Floristic diversity, composition and dominance across Amazonian forest types respond differently to latitude
| dc.contributor.affiliation | Pontificia Universidad Católica del Perú. Departamento de Ciencias | |
| dc.contributor.author | de Aledo, J.G. | |
| dc.contributor.author | Paneghel, M. | |
| dc.contributor.author | Cayuela, L. | |
| dc.contributor.author | Matas-Granados, L. | |
| dc.contributor.author | Ben Saadi, C.B. | |
| dc.contributor.author | Salinas Revilla, N. | |
| dc.contributor.author | La Torre-Cuadros, M.D.L.Á. | |
| dc.contributor.author | García-Villacorta, R. | |
| dc.contributor.author | Macía, M.J. | |
| dc.date.accessioned | 2026-03-13T16:57:29Z | |
| dc.date.issued | 2023 | |
| dc.description.abstract | Abstract Aim The latitudinal biodiversity gradient is considered a first‐order biogeographical pattern for most taxonomic groups. Latitudinal variation in plant diversity is not always consistent, and this could be related to the particular characteristics of different forest types. In this study, we compare latitudinal changes in floristic diversity (alpha diversity), composition (beta diversity) and dominance across different tropical forest types: floodplain, terra firme and submontane forests. Location Western Amazonia (Ecuador, Peru and Bolivia). Taxon Woody plants. Methods We inventoried 1978 species and 31,203 individuals of vascular plants with a diameter at breast height ≥ 2.5 cm in 118 0.1‐ha plots over an 1800 km latitudinal gradient in three different forest types. The relationships between alpha diversity, latitude and forest type were analysed using generalised linear mixed models. Semi‐parametric permutational multivariate analysis of variance was used to investigate the effects of latitude and forest type on beta diversity. Dominant species abundances were correlated with non‐metric multidimensional scaling ordination axes to reflect their contributions in shaping changes in beta diversity. Results Alpha diversity increased towards equatorial latitudes in terra firme and submontane forests but remained relatively constant in floodplains. Beta diversity of all forest types changed with latitude, although less clearly in floodplains. Also, in floodplain forests, there were fewer dominant species contributing to beta diversity and more species homogeneous along the gradient. Main Conclusions Latitudinal diversity patterns are manifested in alpha and beta diversity since latitude summarizes climatic and edaphic changes. However, we found different responses of each forest type. In floodplain forests, inundation regime is a stronger predictor than latitude, limiting floristic diversity and composition. Changes in dominant species abundance over gradients explained species composition, but floodplain forests harboured more homogeneous dominant species than well drained forests. It is key to study environmental trends and habitat characteristics of each forest type to understand their species diversity and dominance patterns. | |
| dc.description.sponsorship | Funding: We thank the native communities that received and assisted us in their forests (Dicaro and Guiyero in Ecuador; Nueva Vida, Leoncio Prado, San Carlos, Yamino, and Infierno in Peru; and Tumupasa, Macahua, and Ixiamas in Bolivia). We thank the local authorities for supporting and allowing our work in their protected areas: Servicio Nacional de Áreas Naturales Protegidas por el Estado (SERNANP) and Servicio Nacional Forestal (SERFOR) in Peru, Ministerio de Medio Ambiente y Agua in Bolivia, and Organización de Nacionalidades Huaorani de la Amazonia Ecuatoriana (ONHAE) in Ecuador. We are very grateful to Luis Torres Montenegro for his valuable work identifying voucher specimens and guidance in the field, to Manuel Marca for his field support and assistance; Guillermo Bañares de Dios, Gabriel Carvalho, Eric Cosio, Alex Nina and Rudi Saúl for their logistic assistance; Iñigo Gómez, Maaike Pyck and Silvia Aguado for their valuable voluntary work, and Gabriel Arellano for his comments on the manuscript. Fieldwork permissions were obtained to access the areas and collect the samples. Peru: Reserva Nacional Tambopata: N° 35-2017-SERNANP-DGANP, Reserva Nacional Pacaya-Samiria: N° 037-2018-SERNANP-JEF, Zona de Amortiguamiento Parque Nacional Cordillera Azul: N° 315-2017-SERFOR-DGGSPFFS, Zona de Amortiguamiento Reserva Comunal Yanesha: N° 401-2018-MINAGRI-SERFOR-DGGSPFFS, Área de Conservación Regional Maijuna-Kichwa: N° 003-2019-GLR-GGR-ARA. Ecuador: Parque Nacional Yasuní funded by the European Union (INCO-DC, IC18-CT960038). Bolivia: Parque Nacional Madidi funded by Ministerio de Desarrollo Rural, Agropecuario y Medio Ambiente MDRAyMA - VBRFMA - DGBAP - UAPVS N° 2869/08. This project received support from the Spanish Ministry of Economy and Competitiveness under grant numbers CGL2016–75414–P and PID2019-105064GB-I00, the Education Department of Madrid (Spain) and the European Union.; Funding text 2: We thank the native communities that received and assisted us in their forests (Dicaro and Guiyero in Ecuador; Nueva Vida, Leoncio Prado, San Carlos, Yamino, and Infierno in Peru; and Tumupasa, Macahua, and Ixiamas in Bolivia). We thank the local authorities for supporting and allowing our work in their protected areas: Servicio Nacional de Áreas Naturales Protegidas por el Estado (SERNANP) and Servicio Nacional Forestal (SERFOR) in Peru, Ministerio de Medio Ambiente y Agua in Bolivia, and Organización de Nacionalidades Huaorani de la Amazonia Ecuatoriana (ONHAE) in Ecuador. We are very grateful to Luis Torres Montenegro for his valuable work identifying voucher specimens and guidance in the field, to Manuel Marca for his field support and assistance; Guillermo Bañares de Dios, Gabriel Carvalho, Eric Cosio, Alex Nina and Rudi Saúl for their logistic assistance; Iñigo Gómez, Maaike Pyck and Silvia Aguado for their valuable voluntary work, and Gabriel Arellano for his comments on the manuscript. Fieldwork permissions were obtained to access the areas and collect the samples. Peru: Reserva Nacional Tambopata: N° 35‐2017‐SERNANP‐DGANP, Reserva Nacional Pacaya‐Samiria: N° 037‐2018‐SERNANP‐JEF, Zona de Amortiguamiento Parque Nacional Cordillera Azul: N° 315‐2017‐SERFOR‐DGGSPFFS, Zona de Amortiguamiento Reserva Comunal Yanesha: N° 401‐2018‐MINAGRI‐SERFOR‐DGGSPFFS, Área de Conservación Regional Maijuna‐Kichwa: N° 003‐2019‐GLR‐GGR‐ARA. Ecuador: Parque Nacional Yasuní funded by the European Union (INCO‐DC, IC18‐CT960038). Bolivia: Parque Nacional Madidi funded by Ministerio de Desarrollo Rural, Agropecuario y Medio Ambiente MDRAyMA ‐ VBRFMA ‐ DGBAP ‐ UAPVS N° 2869/08. This project received support from the Spanish Ministry of Economy and Competitiveness under grant numbers CGL2016–75414–P and PID2019‐105064GB‐I00, the Education Department of Madrid (Spain) and the European Union. | |
| dc.identifier.doi | https://doi.org/10.1111/jbi.14561 | |
| dc.identifier.uri | http://hdl.handle.net/20.500.14657/205568 | |
| dc.language.iso | eng | |
| dc.publisher | John Wiley and Sons | |
| dc.relation.ispartof | urn:issn:0305-0270 | |
| dc.rights | info:eu-repo/semantics/closedAccess | |
| dc.source | Journal of Biogeography; Vol. 50, Núm. 4 (2023) | |
| dc.subject | Alpha diversity | |
| dc.subject | Beta diversity | |
| dc.subject | Ordination | |
| dc.subject | Ecology | |
| dc.subject | Species richness | |
| dc.subject | Gamma diversity | |
| dc.subject | Floodplain | |
| dc.subject | Biodiversity | |
| dc.subject | Dominance (genetics) | |
| dc.subject | Geography | |
| dc.subject | Species diversity | |
| dc.subject | Latitude | |
| dc.subject | Detrended correspondence analysis | |
| dc.subject | Floristics | |
| dc.subject | Biology | |
| dc.subject.ocde | https://purl.org/pe-repo/ocde/ford#1.05.08 | |
| dc.title | Floristic diversity, composition and dominance across Amazonian forest types respond differently to latitude | |
| dc.type | http://purl.org/coar/resource_type/c_6501 | |
| dc.type.other | Artículo | |
| dc.type.version | https://vocabularies.coar-repositories.org/version_types/c_970fb48d4fbd8a85/ |
