Hydrodynamic control of bioparticle deposition in a MBR applied to wastewater treatment
The study of fouling for tubular ceramic ultrafiltration (MWCO 300 kD) membranes during activated sludge filtration under constant flux conditions led to the experimental identification of two fouling processes: (1) At low recirculation velocity (0.5 m/s; Re∼1200), sludge floc particles were deposit...
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creator | Tardieu, E Grasmick, A Geaugey, V Manem, J |
description | The study of fouling for tubular ceramic ultrafiltration (MWCO 300
kD) membranes during activated sludge filtration under constant flux conditions led to the experimental identification of two fouling processes: (1) At low recirculation velocity (0.5
m/s;
Re∼1200), sludge floc particles were deposited on the membrane surface and this cake layer provoked a very quick increase of hydraulic resistance (>10
9
m
−1
s
−1). (2) However, under the usual recirculation conditions (4
m/s;
Re∼9000), floc was not deposited. Filtration was stable for several days even with high fluxes (75–150
l/h
m
2). Progressive membrane fouling resulted in a linear increase of transmembrane pressure over a certain time, and could be described by an increase in the hydraulic resistance, with d
R/d
t varying between 10
5 and 10
8
m
−1
s
−1 depending on hydrodynamic and biological conditions.
Mechanism models (shear induced diffusion, inertial lift, surface transport) led to a very good qualitative description of these results, and revealed the major role of convective backtransport phenomena in fouling processes. |
doi_str_mv | 10.1016/S0376-7388(98)00091-X |
format | Article |
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kD) membranes during activated sludge filtration under constant flux conditions led to the experimental identification of two fouling processes: (1) At low recirculation velocity (0.5
m/s;
Re∼1200), sludge floc particles were deposited on the membrane surface and this cake layer provoked a very quick increase of hydraulic resistance (>10
9
m
−1
s
−1). (2) However, under the usual recirculation conditions (4
m/s;
Re∼9000), floc was not deposited. Filtration was stable for several days even with high fluxes (75–150
l/h
m
2). Progressive membrane fouling resulted in a linear increase of transmembrane pressure over a certain time, and could be described by an increase in the hydraulic resistance, with d
R/d
t varying between 10
5 and 10
8
m
−1
s
−1 depending on hydrodynamic and biological conditions.
Mechanism models (shear induced diffusion, inertial lift, surface transport) led to a very good qualitative description of these results, and revealed the major role of convective backtransport phenomena in fouling processes.</description><identifier>ISSN: 0376-7388</identifier><identifier>EISSN: 1873-3123</identifier><identifier>DOI: 10.1016/S0376-7388(98)00091-X</identifier><identifier>CODEN: JMESDO</identifier><language>eng</language><publisher>Amsterdam: Elsevier B.V</publisher><subject>Activated sludge ; Activated sludge process ; Applied sciences ; Backtransport ; Biological and medical sciences ; Biological treatment of waters ; Bioreactors ; Biotechnology ; Chemical Sciences ; Deposition ; Diffusion in solids ; Environment and pollution ; Exact sciences and technology ; Fouling ; Fundamental and applied biological sciences. Psychology ; General purification processes ; Hydrodynamics ; Industrial applications and implications. Economical aspects ; MBR ; Membranes ; Particles (particulate matter) ; Pollution ; Ultrafiltration ; Wastewater treatment ; Wastewaters ; Water treatment and pollution</subject><ispartof>Journal of membrane science, 1998-08, Vol.147 (1), p.1-12</ispartof><rights>1998 Elsevier Science B.V.</rights><rights>1998 INIST-CNRS</rights><rights>Distributed under a Creative Commons Attribution 4.0 International License</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c498t-ccceec0443bfcd991f0a2c05c14b16823313bc40e0b242ffca63a244566149253</citedby><cites>FETCH-LOGICAL-c498t-ccceec0443bfcd991f0a2c05c14b16823313bc40e0b242ffca63a244566149253</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/S0376-7388(98)00091-X$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>230,314,777,781,882,3537,27905,27906,45976</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=2366749$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://hal.umontpellier.fr/hal-01736304$$DView record in HAL$$Hfree_for_read</backlink></links><search><creatorcontrib>Tardieu, E</creatorcontrib><creatorcontrib>Grasmick, A</creatorcontrib><creatorcontrib>Geaugey, V</creatorcontrib><creatorcontrib>Manem, J</creatorcontrib><title>Hydrodynamic control of bioparticle deposition in a MBR applied to wastewater treatment</title><title>Journal of membrane science</title><description>The study of fouling for tubular ceramic ultrafiltration (MWCO 300
kD) membranes during activated sludge filtration under constant flux conditions led to the experimental identification of two fouling processes: (1) At low recirculation velocity (0.5
m/s;
Re∼1200), sludge floc particles were deposited on the membrane surface and this cake layer provoked a very quick increase of hydraulic resistance (>10
9
m
−1
s
−1). (2) However, under the usual recirculation conditions (4
m/s;
Re∼9000), floc was not deposited. Filtration was stable for several days even with high fluxes (75–150
l/h
m
2). Progressive membrane fouling resulted in a linear increase of transmembrane pressure over a certain time, and could be described by an increase in the hydraulic resistance, with d
R/d
t varying between 10
5 and 10
8
m
−1
s
−1 depending on hydrodynamic and biological conditions.
Mechanism models (shear induced diffusion, inertial lift, surface transport) led to a very good qualitative description of these results, and revealed the major role of convective backtransport phenomena in fouling processes.</description><subject>Activated sludge</subject><subject>Activated sludge process</subject><subject>Applied sciences</subject><subject>Backtransport</subject><subject>Biological and medical sciences</subject><subject>Biological treatment of waters</subject><subject>Bioreactors</subject><subject>Biotechnology</subject><subject>Chemical Sciences</subject><subject>Deposition</subject><subject>Diffusion in solids</subject><subject>Environment and pollution</subject><subject>Exact sciences and technology</subject><subject>Fouling</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General purification processes</subject><subject>Hydrodynamics</subject><subject>Industrial applications and implications. Economical aspects</subject><subject>MBR</subject><subject>Membranes</subject><subject>Particles (particulate matter)</subject><subject>Pollution</subject><subject>Ultrafiltration</subject><subject>Wastewater treatment</subject><subject>Wastewaters</subject><subject>Water treatment and pollution</subject><issn>0376-7388</issn><issn>1873-3123</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1998</creationdate><recordtype>article</recordtype><recordid>eNqFkVtrFEEQhRtRcI3-BKEfRMzDxL5Nz_STxKBZYUXwgnlrampqsGV2euzuJOy_d3Y37GueCorv1OUcxl5LcSGFtO9_CN3YqtFt-86150IIJ6ubJ2wl20ZXWir9lK1OyHP2Iue_QshGtG7Ffq93fYr9boJtQI5xKimOPA68C3GGVAKOxHuaYw4lxImHiQP_-vE7h3keA_W8RH4PudA9FEq8JIKypam8ZM8GGDO9eqhn7NfnTz-v1tXm2_WXq8tNhca1pUJEIhTG6G7A3jk5CFAoapSmk7ZVWkvdoREkOmXUMCBYDcqY2lppnKr1GTs_zv0Do59T2ELa-QjBry83ft9bHtVWC3MnF_btkZ1T_HdLufhtyEjjCBPF2-yV1NY4Zx4Fpa1rYQ9gfQQxxZwTDacTpPD7bPwhG7833rvWH7LxN4vuzcMCyAjjkGDCkE9ipa1tjFuwD0eMFgfvAiWfMdCE1IdEWHwfwyOL_gM-HaLG</recordid><startdate>19980819</startdate><enddate>19980819</enddate><creator>Tardieu, E</creator><creator>Grasmick, A</creator><creator>Geaugey, V</creator><creator>Manem, J</creator><general>Elsevier B.V</general><general>Elsevier</general><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7UA</scope><scope>C1K</scope><scope>1XC</scope></search><sort><creationdate>19980819</creationdate><title>Hydrodynamic control of bioparticle deposition in a MBR applied to wastewater treatment</title><author>Tardieu, E ; Grasmick, A ; Geaugey, V ; Manem, J</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c498t-ccceec0443bfcd991f0a2c05c14b16823313bc40e0b242ffca63a244566149253</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1998</creationdate><topic>Activated sludge</topic><topic>Activated sludge process</topic><topic>Applied sciences</topic><topic>Backtransport</topic><topic>Biological and medical sciences</topic><topic>Biological treatment of waters</topic><topic>Bioreactors</topic><topic>Biotechnology</topic><topic>Chemical Sciences</topic><topic>Deposition</topic><topic>Diffusion in solids</topic><topic>Environment and pollution</topic><topic>Exact sciences and technology</topic><topic>Fouling</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General purification processes</topic><topic>Hydrodynamics</topic><topic>Industrial applications and implications. Economical aspects</topic><topic>MBR</topic><topic>Membranes</topic><topic>Particles (particulate matter)</topic><topic>Pollution</topic><topic>Ultrafiltration</topic><topic>Wastewater treatment</topic><topic>Wastewaters</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Tardieu, E</creatorcontrib><creatorcontrib>Grasmick, A</creatorcontrib><creatorcontrib>Geaugey, V</creatorcontrib><creatorcontrib>Manem, J</creatorcontrib><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Hyper Article en Ligne (HAL)</collection><jtitle>Journal of membrane science</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Tardieu, E</au><au>Grasmick, A</au><au>Geaugey, V</au><au>Manem, J</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Hydrodynamic control of bioparticle deposition in a MBR applied to wastewater treatment</atitle><jtitle>Journal of membrane science</jtitle><date>1998-08-19</date><risdate>1998</risdate><volume>147</volume><issue>1</issue><spage>1</spage><epage>12</epage><pages>1-12</pages><issn>0376-7388</issn><eissn>1873-3123</eissn><coden>JMESDO</coden><abstract>The study of fouling for tubular ceramic ultrafiltration (MWCO 300
kD) membranes during activated sludge filtration under constant flux conditions led to the experimental identification of two fouling processes: (1) At low recirculation velocity (0.5
m/s;
Re∼1200), sludge floc particles were deposited on the membrane surface and this cake layer provoked a very quick increase of hydraulic resistance (>10
9
m
−1
s
−1). (2) However, under the usual recirculation conditions (4
m/s;
Re∼9000), floc was not deposited. Filtration was stable for several days even with high fluxes (75–150
l/h
m
2). Progressive membrane fouling resulted in a linear increase of transmembrane pressure over a certain time, and could be described by an increase in the hydraulic resistance, with d
R/d
t varying between 10
5 and 10
8
m
−1
s
−1 depending on hydrodynamic and biological conditions.
Mechanism models (shear induced diffusion, inertial lift, surface transport) led to a very good qualitative description of these results, and revealed the major role of convective backtransport phenomena in fouling processes.</abstract><cop>Amsterdam</cop><pub>Elsevier B.V</pub><doi>10.1016/S0376-7388(98)00091-X</doi><tpages>12</tpages></addata></record> |
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language | eng |
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source | Elsevier ScienceDirect Journals |
subjects | Activated sludge Activated sludge process Applied sciences Backtransport Biological and medical sciences Biological treatment of waters Bioreactors Biotechnology Chemical Sciences Deposition Diffusion in solids Environment and pollution Exact sciences and technology Fouling Fundamental and applied biological sciences. Psychology General purification processes Hydrodynamics Industrial applications and implications. Economical aspects MBR Membranes Particles (particulate matter) Pollution Ultrafiltration Wastewater treatment Wastewaters Water treatment and pollution |
title | Hydrodynamic control of bioparticle deposition in a MBR applied to wastewater treatment |
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