AustralieFrV1, PascalFrancis, Corpus, bibRecord, 001C86

Assessing granular media filtration for the removal of chemical contaminants from wastewater

Identifieur interne : 001C86 ( PascalFrancis/Corpus ); précédent : 001C85; suivant : 001C87

Assessing granular media filtration for the removal of chemical contaminants from wastewater

Auteurs : Lionel Ho ; Charlotte Grasset ; Daniel Hoefel ; Mike B. Dixon ; Frederic D. L. Leusch ; Gayle Newcombe ; Christopher P. Saint ; Justin D. Brookes

Source :

Water research : (Oxford) [ 0043-1354 ] ; 2011.

RBID : Pascal:11-0267416

Descripteurs français

Pascal (Inist)
- Filtration, Décontamination, Pollution, Eau usée, Charbon actif, Estrone, Ethinylestradiol, En discontinu, Activité biologique, Cinétique, Composé organique, Adsorption, Nitrosamine, Analyse tendance, Composé hydrophobe, Surveillance, Performance, Filtre sable, Station épuration, Dégradation biologique, Biofiltre, Oestrogène, Perturbateur endocrinien, Hormone stéroïde sexuelle, Devenir polluant, Bioréacteur, Epuration biologique.

English descriptors

KwdEn :
- Activated carbon, Adsorption, Batchwise, Biodegradation, Biofilter, Biological activity, Biological purification, Bioreactor, Decontamination, Endocrine disruptor, Estrogen, Estrone, Ethinylestradiol, Filtration, Hydrophobic compound, Kinetics, Nitrosamine, Organic compounds, Performance, Pollutant behavior, Pollution, Sand filter, Sewage treatment plant, Sex steroid hormone, Surveillance, Trend analysis, Waste water.

Abstract

Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10^-3 h^-1. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

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C01	`01`		`ENG`	@0 Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10^-3 h^-1. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.
C02	`01`	`X`		`@0 001D16A`
C03	`01`	`X`	`FRE`	`@0 Filtration @5 01`
C03	`01`	`X`	`ENG`	`@0 Filtration @5 01`
C03	`01`	`X`	`SPA`	`@0 Filtración @5 01`
C03	`02`	`X`	`FRE`	`@0 Décontamination @5 02`
C03	`02`	`X`	`ENG`	`@0 Decontamination @5 02`
C03	`02`	`X`	`SPA`	`@0 Descontaminación @5 02`
C03	`03`	`X`	`FRE`	`@0 Pollution @5 03`
C03	`03`	`X`	`ENG`	`@0 Pollution @5 03`
C03	`03`	`X`	`SPA`	`@0 Polución @5 03`
C03	`04`	`X`	`FRE`	`@0 Eau usée @5 04`
C03	`04`	`X`	`ENG`	`@0 Waste water @5 04`
C03	`04`	`X`	`SPA`	`@0 Agua residual @5 04`
C03	`05`	`X`	`FRE`	`@0 Charbon actif @5 05`
C03	`05`	`X`	`ENG`	`@0 Activated carbon @5 05`
C03	`05`	`X`	`SPA`	`@0 Carbón activado @5 05`
C03	`06`	`X`	`FRE`	`@0 Estrone @2 NK @2 FR @5 06`
C03	`06`	`X`	`ENG`	`@0 Estrone @2 NK @2 FR @5 06`
C03	`06`	`X`	`SPA`	`@0 Estrona @2 NK @2 FR @5 06`
C03	`07`	`X`	`FRE`	`@0 Ethinylestradiol @2 NK @2 FR @5 07`
C03	`07`	`X`	`ENG`	`@0 Ethinylestradiol @2 NK @2 FR @5 07`
C03	`07`	`X`	`SPA`	`@0 Etinilestradiol @2 NK @2 FR @5 07`
C03	`08`	`X`	`FRE`	`@0 En discontinu @5 08`
C03	`08`	`X`	`ENG`	`@0 Batchwise @5 08`
C03	`08`	`X`	`SPA`	`@0 En discontinuo @5 08`
C03	`09`	`X`	`FRE`	`@0 Activité biologique @5 09`
C03	`09`	`X`	`ENG`	`@0 Biological activity @5 09`
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C03	`12`	`X`	`FRE`	`@0 Adsorption @5 12`
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C03	`12`	`X`	`SPA`	`@0 Adsorción @5 12`
C03	`13`	`X`	`FRE`	`@0 Nitrosamine @2 NK @2 FX @5 13`
C03	`13`	`X`	`ENG`	`@0 Nitrosamine @2 NK @2 FX @5 13`
C03	`13`	`X`	`SPA`	`@0 Nitrosamina @2 NK @2 FX @5 13`
C03	`14`	`X`	`FRE`	`@0 Analyse tendance @5 14`
C03	`14`	`X`	`ENG`	`@0 Trend analysis @5 14`
C03	`14`	`X`	`SPA`	`@0 Análisis tendencia @5 14`
C03	`15`	`X`	`FRE`	`@0 Composé hydrophobe @5 15`
C03	`15`	`X`	`ENG`	`@0 Hydrophobic compound @5 15`
C03	`15`	`X`	`SPA`	`@0 Compuesto hidrofobo @5 15`
C03	`16`	`X`	`FRE`	`@0 Surveillance @5 16`
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C03	`17`	`X`	`FRE`	`@0 Performance @5 17`
C03	`17`	`X`	`ENG`	`@0 Performance @5 17`
C03	`17`	`X`	`SPA`	`@0 Rendimiento @5 17`
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C03	`18`	`X`	`ENG`	`@0 Sand filter @5 18`
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C03	`19`	`X`	`FRE`	`@0 Station épuration @5 19`
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C03	`24`	`X`	`FRE`	`@0 Hormone stéroïde sexuelle @5 35`
C03	`24`	`X`	`ENG`	`@0 Sex steroid hormone @5 35`
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C03	`25`	`X`	`FRE`	`@0 Devenir polluant @5 36`
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Format Inist (serveur)

NO :	PASCAL 11-0267416 INIST
ET :	Assessing granular media filtration for the removal of chemical contaminants from wastewater
AU :	HO (Lionel); GRASSET (Charlotte); HOEFEL (Daniel); DIXON (Mike B.); LEUSCH (Frederic D. L.); NEWCOMBE (Gayle); SAINT (Christopher P.); BROOKES (Justin D.)
AF :	Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square/Adelaide SA 5000/Australie (1 aut., 3 aut., 4 aut., 6 aut., 7 aut.); School of Earth & Environmental Sciences, The University of Adelaide/SA 5005/Australie (1 aut., 3 aut., 7 aut., 8 aut.); École Superieure de Chimie Physique Électronique de Lyon, 43 Boulevard du 11 Novembre 1918, BP 2077/69616 Villeurbanne/France (2 aut.); Griffith University, Smart Water Research Centre, Edmund Rice Drive/Southport, QLD 4222/Australie (5 aut.)
DT :	Publication en série; Niveau analytique
SO :	Water research : (Oxford); ISSN 0043-1354; Coden WATRAG; Royaume-Uni; Da. 2011; Vol. 45; No. 11; Pp. 3461-3472; Bibl. 2 p.1/4
LA :	Anglais
EA :	Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10^-3 h^-1. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.
CC :	001D16A
FD :	Filtration; Décontamination; Pollution; Eau usée; Charbon actif; Estrone; Ethinylestradiol; En discontinu; Activité biologique; Cinétique; Composé organique; Adsorption; Nitrosamine; Analyse tendance; Composé hydrophobe; Surveillance; Performance; Filtre sable; Station épuration; Dégradation biologique; Biofiltre; Oestrogène; Perturbateur endocrinien; Hormone stéroïde sexuelle; Devenir polluant; Bioréacteur; Epuration biologique
ED :	Filtration; Decontamination; Pollution; Waste water; Activated carbon; Estrone; Ethinylestradiol; Batchwise; Biological activity; Kinetics; Organic compounds; Adsorption; Nitrosamine; Trend analysis; Hydrophobic compound; Surveillance; Performance; Sand filter; Sewage treatment plant; Biodegradation; Biofilter; Estrogen; Endocrine disruptor; Sex steroid hormone; Pollutant behavior; Bioreactor; Biological purification
SD :	Filtración; Descontaminación; Polución; Agua residual; Carbón activado; Estrona; Etinilestradiol; En discontinuo; Actividad biológica; Cinética; Compuesto orgánico; Adsorción; Nitrosamina; Análisis tendencia; Compuesto hidrofobo; Vigilancia; Rendimiento; Filtro arena; Estación depuradora; Degradación biológica; Biofiltro; Estrógeno; Disruptor endocrino; Hormona esteroide sexual; Evolución contaminante; Biorreactor; Depuración biológica
LO :	INIST-8940A.354000192136290200
ID :	11-0267416

Links to Exploration step

Pascal:11-0267416

Le document en format XML

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<affiliation><inist:fA14 i1="02"><s1>School of Earth & Environmental Sciences, The University of Adelaide</s1>
<s2>SA 5005</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>7 aut.</sZ>
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<author><name sortKey="Dixon, Mike B" sort="Dixon, Mike B" uniqKey="Dixon M" first="Mike B." last="Dixon">Mike B. Dixon</name>
<affiliation><inist:fA14 i1="01"><s1>Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square</s1>
<s2>Adelaide SA 5000</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>4 aut.</sZ>
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</affiliation>
</author>
<author><name sortKey="Leusch, Frederic D L" sort="Leusch, Frederic D L" uniqKey="Leusch F" first="Frederic D. L." last="Leusch">Frederic D. L. Leusch</name>
<affiliation><inist:fA14 i1="04"><s1>Griffith University, Smart Water Research Centre, Edmund Rice Drive</s1>
<s2>Southport, QLD 4222</s2>
<s3>AUS</s3>
<sZ>5 aut.</sZ>
</inist:fA14>
</affiliation>
</author>
<author><name sortKey="Newcombe, Gayle" sort="Newcombe, Gayle" uniqKey="Newcombe G" first="Gayle" last="Newcombe">Gayle Newcombe</name>
<affiliation><inist:fA14 i1="01"><s1>Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square</s1>
<s2>Adelaide SA 5000</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
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</affiliation>
</author>
<author><name sortKey="Saint, Christopher P" sort="Saint, Christopher P" uniqKey="Saint C" first="Christopher P." last="Saint">Christopher P. Saint</name>
<affiliation><inist:fA14 i1="01"><s1>Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square</s1>
<s2>Adelaide SA 5000</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
</inist:fA14>
</affiliation>
<affiliation><inist:fA14 i1="02"><s1>School of Earth & Environmental Sciences, The University of Adelaide</s1>
<s2>SA 5005</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>7 aut.</sZ>
<sZ>8 aut.</sZ>
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</affiliation>
</author>
<author><name sortKey="Brookes, Justin D" sort="Brookes, Justin D" uniqKey="Brookes J" first="Justin D." last="Brookes">Justin D. Brookes</name>
<affiliation><inist:fA14 i1="02"><s1>School of Earth & Environmental Sciences, The University of Adelaide</s1>
<s2>SA 5005</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
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<series><title level="j" type="main">Water research : (Oxford)</title>
<title level="j" type="abbreviated">Water res. : (Oxf.)</title>
<idno type="ISSN">0043-1354</idno>
<imprint><date when="2011">2011</date>
</imprint>
</series>
</biblStruct>
</sourceDesc>
<seriesStmt><title level="j" type="main">Water research : (Oxford)</title>
<title level="j" type="abbreviated">Water res. : (Oxf.)</title>
<idno type="ISSN">0043-1354</idno>
</seriesStmt>
</fileDesc>
<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Activated carbon</term>
<term>Adsorption</term>
<term>Batchwise</term>
<term>Biodegradation</term>
<term>Biofilter</term>
<term>Biological activity</term>
<term>Biological purification</term>
<term>Bioreactor</term>
<term>Decontamination</term>
<term>Endocrine disruptor</term>
<term>Estrogen</term>
<term>Estrone</term>
<term>Ethinylestradiol</term>
<term>Filtration</term>
<term>Hydrophobic compound</term>
<term>Kinetics</term>
<term>Nitrosamine</term>
<term>Organic compounds</term>
<term>Performance</term>
<term>Pollutant behavior</term>
<term>Pollution</term>
<term>Sand filter</term>
<term>Sewage treatment plant</term>
<term>Sex steroid hormone</term>
<term>Surveillance</term>
<term>Trend analysis</term>
<term>Waste water</term>
</keywords>
<keywords scheme="Pascal" xml:lang="fr"><term>Filtration</term>
<term>Décontamination</term>
<term>Pollution</term>
<term>Eau usée</term>
<term>Charbon actif</term>
<term>Estrone</term>
<term>Ethinylestradiol</term>
<term>En discontinu</term>
<term>Activité biologique</term>
<term>Cinétique</term>
<term>Composé organique</term>
<term>Adsorption</term>
<term>Nitrosamine</term>
<term>Analyse tendance</term>
<term>Composé hydrophobe</term>
<term>Surveillance</term>
<term>Performance</term>
<term>Filtre sable</term>
<term>Station épuration</term>
<term>Dégradation biologique</term>
<term>Biofiltre</term>
<term>Oestrogène</term>
<term>Perturbateur endocrinien</term>
<term>Hormone stéroïde sexuelle</term>
<term>Devenir polluant</term>
<term>Bioréacteur</term>
<term>Epuration biologique</term>
</keywords>
</textClass>
</profileDesc>
</teiHeader>
<front><div type="abstract" xml:lang="en">Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10<sup>-3</sup>
 h<sup>-1</sup>
. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.</div>
</front>
</TEI>
<inist><standard h6="B"><pA><fA01 i1="01" i2="1"><s0>0043-1354</s0>
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<fA06><s2>11</s2>
</fA06>
<fA08 i1="01" i2="1" l="ENG"><s1>Assessing granular media filtration for the removal of chemical contaminants from wastewater</s1>
</fA08>
<fA11 i1="01" i2="1"><s1>HO (Lionel)</s1>
</fA11>
<fA11 i1="02" i2="1"><s1>GRASSET (Charlotte)</s1>
</fA11>
<fA11 i1="03" i2="1"><s1>HOEFEL (Daniel)</s1>
</fA11>
<fA11 i1="04" i2="1"><s1>DIXON (Mike B.)</s1>
</fA11>
<fA11 i1="05" i2="1"><s1>LEUSCH (Frederic D. L.)</s1>
</fA11>
<fA11 i1="06" i2="1"><s1>NEWCOMBE (Gayle)</s1>
</fA11>
<fA11 i1="07" i2="1"><s1>SAINT (Christopher P.)</s1>
</fA11>
<fA11 i1="08" i2="1"><s1>BROOKES (Justin D.)</s1>
</fA11>
<fA14 i1="01"><s1>Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square</s1>
<s2>Adelaide SA 5000</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>4 aut.</sZ>
<sZ>6 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="02"><s1>School of Earth & Environmental Sciences, The University of Adelaide</s1>
<s2>SA 5005</s2>
<s3>AUS</s3>
<sZ>1 aut.</sZ>
<sZ>3 aut.</sZ>
<sZ>7 aut.</sZ>
<sZ>8 aut.</sZ>
</fA14>
<fA14 i1="03"><s1>École Superieure de Chimie Physique Électronique de Lyon, 43 Boulevard du 11 Novembre 1918, BP 2077</s1>
<s2>69616 Villeurbanne</s2>
<s3>FRA</s3>
<sZ>2 aut.</sZ>
</fA14>
<fA14 i1="04"><s1>Griffith University, Smart Water Research Centre, Edmund Rice Drive</s1>
<s2>Southport, QLD 4222</s2>
<s3>AUS</s3>
<sZ>5 aut.</sZ>
</fA14>
<fA20><s1>3461-3472</s1>
</fA20>
<fA21><s1>2011</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>8940A</s2>
<s5>354000192136290200</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2011 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>2 p.1/4</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>11-0267416</s0>
</fA47>
<fA60><s1>P</s1>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Water research : (Oxford)</s0>
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<fA66 i1="01"><s0>GBR</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10<sup>-3</sup>
 h<sup>-1</sup>
. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>001D16A</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Filtration</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Filtration</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Filtración</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Décontamination</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Decontamination</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Descontaminación</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Pollution</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Pollution</s0>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Polución</s0>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Eau usée</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Waste water</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Agua residual</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Charbon actif</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Activated carbon</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Carbón activado</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Estrone</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Estrone</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Estrona</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Ethinylestradiol</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Ethinylestradiol</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Etinilestradiol</s0>
<s2>NK</s2>
<s2>FR</s2>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>En discontinu</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Batchwise</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>En discontinuo</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Activité biologique</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Biological activity</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Actividad biológica</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Cinétique</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Kinetics</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Cinética</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Composé organique</s0>
<s2>NA</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Organic compounds</s0>
<s2>NA</s2>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Compuesto orgánico</s0>
<s2>NA</s2>
<s5>11</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Adsorption</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Adsorption</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Adsorción</s0>
<s5>12</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Nitrosamine</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Nitrosamine</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Nitrosamina</s0>
<s2>NK</s2>
<s2>FX</s2>
<s5>13</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE"><s0>Analyse tendance</s0>
<s5>14</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG"><s0>Trend analysis</s0>
<s5>14</s5>
</fC03>
<fC03 i1="14" i2="X" l="SPA"><s0>Análisis tendencia</s0>
<s5>14</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE"><s0>Composé hydrophobe</s0>
<s5>15</s5>
</fC03>
<fC03 i1="15" i2="X" l="ENG"><s0>Hydrophobic compound</s0>
<s5>15</s5>
</fC03>
<fC03 i1="15" i2="X" l="SPA"><s0>Compuesto hidrofobo</s0>
<s5>15</s5>
</fC03>
<fC03 i1="16" i2="X" l="FRE"><s0>Surveillance</s0>
<s5>16</s5>
</fC03>
<fC03 i1="16" i2="X" l="ENG"><s0>Surveillance</s0>
<s5>16</s5>
</fC03>
<fC03 i1="16" i2="X" l="SPA"><s0>Vigilancia</s0>
<s5>16</s5>
</fC03>
<fC03 i1="17" i2="X" l="FRE"><s0>Performance</s0>
<s5>17</s5>
</fC03>
<fC03 i1="17" i2="X" l="ENG"><s0>Performance</s0>
<s5>17</s5>
</fC03>
<fC03 i1="17" i2="X" l="SPA"><s0>Rendimiento</s0>
<s5>17</s5>
</fC03>
<fC03 i1="18" i2="X" l="FRE"><s0>Filtre sable</s0>
<s5>18</s5>
</fC03>
<fC03 i1="18" i2="X" l="ENG"><s0>Sand filter</s0>
<s5>18</s5>
</fC03>
<fC03 i1="18" i2="X" l="SPA"><s0>Filtro arena</s0>
<s5>18</s5>
</fC03>
<fC03 i1="19" i2="X" l="FRE"><s0>Station épuration</s0>
<s5>19</s5>
</fC03>
<fC03 i1="19" i2="X" l="ENG"><s0>Sewage treatment plant</s0>
<s5>19</s5>
</fC03>
<fC03 i1="19" i2="X" l="SPA"><s0>Estación depuradora</s0>
<s5>19</s5>
</fC03>
<fC03 i1="20" i2="X" l="FRE"><s0>Dégradation biologique</s0>
<s5>20</s5>
</fC03>
<fC03 i1="20" i2="X" l="ENG"><s0>Biodegradation</s0>
<s5>20</s5>
</fC03>
<fC03 i1="20" i2="X" l="SPA"><s0>Degradación biológica</s0>
<s5>20</s5>
</fC03>
<fC03 i1="21" i2="X" l="FRE"><s0>Biofiltre</s0>
<s5>21</s5>
</fC03>
<fC03 i1="21" i2="X" l="ENG"><s0>Biofilter</s0>
<s5>21</s5>
</fC03>
<fC03 i1="21" i2="X" l="SPA"><s0>Biofiltro</s0>
<s5>21</s5>
</fC03>
<fC03 i1="22" i2="X" l="FRE"><s0>Oestrogène</s0>
<s5>22</s5>
</fC03>
<fC03 i1="22" i2="X" l="ENG"><s0>Estrogen</s0>
<s5>22</s5>
</fC03>
<fC03 i1="22" i2="X" l="SPA"><s0>Estrógeno</s0>
<s5>22</s5>
</fC03>
<fC03 i1="23" i2="X" l="FRE"><s0>Perturbateur endocrinien</s0>
<s5>23</s5>
</fC03>
<fC03 i1="23" i2="X" l="ENG"><s0>Endocrine disruptor</s0>
<s5>23</s5>
</fC03>
<fC03 i1="23" i2="X" l="SPA"><s0>Disruptor endocrino</s0>
<s5>23</s5>
</fC03>
<fC03 i1="24" i2="X" l="FRE"><s0>Hormone stéroïde sexuelle</s0>
<s5>35</s5>
</fC03>
<fC03 i1="24" i2="X" l="ENG"><s0>Sex steroid hormone</s0>
<s5>35</s5>
</fC03>
<fC03 i1="24" i2="X" l="SPA"><s0>Hormona esteroide sexual</s0>
<s5>35</s5>
</fC03>
<fC03 i1="25" i2="X" l="FRE"><s0>Devenir polluant</s0>
<s5>36</s5>
</fC03>
<fC03 i1="25" i2="X" l="ENG"><s0>Pollutant behavior</s0>
<s5>36</s5>
</fC03>
<fC03 i1="25" i2="X" l="SPA"><s0>Evolución contaminante</s0>
<s5>36</s5>
</fC03>
<fC03 i1="26" i2="X" l="FRE"><s0>Bioréacteur</s0>
<s5>37</s5>
</fC03>
<fC03 i1="26" i2="X" l="ENG"><s0>Bioreactor</s0>
<s5>37</s5>
</fC03>
<fC03 i1="26" i2="X" l="SPA"><s0>Biorreactor</s0>
<s5>37</s5>
</fC03>
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<s5>38</s5>
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<s5>38</s5>
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<server><NO>PASCAL 11-0267416 INIST</NO>
<ET>Assessing granular media filtration for the removal of chemical contaminants from wastewater</ET>
<AU>HO (Lionel); GRASSET (Charlotte); HOEFEL (Daniel); DIXON (Mike B.); LEUSCH (Frederic D. L.); NEWCOMBE (Gayle); SAINT (Christopher P.); BROOKES (Justin D.)</AU>
<AF>Australian Water Quality Centre, SA Water Corporation, 250 Victoria Square/Adelaide SA 5000/Australie (1 aut., 3 aut., 4 aut., 6 aut., 7 aut.); School of Earth & Environmental Sciences, The University of Adelaide/SA 5005/Australie (1 aut., 3 aut., 7 aut., 8 aut.); École Superieure de Chimie Physique Électronique de Lyon, 43 Boulevard du 11 Novembre 1918, BP 2077/69616 Villeurbanne/France (2 aut.); Griffith University, Smart Water Research Centre, Edmund Rice Drive/Southport, QLD 4222/Australie (5 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Water research : (Oxford); ISSN 0043-1354; Coden WATRAG; Royaume-Uni; Da. 2011; Vol. 45; No. 11; Pp. 3461-3472; Bibl. 2 p.1/4</SO>
<LA>Anglais</LA>
<EA>Granular media filtration was evaluated for the removal of a suite of chemical contaminants that can be found in wastewater. Laboratory- and pilot-scale sand and granular activated carbon (GAC) filters were trialled for their ability to remove atrazine, estrone (E1), 17α-ethynylestradiol (EE2), N-nitrosodimethylamine (NDMA), N-nitrosomorpholine (NMOR) and N-nitrosodiethylamine (NDEA). In general, sand filtration was ineffective in removing the contaminants from a tertiary treated wastewater, with the exception of E1 and EE2, where efficient removals were observed after approximately 150 d. Batch degradation experiments confirmed that the removal of E1 was through biological activity, with a pseudo-first-order degradation rate constant of 7.4 x 10<sup>-3</sup>
 h<sup>-1</sup>
. GAC filtration was initially able to effectively remove all contaminants; although removals decreased over time due to competition with other organics present in the water. The only exception was atrazine where removal remained consistently high throughout the experiment. Previously unreported differences were observed in the adsorption of the three nitrosamines, with the ease of removal following the trend, NDEA > NMOR > NDMA, consistent with their hydrophobic character. In most instances the removals from the pilot-scale filters were generally in agreement with the laboratory-scale filter, suggesting that there is potential in using laboratory-scale filters as monitoring tools to evaluate the performance of pilot- and possibly full-scale sand and GAC filters at wastewater treatment plants.</EA>
<CC>001D16A</CC>
<FD>Filtration; Décontamination; Pollution; Eau usée; Charbon actif; Estrone; Ethinylestradiol; En discontinu; Activité biologique; Cinétique; Composé organique; Adsorption; Nitrosamine; Analyse tendance; Composé hydrophobe; Surveillance; Performance; Filtre sable; Station épuration; Dégradation biologique; Biofiltre; Oestrogène; Perturbateur endocrinien; Hormone stéroïde sexuelle; Devenir polluant; Bioréacteur; Epuration biologique</FD>
<ED>Filtration; Decontamination; Pollution; Waste water; Activated carbon; Estrone; Ethinylestradiol; Batchwise; Biological activity; Kinetics; Organic compounds; Adsorption; Nitrosamine; Trend analysis; Hydrophobic compound; Surveillance; Performance; Sand filter; Sewage treatment plant; Biodegradation; Biofilter; Estrogen; Endocrine disruptor; Sex steroid hormone; Pollutant behavior; Bioreactor; Biological purification</ED>
<SD>Filtración; Descontaminación; Polución; Agua residual; Carbón activado; Estrona; Etinilestradiol; En discontinuo; Actividad biológica; Cinética; Compuesto orgánico; Adsorción; Nitrosamina; Análisis tendencia; Compuesto hidrofobo; Vigilancia; Rendimiento; Filtro arena; Estación depuradora; Degradación biológica; Biofiltro; Estrógeno; Disruptor endocrino; Hormona esteroide sexual; Evolución contaminante; Biorreactor; Depuración biológica</SD>
<LO>INIST-8940A.354000192136290200</LO>
<ID>11-0267416</ID>
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Assessing granular media filtration for the removal of chemical contaminants from wastewater

Assessing granular media filtration for the removal of chemical contaminants from wastewater

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