Development of a methanogenic process to degrade exhaustively the organic fraction of municipal grey waste under thermophilic and hyperthermophilic conditions
Different laboratory-scale, continuously driven reactor concepts (up to 3 reactors in series, max. 70 degrees C) for anaerobic digestion of the organic fraction of municipal grey waste were investigated. Over a period of 2 1/2 years several setups of reactors being daily fed and held in steady state...
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description | Different laboratory-scale, continuously driven reactor concepts (up to 3 reactors in series, max. 70 degrees C) for anaerobic digestion of the organic fraction of municipal grey waste were investigated. Over a period of 2 1/2 years several setups of reactors being daily fed and held in steady state balance were investigated. The perferred variant was a 2-stage setup with a HRT of 4.3 d for the 1st and 14.2 d for the 2nd reactor. Removal efficiencies of VS obtained by comparing the organic loading rate (OLR, g VS/l/d) of the effluent with the OLR of the feed could reach 80%. Removal efficiencies determined indirectly by the combined biogas yield of the 1st and 2nd reactor stage revealed even up to 91.5% of the theoretical possible yield of 807 l/kg VS. The produced gas had a methane content of 60-65%. A completely distinct hydrolysis stage with a gas production of only 1.6-5.5% of the theoretical yield could be reached by hyperthermophilic conditions (60-70 degrees C) or by a HRT of 1.25 d. It also demonstrated that a stable methanogenesis was not possible at temperatures of 60-70 degrees C. Kinetic analyses of the 2nd reactor stage revealed that the degradation of VS fell from 80 to 40% with raising organic loading rate (OLR) from 3 to 11 g VS/l/d. In contrast to this the VS-removal of the first hydrolysis reactor stage increased linearily from 5 to 20% at raising OLR's from 12 to 26 g VS/l/d. The same kinetics with linear increase exhibited the specific cellulose degradation with conversion rates of 0.1-3 x 109 g cellulose/single bacterium (10(-12) g)/d. This was an indication for the cellulose degradation as a rate limiting step. Both reactor stages combined allowed an optimal VS removal efficiency at OLR of 10 g VS/l/d. Analysis of bacterial populations of 28 reactors were referred either to eubacteria utilizing different sugars or cellulose or acetate or H2-CO2 or archaea (plus antibiotics) with acetate or H2-CO2 as substrate. H2-CO2 utilizers with numbers of 10(8)-10(10)/g TS dominated obviously the acetotrophic methanogens by the factor 10-10,000. This explained the observed short HRTs being possible. |
doi_str_mv | 10.2166/wst.2000.0059 |
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A ; VOLIMER, G.-R ; FAKHOURI, T ; MARTENSEN, S</creator><contributor>Mata-Alvarez, J ; Tilche, A (eds) ; Cecchi, F</contributor><creatorcontrib>SCHERER, P. A ; VOLIMER, G.-R ; FAKHOURI, T ; MARTENSEN, S ; Mata-Alvarez, J ; Tilche, A (eds) ; Cecchi, F</creatorcontrib><description>Different laboratory-scale, continuously driven reactor concepts (up to 3 reactors in series, max. 70 degrees C) for anaerobic digestion of the organic fraction of municipal grey waste were investigated. Over a period of 2 1/2 years several setups of reactors being daily fed and held in steady state balance were investigated. The perferred variant was a 2-stage setup with a HRT of 4.3 d for the 1st and 14.2 d for the 2nd reactor. Removal efficiencies of VS obtained by comparing the organic loading rate (OLR, g VS/l/d) of the effluent with the OLR of the feed could reach 80%. Removal efficiencies determined indirectly by the combined biogas yield of the 1st and 2nd reactor stage revealed even up to 91.5% of the theoretical possible yield of 807 l/kg VS. The produced gas had a methane content of 60-65%. A completely distinct hydrolysis stage with a gas production of only 1.6-5.5% of the theoretical yield could be reached by hyperthermophilic conditions (60-70 degrees C) or by a HRT of 1.25 d. It also demonstrated that a stable methanogenesis was not possible at temperatures of 60-70 degrees C. Kinetic analyses of the 2nd reactor stage revealed that the degradation of VS fell from 80 to 40% with raising organic loading rate (OLR) from 3 to 11 g VS/l/d. In contrast to this the VS-removal of the first hydrolysis reactor stage increased linearily from 5 to 20% at raising OLR's from 12 to 26 g VS/l/d. The same kinetics with linear increase exhibited the specific cellulose degradation with conversion rates of 0.1-3 x 109 g cellulose/single bacterium (10(-12) g)/d. This was an indication for the cellulose degradation as a rate limiting step. Both reactor stages combined allowed an optimal VS removal efficiency at OLR of 10 g VS/l/d. Analysis of bacterial populations of 28 reactors were referred either to eubacteria utilizing different sugars or cellulose or acetate or H2-CO2 or archaea (plus antibiotics) with acetate or H2-CO2 as substrate. H2-CO2 utilizers with numbers of 10(8)-10(10)/g TS dominated obviously the acetotrophic methanogens by the factor 10-10,000. This explained the observed short HRTs being possible.</description><identifier>ISSN: 0273-1223</identifier><identifier>ISBN: 9781900222266</identifier><identifier>ISBN: 1900222264</identifier><identifier>EISSN: 1996-9732</identifier><identifier>DOI: 10.2166/wst.2000.0059</identifier><identifier>PMID: 11382012</identifier><identifier>CODEN: WSTED4</identifier><language>eng</language><publisher>London: IWA Publishing</publisher><subject>Acetates ; Acetic acid ; Anaerobic Digestion ; Anaerobic treatment ; Antibiotics ; Archaea ; Bacteria ; Bacteria, Anaerobic - metabolism ; Biodegradation ; Biodegradation, Environmental ; Biogas ; Biological and medical sciences ; Biological treatment of sewage sludges and wastes ; Bioreactors ; Bioreactors - microbiology ; Bioreactors - standards ; Biotechnology ; Carbon dioxide ; Cellulose ; Cellulose acetate ; Degradation ; Environment and pollution ; Fatty Acids, Volatile - analysis ; Fundamental and applied biological sciences. Psychology ; Gas production ; Germany ; gray waste ; Hot Temperature ; Hydrolysis ; Incineration - methods ; Industrial applications and implications. Economical aspects ; Kinetics ; Load distribution ; Loading rate ; Methane ; Methane - metabolism ; Methanogenesis ; Methanogenic bacteria ; Methanogens ; Oil and gas production ; Organic loading ; Quaternary Ammonium Compounds - analysis ; Reaction kinetics ; Reactors ; Refuse Disposal - methods ; Removal ; Solid wastes ; Sugar</subject><ispartof>Water science and technology, 2000-01, Vol.41 (3), p.83-91</ispartof><rights>2000 INIST-CNRS</rights><rights>Copyright IWA Publishing Feb 2000</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c439t-eeed4cc47fb188570900dcc17a30d650eba34d90d4712c22ca5b5e286a8199393</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>309,310,314,778,782,787,788,27907,27908</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=1375746$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/11382012$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><contributor>Mata-Alvarez, J</contributor><contributor>Tilche, A (eds)</contributor><contributor>Cecchi, F</contributor><creatorcontrib>SCHERER, P. A</creatorcontrib><creatorcontrib>VOLIMER, G.-R</creatorcontrib><creatorcontrib>FAKHOURI, T</creatorcontrib><creatorcontrib>MARTENSEN, S</creatorcontrib><title>Development of a methanogenic process to degrade exhaustively the organic fraction of municipal grey waste under thermophilic and hyperthermophilic conditions</title><title>Water science and technology</title><addtitle>Water Sci Technol</addtitle><description>Different laboratory-scale, continuously driven reactor concepts (up to 3 reactors in series, max. 70 degrees C) for anaerobic digestion of the organic fraction of municipal grey waste were investigated. Over a period of 2 1/2 years several setups of reactors being daily fed and held in steady state balance were investigated. The perferred variant was a 2-stage setup with a HRT of 4.3 d for the 1st and 14.2 d for the 2nd reactor. Removal efficiencies of VS obtained by comparing the organic loading rate (OLR, g VS/l/d) of the effluent with the OLR of the feed could reach 80%. Removal efficiencies determined indirectly by the combined biogas yield of the 1st and 2nd reactor stage revealed even up to 91.5% of the theoretical possible yield of 807 l/kg VS. The produced gas had a methane content of 60-65%. A completely distinct hydrolysis stage with a gas production of only 1.6-5.5% of the theoretical yield could be reached by hyperthermophilic conditions (60-70 degrees C) or by a HRT of 1.25 d. It also demonstrated that a stable methanogenesis was not possible at temperatures of 60-70 degrees C. Kinetic analyses of the 2nd reactor stage revealed that the degradation of VS fell from 80 to 40% with raising organic loading rate (OLR) from 3 to 11 g VS/l/d. In contrast to this the VS-removal of the first hydrolysis reactor stage increased linearily from 5 to 20% at raising OLR's from 12 to 26 g VS/l/d. The same kinetics with linear increase exhibited the specific cellulose degradation with conversion rates of 0.1-3 x 109 g cellulose/single bacterium (10(-12) g)/d. This was an indication for the cellulose degradation as a rate limiting step. Both reactor stages combined allowed an optimal VS removal efficiency at OLR of 10 g VS/l/d. Analysis of bacterial populations of 28 reactors were referred either to eubacteria utilizing different sugars or cellulose or acetate or H2-CO2 or archaea (plus antibiotics) with acetate or H2-CO2 as substrate. H2-CO2 utilizers with numbers of 10(8)-10(10)/g TS dominated obviously the acetotrophic methanogens by the factor 10-10,000. This explained the observed short HRTs being possible.</description><subject>Acetates</subject><subject>Acetic acid</subject><subject>Anaerobic Digestion</subject><subject>Anaerobic treatment</subject><subject>Antibiotics</subject><subject>Archaea</subject><subject>Bacteria</subject><subject>Bacteria, Anaerobic - metabolism</subject><subject>Biodegradation</subject><subject>Biodegradation, Environmental</subject><subject>Biogas</subject><subject>Biological and medical sciences</subject><subject>Biological treatment of sewage sludges and wastes</subject><subject>Bioreactors</subject><subject>Bioreactors - microbiology</subject><subject>Bioreactors - standards</subject><subject>Biotechnology</subject><subject>Carbon dioxide</subject><subject>Cellulose</subject><subject>Cellulose acetate</subject><subject>Degradation</subject><subject>Environment and pollution</subject><subject>Fatty Acids, Volatile - analysis</subject><subject>Fundamental and applied biological sciences. 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Economical aspects</subject><subject>Kinetics</subject><subject>Load distribution</subject><subject>Loading rate</subject><subject>Methane</subject><subject>Methane - metabolism</subject><subject>Methanogenesis</subject><subject>Methanogenic bacteria</subject><subject>Methanogens</subject><subject>Oil and gas production</subject><subject>Organic loading</subject><subject>Quaternary Ammonium Compounds - analysis</subject><subject>Reaction kinetics</subject><subject>Reactors</subject><subject>Refuse Disposal - methods</subject><subject>Removal</subject><subject>Solid wastes</subject><subject>Sugar</subject><issn>0273-1223</issn><issn>1996-9732</issn><isbn>9781900222266</isbn><isbn>1900222264</isbn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2000</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><recordid>eNqFkk1r3DAQhkU_aLZpjr0WQUNv3urTso4lTZtAIJf0bLTSeO1gS64kN90_099amSyE9hJdBobnfcXMvAi9p2TLaF1_fkh5ywghW0KkfoE2VOu60oqzl-hMq4ZqQlh5df0KbQhTvKKM8RP0NqX7olJckDfohFLeMELZBv35Cr9gDPMEPuPQYYMnyL3xYQ9-sHiOwUJKOAfsYB-NAwy_e7OkPBTZAececIh7s7JdNDYPwa8201I6w2xGvI9wwA8mZcCLdxBXSZzC3A9j0RjvcH-YIf7TtcG7YbVK79DrzowJzo71FP34dnl3cVXd3H6_vvhyU1nBda4AwAlrhep2tGmkImULzlqqDCeulgR2hguniROKMsuYNXIngTW1KQvTXPNT9OnRtwz8c4GU22lIFsbReAhLahkt_wjaPAtSJbnUgjwPCsm1piv48T_wPizRl2lbqgXnQjaqLlT1SNkYUorQtXMcJhMPLSXtGoy2BKNdg9GuwSj8h6PrspvAPdHHyxfg_AiYZM1YjuftkJ44rqQSNf8L2l_BWA</recordid><startdate>20000101</startdate><enddate>20000101</enddate><creator>SCHERER, P. 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A ; VOLIMER, G.-R ; FAKHOURI, T ; MARTENSEN, S</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c439t-eeed4cc47fb188570900dcc17a30d650eba34d90d4712c22ca5b5e286a8199393</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2000</creationdate><topic>Acetates</topic><topic>Acetic acid</topic><topic>Anaerobic Digestion</topic><topic>Anaerobic treatment</topic><topic>Antibiotics</topic><topic>Archaea</topic><topic>Bacteria</topic><topic>Bacteria, Anaerobic - metabolism</topic><topic>Biodegradation</topic><topic>Biodegradation, Environmental</topic><topic>Biogas</topic><topic>Biological and medical sciences</topic><topic>Biological treatment of sewage sludges and wastes</topic><topic>Bioreactors</topic><topic>Bioreactors - microbiology</topic><topic>Bioreactors - standards</topic><topic>Biotechnology</topic><topic>Carbon dioxide</topic><topic>Cellulose</topic><topic>Cellulose acetate</topic><topic>Degradation</topic><topic>Environment and pollution</topic><topic>Fatty Acids, Volatile - analysis</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Gas production</topic><topic>Germany</topic><topic>gray waste</topic><topic>Hot Temperature</topic><topic>Hydrolysis</topic><topic>Incineration - methods</topic><topic>Industrial applications and implications. Economical aspects</topic><topic>Kinetics</topic><topic>Load distribution</topic><topic>Loading rate</topic><topic>Methane</topic><topic>Methane - metabolism</topic><topic>Methanogenesis</topic><topic>Methanogenic bacteria</topic><topic>Methanogens</topic><topic>Oil and gas production</topic><topic>Organic loading</topic><topic>Quaternary Ammonium Compounds - analysis</topic><topic>Reaction kinetics</topic><topic>Reactors</topic><topic>Refuse Disposal - methods</topic><topic>Removal</topic><topic>Solid wastes</topic><topic>Sugar</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>SCHERER, P. 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A</au><au>VOLIMER, G.-R</au><au>FAKHOURI, T</au><au>MARTENSEN, S</au><au>Mata-Alvarez, J</au><au>Tilche, A (eds)</au><au>Cecchi, F</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Development of a methanogenic process to degrade exhaustively the organic fraction of municipal grey waste under thermophilic and hyperthermophilic conditions</atitle><jtitle>Water science and technology</jtitle><addtitle>Water Sci Technol</addtitle><date>2000-01-01</date><risdate>2000</risdate><volume>41</volume><issue>3</issue><spage>83</spage><epage>91</epage><pages>83-91</pages><issn>0273-1223</issn><eissn>1996-9732</eissn><isbn>9781900222266</isbn><isbn>1900222264</isbn><coden>WSTED4</coden><abstract>Different laboratory-scale, continuously driven reactor concepts (up to 3 reactors in series, max. 70 degrees C) for anaerobic digestion of the organic fraction of municipal grey waste were investigated. Over a period of 2 1/2 years several setups of reactors being daily fed and held in steady state balance were investigated. The perferred variant was a 2-stage setup with a HRT of 4.3 d for the 1st and 14.2 d for the 2nd reactor. Removal efficiencies of VS obtained by comparing the organic loading rate (OLR, g VS/l/d) of the effluent with the OLR of the feed could reach 80%. Removal efficiencies determined indirectly by the combined biogas yield of the 1st and 2nd reactor stage revealed even up to 91.5% of the theoretical possible yield of 807 l/kg VS. The produced gas had a methane content of 60-65%. A completely distinct hydrolysis stage with a gas production of only 1.6-5.5% of the theoretical yield could be reached by hyperthermophilic conditions (60-70 degrees C) or by a HRT of 1.25 d. It also demonstrated that a stable methanogenesis was not possible at temperatures of 60-70 degrees C. Kinetic analyses of the 2nd reactor stage revealed that the degradation of VS fell from 80 to 40% with raising organic loading rate (OLR) from 3 to 11 g VS/l/d. In contrast to this the VS-removal of the first hydrolysis reactor stage increased linearily from 5 to 20% at raising OLR's from 12 to 26 g VS/l/d. The same kinetics with linear increase exhibited the specific cellulose degradation with conversion rates of 0.1-3 x 109 g cellulose/single bacterium (10(-12) g)/d. This was an indication for the cellulose degradation as a rate limiting step. Both reactor stages combined allowed an optimal VS removal efficiency at OLR of 10 g VS/l/d. Analysis of bacterial populations of 28 reactors were referred either to eubacteria utilizing different sugars or cellulose or acetate or H2-CO2 or archaea (plus antibiotics) with acetate or H2-CO2 as substrate. H2-CO2 utilizers with numbers of 10(8)-10(10)/g TS dominated obviously the acetotrophic methanogens by the factor 10-10,000. This explained the observed short HRTs being possible.</abstract><cop>London</cop><pub>IWA Publishing</pub><pmid>11382012</pmid><doi>10.2166/wst.2000.0059</doi><tpages>9</tpages></addata></record> |
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subjects | Acetates Acetic acid Anaerobic Digestion Anaerobic treatment Antibiotics Archaea Bacteria Bacteria, Anaerobic - metabolism Biodegradation Biodegradation, Environmental Biogas Biological and medical sciences Biological treatment of sewage sludges and wastes Bioreactors Bioreactors - microbiology Bioreactors - standards Biotechnology Carbon dioxide Cellulose Cellulose acetate Degradation Environment and pollution Fatty Acids, Volatile - analysis Fundamental and applied biological sciences. Psychology Gas production Germany gray waste Hot Temperature Hydrolysis Incineration - methods Industrial applications and implications. Economical aspects Kinetics Load distribution Loading rate Methane Methane - metabolism Methanogenesis Methanogenic bacteria Methanogens Oil and gas production Organic loading Quaternary Ammonium Compounds - analysis Reaction kinetics Reactors Refuse Disposal - methods Removal Solid wastes Sugar |
title | Development of a methanogenic process to degrade exhaustively the organic fraction of municipal grey waste under thermophilic and hyperthermophilic conditions |
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