Please use this identifier to cite or link to this item: http://hdl.handle.net/1893/26403
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dc.contributor.authorFastner, Juttaen_UK
dc.contributor.authorAbella, Sallyen_UK
dc.contributor.authorLitt, Arnien_UK
dc.contributor.authorMorabito, Giuseppeen_UK
dc.contributor.authorVoros, Lajosen_UK
dc.contributor.authorPalffy, Karolyen_UK
dc.contributor.authorStraile, Dietmaren_UK
dc.contributor.authorKummerlin, Reineren_UK
dc.contributor.authorMatthews, Daviden_UK
dc.contributor.authorPhillips, Geoffen_UK
dc.contributor.authorChorus, Ingriden_UK
dc.date.accessioned2017-12-21T02:45:17Z-
dc.date.available2017-12-21T02:45:17Z-
dc.date.issued2016-09en_UK
dc.identifier.urihttp://hdl.handle.net/1893/26403-
dc.description.abstractIncreased external nutrient loads of anthropogenic origin, especially those of phosphorus (P), were one of the major causes of eutrophication during the first half of the twentieth century in Europe. They led to deterioration of lake ecosystems, particularly including noxious blooms of (potentially toxic) cyanobacteria. From the 1970–1980s, strategies to decrease the phosphorus loads from sewage were increasingly implemented, among them are the ban of phosphates in detergents, the expansion of sewer systems and improvement in wastewater treatment to remove nutrients. Case studies of eight lakes, whose response to point source reduction of phosphorus was observed over decades, show that a pronounced reduction of the phosphorus load from point sources can be achieved either by the diversion of inflows carrying high loads, by upgraded sewage treatment, or by phosphorus precipitation in the major tributary directly before its inflow into the water body. Outcomes demonstrate that in order to effectively control cyanobacterial blooms, the measures taken need to reduce in-lake concentrations of total phosphorus below 20–50 µg L−1, with this threshold varying somewhat between lakes depending in particular on hydromorphological and biological conditions. Whether and when load reduction succeeds in controlling cyanobacteria depends primarily on the load remaining after remediation and on the water residence time.en_UK
dc.language.isoenen_UK
dc.publisherSpringeren_UK
dc.relationFastner J, Abella S, Litt A, Morabito G, Voros L, Palffy K, Straile D, Kummerlin R, Matthews D, Phillips G & Chorus I (2016) Combating cyanobacterial proliferation by avoiding or treating inflows with high P load—experiences from eight case studies. Aquatic Ecology, 50 (3), pp. 367-383. https://doi.org/10.1007/s10452-015-9558-8en_UK
dc.rights© The Author(s) 2015 This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.en_UK
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/en_UK
dc.subjectLakeen_UK
dc.subjectNutrientsen_UK
dc.subjectPhosphorusen_UK
dc.subjectPoint sourcesen_UK
dc.subjectTreatmenten_UK
dc.subjectDiversionen_UK
dc.subjectCyanobacteriaen_UK
dc.titleCombating cyanobacterial proliferation by avoiding or treating inflows with high P load—experiences from eight case studiesen_UK
dc.typeJournal Articleen_UK
dc.identifier.doi10.1007/s10452-015-9558-8en_UK
dc.citation.jtitleAquatic Ecologyen_UK
dc.citation.issn1573-5125en_UK
dc.citation.issn1386-2588en_UK
dc.citation.volume50en_UK
dc.citation.issue3en_UK
dc.citation.spage367en_UK
dc.citation.epage383en_UK
dc.citation.publicationstatusPublisheden_UK
dc.citation.peerreviewedRefereeden_UK
dc.type.statusVoR - Version of Recorden_UK
dc.citation.date23/12/2015en_UK
dc.contributor.affiliationFederal Environment Agencyen_UK
dc.contributor.affiliationKing County Water and Land Resources Divisionen_UK
dc.contributor.affiliationUniversity of Washingtonen_UK
dc.contributor.affiliationCNR–Institute for Ecosystem Studies, Italyen_UK
dc.contributor.affiliationBalaton Limnological Instituteen_UK
dc.contributor.affiliationBalaton Limnological Instituteen_UK
dc.contributor.affiliationUniversity of Konstanzen_UK
dc.contributor.affiliationGerman Institute for Lake Researchen_UK
dc.contributor.affiliationUpstate Freshwater Instituteen_UK
dc.contributor.affiliationBiological and Environmental Sciencesen_UK
dc.contributor.affiliationFederal Environment Agencyen_UK
dc.identifier.isiWOS:000382632100004en_UK
dc.identifier.scopusid2-s2.0-84951788375en_UK
dc.identifier.wtid508010en_UK
dc.date.accepted2015-11-19en_UK
dcterms.dateAccepted2015-11-19en_UK
dc.date.filedepositdate2017-12-20en_UK
rioxxterms.apcnot requireden_UK
rioxxterms.typeJournal Article/Reviewen_UK
rioxxterms.versionVoRen_UK
local.rioxx.authorFastner, Jutta|en_UK
local.rioxx.authorAbella, Sally|en_UK
local.rioxx.authorLitt, Arni|en_UK
local.rioxx.authorMorabito, Giuseppe|en_UK
local.rioxx.authorVoros, Lajos|en_UK
local.rioxx.authorPalffy, Karoly|en_UK
local.rioxx.authorStraile, Dietmar|en_UK
local.rioxx.authorKummerlin, Reiner|en_UK
local.rioxx.authorMatthews, David|en_UK
local.rioxx.authorPhillips, Geoff|en_UK
local.rioxx.authorChorus, Ingrid|en_UK
local.rioxx.projectInternal Project|University of Stirling|https://isni.org/isni/0000000122484331en_UK
local.rioxx.freetoreaddate2017-12-20en_UK
local.rioxx.licencehttp://creativecommons.org/licenses/by/4.0/|2017-12-20|en_UK
local.rioxx.filenameFastner_etal_AquaticEcology_2016.pdfen_UK
local.rioxx.filecount1en_UK
local.rioxx.source1386-2588en_UK
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