Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade)
Main Author: | |
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Publication Date: | 2015 |
Format: | Master thesis |
Language: | por |
Source: | Repositório Institucional da UFSCAR |
Download full: | https://repositorio.ufscar.br/handle/20.500.14289/8371 |
Summary: | In Brazil, there are about 6,500 individuals of Anodorhynchus hyacinthinus (Hyacinth macaw) in wild, located in three physiognomically distinct regions. The specie is demanding as to breeding habitat, and can be regarded as feeding specialist. Currently, the species is endangered because the reduction of their originally habitat, as consequence of the disorderly process of land occupation. This process, broadly, causes negative effects on landscape, in particular the remaining native forest vegetation. In this context, the study aimed to evaluate the occurrence of Hyacinth macaw in mosaic Carajás landscape, considering the intrinsic characteristics of the landscape structure and biology of this species. We considered three regions of the Carajás mosaic: R1- Itacaiúnas river, R2-FLONA Itacaiúnas and, R3 - Canaã dos Carajás. The sampling of Hyacinth macaw was done through direct observation and calculated the frequency records for R1 (1.26 region/hour), R2 (0.38 reg./hour) and R3 (0.44 reg. /hour), and after, was estimated area of life for each region (R1 = 22187.87 ha; R2= 66397.0ha, R3 = 41841.2ha). We made the land-use/land-cover map to support evaluation of the landscape, through unsupervised classification of satellite images. The final map was reclassified two classes: forest and non-forest. The follow landscape metrics were calculated: distance between fragments (R2 = 499 m; R3 = 364m), midsize (R2 = 148,5ha; R3 = 10,6ha), the size of the largest fragment (R2 = 39.360,8ha; R3 = 888,1ha), and number of fragments (R2 = 337, R3 = 863). From the results, we can said that forested areas with riparian vegetation presence appear to be more propitious to Hyacinth macaw occurrence in the mosaic Carajás, Pará, Brazil, but the preference for open areas is not ruled out. Furthermore, the species occupy different degraded patterns landscape, because there is a large displacement capacity and proximity to the mosaic. Atropism and interaction with other species, such as red macaws may be other factors that affect the distribution of species in the Carajás region. |
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Conrado, Ludmila PereiraValente, Roberta de Oliveira Avernahttp://lattes.cnpq.br/1582627535733911http://lattes.cnpq.br/4212904334696001916649c7-7b0e-4093-9b57-025a3b1395492017-01-12T19:25:20Z2017-01-12T19:25:20Z2015-09-04CONRADO, Ludmila Pereira. Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade). 2015. Dissertação (Mestrado em Diversidade Biológica e Conservação) – Universidade Federal de São Carlos, Sorocaba, 2015. Disponível em: https://repositorio.ufscar.br/handle/20.500.14289/8371.https://repositorio.ufscar.br/handle/20.500.14289/8371In Brazil, there are about 6,500 individuals of Anodorhynchus hyacinthinus (Hyacinth macaw) in wild, located in three physiognomically distinct regions. The specie is demanding as to breeding habitat, and can be regarded as feeding specialist. Currently, the species is endangered because the reduction of their originally habitat, as consequence of the disorderly process of land occupation. This process, broadly, causes negative effects on landscape, in particular the remaining native forest vegetation. In this context, the study aimed to evaluate the occurrence of Hyacinth macaw in mosaic Carajás landscape, considering the intrinsic characteristics of the landscape structure and biology of this species. We considered three regions of the Carajás mosaic: R1- Itacaiúnas river, R2-FLONA Itacaiúnas and, R3 - Canaã dos Carajás. The sampling of Hyacinth macaw was done through direct observation and calculated the frequency records for R1 (1.26 region/hour), R2 (0.38 reg./hour) and R3 (0.44 reg. /hour), and after, was estimated area of life for each region (R1 = 22187.87 ha; R2= 66397.0ha, R3 = 41841.2ha). We made the land-use/land-cover map to support evaluation of the landscape, through unsupervised classification of satellite images. The final map was reclassified two classes: forest and non-forest. The follow landscape metrics were calculated: distance between fragments (R2 = 499 m; R3 = 364m), midsize (R2 = 148,5ha; R3 = 10,6ha), the size of the largest fragment (R2 = 39.360,8ha; R3 = 888,1ha), and number of fragments (R2 = 337, R3 = 863). From the results, we can said that forested areas with riparian vegetation presence appear to be more propitious to Hyacinth macaw occurrence in the mosaic Carajás, Pará, Brazil, but the preference for open areas is not ruled out. Furthermore, the species occupy different degraded patterns landscape, because there is a large displacement capacity and proximity to the mosaic. Atropism and interaction with other species, such as red macaws may be other factors that affect the distribution of species in the Carajás region.No Brasil, estima-se um total de 6.500 indivíduos de Anodorhynchus hyacinthinus (araraazul-grande) em vida livre, distribuídos em três regiões fisionomicamente distintas. A espécie é exigente quanto ao seu hábitat reprodutivo, e pode ser considerada especialista quanto à alimentação. Encontra-se, atualmente, ameaçada de extinção em função da redução de seu habitat natural, por consequência do processo desordenado de uso e ocupação do solo. Este processo, por sua vez, acarreta efeitos negativos na paisagem como um todo e, em especial nos remanescentes de vegetação florestal nativa. Nesse contexto, o trabalho teve como objetivo avaliar a ocorrência da arara-azul-grande, na paisagem do mosaico Carajás, considerando as características intrínsecas da estrutura da paisagem e a biologia da espécie. Considerou-se para o estudo, três regiões do mosaico Carajás: R1- rio Itacaiúnas, R2- FLONA Itacaiúnas, R3- Canaã dos Carajás. Para a amostragem da arara-azul-grande foi feita observação direta e calculou-se a frequência de avistamentos para R1 (1,26 reg./hora), R2 (0,38reg./hora) e R3 (0,44 reg./hora), posteriormente foi estimada a área de vida da espécie em cada região (R1= 22.187,87 ha; R2= 66.397,0ha; R3= 41.841,2ha). Para subsidiar a avaliação da paisagem foi feito o mapa de uso e cobertura do solo, através da classificação não supervisionada de imagens orbitais, sendo que as classes resultantes foram reclassificadas em floresta e não floresta. As métricas da paisagem calculadas foram: distância entre fragmentos (R2= 499 m; R3=364m), tamanho médio (R2=148,5ha; R3= 10,6ha), tamanho do maior fragmento (R2= 39.360,8ha; R3=888,1ha) e número de fragmentos (R2= 337; R3=863). A partir dos resultados obtidos pode-se dizer que as áreas florestadas, com presença de mata ciliar, parecem ser um ambiente mais propicio à ocorrência da arara-azul-grande no mosaico Carajás/PA, porém a preferência por áreas abertas não é descartada. Além disso, os indivíduos da espécie ocupam diferentes padrões de paisagem degradada, devido sua ampla capacidade de deslocamento e proximidade com o mosaico. Entre outros fatores que podem afetar sua ocorrência na região de Carajás, pode-se citar a antropização e interação com outras espécies, como a arara-vermelha.Não recebi financiamentoporUniversidade Federal de São CarlosCâmpus SorocabaPrograma de Pós-Graduação em Diversidade Biológica e Conservação - PPGDBC-SoUFSCarEcologia das paisagensPaisagens fragmentadasAveLandscape ecologyFragmented landscapesBirdsCIENCIAS AGRARIAS::RECURSOS FLORESTAIS E ENGENHARIA FLORESTAL::CONSERVACAO DA NATUREZARelação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade)Relationship between landscape structure mOSaIC Carajás, PA with the occurrence of Anodorhynchus hyacinthinus (Hyacinth macaw)info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/masterThesisOnline6006003da59c04-c9ab-40ae-8977-de263adbf68dinfo:eu-repo/semantics/openAccessreponame:Repositório Institucional da UFSCARinstname:Universidade Federal de São Carlos (UFSCAR)instacron:UFSCARORIGINALCONRADO_Ludmila Pereira_2016.pdfCONRADO_Ludmila Pereira_2016.pdfapplication/pdf10153126https://repositorio.ufscar.br/bitstreams/aa22de8d-d191-49a4-b1f8-a68e164313af/downloadf7c09775254235adf2760cfd25fb8a1bMD51trueAnonymousREADLICENSElicense.txtlicense.txttext/plain; charset=utf-81957https://repositorio.ufscar.br/bitstreams/78544744-38d2-42b3-96e3-4f61f0d73c2a/downloadae0398b6f8b235e40ad82cba6c50031dMD52falseAnonymousREADTEXTCONRADO_Ludmila Pereira_2016.pdf.txtCONRADO_Ludmila Pereira_2016.pdf.txtExtracted texttext/plain74403https://repositorio.ufscar.br/bitstreams/a9e2002a-2ce5-42ff-b8f2-ed947de873c6/download2deb70e7c876a74d9c19314114c95c04MD55falseAnonymousREADTHUMBNAILCONRADO_Ludmila Pereira_2016.pdf.jpgCONRADO_Ludmila Pereira_2016.pdf.jpgIM Thumbnailimage/jpeg4199https://repositorio.ufscar.br/bitstreams/2c09acf0-e5f8-463d-bd45-055b673640d1/download2f374020f1d22ef1a84f05d17437d3adMD56falseAnonymousREAD20.500.14289/83712025-02-05 17:28:30.52Acesso abertoopen.accessoai:repositorio.ufscar.br:20.500.14289/8371https://repositorio.ufscar.brRepositório InstitucionalPUBhttps://repositorio.ufscar.br/oai/requestrepositorio.sibi@ufscar.bropendoar:43222025-02-05T20:28:30Repositório Institucional da UFSCAR - Universidade Federal de São Carlos (UFSCAR)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 |
dc.title.por.fl_str_mv |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
dc.title.alternative.eng.fl_str_mv |
Relationship between landscape structure mOSaIC Carajás, PA with the occurrence of Anodorhynchus hyacinthinus (Hyacinth macaw) |
title |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
spellingShingle |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) Conrado, Ludmila Pereira Ecologia das paisagens Paisagens fragmentadas Ave Landscape ecology Fragmented landscapes Birds CIENCIAS AGRARIAS::RECURSOS FLORESTAIS E ENGENHARIA FLORESTAL::CONSERVACAO DA NATUREZA |
title_short |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
title_full |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
title_fullStr |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
title_full_unstemmed |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
title_sort |
Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade) |
author |
Conrado, Ludmila Pereira |
author_facet |
Conrado, Ludmila Pereira |
author_role |
author |
dc.contributor.authorlattes.por.fl_str_mv |
http://lattes.cnpq.br/4212904334696001 |
dc.contributor.author.fl_str_mv |
Conrado, Ludmila Pereira |
dc.contributor.advisor1.fl_str_mv |
Valente, Roberta de Oliveira Averna |
dc.contributor.advisor1Lattes.fl_str_mv |
http://lattes.cnpq.br/1582627535733911 |
dc.contributor.authorID.fl_str_mv |
916649c7-7b0e-4093-9b57-025a3b139549 |
contributor_str_mv |
Valente, Roberta de Oliveira Averna |
dc.subject.por.fl_str_mv |
Ecologia das paisagens Paisagens fragmentadas Ave |
topic |
Ecologia das paisagens Paisagens fragmentadas Ave Landscape ecology Fragmented landscapes Birds CIENCIAS AGRARIAS::RECURSOS FLORESTAIS E ENGENHARIA FLORESTAL::CONSERVACAO DA NATUREZA |
dc.subject.eng.fl_str_mv |
Landscape ecology Fragmented landscapes Birds |
dc.subject.cnpq.fl_str_mv |
CIENCIAS AGRARIAS::RECURSOS FLORESTAIS E ENGENHARIA FLORESTAL::CONSERVACAO DA NATUREZA |
description |
In Brazil, there are about 6,500 individuals of Anodorhynchus hyacinthinus (Hyacinth macaw) in wild, located in three physiognomically distinct regions. The specie is demanding as to breeding habitat, and can be regarded as feeding specialist. Currently, the species is endangered because the reduction of their originally habitat, as consequence of the disorderly process of land occupation. This process, broadly, causes negative effects on landscape, in particular the remaining native forest vegetation. In this context, the study aimed to evaluate the occurrence of Hyacinth macaw in mosaic Carajás landscape, considering the intrinsic characteristics of the landscape structure and biology of this species. We considered three regions of the Carajás mosaic: R1- Itacaiúnas river, R2-FLONA Itacaiúnas and, R3 - Canaã dos Carajás. The sampling of Hyacinth macaw was done through direct observation and calculated the frequency records for R1 (1.26 region/hour), R2 (0.38 reg./hour) and R3 (0.44 reg. /hour), and after, was estimated area of life for each region (R1 = 22187.87 ha; R2= 66397.0ha, R3 = 41841.2ha). We made the land-use/land-cover map to support evaluation of the landscape, through unsupervised classification of satellite images. The final map was reclassified two classes: forest and non-forest. The follow landscape metrics were calculated: distance between fragments (R2 = 499 m; R3 = 364m), midsize (R2 = 148,5ha; R3 = 10,6ha), the size of the largest fragment (R2 = 39.360,8ha; R3 = 888,1ha), and number of fragments (R2 = 337, R3 = 863). From the results, we can said that forested areas with riparian vegetation presence appear to be more propitious to Hyacinth macaw occurrence in the mosaic Carajás, Pará, Brazil, but the preference for open areas is not ruled out. Furthermore, the species occupy different degraded patterns landscape, because there is a large displacement capacity and proximity to the mosaic. Atropism and interaction with other species, such as red macaws may be other factors that affect the distribution of species in the Carajás region. |
publishDate |
2015 |
dc.date.issued.fl_str_mv |
2015-09-04 |
dc.date.accessioned.fl_str_mv |
2017-01-12T19:25:20Z |
dc.date.available.fl_str_mv |
2017-01-12T19:25:20Z |
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info:eu-repo/semantics/publishedVersion |
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info:eu-repo/semantics/masterThesis |
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masterThesis |
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publishedVersion |
dc.identifier.citation.fl_str_mv |
CONRADO, Ludmila Pereira. Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade). 2015. Dissertação (Mestrado em Diversidade Biológica e Conservação) – Universidade Federal de São Carlos, Sorocaba, 2015. Disponível em: https://repositorio.ufscar.br/handle/20.500.14289/8371. |
dc.identifier.uri.fl_str_mv |
https://repositorio.ufscar.br/handle/20.500.14289/8371 |
identifier_str_mv |
CONRADO, Ludmila Pereira. Relação da estrutura da paisagem mosaico Carajás, PA com a ocorrência de Anodorlynchus hyacinthinus (arara-azul-grade). 2015. Dissertação (Mestrado em Diversidade Biológica e Conservação) – Universidade Federal de São Carlos, Sorocaba, 2015. Disponível em: https://repositorio.ufscar.br/handle/20.500.14289/8371. |
url |
https://repositorio.ufscar.br/handle/20.500.14289/8371 |
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por |
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openAccess |
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Universidade Federal de São Carlos Câmpus Sorocaba |
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Programa de Pós-Graduação em Diversidade Biológica e Conservação - PPGDBC-So |
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UFSCar |
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Universidade Federal de São Carlos Câmpus Sorocaba |
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