Accumulation of inorganic and organic pollutants by biofilms in the aquatic environment
Identifieur interne : 001349 ( PascalFrancis/Corpus ); précédent : 001348; suivant : 001350Accumulation of inorganic and organic pollutants by biofilms in the aquatic environment
Auteurs : M. Schorer ; M. EiseleSource :
- Water, air and soil pollution [ 0049-6979 ] ; 1997.
Descripteurs français
- Pascal (Inist)
- Allemagne, Concentration, Elément métallique, Métal lourd, Hydrocarbure aromatique polycyclique, Variation temporelle, Sorption, Transport, Accumulation, Milieu aquatique, Particule, Polluant, Transport fluviatile, Pollution, Effet biogène, Bassin versant, Sédimentation fluviatile, Alluvion, Microorganisme, Cuivre, Zinc, Plomb.
English descriptors
- KwdEn :
- Germany, accumulation, alluvium, aquatic environment, biogenic effects, concentration, copper, drainage basins, fluvial sedimentation, heavy metals, lead, metals, microorganisms, particles, pollutants, pollution, polycyclic aromatic hydrocarbons, sorption, stream transport, time variations, transport, zinc.
Abstract
In a partly urbanized catchment to the south of Trier, Germany, short term variations in river sediment compounds as well as the bioaccumulation of pollutants on surface associated microbial coatings (biofilms) were investigated weekly during a period of six months. Concentrations of selected heavy metals (Cu, Zn, Pb), polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and for microbial characterisation protein, carbohydrate and uronic acid were analyzed. Sorption processes on biofilms were determined by temporal variations in pollutants and microbial parameters and through the comparison of sorbed substances in biofilms and sediments. The results show, that sorption events on biofilms play an important and dynamic role in spring and summer for transport and accumulation of the investigated pollutants in the aquatic environment. The amount of pollutants sorbed on sediment particles is not only dependent on the particulate bound or solved pollutants in the river water, but is strongly controlled by the changing conditions of the biofilms.
Notice en format standard (ISO 2709)
Pour connaître la documentation sur le format Inist Standard.
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Format Inist (serveur)
NO : | PASCAL 97-0547893 INIST |
---|---|
ET : | Accumulation of inorganic and organic pollutants by biofilms in the aquatic environment |
AU : | SCHORER (M.); EISELE (M.); EVANS (R. Douglas); WISNIEWSKI (Joe); WISNIEWSKI (Jan R.) |
AF : | Department of Hydrology, University of Trier/54286 Trier/Allemagne (1 aut., 2 aut.); Trent University/Peterborough, K9J 7B8/Canada (1 aut.) |
DT : | Publication en série; Congrès; Niveau analytique |
SO : | Water, air and soil pollution; ISSN 0049-6979; Coden WAPLAC; Pays-Bas; Da. 1997; Vol. 99; No. 1-4; Pp. 651-659; Bibl. 23 ref. |
LA : | Anglais |
EA : | In a partly urbanized catchment to the south of Trier, Germany, short term variations in river sediment compounds as well as the bioaccumulation of pollutants on surface associated microbial coatings (biofilms) were investigated weekly during a period of six months. Concentrations of selected heavy metals (Cu, Zn, Pb), polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and for microbial characterisation protein, carbohydrate and uronic acid were analyzed. Sorption processes on biofilms were determined by temporal variations in pollutants and microbial parameters and through the comparison of sorbed substances in biofilms and sediments. The results show, that sorption events on biofilms play an important and dynamic role in spring and summer for transport and accumulation of the investigated pollutants in the aquatic environment. The amount of pollutants sorbed on sediment particles is not only dependent on the particulate bound or solved pollutants in the river water, but is strongly controlled by the changing conditions of the biofilms. |
CC : | 226B04; 001E01O04 |
FD : | Allemagne; Concentration; Elément métallique; Métal lourd; Hydrocarbure aromatique polycyclique; Variation temporelle; Sorption; Transport; Accumulation; Milieu aquatique; Particule; Polluant; Transport fluviatile; Pollution; Effet biogène; Bassin versant; Sédimentation fluviatile; Alluvion; Microorganisme; Cuivre; Zinc; Plomb |
FG : | Europe Centrale; Europe |
ED : | Germany; concentration; metals; heavy metals; polycyclic aromatic hydrocarbons; time variations; sorption; transport; accumulation; aquatic environment; particles; pollutants; stream transport; pollution; biogenic effects; drainage basins; fluvial sedimentation; alluvium; microorganisms; copper; zinc; lead |
EG : | Central Europe; Europe |
SD : | Alemania; Concentración; Elemento metálico; Metal pesado; Variación temporal; Sorción; Transporte; Contaminante; Transporte fluvial; Polución; Cuenca; Sedimentación fluvial; Aluvión; Microorganismo; Cobre; Zinc; Plomo |
LO : | INIST-15302.354000069179500650 |
ID : | 97-0547893 |
Links to Exploration step
Pascal:97-0547893Le document en format XML
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<author><name sortKey="Schorer, M" sort="Schorer, M" uniqKey="Schorer M" first="M." last="Schorer">M. Schorer</name>
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<sZ>2 aut.</sZ>
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<author><name sortKey="Eisele, M" sort="Eisele, M" uniqKey="Eisele M" first="M." last="Eisele">M. Eisele</name>
<affiliation><inist:fA14 i1="01"><s1>Department of Hydrology, University of Trier</s1>
<s2>54286 Trier</s2>
<s3>DEU</s3>
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<author><name sortKey="Eisele, M" sort="Eisele, M" uniqKey="Eisele M" first="M." last="Eisele">M. Eisele</name>
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<term>concentration</term>
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<term>drainage basins</term>
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<term>lead</term>
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<term>particles</term>
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<term>transport</term>
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<keywords scheme="Pascal" xml:lang="fr"><term>Allemagne</term>
<term>Concentration</term>
<term>Elément métallique</term>
<term>Métal lourd</term>
<term>Hydrocarbure aromatique polycyclique</term>
<term>Variation temporelle</term>
<term>Sorption</term>
<term>Transport</term>
<term>Accumulation</term>
<term>Milieu aquatique</term>
<term>Particule</term>
<term>Polluant</term>
<term>Transport fluviatile</term>
<term>Pollution</term>
<term>Effet biogène</term>
<term>Bassin versant</term>
<term>Sédimentation fluviatile</term>
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<front><div type="abstract" xml:lang="en">In a partly urbanized catchment to the south of Trier, Germany, short term variations in river sediment compounds as well as the bioaccumulation of pollutants on surface associated microbial coatings (biofilms) were investigated weekly during a period of six months. Concentrations of selected heavy metals (Cu, Zn, Pb), polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and for microbial characterisation protein, carbohydrate and uronic acid were analyzed. Sorption processes on biofilms were determined by temporal variations in pollutants and microbial parameters and through the comparison of sorbed substances in biofilms and sediments. The results show, that sorption events on biofilms play an important and dynamic role in spring and summer for transport and accumulation of the investigated pollutants in the aquatic environment. The amount of pollutants sorbed on sediment particles is not only dependent on the particulate bound or solved pollutants in the river water, but is strongly controlled by the changing conditions of the biofilms.</div>
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<fA12 i1="02" i2="1"><s1>WISNIEWSKI (Joe)</s1>
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<fA12 i1="03" i2="1"><s1>WISNIEWSKI (Jan R.)</s1>
<s9>ed.</s9>
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<fA14 i1="01"><s1>Department of Hydrology, University of Trier</s1>
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<sZ>2 aut.</sZ>
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<fA15 i1="01"><s1>Trent University</s1>
<s2>Peterborough, K9J 7B8</s2>
<s3>CAN</s3>
<sZ>1 aut.</sZ>
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<fC01 i1="01" l="ENG"><s0>In a partly urbanized catchment to the south of Trier, Germany, short term variations in river sediment compounds as well as the bioaccumulation of pollutants on surface associated microbial coatings (biofilms) were investigated weekly during a period of six months. Concentrations of selected heavy metals (Cu, Zn, Pb), polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and for microbial characterisation protein, carbohydrate and uronic acid were analyzed. Sorption processes on biofilms were determined by temporal variations in pollutants and microbial parameters and through the comparison of sorbed substances in biofilms and sediments. The results show, that sorption events on biofilms play an important and dynamic role in spring and summer for transport and accumulation of the investigated pollutants in the aquatic environment. The amount of pollutants sorbed on sediment particles is not only dependent on the particulate bound or solved pollutants in the river water, but is strongly controlled by the changing conditions of the biofilms.</s0>
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</fC02>
<fC03 i1="01" i2="2" l="FRE"><s0>Allemagne</s0>
<s2>NG</s2>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="2" l="ENG"><s0>Germany</s0>
<s2>NG</s2>
<s5>01</s5>
</fC03>
<fC03 i1="01" i2="2" l="SPA"><s0>Alemania</s0>
<s2>NG</s2>
<s5>01</s5>
</fC03>
<fC03 i1="02" i2="2" l="FRE"><s0>Concentration</s0>
<s5>07</s5>
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<fC03 i1="02" i2="2" l="ENG"><s0>concentration</s0>
<s5>07</s5>
</fC03>
<fC03 i1="02" i2="2" l="SPA"><s0>Concentración</s0>
<s5>07</s5>
</fC03>
<fC03 i1="03" i2="2" l="FRE"><s0>Elément métallique</s0>
<s5>08</s5>
</fC03>
<fC03 i1="03" i2="2" l="ENG"><s0>metals</s0>
<s5>08</s5>
</fC03>
<fC03 i1="03" i2="2" l="SPA"><s0>Elemento metálico</s0>
<s5>08</s5>
</fC03>
<fC03 i1="04" i2="2" l="FRE"><s0>Métal lourd</s0>
<s5>09</s5>
</fC03>
<fC03 i1="04" i2="2" l="ENG"><s0>heavy metals</s0>
<s5>09</s5>
</fC03>
<fC03 i1="04" i2="2" l="SPA"><s0>Metal pesado</s0>
<s5>09</s5>
</fC03>
<fC03 i1="05" i2="2" l="FRE"><s0>Hydrocarbure aromatique polycyclique</s0>
<s5>10</s5>
</fC03>
<fC03 i1="05" i2="2" l="ENG"><s0>polycyclic aromatic hydrocarbons</s0>
<s5>10</s5>
</fC03>
<fC03 i1="06" i2="2" l="FRE"><s0>Variation temporelle</s0>
<s5>11</s5>
</fC03>
<fC03 i1="06" i2="2" l="ENG"><s0>time variations</s0>
<s5>11</s5>
</fC03>
<fC03 i1="06" i2="2" l="SPA"><s0>Variación temporal</s0>
<s5>11</s5>
</fC03>
<fC03 i1="07" i2="2" l="FRE"><s0>Sorption</s0>
<s5>12</s5>
</fC03>
<fC03 i1="07" i2="2" l="ENG"><s0>sorption</s0>
<s5>12</s5>
</fC03>
<fC03 i1="07" i2="2" l="SPA"><s0>Sorción</s0>
<s5>12</s5>
</fC03>
<fC03 i1="08" i2="2" l="FRE"><s0>Transport</s0>
<s5>15</s5>
</fC03>
<fC03 i1="08" i2="2" l="ENG"><s0>transport</s0>
<s5>15</s5>
</fC03>
<fC03 i1="08" i2="2" l="SPA"><s0>Transporte</s0>
<s5>15</s5>
</fC03>
<fC03 i1="09" i2="2" l="FRE"><s0>Accumulation</s0>
<s5>16</s5>
</fC03>
<fC03 i1="09" i2="2" l="ENG"><s0>accumulation</s0>
<s5>16</s5>
</fC03>
<fC03 i1="10" i2="2" l="FRE"><s0>Milieu aquatique</s0>
<s5>17</s5>
</fC03>
<fC03 i1="10" i2="2" l="ENG"><s0>aquatic environment</s0>
<s5>17</s5>
</fC03>
<fC03 i1="11" i2="2" l="FRE"><s0>Particule</s0>
<s5>18</s5>
</fC03>
<fC03 i1="11" i2="2" l="ENG"><s0>particles</s0>
<s5>18</s5>
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<fC03 i1="12" i2="2" l="FRE"><s0>Polluant</s0>
<s5>19</s5>
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<fC03 i1="12" i2="2" l="ENG"><s0>pollutants</s0>
<s5>19</s5>
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<fC03 i1="12" i2="2" l="SPA"><s0>Contaminante</s0>
<s5>19</s5>
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<s5>20</s5>
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<s5>20</s5>
</fC03>
<fC03 i1="13" i2="2" l="SPA"><s0>Transporte fluvial</s0>
<s5>20</s5>
</fC03>
<fC03 i1="14" i2="2" l="FRE"><s0>Pollution</s0>
<s5>21</s5>
</fC03>
<fC03 i1="14" i2="2" l="ENG"><s0>pollution</s0>
<s5>21</s5>
</fC03>
<fC03 i1="14" i2="2" l="SPA"><s0>Polución</s0>
<s5>21</s5>
</fC03>
<fC03 i1="15" i2="2" l="FRE"><s0>Effet biogène</s0>
<s5>22</s5>
</fC03>
<fC03 i1="15" i2="2" l="ENG"><s0>biogenic effects</s0>
<s5>22</s5>
</fC03>
<fC03 i1="16" i2="2" l="FRE"><s0>Bassin versant</s0>
<s5>23</s5>
</fC03>
<fC03 i1="16" i2="2" l="ENG"><s0>drainage basins</s0>
<s5>23</s5>
</fC03>
<fC03 i1="16" i2="2" l="SPA"><s0>Cuenca</s0>
<s5>23</s5>
</fC03>
<fC03 i1="17" i2="2" l="FRE"><s0>Sédimentation fluviatile</s0>
<s5>24</s5>
</fC03>
<fC03 i1="17" i2="2" l="ENG"><s0>fluvial sedimentation</s0>
<s5>24</s5>
</fC03>
<fC03 i1="17" i2="2" l="SPA"><s0>Sedimentación fluvial</s0>
<s5>24</s5>
</fC03>
<fC03 i1="18" i2="2" l="FRE"><s0>Alluvion</s0>
<s5>25</s5>
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<s5>25</s5>
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<fC03 i1="18" i2="2" l="SPA"><s0>Aluvión</s0>
<s5>25</s5>
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<s5>61</s5>
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<fC03 i1="19" i2="2" l="ENG"><s0>microorganisms</s0>
<s5>61</s5>
</fC03>
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<s5>61</s5>
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<s5>62</s5>
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<s5>62</s5>
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<fC03 i1="20" i2="2" l="SPA"><s0>Cobre</s0>
<s5>62</s5>
</fC03>
<fC03 i1="21" i2="2" l="FRE"><s0>Zinc</s0>
<s5>63</s5>
</fC03>
<fC03 i1="21" i2="2" l="ENG"><s0>zinc</s0>
<s5>63</s5>
</fC03>
<fC03 i1="21" i2="2" l="SPA"><s0>Zinc</s0>
<s5>63</s5>
</fC03>
<fC03 i1="22" i2="2" l="FRE"><s0>Plomb</s0>
<s5>64</s5>
</fC03>
<fC03 i1="22" i2="2" l="ENG"><s0>lead</s0>
<s5>64</s5>
</fC03>
<fC03 i1="22" i2="2" l="SPA"><s0>Plomo</s0>
<s5>64</s5>
</fC03>
<fC06><s0>ILS</s0>
</fC06>
<fC07 i1="01" i2="2" l="FRE"><s0>Europe Centrale</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="2" l="ENG"><s0>Central Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="2" l="SPA"><s0>Europa central</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="2" l="FRE"><s0>Europe</s0>
</fC07>
<fC07 i1="02" i2="2" l="ENG"><s0>Europe</s0>
</fC07>
<fC07 i1="02" i2="2" l="SPA"><s0>Europa</s0>
</fC07>
<fN21><s1>342</s1>
</fN21>
</pA>
<pR><fA30 i1="01" i2="1" l="ENG"><s1>The Interactions Between Sediments and Water. International Symposium</s1>
<s2>7</s2>
<s3>Baveno ITA</s3>
<s4>1996-09-22</s4>
</fA30>
</pR>
</standard>
<server><NO>PASCAL 97-0547893 INIST</NO>
<ET>Accumulation of inorganic and organic pollutants by biofilms in the aquatic environment</ET>
<AU>SCHORER (M.); EISELE (M.); EVANS (R. Douglas); WISNIEWSKI (Joe); WISNIEWSKI (Jan R.)</AU>
<AF>Department of Hydrology, University of Trier/54286 Trier/Allemagne (1 aut., 2 aut.); Trent University/Peterborough, K9J 7B8/Canada (1 aut.)</AF>
<DT>Publication en série; Congrès; Niveau analytique</DT>
<SO>Water, air and soil pollution; ISSN 0049-6979; Coden WAPLAC; Pays-Bas; Da. 1997; Vol. 99; No. 1-4; Pp. 651-659; Bibl. 23 ref.</SO>
<LA>Anglais</LA>
<EA>In a partly urbanized catchment to the south of Trier, Germany, short term variations in river sediment compounds as well as the bioaccumulation of pollutants on surface associated microbial coatings (biofilms) were investigated weekly during a period of six months. Concentrations of selected heavy metals (Cu, Zn, Pb), polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and for microbial characterisation protein, carbohydrate and uronic acid were analyzed. Sorption processes on biofilms were determined by temporal variations in pollutants and microbial parameters and through the comparison of sorbed substances in biofilms and sediments. The results show, that sorption events on biofilms play an important and dynamic role in spring and summer for transport and accumulation of the investigated pollutants in the aquatic environment. The amount of pollutants sorbed on sediment particles is not only dependent on the particulate bound or solved pollutants in the river water, but is strongly controlled by the changing conditions of the biofilms.</EA>
<CC>226B04; 001E01O04</CC>
<FD>Allemagne; Concentration; Elément métallique; Métal lourd; Hydrocarbure aromatique polycyclique; Variation temporelle; Sorption; Transport; Accumulation; Milieu aquatique; Particule; Polluant; Transport fluviatile; Pollution; Effet biogène; Bassin versant; Sédimentation fluviatile; Alluvion; Microorganisme; Cuivre; Zinc; Plomb</FD>
<FG>Europe Centrale; Europe</FG>
<ED>Germany; concentration; metals; heavy metals; polycyclic aromatic hydrocarbons; time variations; sorption; transport; accumulation; aquatic environment; particles; pollutants; stream transport; pollution; biogenic effects; drainage basins; fluvial sedimentation; alluvium; microorganisms; copper; zinc; lead</ED>
<EG>Central Europe; Europe</EG>
<SD>Alemania; Concentración; Elemento metálico; Metal pesado; Variación temporal; Sorción; Transporte; Contaminante; Transporte fluvial; Polución; Cuenca; Sedimentación fluvial; Aluvión; Microorganismo; Cobre; Zinc; Plomo</SD>
<LO>INIST-15302.354000069179500650</LO>
<ID>97-0547893</ID>
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