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Optimizing water and resource recovery facilities (WRRF) for energy generation without compromising effluent quality
The primary separation unit (PSU) splits the organic load on the water and resource recovery facility (WRRF) between the primary sludge (PS) anaerobic digester (AD), where energy can be generated, and the biological nutrient removal (BNR) activated sludge (AS) reactor, where energy is consumed. With...
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Published in: | Water S. A. 2021-04, Vol.47 (2), p.141-153 |
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description | The primary separation unit (PSU) splits the organic load on the water and resource recovery facility (WRRF) between the primary sludge (PS) anaerobic digester (AD), where energy can be generated, and the biological nutrient removal (BNR) activated sludge (AS) reactor, where energy is consumed. With a CHONP element massbalanced plant-wide stoichiometric and kinetic steady-state model, this paper explores quantitatively the impact of four cases of increasing organics removal efficiencies in the PSU on (i) settled wastewater characteristics, (ii) balanced solids retention time (SRT) of the Modified Ludzack-Ettinger (MLE) and University of Cape Town/ Johannesburg (UCT/JHB) systems for lowest economical effluent N and P concentrations, (iii) reactor volume, (iv) energy consumption for aeration, pumping and mixing, (v) energy generation by AD of PS and waste activated sludge (WAS), (vi) N&P content of the PS and WAS AD dewatering liquor (DWL) and (vii) final effluent N and P concentrations with and without enhanced biological P removal (EBPR), and looks for an optimum WRRF layout for maximum energy recovery without compromising effluent quality. For the low biogas yield from the WAS AD, decreasing as the SRT of the BNRAS system gets longer and with the added complexity of N&P removal from the digested sludge DWL, makes AD of WAS undesirable unless P recovery is required. Because the wastewater biodegradable particulate organics (BPO) have a low N&P content, it is better to divert more biodegradable particulate organics to the PSAD with enhanced primary separation than digest WAS - the PSAD DWL can be returned to the influent with relatively small impact on final effluent N and P concentration. |
doi_str_mv | 10.17159/wsa/2021.v47.i2.10910 |
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With a CHONP element massbalanced plant-wide stoichiometric and kinetic steady-state model, this paper explores quantitatively the impact of four cases of increasing organics removal efficiencies in the PSU on (i) settled wastewater characteristics, (ii) balanced solids retention time (SRT) of the Modified Ludzack-Ettinger (MLE) and University of Cape Town/ Johannesburg (UCT/JHB) systems for lowest economical effluent N and P concentrations, (iii) reactor volume, (iv) energy consumption for aeration, pumping and mixing, (v) energy generation by AD of PS and waste activated sludge (WAS), (vi) N&P content of the PS and WAS AD dewatering liquor (DWL) and (vii) final effluent N and P concentrations with and without enhanced biological P removal (EBPR), and looks for an optimum WRRF layout for maximum energy recovery without compromising effluent quality. For the low biogas yield from the WAS AD, decreasing as the SRT of the BNRAS system gets longer and with the added complexity of N&P removal from the digested sludge DWL, makes AD of WAS undesirable unless P recovery is required. Because the wastewater biodegradable particulate organics (BPO) have a low N&P content, it is better to divert more biodegradable particulate organics to the PSAD with enhanced primary separation than digest WAS - the PSAD DWL can be returned to the influent with relatively small impact on final effluent N and P concentration.</description><identifier>ISSN: 0378-4738</identifier><identifier>DOI: 10.17159/wsa/2021.v47.i2.10910</identifier><language>eng</language><publisher>Gezina: Water Research Commission</publisher><subject>Activated sludge ; Aeration ; Biodegradability ; Biodegradation ; Biogas ; Biological wastewater treatment ; Biomass ; Dewatering ; Effluents ; Energy ; Energy consumption ; Energy recovery ; Influents ; Liquor ; Nutrient removal ; Optimization ; Organic loading ; Primary sludge ; Reactors ; Recovery ; Removal ; Resource recovery ; Retention ; Retention time ; Separation ; Simulation ; Sludge ; Sludge digestion ; Steady state models ; Wastewater</subject><ispartof>Water S. 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A.</title><description>The primary separation unit (PSU) splits the organic load on the water and resource recovery facility (WRRF) between the primary sludge (PS) anaerobic digester (AD), where energy can be generated, and the biological nutrient removal (BNR) activated sludge (AS) reactor, where energy is consumed. With a CHONP element massbalanced plant-wide stoichiometric and kinetic steady-state model, this paper explores quantitatively the impact of four cases of increasing organics removal efficiencies in the PSU on (i) settled wastewater characteristics, (ii) balanced solids retention time (SRT) of the Modified Ludzack-Ettinger (MLE) and University of Cape Town/ Johannesburg (UCT/JHB) systems for lowest economical effluent N and P concentrations, (iii) reactor volume, (iv) energy consumption for aeration, pumping and mixing, (v) energy generation by AD of PS and waste activated sludge (WAS), (vi) N&P content of the PS and WAS AD dewatering liquor (DWL) and (vii) final effluent N and P concentrations with and without enhanced biological P removal (EBPR), and looks for an optimum WRRF layout for maximum energy recovery without compromising effluent quality. 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Because the wastewater biodegradable particulate organics (BPO) have a low N&P content, it is better to divert more biodegradable particulate organics to the PSAD with enhanced primary separation than digest WAS - the PSAD DWL can be returned to the influent with relatively small impact on final effluent N and P concentration.</description><subject>Activated sludge</subject><subject>Aeration</subject><subject>Biodegradability</subject><subject>Biodegradation</subject><subject>Biogas</subject><subject>Biological wastewater treatment</subject><subject>Biomass</subject><subject>Dewatering</subject><subject>Effluents</subject><subject>Energy</subject><subject>Energy consumption</subject><subject>Energy recovery</subject><subject>Influents</subject><subject>Liquor</subject><subject>Nutrient removal</subject><subject>Optimization</subject><subject>Organic loading</subject><subject>Primary 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A.</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Ekama, George A</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Optimizing water and resource recovery facilities (WRRF) for energy generation without compromising effluent quality</atitle><jtitle>Water S. A.</jtitle><date>2021-04-01</date><risdate>2021</risdate><volume>47</volume><issue>2</issue><spage>141</spage><epage>153</epage><pages>141-153</pages><issn>0378-4738</issn><abstract>The primary separation unit (PSU) splits the organic load on the water and resource recovery facility (WRRF) between the primary sludge (PS) anaerobic digester (AD), where energy can be generated, and the biological nutrient removal (BNR) activated sludge (AS) reactor, where energy is consumed. With a CHONP element massbalanced plant-wide stoichiometric and kinetic steady-state model, this paper explores quantitatively the impact of four cases of increasing organics removal efficiencies in the PSU on (i) settled wastewater characteristics, (ii) balanced solids retention time (SRT) of the Modified Ludzack-Ettinger (MLE) and University of Cape Town/ Johannesburg (UCT/JHB) systems for lowest economical effluent N and P concentrations, (iii) reactor volume, (iv) energy consumption for aeration, pumping and mixing, (v) energy generation by AD of PS and waste activated sludge (WAS), (vi) N&P content of the PS and WAS AD dewatering liquor (DWL) and (vii) final effluent N and P concentrations with and without enhanced biological P removal (EBPR), and looks for an optimum WRRF layout for maximum energy recovery without compromising effluent quality. For the low biogas yield from the WAS AD, decreasing as the SRT of the BNRAS system gets longer and with the added complexity of N&P removal from the digested sludge DWL, makes AD of WAS undesirable unless P recovery is required. Because the wastewater biodegradable particulate organics (BPO) have a low N&P content, it is better to divert more biodegradable particulate organics to the PSAD with enhanced primary separation than digest WAS - the PSAD DWL can be returned to the influent with relatively small impact on final effluent N and P concentration.</abstract><cop>Gezina</cop><pub>Water Research Commission</pub><doi>10.17159/wsa/2021.v47.i2.10910</doi><tpages>13</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Activated sludge Aeration Biodegradability Biodegradation Biogas Biological wastewater treatment Biomass Dewatering Effluents Energy Energy consumption Energy recovery Influents Liquor Nutrient removal Optimization Organic loading Primary sludge Reactors Recovery Removal Resource recovery Retention Retention time Separation Simulation Sludge Sludge digestion Steady state models Wastewater |
title | Optimizing water and resource recovery facilities (WRRF) for energy generation without compromising effluent quality |
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