Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment
Identifieur interne :
000F90 ( PascalFrancis/Corpus );
précédent :
000F89;
suivant :
000F91
Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment
Auteurs : A. Krein ;
R. BierlSource :
-
IAHS-AISH publication [ 0144-7815 ] ; 1999.
RBID : Pascal:99-0526389
Descripteurs français
- Pascal (Inist)
- Bassin versant,
Crue,
Pollution,
Métal lourd,
Composé organique,
Polluant,
Origine,
Urbanisation,
Hydrogramme,
Matière en suspension,
Sédiment,
Hydrocarbure aromatique polycyclique,
Solubilité,
Dilution,
Utilisation terrain,
Bedrock,
Hunsruck,
Précipitation atmosphérique,
Micropolluant,
Remise en suspension.
English descriptors
- KwdEn :
- Hunsruck,
atmospheric precipitation,
bedrock,
dilution,
drainage basins,
floods,
heavy metals,
hydrographs,
land use,
organic compounds,
pollutants,
pollution,
polycyclic aromatic hydrocarbons,
provenance,
sediments,
solubility,
suspended materials,
urbanization.
Abstract
Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions.
Notice en format standard (ISO 2709)
Pour connaître la documentation sur le format Inist Standard.
| pA |
| A01 | 01 | 1 | | @0 0144-7815 |
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| A06 | | | | @2 259 |
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| A08 | 01 | 1 | ENG | @1 Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment |
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| A09 | 01 | 1 | ENG | @1 Impacts of urban growth on surface water and groundwater quality : Birmingham, 18-30 July 1999 |
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| A11 | 01 | 1 | | @1 KREIN (A.) |
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| A11 | 02 | 1 | | @1 BIERL (R.) |
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| A12 | 01 | 1 | | @1 ELLIS (J. Bryan) @9 ed. |
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| A14 | 01 | | | @1 University of Trier, Department of Hydrology @2 54286 Trier @3 DEU @Z 1 aut. @Z 2 aut. |
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| A18 | 01 | 1 | | @1 International Union of Geodesy and Geophysics @2 Bruxelles @3 BEL @9 patr. |
|---|
| A20 | | | | @1 263-268 |
|---|
| A21 | | | | @1 1999 |
|---|
| A23 | 01 | | | @0 ENG |
|---|
| A26 | 01 | | | @0 1-901502-06-6 |
|---|
| A43 | 01 | | | @1 INIST @2 8967 @5 354000080041610320 |
|---|
| A44 | | | | @0 0000 @1 © 1999 INIST-CNRS. All rights reserved. |
|---|
| A45 | | | | @0 2 ref. |
|---|
| A47 | 01 | 1 | | @0 99-0526389 |
|---|
| A60 | | | | @1 P @2 C |
|---|
| A61 | | | | @0 A |
|---|
| A64 | 01 | 1 | | @0 IAHS-AISH publication |
|---|
| A66 | 01 | | | @0 GBR |
|---|
| C01 | 01 | | ENG | @0 Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions. |
|---|
| C02 | 01 | 2 | | @0 226B04 |
|---|
| C02 | 02 | 2 | | @0 226A01 |
|---|
| C02 | 03 | X | | @0 001E01O04 |
|---|
| C02 | 04 | X | | @0 001E01N01 |
|---|
| C03 | 01 | 2 | FRE | @0 Bassin versant @5 01 |
|---|
| C03 | 01 | 2 | ENG | @0 drainage basins @5 01 |
|---|
| C03 | 01 | 2 | SPA | @0 Cuenca @5 01 |
|---|
| C03 | 02 | 2 | FRE | @0 Crue @5 02 |
|---|
| C03 | 02 | 2 | ENG | @0 floods @5 02 |
|---|
| C03 | 02 | 2 | SPA | @0 Crecida @5 02 |
|---|
| C03 | 03 | 2 | FRE | @0 Pollution @5 03 |
|---|
| C03 | 03 | 2 | ENG | @0 pollution @5 03 |
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| C03 | 03 | 2 | SPA | @0 Polución @5 03 |
|---|
| C03 | 04 | 2 | FRE | @0 Métal lourd @5 04 |
|---|
| C03 | 04 | 2 | ENG | @0 heavy metals @5 04 |
|---|
| C03 | 04 | 2 | SPA | @0 Metal pesado @5 04 |
|---|
| C03 | 05 | 2 | FRE | @0 Composé organique @5 05 |
|---|
| C03 | 05 | 2 | ENG | @0 organic compounds @5 05 |
|---|
| C03 | 06 | 2 | FRE | @0 Polluant @5 06 |
|---|
| C03 | 06 | 2 | ENG | @0 pollutants @5 06 |
|---|
| C03 | 06 | 2 | SPA | @0 Contaminante @5 06 |
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| C03 | 07 | 2 | FRE | @0 Origine @5 07 |
|---|
| C03 | 07 | 2 | ENG | @0 provenance @5 07 |
|---|
| C03 | 07 | 2 | SPA | @0 Origen @5 07 |
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| C03 | 08 | 2 | FRE | @0 Urbanisation @5 08 |
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| C03 | 08 | 2 | ENG | @0 urbanization @5 08 |
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| C03 | 08 | 2 | SPA | @0 Urbanización @5 08 |
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| C03 | 09 | 2 | FRE | @0 Hydrogramme @5 09 |
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| C03 | 09 | 2 | ENG | @0 hydrographs @5 09 |
|---|
| C03 | 09 | 2 | SPA | @0 Hidrograma @5 09 |
|---|
| C03 | 10 | 2 | FRE | @0 Matière en suspension @5 10 |
|---|
| C03 | 10 | 2 | ENG | @0 suspended materials @5 10 |
|---|
| C03 | 10 | 2 | SPA | @0 Materia en suspensión @5 10 |
|---|
| C03 | 11 | 2 | FRE | @0 Sédiment @5 11 |
|---|
| C03 | 11 | 2 | ENG | @0 sediments @5 11 |
|---|
| C03 | 11 | 2 | SPA | @0 Sedimento @5 11 |
|---|
| C03 | 12 | 2 | FRE | @0 Hydrocarbure aromatique polycyclique @5 12 |
|---|
| C03 | 12 | 2 | ENG | @0 polycyclic aromatic hydrocarbons @5 12 |
|---|
| C03 | 13 | 2 | FRE | @0 Solubilité @5 13 |
|---|
| C03 | 13 | 2 | ENG | @0 solubility @5 13 |
|---|
| C03 | 13 | 2 | SPA | @0 Solubilidad @5 13 |
|---|
| C03 | 14 | 2 | FRE | @0 Dilution @5 14 |
|---|
| C03 | 14 | 2 | ENG | @0 dilution @5 14 |
|---|
| C03 | 14 | 2 | SPA | @0 Dilución @5 14 |
|---|
| C03 | 15 | 2 | FRE | @0 Utilisation terrain @5 16 |
|---|
| C03 | 15 | 2 | ENG | @0 land use @5 16 |
|---|
| C03 | 15 | 2 | SPA | @0 Utilización terreno @5 16 |
|---|
| C03 | 16 | 2 | FRE | @0 Bedrock @5 17 |
|---|
| C03 | 16 | 2 | ENG | @0 bedrock @5 17 |
|---|
| C03 | 16 | 2 | SPA | @0 Roca firme @5 17 |
|---|
| C03 | 17 | 2 | FRE | @0 Hunsruck @2 NG @5 18 |
|---|
| C03 | 17 | 2 | ENG | @0 Hunsruck @2 NG @5 18 |
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| C03 | 18 | 2 | FRE | @0 Précipitation atmosphérique @5 19 |
|---|
| C03 | 18 | 2 | ENG | @0 atmospheric precipitation @5 19 |
|---|
| C03 | 18 | 2 | SPA | @0 Precipitación atmosférica @5 19 |
|---|
| C03 | 19 | 2 | FRE | @0 Micropolluant @4 INC @5 52 |
|---|
| C03 | 20 | 2 | FRE | @0 Remise en suspension @4 INC @5 53 |
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| C06 | | | | @0 ILS |
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| C07 | 01 | 2 | FRE | @0 Rhénanie Palatinat @2 NG |
|---|
| C07 | 01 | 2 | ENG | @0 Rhineland-Palatinate Germany @2 NG |
|---|
| C07 | 01 | 2 | SPA | @0 Renania Palatinado @2 NG |
|---|
| C07 | 02 | 2 | FRE | @0 Allemagne @2 NG |
|---|
| C07 | 02 | 2 | ENG | @0 Germany @2 NG |
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| C07 | 02 | 2 | SPA | @0 Alemania @2 NG |
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| C07 | 03 | 2 | FRE | @0 Europe Centrale @2 NG |
|---|
| C07 | 03 | 2 | ENG | @0 Central Europe @2 NG |
|---|
| C07 | 03 | 2 | SPA | @0 Europa central @2 NG |
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| C07 | 04 | 2 | FRE | @0 Europe |
|---|
| C07 | 04 | 2 | ENG | @0 Europe |
|---|
| C07 | 04 | 2 | SPA | @0 Europa |
|---|
| N21 | | | | @1 340 |
|---|
|
|---|
| pR |
| A30 | 01 | 1 | ENG | @1 Impacts of urban growth on surface water and groundwater quality. International symposium @3 Birmingham GBR @4 1999-07-18 |
|---|
|
|---|
Format Inist (serveur)
| NO : | PASCAL 99-0526389 INIST |
|---|
| ET : | Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment |
|---|
| AU : | KREIN (A.); BIERL (R.); ELLIS (J. Bryan) |
|---|
| AF : | University of Trier, Department of Hydrology/54286 Trier/Allemagne (1 aut., 2 aut.) |
|---|
| DT : | Publication en série; Congrès; Niveau analytique |
|---|
| SO : | IAHS-AISH publication; ISSN 0144-7815; Royaume-Uni; Da. 1999; No. 259; Pp. 263-268; Bibl. 2 ref. |
|---|
| LA : | Anglais |
|---|
| EA : | Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions. |
|---|
| CC : | 226B04; 226A01; 001E01O04; 001E01N01 |
|---|
| FD : | Bassin versant; Crue; Pollution; Métal lourd; Composé organique; Polluant; Origine; Urbanisation; Hydrogramme; Matière en suspension; Sédiment; Hydrocarbure aromatique polycyclique; Solubilité; Dilution; Utilisation terrain; Bedrock; Hunsruck; Précipitation atmosphérique; Micropolluant; Remise en suspension |
|---|
| FG : | Rhénanie Palatinat; Allemagne; Europe Centrale; Europe |
|---|
| ED : | drainage basins; floods; pollution; heavy metals; organic compounds; pollutants; provenance; urbanization; hydrographs; suspended materials; sediments; polycyclic aromatic hydrocarbons; solubility; dilution; land use; bedrock; Hunsruck; atmospheric precipitation |
|---|
| EG : | Rhineland-Palatinate Germany; Germany; Central Europe; Europe |
|---|
| SD : | Cuenca; Crecida; Polución; Metal pesado; Contaminante; Origen; Urbanización; Hidrograma; Materia en suspensión; Sedimento; Solubilidad; Dilución; Utilización terreno; Roca firme; Precipitación atmosférica |
|---|
| LO : | INIST-8967.354000080041610320 |
|---|
| ID : | 99-0526389 |
|---|
Links to Exploration step
Pascal:99-0526389
Le document en format XML
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<author><name sortKey="Krein, A" sort="Krein, A" uniqKey="Krein A" first="A." last="Krein">A. Krein</name>
<affiliation><inist:fA14 i1="01"><s1>University of Trier, Department of Hydrology</s1>
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</publicationStmt><sourceDesc><biblStruct><analytic><title xml:lang="en" level="a">Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment</title>
<author><name sortKey="Krein, A" sort="Krein, A" uniqKey="Krein A" first="A." last="Krein">A. Krein</name>
<affiliation><inist:fA14 i1="01"><s1>University of Trier, Department of Hydrology</s1>
<s2>54286 Trier</s2>
<s3>DEU</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
</inist:fA14><author><name sortKey="Bierl, R" sort="Bierl, R" uniqKey="Bierl R" first="R." last="Bierl">R. Bierl</name>
<affiliation><inist:fA14 i1="01"><s1>University of Trier, Department of Hydrology</s1>
<s2>54286 Trier</s2>
<s3>DEU</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
</inist:fA14><series><title level="j" type="main">IAHS-AISH publication</title>
<idno type="ISSN">0144-7815</idno>
<imprint><date when="1999">1999</date>
</imprint><seriesStmt><title level="j" type="main">IAHS-AISH publication</title>
<idno type="ISSN">0144-7815</idno>
</seriesStmt><profileDesc><textClass><keywords scheme="KwdEn" xml:lang="en"><term>Hunsruck</term>
<term>atmospheric precipitation</term>
<term>bedrock</term>
<term>dilution</term>
<term>drainage basins</term>
<term>floods</term>
<term>heavy metals</term>
<term>hydrographs</term>
<term>land use</term>
<term>organic compounds</term>
<term>pollutants</term>
<term>pollution</term>
<term>polycyclic aromatic hydrocarbons</term>
<term>provenance</term>
<term>sediments</term>
<term>solubility</term>
<term>suspended materials</term>
<term>urbanization</term>
</keywords><keywords scheme="Pascal" xml:lang="fr"><term>Bassin versant</term>
<term>Crue</term>
<term>Pollution</term>
<term>Métal lourd</term>
<term>Composé organique</term>
<term>Polluant</term>
<term>Origine</term>
<term>Urbanisation</term>
<term>Hydrogramme</term>
<term>Matière en suspension</term>
<term>Sédiment</term>
<term>Hydrocarbure aromatique polycyclique</term>
<term>Solubilité</term>
<term>Dilution</term>
<term>Utilisation terrain</term>
<term>Bedrock</term>
<term>Hunsruck</term>
<term>Précipitation atmosphérique</term>
<term>Micropolluant</term>
<term>Remise en suspension</term>
</keywords><front><div type="abstract" xml:lang="en">Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions.</div>
</front><inist><standard h6="B"><pA><fA01 i1="01" i2="1"><s0>0144-7815</s0>
</fA01><fA06><s2>259</s2>
</fA06><fA08 i1="01" i2="1" l="ENG"><s1>Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment</s1>
</fA08><fA09 i1="01" i2="1" l="ENG"><s1>Impacts of urban growth on surface water and groundwater quality : Birmingham, 18-30 July 1999</s1>
</fA09><fA11 i1="01" i2="1"><s1>KREIN (A.)</s1>
</fA11><fA11 i1="02" i2="1"><s1>BIERL (R.)</s1>
</fA11><fA12 i1="01" i2="1"><s1>ELLIS (J. Bryan)</s1>
<s9>ed.</s9>
</fA12><fA14 i1="01"><s1>University of Trier, Department of Hydrology</s1>
<s2>54286 Trier</s2>
<s3>DEU</s3>
<sZ>1 aut.</sZ>
<sZ>2 aut.</sZ>
</fA14><fA18 i1="01" i2="1"><s1>International Union of Geodesy and Geophysics</s1>
<s2>Bruxelles</s2>
<s3>BEL</s3>
<s9>patr.</s9>
</fA18><fA20><s1>263-268</s1>
</fA20><fA21><s1>1999</s1>
</fA21><fA23 i1="01"><s0>ENG</s0>
</fA23><fA26 i1="01"><s0>1-901502-06-6</s0>
</fA26><fA43 i1="01"><s1>INIST</s1>
<s2>8967</s2>
<s5>354000080041610320</s5>
</fA43><fA44><s0>0000</s0>
<s1>© 1999 INIST-CNRS. All rights reserved.</s1>
</fA44><fA45><s0>2 ref.</s0>
</fA45><fA47 i1="01" i2="1"><s0>99-0526389</s0>
</fA47><fA60><s1>P</s1>
<s2>C</s2>
</fA60><fA64 i1="01" i2="1"><s0>IAHS-AISH publication</s0>
</fA64><fA66 i1="01"><s0>GBR</s0>
</fA66><fC01 i1="01" l="ENG"><s0>Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions.</s0>
</fC01><fC02 i1="01" i2="2"><s0>226B04</s0>
</fC02><fC02 i1="02" i2="2"><s0>226A01</s0>
</fC02><fC02 i1="03" i2="X"><s0>001E01O04</s0>
</fC02><fC02 i1="04" i2="X"><s0>001E01N01</s0>
</fC02><fC03 i1="01" i2="2" l="FRE"><s0>Bassin versant</s0>
<s5>01</s5>
</fC03><fC03 i1="01" i2="2" l="ENG"><s0>drainage basins</s0>
<s5>01</s5>
</fC03><fC03 i1="01" i2="2" l="SPA"><s0>Cuenca</s0>
<s5>01</s5>
</fC03><fC03 i1="02" i2="2" l="FRE"><s0>Crue</s0>
<s5>02</s5>
</fC03><fC03 i1="02" i2="2" l="ENG"><s0>floods</s0>
<s5>02</s5>
</fC03><fC03 i1="02" i2="2" l="SPA"><s0>Crecida</s0>
<s5>02</s5>
</fC03><fC03 i1="03" i2="2" l="FRE"><s0>Pollution</s0>
<s5>03</s5>
</fC03><fC03 i1="03" i2="2" l="ENG"><s0>pollution</s0>
<s5>03</s5>
</fC03><fC03 i1="03" i2="2" l="SPA"><s0>Polución</s0>
<s5>03</s5>
</fC03><fC03 i1="04" i2="2" l="FRE"><s0>Métal lourd</s0>
<s5>04</s5>
</fC03><fC03 i1="04" i2="2" l="ENG"><s0>heavy metals</s0>
<s5>04</s5>
</fC03><fC03 i1="04" i2="2" l="SPA"><s0>Metal pesado</s0>
<s5>04</s5>
</fC03><fC03 i1="05" i2="2" l="FRE"><s0>Composé organique</s0>
<s5>05</s5>
</fC03><fC03 i1="05" i2="2" l="ENG"><s0>organic compounds</s0>
<s5>05</s5>
</fC03><fC03 i1="06" i2="2" l="FRE"><s0>Polluant</s0>
<s5>06</s5>
</fC03><fC03 i1="06" i2="2" l="ENG"><s0>pollutants</s0>
<s5>06</s5>
</fC03><fC03 i1="06" i2="2" l="SPA"><s0>Contaminante</s0>
<s5>06</s5>
</fC03><fC03 i1="07" i2="2" l="FRE"><s0>Origine</s0>
<s5>07</s5>
</fC03><fC03 i1="07" i2="2" l="ENG"><s0>provenance</s0>
<s5>07</s5>
</fC03><fC03 i1="07" i2="2" l="SPA"><s0>Origen</s0>
<s5>07</s5>
</fC03><fC03 i1="08" i2="2" l="FRE"><s0>Urbanisation</s0>
<s5>08</s5>
</fC03><fC03 i1="08" i2="2" l="ENG"><s0>urbanization</s0>
<s5>08</s5>
</fC03><fC03 i1="08" i2="2" l="SPA"><s0>Urbanización</s0>
<s5>08</s5>
</fC03><fC03 i1="09" i2="2" l="FRE"><s0>Hydrogramme</s0>
<s5>09</s5>
</fC03><fC03 i1="09" i2="2" l="ENG"><s0>hydrographs</s0>
<s5>09</s5>
</fC03><fC03 i1="09" i2="2" l="SPA"><s0>Hidrograma</s0>
<s5>09</s5>
</fC03><fC03 i1="10" i2="2" l="FRE"><s0>Matière en suspension</s0>
<s5>10</s5>
</fC03><fC03 i1="10" i2="2" l="ENG"><s0>suspended materials</s0>
<s5>10</s5>
</fC03><fC03 i1="10" i2="2" l="SPA"><s0>Materia en suspensión</s0>
<s5>10</s5>
</fC03><fC03 i1="11" i2="2" l="FRE"><s0>Sédiment</s0>
<s5>11</s5>
</fC03><fC03 i1="11" i2="2" l="ENG"><s0>sediments</s0>
<s5>11</s5>
</fC03><fC03 i1="11" i2="2" l="SPA"><s0>Sedimento</s0>
<s5>11</s5>
</fC03><fC03 i1="12" i2="2" l="FRE"><s0>Hydrocarbure aromatique polycyclique</s0>
<s5>12</s5>
</fC03><fC03 i1="12" i2="2" l="ENG"><s0>polycyclic aromatic hydrocarbons</s0>
<s5>12</s5>
</fC03><fC03 i1="13" i2="2" l="FRE"><s0>Solubilité</s0>
<s5>13</s5>
</fC03><fC03 i1="13" i2="2" l="ENG"><s0>solubility</s0>
<s5>13</s5>
</fC03><fC03 i1="13" i2="2" l="SPA"><s0>Solubilidad</s0>
<s5>13</s5>
</fC03><fC03 i1="14" i2="2" l="FRE"><s0>Dilution</s0>
<s5>14</s5>
</fC03><fC03 i1="14" i2="2" l="ENG"><s0>dilution</s0>
<s5>14</s5>
</fC03><fC03 i1="14" i2="2" l="SPA"><s0>Dilución</s0>
<s5>14</s5>
</fC03><fC03 i1="15" i2="2" l="FRE"><s0>Utilisation terrain</s0>
<s5>16</s5>
</fC03><fC03 i1="15" i2="2" l="ENG"><s0>land use</s0>
<s5>16</s5>
</fC03><fC03 i1="15" i2="2" l="SPA"><s0>Utilización terreno</s0>
<s5>16</s5>
</fC03><fC03 i1="16" i2="2" l="FRE"><s0>Bedrock</s0>
<s5>17</s5>
</fC03><fC03 i1="16" i2="2" l="ENG"><s0>bedrock</s0>
<s5>17</s5>
</fC03><fC03 i1="16" i2="2" l="SPA"><s0>Roca firme</s0>
<s5>17</s5>
</fC03><fC03 i1="17" i2="2" l="FRE"><s0>Hunsruck</s0>
<s2>NG</s2>
<s5>18</s5>
</fC03><fC03 i1="17" i2="2" l="ENG"><s0>Hunsruck</s0>
<s2>NG</s2>
<s5>18</s5>
</fC03><fC03 i1="18" i2="2" l="FRE"><s0>Précipitation atmosphérique</s0>
<s5>19</s5>
</fC03><fC03 i1="18" i2="2" l="ENG"><s0>atmospheric precipitation</s0>
<s5>19</s5>
</fC03><fC03 i1="18" i2="2" l="SPA"><s0>Precipitación atmosférica</s0>
<s5>19</s5>
</fC03><fC03 i1="19" i2="2" l="FRE"><s0>Micropolluant</s0>
<s4>INC</s4>
<s5>52</s5>
</fC03><fC03 i1="20" i2="2" l="FRE"><s0>Remise en suspension</s0>
<s4>INC</s4>
<s5>53</s5>
</fC03><fC06><s0>ILS</s0>
</fC06><fC07 i1="01" i2="2" l="FRE"><s0>Rhénanie Palatinat</s0>
<s2>NG</s2>
</fC07><fC07 i1="01" i2="2" l="ENG"><s0>Rhineland-Palatinate Germany</s0>
<s2>NG</s2>
</fC07><fC07 i1="01" i2="2" l="SPA"><s0>Renania Palatinado</s0>
<s2>NG</s2>
</fC07><fC07 i1="02" i2="2" l="FRE"><s0>Allemagne</s0>
<s2>NG</s2>
</fC07><fC07 i1="02" i2="2" l="ENG"><s0>Germany</s0>
<s2>NG</s2>
</fC07><fC07 i1="02" i2="2" l="SPA"><s0>Alemania</s0>
<s2>NG</s2>
</fC07><fC07 i1="03" i2="2" l="FRE"><s0>Europe Centrale</s0>
<s2>NG</s2>
</fC07><fC07 i1="03" i2="2" l="ENG"><s0>Central Europe</s0>
<s2>NG</s2>
</fC07><fC07 i1="03" i2="2" l="SPA"><s0>Europa central</s0>
<s2>NG</s2>
</fC07><fC07 i1="04" i2="2" l="FRE"><s0>Europe</s0>
</fC07><fC07 i1="04" i2="2" l="ENG"><s0>Europe</s0>
</fC07><fC07 i1="04" i2="2" l="SPA"><s0>Europa</s0>
</fC07><fN21><s1>340</s1>
</fN21><pR><fA30 i1="01" i2="1" l="ENG"><s1>Impacts of urban growth on surface water and groundwater quality. International symposium</s1>
<s3>Birmingham GBR</s3>
<s4>1999-07-18</s4>
</fA30><server><NO>PASCAL 99-0526389 INIST</NO>
<ET>Identifying major sources of organic micropollutants and heavy metals during flood events in a partly urbanized headwater catchment</ET>
<AU>KREIN (A.); BIERL (R.); ELLIS (J. Bryan)</AU>
<AF>University of Trier, Department of Hydrology/54286 Trier/Allemagne (1 aut., 2 aut.)</AF>
<DT>Publication en série; Congrès; Niveau analytique</DT>
<SO>IAHS-AISH publication; ISSN 0144-7815; Royaume-Uni; Da. 1999; No. 259; Pp. 263-268; Bibl. 2 ref.</SO>
<LA>Anglais</LA>
<EA>Since 1988 we have investigated flood events in a headwater catchment. Dissolved and particle-bound solids were analysed as well as particle characteristics. By surveying all the data, pollutant profiles and hydrograph patterns, different sources of pollutants can be identified and related to particular locations in the basin. The influence of main roads and sewer systems is obvious. Heavy metals are additionally mobilized from pore water during resuspension of sediments. There is also a clear tendency for a fast and distinct response of smaller polycyclic aromatic hydrocarbons (PAH) with higher solubility, which could be explained by a gradual enrichment of these partly mobile molecules at locations along the flow path. Patterns of PAH chemographs are further determined by chemical alteration and season. The maximum contents during flood events are controlled by pre-event climatic and hydrological conditions with storm intensity and duration controlling inputs of unpolluted material causing dilution. Experiments with artificial flood releases give some indications of in-channel source reactions.</EA>
<CC>226B04; 226A01; 001E01O04; 001E01N01</CC>
<FD>Bassin versant; Crue; Pollution; Métal lourd; Composé organique; Polluant; Origine; Urbanisation; Hydrogramme; Matière en suspension; Sédiment; Hydrocarbure aromatique polycyclique; Solubilité; Dilution; Utilisation terrain; Bedrock; Hunsruck; Précipitation atmosphérique; Micropolluant; Remise en suspension</FD>
<FG>Rhénanie Palatinat; Allemagne; Europe Centrale; Europe</FG>
<ED>drainage basins; floods; pollution; heavy metals; organic compounds; pollutants; provenance; urbanization; hydrographs; suspended materials; sediments; polycyclic aromatic hydrocarbons; solubility; dilution; land use; bedrock; Hunsruck; atmospheric precipitation</ED>
<EG>Rhineland-Palatinate Germany; Germany; Central Europe; Europe</EG>
<SD>Cuenca; Crecida; Polución; Metal pesado; Contaminante; Origen; Urbanización; Hidrograma; Materia en suspensión; Sedimento; Solubilidad; Dilución; Utilización terreno; Roca firme; Precipitación atmosférica</SD>
<LO>INIST-8967.354000080041610320</LO>
<ID>99-0526389</ID>
</server>
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