ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL
Autor(a) principal: | |
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Data de Publicação: | 2017 |
Outros Autores: | |
Tipo de documento: | Artigo |
Idioma: | por |
Título da fonte: | Revista Brasileira de Ciências Ambientais (Online) |
Texto Completo: | https://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/115 |
Resumo: | The ecological functionality of a restored area is associated with the return of processes such as nutrient cycling, input and establishment of new propagules, which can be promoted by the appropriate species selection and the promotion of functional diversity and of species. In a restoration of 50 ha in Rio de Janeiro, Brazil, evaluations were carried out at 5 and 20 months after planting, aiming to analyze the establishment of ecological processes in the restoration and to identify representative indicators. For this purpose, a set of indicators was applied in 23 plots (25 x 4 m): (a) structure - basal area (AB) [ΣAB and AB/m²], mean height of individuals and density (number of individuals/ha); (b) community diversity - Shannon diversity (H’) and equitability (J’) indexes, and species richness (S=number of species); (c) ecological function - presence of species of functional groups (% of zoocoric, pioneers and N2 fixers) and; (d) landscape context - grass cover (soil cover with grasses and projections of crowns in soil and % of natural regeneration). The differences between the years for the indicators were assessed by the chi-square test. To determine which indicators influenced the results, using the unweighted pair group method with arithmetic mean method to principal components analysis (PCA) with 15 indicators x age was performed. Of the total of 88 species observed in both periods, 15 were dominant, with 51.1% of the planted individuals. In this group, 8 had mortality rates over 70%. It is suggested that the planting of these species in high density can cause a so-called process of looping, caused by the opening of gaps over time, facilitating the reestablishment of invasive grasses. The most efficient indicators for evaluating the areas were density, diversity, equitability (H’ and J) and canopy cover. Between 5 and 20 months of age, there was a significant reduction of richness, higher for families than for species. However, the ecological function did not vary among the ages, despite the reduction in diversity, showing that there was functional redundancy between different species. |
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ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZILFUNCIONALIDADE ECOLÓGICA DA RESTAURAÇÃO DE ÁREAS DEGRADADAS NO BIOMA MATA ATLÂNTICA, RIO DE JANEIROindicadores; monitoramento; processos ecológicos.indicators; monitoring; ecological process.The ecological functionality of a restored area is associated with the return of processes such as nutrient cycling, input and establishment of new propagules, which can be promoted by the appropriate species selection and the promotion of functional diversity and of species. In a restoration of 50 ha in Rio de Janeiro, Brazil, evaluations were carried out at 5 and 20 months after planting, aiming to analyze the establishment of ecological processes in the restoration and to identify representative indicators. For this purpose, a set of indicators was applied in 23 plots (25 x 4 m): (a) structure - basal area (AB) [ΣAB and AB/m²], mean height of individuals and density (number of individuals/ha); (b) community diversity - Shannon diversity (H’) and equitability (J’) indexes, and species richness (S=number of species); (c) ecological function - presence of species of functional groups (% of zoocoric, pioneers and N2 fixers) and; (d) landscape context - grass cover (soil cover with grasses and projections of crowns in soil and % of natural regeneration). The differences between the years for the indicators were assessed by the chi-square test. To determine which indicators influenced the results, using the unweighted pair group method with arithmetic mean method to principal components analysis (PCA) with 15 indicators x age was performed. Of the total of 88 species observed in both periods, 15 were dominant, with 51.1% of the planted individuals. In this group, 8 had mortality rates over 70%. It is suggested that the planting of these species in high density can cause a so-called process of looping, caused by the opening of gaps over time, facilitating the reestablishment of invasive grasses. The most efficient indicators for evaluating the areas were density, diversity, equitability (H’ and J) and canopy cover. Between 5 and 20 months of age, there was a significant reduction of richness, higher for families than for species. However, the ecological function did not vary among the ages, despite the reduction in diversity, showing that there was functional redundancy between different species.A funcionalidade ecológica de uma área restaurada está associada ao retornode processos como a ciclagem de nutrientes, aporte e estabelecimento denovos propágulos, os quais podem ser promovidos pela escolha adequadade espécies e pela promoção da diversidade funcional e de espécies. Em umarestauração de 50 ha situada no Rio de Janeiro, foram realizadas avaliações aos5 e aos 20 meses após o plantio, visando avaliar o estabelecimento de processosecológicos na restauração assim como identificar indicadores representativosdas alterações observadas. Para tanto, em 23 parcelas (25 x 4 m) foi empregadoum conjunto de indicadores de: (a) estrutura – área basal (AB) [ΣAB e AB/m²],altura média dos indivíduos e densidade (nº de indivíduos/ha); (b) diversidadeda comunidade – índices de diversidade de Shannon (H´) e de equitabilidade (J´)e riqueza de espécies (S=número de espécies); (c) função ecológica - presençade espécies de diferentes grupos funcionais (% de zoocóricas, pioneiras efixadoras de N2) e; (d) contexto da paisagem – cobertura de gramíneas (% decobertura do solo com gramíneas e com as projeções das copas no solo e% de regenerantes). As diferenças entre os anos para os indicadores foramavaliadas pelo teste do qui-quadrado. Para determinar quais indicadoresinfluenciaram nos resultados obtidos, foi efetuada a análise de componentesprincipais (PCA) pelo método de médias aritméticas não ponderadas(UPGMA) com 15 indicadores x idade. Do total de 88 espécies observadas nos2 períodos, 15 delas foram dominantes, com 51,1% dos indivíduos plantados.Nesse grupo, 8 tiveram taxas de mortalidade dos indivíduos superioresa 70%. Sugere-se que o plantio dessas espécies em alta densidade podecausar um processo de abertura de clareiras ao longo do tempo, facilitando orestabelecimento de gramíneas invasoras. Os indicadores mais eficientes paraavaliação das áreas foram: densidade, diversidade, equitabilidade (H´ e J) ecobertura de copa. Entre 5 e 20 meses de idade, houve redução significativada riqueza, sendo maior para famílias do que para espécies. Contudo,os indicadores de funções ecológicas não variaram entre as idades, apesar daredução na diversidade, mostrando que houve redundância funcional entrediferentes espécies.Zeppelini Publishers2017-07-01info:eu-repo/semantics/articleinfo:eu-repo/semantics/publishedVersionapplication/pdfhttps://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/11510.5327/Z2176-947820170175Revista Brasileira de Ciências Ambientais (Online); n. 43 (2017): RBCIAMB - ISSN 2176-9478 - Março; 17-31Brazilian Journal of Environmental Sciences (Online); No. 43 (2017): RBCIAMB - ISSN 2176-9478 - March; 17-312176-94781808-4524reponame:Revista Brasileira de Ciências Ambientais (Online)instname:Associação Brasileira de Engenharia Sanitária e Ambiental (ABES)instacron:ABESporhttps://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/115/83Copyright (c) 2017 Revista Brasileira de Ciências Ambientais (Online)info:eu-repo/semantics/openAccessAltivo, Felipe de SouzaPiña Rodrigues, Fatima Conceição Marquéz2022-02-22T21:22:19Zoai:ojs.www.rbciamb.com.br:article/115Revistahttp://www.rbciamb.com.br/index.php/Publicacoes_RBCIAMBhttps://www.rbciamb.com.br/Publicacoes_RBCIAMB/oairbciamb@abes-dn.org.br||2176-94781804-4524opendoar:2022-02-22T21:22:19Revista Brasileira de Ciências Ambientais (Online) - Associação Brasileira de Engenharia Sanitária e Ambiental (ABES)false |
dc.title.none.fl_str_mv |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL FUNCIONALIDADE ECOLÓGICA DA RESTAURAÇÃO DE ÁREAS DEGRADADAS NO BIOMA MATA ATLÂNTICA, RIO DE JANEIRO |
title |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
spellingShingle |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL Altivo, Felipe de Souza indicadores; monitoramento; processos ecológicos. indicators; monitoring; ecological process. |
title_short |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
title_full |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
title_fullStr |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
title_full_unstemmed |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
title_sort |
ECOLOGICAL FUNCTIONALITY OF RESTORATION OF DEGRADED AREAS IN THE MATA ATLANTICA BIOME, RIO DE JANEIRO, BRAZIL |
author |
Altivo, Felipe de Souza |
author_facet |
Altivo, Felipe de Souza Piña Rodrigues, Fatima Conceição Marquéz |
author_role |
author |
author2 |
Piña Rodrigues, Fatima Conceição Marquéz |
author2_role |
author |
dc.contributor.author.fl_str_mv |
Altivo, Felipe de Souza Piña Rodrigues, Fatima Conceição Marquéz |
dc.subject.por.fl_str_mv |
indicadores; monitoramento; processos ecológicos. indicators; monitoring; ecological process. |
topic |
indicadores; monitoramento; processos ecológicos. indicators; monitoring; ecological process. |
description |
The ecological functionality of a restored area is associated with the return of processes such as nutrient cycling, input and establishment of new propagules, which can be promoted by the appropriate species selection and the promotion of functional diversity and of species. In a restoration of 50 ha in Rio de Janeiro, Brazil, evaluations were carried out at 5 and 20 months after planting, aiming to analyze the establishment of ecological processes in the restoration and to identify representative indicators. For this purpose, a set of indicators was applied in 23 plots (25 x 4 m): (a) structure - basal area (AB) [ΣAB and AB/m²], mean height of individuals and density (number of individuals/ha); (b) community diversity - Shannon diversity (H’) and equitability (J’) indexes, and species richness (S=number of species); (c) ecological function - presence of species of functional groups (% of zoocoric, pioneers and N2 fixers) and; (d) landscape context - grass cover (soil cover with grasses and projections of crowns in soil and % of natural regeneration). The differences between the years for the indicators were assessed by the chi-square test. To determine which indicators influenced the results, using the unweighted pair group method with arithmetic mean method to principal components analysis (PCA) with 15 indicators x age was performed. Of the total of 88 species observed in both periods, 15 were dominant, with 51.1% of the planted individuals. In this group, 8 had mortality rates over 70%. It is suggested that the planting of these species in high density can cause a so-called process of looping, caused by the opening of gaps over time, facilitating the reestablishment of invasive grasses. The most efficient indicators for evaluating the areas were density, diversity, equitability (H’ and J) and canopy cover. Between 5 and 20 months of age, there was a significant reduction of richness, higher for families than for species. However, the ecological function did not vary among the ages, despite the reduction in diversity, showing that there was functional redundancy between different species. |
publishDate |
2017 |
dc.date.none.fl_str_mv |
2017-07-01 |
dc.type.driver.fl_str_mv |
info:eu-repo/semantics/article info:eu-repo/semantics/publishedVersion |
format |
article |
status_str |
publishedVersion |
dc.identifier.uri.fl_str_mv |
https://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/115 10.5327/Z2176-947820170175 |
url |
https://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/115 |
identifier_str_mv |
10.5327/Z2176-947820170175 |
dc.language.iso.fl_str_mv |
por |
language |
por |
dc.relation.none.fl_str_mv |
https://www.rbciamb.com.br/Publicacoes_RBCIAMB/article/view/115/83 |
dc.rights.driver.fl_str_mv |
Copyright (c) 2017 Revista Brasileira de Ciências Ambientais (Online) info:eu-repo/semantics/openAccess |
rights_invalid_str_mv |
Copyright (c) 2017 Revista Brasileira de Ciências Ambientais (Online) |
eu_rights_str_mv |
openAccess |
dc.format.none.fl_str_mv |
application/pdf |
dc.publisher.none.fl_str_mv |
Zeppelini Publishers |
publisher.none.fl_str_mv |
Zeppelini Publishers |
dc.source.none.fl_str_mv |
Revista Brasileira de Ciências Ambientais (Online); n. 43 (2017): RBCIAMB - ISSN 2176-9478 - Março; 17-31 Brazilian Journal of Environmental Sciences (Online); No. 43 (2017): RBCIAMB - ISSN 2176-9478 - March; 17-31 2176-9478 1808-4524 reponame:Revista Brasileira de Ciências Ambientais (Online) instname:Associação Brasileira de Engenharia Sanitária e Ambiental (ABES) instacron:ABES |
instname_str |
Associação Brasileira de Engenharia Sanitária e Ambiental (ABES) |
instacron_str |
ABES |
institution |
ABES |
reponame_str |
Revista Brasileira de Ciências Ambientais (Online) |
collection |
Revista Brasileira de Ciências Ambientais (Online) |
repository.name.fl_str_mv |
Revista Brasileira de Ciências Ambientais (Online) - Associação Brasileira de Engenharia Sanitária e Ambiental (ABES) |
repository.mail.fl_str_mv |
rbciamb@abes-dn.org.br|| |
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1797068920096555008 |