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Macrohabitat classification of wetlands as a powerful tool for management and protection: The example of the Paraná River floodplain, Brazil

dc.contributor.authorJunk, Wolfgang Johannes
dc.contributor.authorCunha, Nunes da
dc.contributor.authorThomaz, Sidinei Magela
dc.contributor.authorAgostinho, Angelo Antonio
dc.contributor.authorFerreira, Fernando Alves
dc.contributor.authorFilho, Edvard Elias de Souza
dc.contributor.authorStevaux, José Cândido
dc.contributor.authorda Silva, João Carlos Barbosa
dc.contributor.authorRocha, Paulo Cesar [UNESP]
dc.contributor.authorKawakita, Kazue
dc.contributor.institution(UFMT)
dc.contributor.institutionUniversidade Estadual de Maringá (UEM)
dc.contributor.institutionInstituto SENAI de Inovação Biomassa
dc.contributor.institutionBioLogic Consultoria Ambiental
dc.contributor.institutionUniversidade Estadual Paulista (UNESP)
dc.date.accessioned2022-05-01T09:30:31Z
dc.date.available2022-05-01T09:30:31Z
dc.date.issued2021-01-01
dc.description.abstractThe construction of four large reservoirs for hydroelectric power generation in the main channel of the Paraná River and many others in the tributaries has eliminated important wetlands, except over an area of ∼2000 km2 between the reservoirs of the UHE Engenheiro Sérgio Motta (Porto Primavera) and the Itaipu. The up-river reservoirs created large changes in the river's hydrology and in its loads of suspended, bed and dissolved material. A detailed assessment of the impact of these changes requires a description and classification of the floodplain's different subunits, called macrohabitats, according to hydrological, hydromorphological, and vegetational parameters. The classification system presented herein is hierarchical and is embedded in the classifications of Brazilian wetlands. The system differentiates the Paraná River floodplain into 6 functional units, 13 subclasses, and 23 macrohabitats, which are presented in this paper. Changes in hydrology have reduced the flood amplitude, frequency and permanence, and thus confined the macrohabitats to an area currently subjected to a regular flood pulse of ∼3 m rather than the previous ∼6 m. The gradual terrestrialization of macrohabitats at the upper end of the flood gradient is expected, accompanied by a loss of macrohabitats at its lower end because of long-term flooding. The retention of sediments and dissolved nutrients in the reservoirs will lead to the oligotrophication of aquatic macrohabitats, the degradation of near-channel hydromorphic structures and their vegetation, and a general reduction of overall primary production in the floodplain, which may extend also to higher trophic levels.en
dc.description.affiliationNational Institute for Science and Development in Wetlands (INCT-INAU) Federal University of Mato Grosso (UFMT)
dc.description.affiliationUniversidade Estadual de Maringá (UEM)
dc.description.affiliationInstituto SENAI de Inovação Biomassa
dc.description.affiliationBioLogic Consultoria Ambiental
dc.description.affiliationUniversidade Estadual Paulista (Unesp)
dc.description.affiliationUnespUniversidade Estadual Paulista (Unesp)
dc.identifierhttp://dx.doi.org/10.1016/j.ecohyd.2021.05.006
dc.identifier.citationEcohydrology and Hydrobiology.
dc.identifier.doi10.1016/j.ecohyd.2021.05.006
dc.identifier.issn2080-3397
dc.identifier.issn1642-3593
dc.identifier.scopus2-s2.0-85115031634
dc.identifier.urihttp://hdl.handle.net/11449/233546
dc.language.isoeng
dc.relation.ispartofEcohydrology and Hydrobiology
dc.sourceScopus
dc.subjectdam impacts
dc.subjectFlood pulse
dc.subjecthydrophytes
dc.subjectoligotrophication
dc.titleMacrohabitat classification of wetlands as a powerful tool for management and protection: The example of the Paraná River floodplain, Brazilen
dc.typeArtigo
dspace.entity.typePublication
unesp.author.orcid0000-0002-5236-1364[1]
unesp.author.orcid0000-0002-4557-7052[6]
unesp.author.orcid0000-0003-0917-6195[10]
unesp.departmentGeografia - FCTpt

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