LeHavreV1, PascalFrancis, Corpus, bibRecord, 000208

Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet

Identifieur interne : 000208 ( PascalFrancis/Corpus ); précédent : 000207; suivant : 000209

Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet

Auteurs : A. Motelay-Massei ; B. Garban ; K. Tiphagne-Larcher ; M. Chevreuil ; D. Ollivon

Source :

Water research : (Oxford) [ 0043-1354 ] ; 2006.

RBID : Pascal:06-0325876

Descripteurs français

Pascal (Inist)
- Bilan matière, Composé aromatique polycyclique, Hydrocarbure, Zone urbaine, Bassin versant, Phénomène transport, Surveillance, Pollution air, Retombée atmosphérique, Eau ruissellement, Cours eau, Rue, Eau surface, France, Devenir polluant.

English descriptors

KwdEn :
- Air pollution, Atmospheric fallout, France, Hydrocarbon, Material balance, Pollutant behavior, Polycyclic aromatic compound, Runoff water, Stream, Street, Surface water, Surveillance, Transport process, Urban area, Watershed.

Abstract

Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km^-2yr^-1 while PAH atmospheric deposition was 0.21 kg km^-2yr^-1. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).

Notice en format standard (ISO 2709)

Pour connaître la documentation sur le format Inist Standard.

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A14	`01`			`@1 Département de Géologie, UMR CNRS 6143, Faculté des Sciences et Techniques, Université de Rouen, 10 Boulevard de Broglie @2 76821 Mont-Saint-Aignan @3 FRA @Z 1 aut.`
A14	`02`			`@1 Laboratoire Hydrologie et Environnement, Ecole Pratique des Hautes Etudes, UMR Sisyphe 7619,Uniuersité Pierre et Marie Curie, 4 place Jussieu, case 105 @2 75252 Paris @3 FRA @Z 2 aut. @Z 3 aut. @Z 4 aut. @Z 5 aut.`
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C01	`01`		`ENG`	@0 Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km^-2yr^-1 while PAH atmospheric deposition was 0.21 kg km^-2yr^-1. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).
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C07	`03`	`X`	`FRE`	`@0 Composé organique @2 NA @5 44`
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Format Inist (serveur)

NO :	PASCAL 06-0325876 INIST
ET :	Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet
AU :	MOTELAY-MASSEI (A.); GARBAN (B.); TIPHAGNE-LARCHER (K.); CHEVREUIL (M.); OLLIVON (D.)
AF :	Département de Géologie, UMR CNRS 6143, Faculté des Sciences et Techniques, Université de Rouen, 10 Boulevard de Broglie/76821 Mont-Saint-Aignan/France (1 aut.); Laboratoire Hydrologie et Environnement, Ecole Pratique des Hautes Etudes, UMR Sisyphe 7619,Uniuersité Pierre et Marie Curie, 4 place Jussieu, case 105/75252 Paris/France (2 aut., 3 aut., 4 aut., 5 aut.)
DT :	Publication en série; Niveau analytique
SO :	Water research : (Oxford); ISSN 0043-1354; Coden WATRAG; Royaume-Uni; Da. 2006; Vol. 40; No. 10; Pp. 1995-2006; Bibl. 1 p.1/4
LA :	Anglais
EA :	Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km^-2yr^-1 while PAH atmospheric deposition was 0.21 kg km^-2yr^-1. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).
CC :	001D16A; 001D16B06
FD :	Bilan matière; Composé aromatique polycyclique; Hydrocarbure; Zone urbaine; Bassin versant; Phénomène transport; Surveillance; Pollution air; Retombée atmosphérique; Eau ruissellement; Cours eau; Rue; Eau surface; France; Devenir polluant
FG :	Europe; Polluant organique persistant; Composé organique
ED :	Material balance; Polycyclic aromatic compound; Hydrocarbon; Urban area; Watershed; Transport process; Surveillance; Air pollution; Atmospheric fallout; Runoff water; Stream; Street; Surface water; France; Pollutant behavior
EG :	Europe; Persistent organic pollutant; Organic compounds
SD :	Balance materia; Compuesto aromático policíclico; Hidrocarburo; Zona urbana; Cuenca; Fenómeno transporte; Vigilancia; Contaminación aire; Recaída atmosférica; Escorrentía; Curso agua; Calle; Agua superficie; Francia; Evolución contaminante
LO :	INIST-8940A.354000142583300080
ID :	06-0325876

Links to Exploration step

Pascal:06-0325876

Le document en format XML

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<front><div type="abstract" xml:lang="en">Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km<sup>-2</sup>
yr<sup>-1</sup>
 while PAH atmospheric deposition was 0.21 kg km<sup>-2</sup>
yr<sup>-1</sup>
. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).</div>
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<fA66 i1="01"><s0>GBR</s0>
</fA66>
<fC01 i1="01" l="ENG"><s0>Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km<sup>-2</sup>
yr<sup>-1</sup>
 while PAH atmospheric deposition was 0.21 kg km<sup>-2</sup>
yr<sup>-1</sup>
. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).</s0>
</fC01>
<fC02 i1="01" i2="X"><s0>001D16A</s0>
</fC02>
<fC02 i1="02" i2="X"><s0>001D16B06</s0>
</fC02>
<fC03 i1="01" i2="X" l="FRE"><s0>Bilan matière</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="ENG"><s0>Material balance</s0>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="X" l="SPA"><s0>Balance materia</s0>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="X" l="FRE"><s0>Composé aromatique polycyclique</s0>
<s2>FX</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="ENG"><s0>Polycyclic aromatic compound</s0>
<s2>FX</s2>
<s5>02</s5>
</fC03>
<fC03 i1="02" i2="X" l="SPA"><s0>Compuesto aromático policíclico</s0>
<s2>FX</s2>
<s5>02</s5>
</fC03>
<fC03 i1="03" i2="X" l="FRE"><s0>Hydrocarbure</s0>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="ENG"><s0>Hydrocarbon</s0>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="03" i2="X" l="SPA"><s0>Hidrocarburo</s0>
<s2>FX</s2>
<s5>03</s5>
</fC03>
<fC03 i1="04" i2="X" l="FRE"><s0>Zone urbaine</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="ENG"><s0>Urban area</s0>
<s5>04</s5>
</fC03>
<fC03 i1="04" i2="X" l="SPA"><s0>Zona urbana</s0>
<s5>04</s5>
</fC03>
<fC03 i1="05" i2="X" l="FRE"><s0>Bassin versant</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="ENG"><s0>Watershed</s0>
<s5>05</s5>
</fC03>
<fC03 i1="05" i2="X" l="SPA"><s0>Cuenca</s0>
<s5>05</s5>
</fC03>
<fC03 i1="06" i2="X" l="FRE"><s0>Phénomène transport</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="ENG"><s0>Transport process</s0>
<s5>06</s5>
</fC03>
<fC03 i1="06" i2="X" l="SPA"><s0>Fenómeno transporte</s0>
<s5>06</s5>
</fC03>
<fC03 i1="07" i2="X" l="FRE"><s0>Surveillance</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="ENG"><s0>Surveillance</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="X" l="SPA"><s0>Vigilancia</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Pollution air</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Air pollution</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Contaminación aire</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Retombée atmosphérique</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Atmospheric fallout</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Recaída atmosférica</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="X" l="FRE"><s0>Eau ruissellement</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="ENG"><s0>Runoff water</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="X" l="SPA"><s0>Escorrentía</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="X" l="FRE"><s0>Cours eau</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="ENG"><s0>Stream</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="X" l="SPA"><s0>Curso agua</s0>
<s5>11</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Rue</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Street</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Calle</s0>
<s5>12</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Eau surface</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Surface water</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Agua superficie</s0>
<s5>13</s5>
</fC03>
<fC03 i1="14" i2="X" l="FRE"><s0>France</s0>
<s2>NG</s2>
<s5>31</s5>
</fC03>
<fC03 i1="14" i2="X" l="ENG"><s0>France</s0>
<s2>NG</s2>
<s5>31</s5>
</fC03>
<fC03 i1="14" i2="X" l="SPA"><s0>Francia</s0>
<s2>NG</s2>
<s5>31</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE"><s0>Devenir polluant</s0>
<s5>35</s5>
</fC03>
<fC03 i1="15" i2="X" l="ENG"><s0>Pollutant behavior</s0>
<s5>35</s5>
</fC03>
<fC03 i1="15" i2="X" l="SPA"><s0>Evolución contaminante</s0>
<s5>35</s5>
</fC03>
<fC07 i1="01" i2="X" l="FRE"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="ENG"><s0>Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="X" l="SPA"><s0>Europa</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="X" l="FRE"><s0>Polluant organique persistant</s0>
<s5>43</s5>
</fC07>
<fC07 i1="02" i2="X" l="ENG"><s0>Persistent organic pollutant</s0>
<s5>43</s5>
</fC07>
<fC07 i1="02" i2="X" l="SPA"><s0>Contaminante organico persistente</s0>
<s5>43</s5>
</fC07>
<fC07 i1="03" i2="X" l="FRE"><s0>Composé organique</s0>
<s2>NA</s2>
<s5>44</s5>
</fC07>
<fC07 i1="03" i2="X" l="ENG"><s0>Organic compounds</s0>
<s2>NA</s2>
<s5>44</s5>
</fC07>
<fC07 i1="03" i2="X" l="SPA"><s0>Compuesto orgánico</s0>
<s2>NA</s2>
<s5>44</s5>
</fC07>
<fN21><s1>212</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
<server><NO>PASCAL 06-0325876 INIST</NO>
<ET>Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet</ET>
<AU>MOTELAY-MASSEI (A.); GARBAN (B.); TIPHAGNE-LARCHER (K.); CHEVREUIL (M.); OLLIVON (D.)</AU>
<AF>Département de Géologie, UMR CNRS 6143, Faculté des Sciences et Techniques, Université de Rouen, 10 Boulevard de Broglie/76821 Mont-Saint-Aignan/France (1 aut.); Laboratoire Hydrologie et Environnement, Ecole Pratique des Hautes Etudes, UMR Sisyphe 7619,Uniuersité Pierre et Marie Curie, 4 place Jussieu, case 105/75252 Paris/France (2 aut., 3 aut., 4 aut., 5 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Water research : (Oxford); ISSN 0043-1354; Coden WATRAG; Royaume-Uni; Da. 2006; Vol. 40; No. 10; Pp. 1995-2006; Bibl. 1 p.1/4</SO>
<LA>Anglais</LA>
<EA>Polycyclic aromatic hydrocarbon (PAH) concentrations have been monitored simultaneously in ambient air, bulk atmospheric deposition and runoff waters during one year in a small urban watershed of the Seine river basin (France). PAH fluxes from the atmosphere to the outlet of the urban watershed have been calculated to establish a mass balance for PAHs. PAH flux in runoff waters was 5.2 kg km<sup>-2</sup>
yr<sup>-1</sup>
 while PAH atmospheric deposition was 0.21 kg km<sup>-2</sup>
yr<sup>-1</sup>
. The comparison between atmospheric input and output by runoff has shown the importance of street deposits that appeared to be the most important source of PAHs for surface waters in urban areas. PAH profiles in the various compartments showed the fate of PAHs in the air-water system: proportion of carcinogenic PAHs was more important in runoff waters (35%) than in bulk atmospheric deposition (22%) and air (6%).</EA>
<CC>001D16A; 001D16B06</CC>
<FD>Bilan matière; Composé aromatique polycyclique; Hydrocarbure; Zone urbaine; Bassin versant; Phénomène transport; Surveillance; Pollution air; Retombée atmosphérique; Eau ruissellement; Cours eau; Rue; Eau surface; France; Devenir polluant</FD>
<FG>Europe; Polluant organique persistant; Composé organique</FG>
<ED>Material balance; Polycyclic aromatic compound; Hydrocarbon; Urban area; Watershed; Transport process; Surveillance; Air pollution; Atmospheric fallout; Runoff water; Stream; Street; Surface water; France; Pollutant behavior</ED>
<EG>Europe; Persistent organic pollutant; Organic compounds</EG>
<SD>Balance materia; Compuesto aromático policíclico; Hidrocarburo; Zona urbana; Cuenca; Fenómeno transporte; Vigilancia; Contaminación aire; Recaída atmosférica; Escorrentía; Curso agua; Calle; Agua superficie; Francia; Evolución contaminante</SD>
<LO>INIST-8940A.354000142583300080</LO>
<ID>06-0325876</ID>
</server>
</inist>
</record>

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Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet

Mass balance for polycyclic aromatic hydrocarbons in the urban watershed of Le Havre (France) : Transport and fate of PAHs from the atmosphere to the outlet

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