UnivTrevesV1, PascalFrancis, Curation, bibRecord, 000C07

Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar

Identifieur interne : 000C07 ( PascalFrancis/Curation ); précédent : 000C06; suivant : 000C08

Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar

Auteurs : Meththika Vithanage [Corée du Sud, Sri Lanka] ; ANUSHKA UPAMALI RAJAPAKSHA [Corée du Sud, Sri Lanka] ; XIANGYU TANG [République populaire de Chine] ; Sören Thiele-Bruhn [Allemagne] ; KYE HOON KIM [Corée du Sud] ; Sung-Eun Lee [Corée du Sud] ; YONG SIK OK [Corée du Sud, Canada]

Source :

Journal of environmental management [ 0301-4797 ] ; 2014.

RBID : Pascal:14-0170411

Descripteurs français

Pascal (Inist)
- Sorption, Transport, Sol agricole, Plante, Espèce envahissante, Charbon bois, Suie, Médicament, Biosorption, Matière organique, Gestion environnement, Surveillance écologique, Protection environnement, Polluant émergent.
Wicri :
- topic : Médicament.

English descriptors

KwdEn :
- Agricultural soil, Biosorption, Charcoal, Drug, Emerging contaminant, Environmental management, Environmental monitoring, Environmental protection, Invasive species, Organic matter, Plant, Soot, Sorption, Transport.

Abstract

Sulfonamides (SAs) are one of the most frequently used antibiotics in the veterinary industry, showing high mobility in soils. Objectives of this research were to determine the sorption, distribution coefficients and involvement of different ionic forms of sulfamethazine (SMZ), a representative SAs, and to evaluate the transport of SMZ in biochar treated soils. Biochars were produced from an invasive plant, burcucumber (Sicyos angulatus L.), under slow pyrolysis conditions at peak temperatures of 300 °C (biochar-300) and 700 °C (biochar-700), respectively. The abilities of the biochars to retain SMZ in loamy sand and sandy loam soils were examined under different pHs and SMZ loadings. Soil column experiments were performed with and without biochars addition. Results showed that biochar-700 had a high degree of SMZ retention, with resultant decreased pH in both soils. Modeled effective sorption coefficients (K_D,eff) values indicated that the observed high SMZ retention at pH 3 could be attributed to the π-π electron donor-acceptor interaction and electrostatic cation exchange, whereas at pH 5 and 7, cation exchange was the main mechanisms responsible. There was no temporal retardation of SMZ in biochar treated soil as compared to the untreated soil. However, biochar-700 treatment achieved up to 89% and 82% increase in the SMZ retention in sandy loam and loamy sand soils, respectively. The overall results demonstrated that burcucumber biochar produced at higher temperature was effective in reducing the mobility of SMZ in the studied soils.

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A03		`1`		`@0 J. environ. manage.`
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A08	`01`	`1`	`ENG`	`@1 Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar`
A11	`01`	`1`		`@1 VITHANAGE (Meththika)`
A11	`02`	`1`		`@1 ANUSHKA UPAMALI RAJAPAKSHA`
A11	`03`	`1`		`@1 XIANGYU TANG`
A11	`04`	`1`		`@1 THIELE-BRUHN (Sören)`
A11	`05`	`1`		`@1 KYE HOON KIM`
A11	`06`	`1`		`@1 LEE (Sung-Eun)`
A11	`07`	`1`		`@1 YONG SIK OK`
A14	`01`			`@1 Korea Biochar Research Center and Department of Biological Environment, Kangwon National University @2 Chuncheon @3 KOR @Z 1 aut. @Z 2 aut. @Z 7 aut.`
A14	`02`			`@1 Chemical and Environmental Systems Modeling Research Group, Institute of Fundamental Studies @2 Kandy @3 LKA @Z 1 aut. @Z 2 aut.`
A14	`03`			`@1 Institute of Mountain Hazards and Environment, Chinese Academy of Sciences @2 Chengdu @3 CHN @Z 3 aut.`
A14	`04`			`@1 Department of Soil Science, University of Trier @2 Trier @3 DEU @Z 4 aut.`
A14	`05`			`@1 Department of Environmental Horticulture, The University of Seoul @2 Seoul @3 KOR @Z 5 aut.`
A14	`06`			`@1 School of Applied Biosciences, Kyungpook National University @2 Daegu @3 KOR @Z 6 aut.`
A14	`07`			`@1 Department of Renewable Resources, University of Alberta @2 Edmonton @3 CAN @Z 7 aut.`
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A23	`01`			`@0 ENG`
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C01	`01`		`ENG`	@0 Sulfonamides (SAs) are one of the most frequently used antibiotics in the veterinary industry, showing high mobility in soils. Objectives of this research were to determine the sorption, distribution coefficients and involvement of different ionic forms of sulfamethazine (SMZ), a representative SAs, and to evaluate the transport of SMZ in biochar treated soils. Biochars were produced from an invasive plant, burcucumber (Sicyos angulatus L.), under slow pyrolysis conditions at peak temperatures of 300 °C (biochar-300) and 700 °C (biochar-700), respectively. The abilities of the biochars to retain SMZ in loamy sand and sandy loam soils were examined under different pHs and SMZ loadings. Soil column experiments were performed with and without biochars addition. Results showed that biochar-700 had a high degree of SMZ retention, with resultant decreased pH in both soils. Modeled effective sorption coefficients (K_D,eff) values indicated that the observed high SMZ retention at pH 3 could be attributed to the π-π electron donor-acceptor interaction and electrostatic cation exchange, whereas at pH 5 and 7, cation exchange was the main mechanisms responsible. There was no temporal retardation of SMZ in biochar treated soil as compared to the untreated soil. However, biochar-700 treatment achieved up to 89% and 82% increase in the SMZ retention in sandy loam and loamy sand soils, respectively. The overall results demonstrated that burcucumber biochar produced at higher temperature was effective in reducing the mobility of SMZ in the studied soils.
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C03	`01`	`X`	`FRE`	`@0 Sorption @5 01`
C03	`01`	`X`	`ENG`	`@0 Sorption @5 01`
C03	`01`	`X`	`SPA`	`@0 Sorción @5 01`
C03	`02`	`X`	`FRE`	`@0 Transport @5 02`
C03	`02`	`X`	`ENG`	`@0 Transport @5 02`
C03	`02`	`X`	`SPA`	`@0 Transporte @5 02`
C03	`03`	`X`	`FRE`	`@0 Sol agricole @2 NT @5 03`
C03	`03`	`X`	`ENG`	`@0 Agricultural soil @2 NT @5 03`
C03	`03`	`X`	`SPA`	`@0 Suelo agrícola @2 NT @5 03`
C03	`04`	`X`	`FRE`	`@0 Plante @5 04`
C03	`04`	`X`	`ENG`	`@0 Plant @5 04`
C03	`04`	`X`	`SPA`	`@0 Planta @5 04`
C03	`05`	`X`	`FRE`	`@0 Espèce envahissante @5 05`
C03	`05`	`X`	`ENG`	`@0 Invasive species @5 05`
C03	`05`	`X`	`SPA`	`@0 Especie invasora @5 05`
C03	`06`	`X`	`FRE`	`@0 Charbon bois @5 06`
C03	`06`	`X`	`ENG`	`@0 Charcoal @5 06`
C03	`06`	`X`	`SPA`	`@0 Carbón madera @5 06`
C03	`07`	`X`	`FRE`	`@0 Suie @5 07`
C03	`07`	`X`	`ENG`	`@0 Soot @5 07`
C03	`07`	`X`	`SPA`	`@0 Hollín @5 07`
C03	`08`	`X`	`FRE`	`@0 Médicament @5 08`
C03	`08`	`X`	`ENG`	`@0 Drug @5 08`
C03	`08`	`X`	`SPA`	`@0 Medicamento @5 08`
C03	`09`	`X`	`FRE`	`@0 Biosorption @5 09`
C03	`09`	`X`	`ENG`	`@0 Biosorption @5 09`
C03	`09`	`X`	`SPA`	`@0 Biosorción @5 09`
C03	`10`	`X`	`FRE`	`@0 Matière organique @5 10`
C03	`10`	`X`	`ENG`	`@0 Organic matter @5 10`
C03	`10`	`X`	`SPA`	`@0 Materia orgánica @5 10`
C03	`11`	`X`	`FRE`	`@0 Gestion environnement @5 11`
C03	`11`	`X`	`ENG`	`@0 Environmental management @5 11`
C03	`11`	`X`	`SPA`	`@0 Gestiòn medio ambiente @5 11`
C03	`12`	`X`	`FRE`	`@0 Surveillance écologique @5 12`
C03	`12`	`X`	`ENG`	`@0 Environmental monitoring @5 12`
C03	`12`	`X`	`SPA`	`@0 Vigilancia ecológica @5 12`
C03	`13`	`X`	`FRE`	`@0 Protection environnement @5 13`
C03	`13`	`X`	`ENG`	`@0 Environmental protection @5 13`
C03	`13`	`X`	`SPA`	`@0 Protección medio ambiente @5 13`
C03	`14`	`X`	`FRE`	`@0 Polluant émergent @4 CD @5 96`
C03	`14`	`X`	`ENG`	`@0 Emerging contaminant @4 CD @5 96`
N21				`@1 209`
N44	`01`			`@1 OTO`
N82				`@1 OTO`

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Le document en format XML

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<sourceDesc><biblStruct><analytic><title xml:lang="en" level="a">Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar</title>
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<author><name sortKey="Yong Sik Ok" sort="Yong Sik Ok" uniqKey="Yong Sik Ok" last="Yong Sik Ok">YONG SIK OK</name>
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<s2>Chuncheon</s2>
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<series><title level="j" type="main">Journal of environmental management</title>
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<profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Agricultural soil</term>
<term>Biosorption</term>
<term>Charcoal</term>
<term>Drug</term>
<term>Emerging contaminant</term>
<term>Environmental management</term>
<term>Environmental monitoring</term>
<term>Environmental protection</term>
<term>Invasive species</term>
<term>Organic matter</term>
<term>Plant</term>
<term>Soot</term>
<term>Sorption</term>
<term>Transport</term>
</keywords>
<keywords scheme="Pascal" xml:lang="fr"><term>Sorption</term>
<term>Transport</term>
<term>Sol agricole</term>
<term>Plante</term>
<term>Espèce envahissante</term>
<term>Charbon bois</term>
<term>Suie</term>
<term>Médicament</term>
<term>Biosorption</term>
<term>Matière organique</term>
<term>Gestion environnement</term>
<term>Surveillance écologique</term>
<term>Protection environnement</term>
<term>Polluant émergent</term>
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<front><div type="abstract" xml:lang="en">Sulfonamides (SAs) are one of the most frequently used antibiotics in the veterinary industry, showing high mobility in soils. Objectives of this research were to determine the sorption, distribution coefficients and involvement of different ionic forms of sulfamethazine (SMZ), a representative SAs, and to evaluate the transport of SMZ in biochar treated soils. Biochars were produced from an invasive plant, burcucumber (Sicyos angulatus L.), under slow pyrolysis conditions at peak temperatures of 300 °C (biochar-300) and 700 °C (biochar-700), respectively. The abilities of the biochars to retain SMZ in loamy sand and sandy loam soils were examined under different pHs and SMZ loadings. Soil column experiments were performed with and without biochars addition. Results showed that biochar-700 had a high degree of SMZ retention, with resultant decreased pH in both soils. Modeled effective sorption coefficients (K<sub>D,eff</sub>
) values indicated that the observed high SMZ retention at pH 3 could be attributed to the π-π electron donor-acceptor interaction and electrostatic cation exchange, whereas at pH 5 and 7, cation exchange was the main mechanisms responsible. There was no temporal retardation of SMZ in biochar treated soil as compared to the untreated soil. However, biochar-700 treatment achieved up to 89% and 82% increase in the SMZ retention in sandy loam and loamy sand soils, respectively. The overall results demonstrated that burcucumber biochar produced at higher temperature was effective in reducing the mobility of SMZ in the studied soils.</div>
</front>
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<fA08 i1="01" i2="1" l="ENG"><s1>Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar</s1>
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<fA11 i1="01" i2="1"><s1>VITHANAGE (Meththika)</s1>
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<fA11 i1="02" i2="1"><s1>ANUSHKA UPAMALI RAJAPAKSHA</s1>
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<fA11 i1="03" i2="1"><s1>XIANGYU TANG</s1>
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<fA11 i1="04" i2="1"><s1>THIELE-BRUHN (Sören)</s1>
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<fA11 i1="05" i2="1"><s1>KYE HOON KIM</s1>
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<fA11 i1="06" i2="1"><s1>LEE (Sung-Eun)</s1>
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<fA11 i1="07" i2="1"><s1>YONG SIK OK</s1>
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<fA14 i1="01"><s1>Korea Biochar Research Center and Department of Biological Environment, Kangwon National University</s1>
<s2>Chuncheon</s2>
<s3>KOR</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
<sZ>7 aut.</sZ>
</fA14>
<fA14 i1="02"><s1>Chemical and Environmental Systems Modeling Research Group, Institute of Fundamental Studies</s1>
<s2>Kandy</s2>
<s3>LKA</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
</fA14>
<fA14 i1="03"><s1>Institute of Mountain Hazards and Environment, Chinese Academy of Sciences</s1>
<s2>Chengdu</s2>
<s3>CHN</s3>
<sZ>3 aut.</sZ>
</fA14>
<fA14 i1="04"><s1>Department of Soil Science, University of Trier</s1>
<s2>Trier</s2>
<s3>DEU</s3>
<sZ>4 aut.</sZ>
</fA14>
<fA14 i1="05"><s1>Department of Environmental Horticulture, The University of Seoul</s1>
<s2>Seoul</s2>
<s3>KOR</s3>
<sZ>5 aut.</sZ>
</fA14>
<fA14 i1="06"><s1>School of Applied Biosciences, Kyungpook National University</s1>
<s2>Daegu</s2>
<s3>KOR</s3>
<sZ>6 aut.</sZ>
</fA14>
<fA14 i1="07"><s1>Department of Renewable Resources, University of Alberta</s1>
<s2>Edmonton</s2>
<s3>CAN</s3>
<sZ>7 aut.</sZ>
</fA14>
<fA20><s1>95-103</s1>
</fA20>
<fA21><s1>2014</s1>
</fA21>
<fA23 i1="01"><s0>ENG</s0>
</fA23>
<fA43 i1="01"><s1>INIST</s1>
<s2>16218</s2>
<s5>354000502757270110</s5>
</fA43>
<fA44><s0>0000</s0>
<s1>© 2014 INIST-CNRS. All rights reserved.</s1>
</fA44>
<fA45><s0>3/4 p.</s0>
</fA45>
<fA47 i1="01" i2="1"><s0>14-0170411</s0>
</fA47>
<fA60><s1>P</s1>
</fA60>
<fA61><s0>A</s0>
</fA61>
<fA64 i1="01" i2="1"><s0>Journal of environmental management</s0>
</fA64>
<fA66 i1="01"><s0>GBR</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>Sulfonamides (SAs) are one of the most frequently used antibiotics in the veterinary industry, showing high mobility in soils. Objectives of this research were to determine the sorption, distribution coefficients and involvement of different ionic forms of sulfamethazine (SMZ), a representative SAs, and to evaluate the transport of SMZ in biochar treated soils. Biochars were produced from an invasive plant, burcucumber (Sicyos angulatus L.), under slow pyrolysis conditions at peak temperatures of 300 °C (biochar-300) and 700 °C (biochar-700), respectively. The abilities of the biochars to retain SMZ in loamy sand and sandy loam soils were examined under different pHs and SMZ loadings. Soil column experiments were performed with and without biochars addition. Results showed that biochar-700 had a high degree of SMZ retention, with resultant decreased pH in both soils. Modeled effective sorption coefficients (K<sub>D,eff</sub>
) values indicated that the observed high SMZ retention at pH 3 could be attributed to the π-π electron donor-acceptor interaction and electrostatic cation exchange, whereas at pH 5 and 7, cation exchange was the main mechanisms responsible. There was no temporal retardation of SMZ in biochar treated soil as compared to the untreated soil. However, biochar-700 treatment achieved up to 89% and 82% increase in the SMZ retention in sandy loam and loamy sand soils, respectively. The overall results demonstrated that burcucumber biochar produced at higher temperature was effective in reducing the mobility of SMZ in the studied soils.</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>002A14D02A</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>002A14D02B</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Sorption</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Sorption</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Sorción</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Transport</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Transport</s0>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Transporte</s0>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Sol agricole</s0>
<s2>NT</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Agricultural soil</s0>
<s2>NT</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Suelo agrícola</s0>
<s2>NT</s2>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Plante</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Plant</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Planta</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Espèce envahissante</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Invasive species</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Especie invasora</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Charbon bois</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Charcoal</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Carbón madera</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Suie</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Soot</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Hollín</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Médicament</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Drug</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Medicamento</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Biosorption</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Biosorption</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Biosorción</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Matière organique</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Organic matter</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Materia orgánica</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Gestion environnement</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Environmental management</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Gestiòn medio ambiente</s0>
<s5>11</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Surveillance écologique</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Environmental monitoring</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Vigilancia ecológica</s0>
<s5>12</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Protection environnement</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Environmental protection</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Protección medio ambiente</s0>
<s5>13</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE"><s0>Polluant émergent</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG"><s0>Emerging contaminant</s0>
<s4>CD</s4>
<s5>96</s5>
</fC03>
<fN21><s1>209</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
</inist>
</record>

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Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar

Sorption and transport of sulfamethazine in agricultural soils amended with invasive-plant-derived biochar

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