Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity

Detalhes bibliográficos
Autor(a) principal: Renato Tavares Martins
Data de Publicação: 2021
Outros Autores: Janaina Gomes de Brito, Karina Dias da Silva, Cecília Gontijo Leal, Rafael Pereira Leitão, Vivian Campos de Oliveira, José Max Barbosa de Oliveira Júnior, Sílvio Frosini de Barros Ferraz, Felipe Rossetti de Paula, Fábio de Oliveira Roque, Neusa Hamada, Leandro Juen, Jorge Luiz Nessimian, Paulo dos Santos Pompeu, Robert M. Hughes
Tipo de documento: Artigo
Idioma: eng
Título da fonte: Repositório Institucional da UFMG
Texto Completo: https://doi.org/10.1016/j.ecolind.2021.107773
http://hdl.handle.net/1843/56285
https://orcid.org/0000-0003-3464-7905
https://orcid.org/0000-0001-5548-4995
https://orcid.org/0000-0002-0108-8572
https://orcid.org/0000-0001-7990-0068
https://orcid.org/0000-0002-0689-205X
https://orcid.org/0000-0003-1808-5420
https://orcid.org/0000-0001-5568-8824
https://orcid.org/0000-0001-5635-0622
https://orcid.org/0000-0002-3526-5426
https://orcid.org/0000-0002-6188-4386
https://orcid.org/0000-0001-8795-2538
https://orcid.org/0000-0002-7938-1517
Resumo: Deforestation is a major threat globally, but especially in tropical regions because they are biodiversity strongholds and carbon storehouses. Some studies have reported changes in species richness and composition in lotic ecosystems with increased forest-loss in their catchment, presumably resulting from the replacement of sensitive taxa by more resistant or tolerant taxa. Also, sensitive taxa respond to deforestation in a non-linear manner and fish and macroinvertebrates have different sensitivities to landscape pressures. Therefore, it is useful to determine the effects of forest-loss on widespread sensitive or threshold taxa in aquatic ecosystems. We used Threshold Indicator Taxa Analysis (TITAN) to assess forest-loss and land use history impacts in 92 eastern Amazonian stream sites. We determined TITAN peak-change thresholds for fish at 1% and 6% of forest-loss at total-catchment and local-riparian spatial extents, respectively, and at 2% and 40% of land-use intensity change at total-catchment and local-riparian spatial extents, respectively. For macroinvertebrates, TITAN peak-change thresholds were 1% and 11% of forest loss at total-catchment and local-riparian spatial extents, respectively, and at 3% of land-use intensity change for both total-catchment and local-riparian spatial extents. Because of these thresholds, inherent ecoregional variability and key literature, we have three major recommendations. 1) Logging should be prohibited in riparian reserves that are at least 100-m wide on each side of headwater streams and in a network of catchments across all biomes and as many landscape types as possible. 2) An ecologically and statistically rigorous monitoring program with standard methods should be implemented to assess and regulate land uses better. 3) Conservation planning areas should consider aquatic biota as well as terrestrial biota.
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spelling 2023-07-14T20:24:53Z2023-07-14T20:24:53Z2021-08127https://doi.org/10.1016/j.ecolind.2021.1077731872-7034http://hdl.handle.net/1843/56285https://orcid.org/0000-0003-3464-7905https://orcid.org/0000-0001-5548-4995https://orcid.org/0000-0002-0108-8572https://orcid.org/0000-0001-7990-0068https://orcid.org/0000-0002-0689-205Xhttps://orcid.org/0000-0003-1808-5420https://orcid.org/0000-0001-5568-8824https://orcid.org/0000-0001-5635-0622https://orcid.org/0000-0002-3526-5426https://orcid.org/0000-0002-6188-4386https://orcid.org/0000-0001-8795-2538https://orcid.org/0000-0002-7938-1517Deforestation is a major threat globally, but especially in tropical regions because they are biodiversity strongholds and carbon storehouses. Some studies have reported changes in species richness and composition in lotic ecosystems with increased forest-loss in their catchment, presumably resulting from the replacement of sensitive taxa by more resistant or tolerant taxa. Also, sensitive taxa respond to deforestation in a non-linear manner and fish and macroinvertebrates have different sensitivities to landscape pressures. Therefore, it is useful to determine the effects of forest-loss on widespread sensitive or threshold taxa in aquatic ecosystems. We used Threshold Indicator Taxa Analysis (TITAN) to assess forest-loss and land use history impacts in 92 eastern Amazonian stream sites. We determined TITAN peak-change thresholds for fish at 1% and 6% of forest-loss at total-catchment and local-riparian spatial extents, respectively, and at 2% and 40% of land-use intensity change at total-catchment and local-riparian spatial extents, respectively. For macroinvertebrates, TITAN peak-change thresholds were 1% and 11% of forest loss at total-catchment and local-riparian spatial extents, respectively, and at 3% of land-use intensity change for both total-catchment and local-riparian spatial extents. Because of these thresholds, inherent ecoregional variability and key literature, we have three major recommendations. 1) Logging should be prohibited in riparian reserves that are at least 100-m wide on each side of headwater streams and in a network of catchments across all biomes and as many landscape types as possible. 2) An ecologically and statistically rigorous monitoring program with standard methods should be implemented to assess and regulate land uses better. 3) Conservation planning areas should consider aquatic biota as well as terrestrial biota.O desmatamento é uma grande ameaça globalmente, mas especialmente nas regiões tropicais porque são redutos da biodiversidade e depósitos de carbono. Alguns estudos relataram mudanças na riqueza e composição de espécies em ecossistemas lóticos com aumento da perda de floresta em sua bacia hidrográfica, presumivelmente resultante da substituição de táxons sensíveis por táxons mais resistentes ou tolerantes. Além disso, táxons sensíveis respondem ao desmatamento de maneira não linear e peixes e macroinvertebrados têm diferentes sensibilidades às pressões da paisagem. Portanto, é útil determinar os efeitos da perda de floresta em táxons sensíveis ou limiares generalizados em ecossistemas aquáticos. Usamos Threshold Indicator Taxa Analysis (TITAN) para avaliar a perda de floresta e os impactos do histórico de uso da terra em 92 locais de riachos da Amazônia oriental. Nós determinamos limites de mudança de pico TITAN para peixes em 1% e 6% de perda de floresta na captação total e extensões espaciais ribeirinhas locais, respectivamente, e em 2% e 40% de mudança de intensidade de uso da terra na captação total e extensões espaciais locais-ciliares, respectivamente. Para macroinvertebrados, os limiares de mudança de pico do TITAN foram de 1% e 11% de perda de floresta na bacia total e extensões espaciais ribeirinhas locais, respectivamente, e em 3% de mudança de intensidade de uso da terra para a bacia total e espacial ribeirinha local. extensões. Por causa desses limiares, variabilidade ecorregional inerente e literatura chave, temos três recomendações principais. 1) A exploração madeireira deve ser proibida em reservas ciliares com pelo menos 100 m de largura em cada lado dos córregos de cabeceira e em uma rede de bacias hidrográficas em todos os biomas e tantos tipos de paisagem quanto possível. 2) Um programa de monitoramento ecologicamente e estatisticamente rigoroso com métodos padrão deve ser implementado para avaliar e regular melhor os usos da terra. 3) As áreas de planejamento de conservação devem considerar tanto a biota aquática quanto a biota terrestre.CNPq - Conselho Nacional de Desenvolvimento Científico e TecnológicoFAPEMIG - Fundação de Amparo à Pesquisa do Estado de Minas GeraisCAPES - Coordenação de Aperfeiçoamento de Pessoal de Nível SuperiorFAPESP - Fundação de Amparo à Pesquisa do Estado de São PauloOutra AgênciaengUniversidade Federal de Minas GeraisUFMGBrasilICB - DEPARTAMENTO DE BIOLOGIA GERALEcological IndicatorsBiodiversidadeDesmatamento - AmazonasRios - BrasilFlorestas tropicais - AmazôniaMadeira - ExploraçãoFlorestas - ConservaçãoEcological thresholdsAmazonian deforestationSmall streamsIndicator taxaIntegrityBiodiversityLow forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrityBaixos limiares de perda florestal ameaçam a integridade da assembléia de peixes e macroinvertebrados amazônicosinfo:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/articlehttps://www.sciencedirect.com/science/article/pii/S1470160X21004386?via%3DihubRenato Tavares MartinsJanaina Gomes de BritoKarina Dias da SilvaCecília Gontijo LealRafael Pereira LeitãoVivian Campos de OliveiraJosé Max Barbosa de Oliveira JúniorSílvio Frosini de Barros FerrazFelipe Rossetti de PaulaFábio de Oliveira RoqueNeusa HamadaLeandro JuenJorge Luiz NessimianPaulo dos Santos PompeuRobert M. Hughesapplication/pdfinfo:eu-repo/semantics/openAccessreponame:Repositório Institucional da UFMGinstname:Universidade Federal de Minas Gerais (UFMG)instacron:UFMGLICENSELicense.txtLicense.txttext/plain; charset=utf-82042https://repositorio.ufmg.br/bitstream/1843/56285/1/License.txtfa505098d172de0bc8864fc1287ffe22MD51ORIGINALLow forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity.pdfLow forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity.pdfapplication/pdf2886725https://repositorio.ufmg.br/bitstream/1843/56285/2/Low%20forest-loss%20thresholds%20threaten%20Amazonian%20fish%20and%20macroinvertebrate%20assemblage%20integrity.pdf0ed85fa2034e82f3f37066f1c557aa70MD521843/562852023-07-14 17:24:53.867oai:repositorio.ufmg.br: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Repositório de PublicaçõesPUBhttps://repositorio.ufmg.br/oaiopendoar:2023-07-14T20:24:53Repositório Institucional da UFMG - Universidade Federal de Minas Gerais (UFMG)false
dc.title.pt_BR.fl_str_mv Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
dc.title.alternative.pt_BR.fl_str_mv Baixos limiares de perda florestal ameaçam a integridade da assembléia de peixes e macroinvertebrados amazônicos
title Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
spellingShingle Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
Renato Tavares Martins
Ecological thresholds
Amazonian deforestation
Small streams
Indicator taxa
Integrity
Biodiversity
Biodiversidade
Desmatamento - Amazonas
Rios - Brasil
Florestas tropicais - Amazônia
Madeira - Exploração
Florestas - Conservação
title_short Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
title_full Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
title_fullStr Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
title_full_unstemmed Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
title_sort Low forest-loss thresholds threaten Amazonian fish and macroinvertebrate assemblage integrity
author Renato Tavares Martins
author_facet Renato Tavares Martins
Janaina Gomes de Brito
Karina Dias da Silva
Cecília Gontijo Leal
Rafael Pereira Leitão
Vivian Campos de Oliveira
José Max Barbosa de Oliveira Júnior
Sílvio Frosini de Barros Ferraz
Felipe Rossetti de Paula
Fábio de Oliveira Roque
Neusa Hamada
Leandro Juen
Jorge Luiz Nessimian
Paulo dos Santos Pompeu
Robert M. Hughes
author_role author
author2 Janaina Gomes de Brito
Karina Dias da Silva
Cecília Gontijo Leal
Rafael Pereira Leitão
Vivian Campos de Oliveira
José Max Barbosa de Oliveira Júnior
Sílvio Frosini de Barros Ferraz
Felipe Rossetti de Paula
Fábio de Oliveira Roque
Neusa Hamada
Leandro Juen
Jorge Luiz Nessimian
Paulo dos Santos Pompeu
Robert M. Hughes
author2_role author
author
author
author
author
author
author
author
author
author
author
author
author
author
dc.contributor.author.fl_str_mv Renato Tavares Martins
Janaina Gomes de Brito
Karina Dias da Silva
Cecília Gontijo Leal
Rafael Pereira Leitão
Vivian Campos de Oliveira
José Max Barbosa de Oliveira Júnior
Sílvio Frosini de Barros Ferraz
Felipe Rossetti de Paula
Fábio de Oliveira Roque
Neusa Hamada
Leandro Juen
Jorge Luiz Nessimian
Paulo dos Santos Pompeu
Robert M. Hughes
dc.subject.por.fl_str_mv Ecological thresholds
Amazonian deforestation
Small streams
Indicator taxa
Integrity
Biodiversity
topic Ecological thresholds
Amazonian deforestation
Small streams
Indicator taxa
Integrity
Biodiversity
Biodiversidade
Desmatamento - Amazonas
Rios - Brasil
Florestas tropicais - Amazônia
Madeira - Exploração
Florestas - Conservação
dc.subject.other.pt_BR.fl_str_mv Biodiversidade
Desmatamento - Amazonas
Rios - Brasil
Florestas tropicais - Amazônia
Madeira - Exploração
Florestas - Conservação
description Deforestation is a major threat globally, but especially in tropical regions because they are biodiversity strongholds and carbon storehouses. Some studies have reported changes in species richness and composition in lotic ecosystems with increased forest-loss in their catchment, presumably resulting from the replacement of sensitive taxa by more resistant or tolerant taxa. Also, sensitive taxa respond to deforestation in a non-linear manner and fish and macroinvertebrates have different sensitivities to landscape pressures. Therefore, it is useful to determine the effects of forest-loss on widespread sensitive or threshold taxa in aquatic ecosystems. We used Threshold Indicator Taxa Analysis (TITAN) to assess forest-loss and land use history impacts in 92 eastern Amazonian stream sites. We determined TITAN peak-change thresholds for fish at 1% and 6% of forest-loss at total-catchment and local-riparian spatial extents, respectively, and at 2% and 40% of land-use intensity change at total-catchment and local-riparian spatial extents, respectively. For macroinvertebrates, TITAN peak-change thresholds were 1% and 11% of forest loss at total-catchment and local-riparian spatial extents, respectively, and at 3% of land-use intensity change for both total-catchment and local-riparian spatial extents. Because of these thresholds, inherent ecoregional variability and key literature, we have three major recommendations. 1) Logging should be prohibited in riparian reserves that are at least 100-m wide on each side of headwater streams and in a network of catchments across all biomes and as many landscape types as possible. 2) An ecologically and statistically rigorous monitoring program with standard methods should be implemented to assess and regulate land uses better. 3) Conservation planning areas should consider aquatic biota as well as terrestrial biota.
publishDate 2021
dc.date.issued.fl_str_mv 2021-08
dc.date.accessioned.fl_str_mv 2023-07-14T20:24:53Z
dc.date.available.fl_str_mv 2023-07-14T20:24:53Z
dc.type.status.fl_str_mv info:eu-repo/semantics/publishedVersion
dc.type.driver.fl_str_mv info:eu-repo/semantics/article
format article
status_str publishedVersion
dc.identifier.uri.fl_str_mv http://hdl.handle.net/1843/56285
dc.identifier.doi.pt_BR.fl_str_mv https://doi.org/10.1016/j.ecolind.2021.107773
dc.identifier.issn.pt_BR.fl_str_mv 1872-7034
dc.identifier.orcid.pt_BR.fl_str_mv https://orcid.org/0000-0003-3464-7905
https://orcid.org/0000-0001-5548-4995
https://orcid.org/0000-0002-0108-8572
https://orcid.org/0000-0001-7990-0068
https://orcid.org/0000-0002-0689-205X
https://orcid.org/0000-0003-1808-5420
https://orcid.org/0000-0001-5568-8824
https://orcid.org/0000-0001-5635-0622
https://orcid.org/0000-0002-3526-5426
https://orcid.org/0000-0002-6188-4386
https://orcid.org/0000-0001-8795-2538
https://orcid.org/0000-0002-7938-1517
url https://doi.org/10.1016/j.ecolind.2021.107773
http://hdl.handle.net/1843/56285
https://orcid.org/0000-0003-3464-7905
https://orcid.org/0000-0001-5548-4995
https://orcid.org/0000-0002-0108-8572
https://orcid.org/0000-0001-7990-0068
https://orcid.org/0000-0002-0689-205X
https://orcid.org/0000-0003-1808-5420
https://orcid.org/0000-0001-5568-8824
https://orcid.org/0000-0001-5635-0622
https://orcid.org/0000-0002-3526-5426
https://orcid.org/0000-0002-6188-4386
https://orcid.org/0000-0001-8795-2538
https://orcid.org/0000-0002-7938-1517
identifier_str_mv 1872-7034
dc.language.iso.fl_str_mv eng
language eng
dc.relation.ispartof.pt_BR.fl_str_mv Ecological Indicators
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dc.publisher.none.fl_str_mv Universidade Federal de Minas Gerais
dc.publisher.initials.fl_str_mv UFMG
dc.publisher.country.fl_str_mv Brasil
dc.publisher.department.fl_str_mv ICB - DEPARTAMENTO DE BIOLOGIA GERAL
publisher.none.fl_str_mv Universidade Federal de Minas Gerais
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