 70% in B and PA. For nitrogen metabolism, genes associated with ammonia, nitrate and nitrite assimilation were more abundant than the genes responsible for denitrification and dissimilatory nitrite reductase. The dominant genera involved in nitrogen metabolism were Burkholderia, Polaromonas, Albidiferax, Acidovorax, Geobacter, Dechloromonas, Pseudomonas, and Rhodopseudomonas. Glutamate synthase, glutamate dehydrogenase, nitrous oxide reductase and nitrate reductase were distinctively observed depending on the kinds of these genera. Glutamate synthase (GS) and glutamate dehydrogenase (GDH) were abundant in Burkholderia, Delfia, Bordetella Albidiferax, Acidovorax, Cupriavidu genes such s, Thiobacillus, Methylibium, Azoarcus, Dechloromonas, and Aromatoleum while as nitric oxide reductase and nitrate reductase (NAR) showed high abundance in Geobacter, Burkholderia, Acidovorax, Cupriavidus, Thiobacillus, and Chromobacterium in the different stages of the treatment process. Most of the metabolic processes were relatively more active in PA and B which corroborated with the chemical data (COD, T-N and T-P, etc.) obtained from all the stages during the treatment process. These results provide a detailed understanding into the structures and functions of the microbial communities in the eco-friendly tannery wastewater treatment. Furthermore, these data would provide useful information for designing the full scale treatment system. -
dc.description.tableofcontents Chapter 1 Introduction 1.1 General introduction…………………………………....…………………. 1 1.2 Literature review ……………………….……………………..…………... 4 1.2.1 Tannery production and its wastewater ………………......………….. 4 1.2.2 Details about BM-S-1 consortium ………………………………….... 8 1.3 Overview of the nitrogen cycle .................................................................. 12 1.3.1 Nitrification pathways in wastewater …………...….……………….. 14 1.3.2 Denitrification pathways in wastewater .............................................. 15 1.3.3 Anaerobic ammonium oxidation in wastewater ................................. 18 Chapter 2 Materials and Methods 2.1 Design and operation of the pilot tannery wastewater treatment system ... 19 2.2 Growing BM-S-1 for treatment of tannery wastewater.............................. 22 2.3 Monitoring water quality of the tannery wastewater in the pilot scale system …………………………………………………………………… 22 2.4 Pyrosequencing analysis of microbial communities in the pilot scale treatment system ........................................................................................ 24 2.5 Community analysis of denitrifying bacteria by real time qPCR in the pilot scale system …………………………………………………………. 25 2.6 Design and operation of the full scale tannery wastewater treatment system ........................................................................................................ 25 2.7 Analysis of wastewater and mass flow calculation in the full scale system ........................................................................................................ 30 2.8 Pyrosequencing analysis of microbial communities in full scale treatment of wastewater ……………………………………...…………………….. 31 2.9 Community analysis of denitrifying bacteria by real time qPCR in the full scale system ……………………………...………………………….. 32 2.10 Sampling and metagenomic analysis of microbial communities .............. 33 2.10.1 Sample collection and DNA extraction ............................................ 33 2.10.2 Whole metagenome sequencing ....................................................... 33 2.10.3 Metagenomic sequence analysis ………………………………….. 34 Chapter 3 Treatment of tannery wastewater using the pilot scale system 3.1 Monitoring water quality of the tannery wastewater in the pilot scale system .............................................................................................................. 35 3.2 Pyrosequencing analysis of microbial communities in the pilot scale system ……………………………………………………………………….. 38 3.3 Denitrifying bacteria genes by real time qPCR in pilot scale system ............. 49 Chapter 4 Treatment of tannery wastewater using the full scale system 4.1 Monitoring water quality of the tannery wastewater in the full scale system ............................................................................................................ 51 4.2 Sludge reduction in the full scale system....................................................... 56 4.3 Pyrosequencing analysis of microbial communities in the full scale system ...……………..……………………………………………...…….. 57 4.4 Quantification of denitrifying bacteria using qPCR in the full scale system …………………………………………………………....……...... 66 Chapter 5 Metagenomic analysis of the microbial communities full scale system 5.1 Metagenome library construction of the microbial samples ........................ 68 5.2 Microbial community structure in the full scale system ............................... 68 5.3 The SEED subsystem distributions in the microbial communities ................73 5.4 Comparative study of total nitrogen metabolic functions ............................. 80 5.5 Comparative study of the dominant nitrogen functions ................................ 82 5.6 Relationship between the different treatment stages in terms of nitrogen metabolic functional genes ............................................................................ 84 5.7 Analysis of the specific nitrogen metabolic functional genes using biomakers ...................................................................................................... 87 5.8 Proposed nitrogen metabolic pathways in the full scale treatment system …………. 91 Chapter 6 Conclusions ........................................................................................ 93 References ............................................................................................................ 95 Acknowledgments …………………………...………..……………………… 109 -
dc.language eng -
dc.publisher International Meeting of the Microbiology Society of Korea -
dc.title Microbial Functional Roles In Eco-friendly Treatment for Tannery Wastewater Using a Microbial Consortium -
dc.type Thesis -
dc.date.awarded 2014-08 -
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토목환경공학과 > Thesis
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