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               <dc:title>Effects of low concentrations of the phenylurea herbicide diuron on biofilm algae and bacteria</dc:title>
               <dc:creator>Ricart Viladomat, Marta</dc:creator>
               <dc:creator>Barceló i Cullerés, Damià</dc:creator>
               <dc:creator>Geiszinger, Anita</dc:creator>
               <dc:creator>Guasch i Padró, Helena</dc:creator>
               <dc:creator>López de Alda, Miren</dc:creator>
               <dc:creator>Romaní i Cornet, Anna M.</dc:creator>
               <dc:creator>Vidal, Gemma</dc:creator>
               <dc:creator>Villagrasa, Marta</dc:creator>
               <dc:creator>Sabater, Sergi</dc:creator>
               <dc:subject>Biofilms</dc:subject>
               <dc:subject>Plaguicides -- Aspectes ambientals</dc:subject>
               <dc:subject>Pesticides -- Environmental aspects</dc:subject>
               <dc:subject>Bacteris</dc:subject>
               <dc:subject>Bacteria</dc:subject>
               <dc:description>A system of recirculating channels was used in this study to examine the long-term effects (29 d) of environmentally realistic concentrations of the herbicide diuron (from 0.07 to 7 μg L-1) on biofilm communities. The autotrophic activity of biofilms was affected by this herbicide, as reflected by a marked decrease in the photosynthetic efficiency. Diuron exposure also increased chlorophyll-a content and reduced the biovolume of diatom taxa at low concentrations. The effects on bacteria were also remarkable. Bacterial abundance was reduced after a week of exposure to the herbicide at a range of concentrations. Effects were on the number of live bacteria and on the increase in the leucine-aminopeptidase activity. It is suggested that inputs of herbicides to the river ecosystem at low concentrations may cause a chain of effects in the biofilm, which include inhibitory effects on algae but also indirect effects on the relationships between biofilm components. © 2009 Elsevier Ltd. All rights reserved</dc:description>
               <dc:description>This study was supported by the European Commission project Modelkey (Project 511237-2 GOCE). Additional funds were provided by the European Project Keybioeffects (MRTN-CT-2006-035695) and by the Spanish Ministry of Science and Technology (Project GCL2006-12785/HID) and the VIECO program (009/RN08/011) of the Spanish Ministry of the Environment and Rural and Marine Affairs</dc:description>
               <dc:date>2024-06-18T11:53:01Z</dc:date>
               <dc:date>2024-06-18T11:53:01Z</dc:date>
               <dc:date>info:eu-repo/date/embargoEnd/2026-01-01</dc:date>
               <dc:date>info:eu-repo/date/embargoEnd/2026-01-01</dc:date>
               <dc:date>2009-09-01</dc:date>
               <dc:type>info:eu-repo/semantics/article</dc:type>
               <dc:type>info:eu-repo/semantics/publishedVersion</dc:type>
               <dc:identifier>http://hdl.handle.net/10256/12728</dc:identifier>
               <dc:relation>info:eu-repo/semantics/altIdentifier/doi/10.1016/j.chemosphere.2009.06.017</dc:relation>
               <dc:relation>info:eu-repo/semantics/altIdentifier/issn/0045-6535</dc:relation>
               <dc:relation>info:eu-repo/grantAgreement/MEC//CGL2006-12785/ES/USO DEL PERIFITON COMO HERRAMIENTA PARA LA EVALUACION DEL EFECTO DE LOS CONTAMINANTES SOBRE LA ESTRUCTURA Y FUNCION DEL ECOSISTEMA FLUVIAL/</dc:relation>
               <dc:rights>Tots els drets reservats</dc:rights>
               <dc:rights>info:eu-repo/semantics/embargoedAccess</dc:rights>
               <dc:publisher>Elsevier</dc:publisher>
               <dc:source>© Chemosphere, 2009, vol. 76, p. 1392-1401</dc:source>
               <dc:source>Articles publicats (D-CCAA)</dc:source>
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