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Changes in Size of Deforested Patches in the Brazilian Amazon
Different deforestation agents, such as small farmers and large agricultural businesses, create different spatial patterns of deforestation. We analyzed the proportion of deforestation associated with different-sized clearings in the Brazilian Amazon from 2002 through 2009. We used annual deforestat...
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Published in: | Conservation biology 2012-10, Vol.26 (5), p.932-937 |
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description | Different deforestation agents, such as small farmers and large agricultural businesses, create different spatial patterns of deforestation. We analyzed the proportion of deforestation associated with different-sized clearings in the Brazilian Amazon from 2002 through 2009. We used annual deforestation maps to determine total area deforested and the size distribution of deforested patches per year. The size distribution of deforested areas changed over time in a consistent, directional manner. Large clearings (> 1000 ha) comprised progressively smaller amounts of total annual deforestation. The number of smaller clearings (6.25—50.00 ha) remained unchanged over time. Small clearings accounted for 73% of all deforestation in 2009, up from 30% in 2002, whereas the proportion of deforestation attributable to large clearings decreased from 13% to 3% between 2002 and 2009. Large clearings were concentrated in Mato Grosso, but also occurred in eastern Pará and in Rondônia. In 2002 large clearings accounted for 17%, 15%, and 10% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. Even in these states, where there is a highly developed agricultural business dominated by soybean production and cattle ranching, the proportional contribution of large clearings to total deforestation declined. By 2009 large clearings accounted for 2.5%, 3.5%, and 1% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. These changes in deforestation patch size are coincident with the implementation of new conservation policies by the Brazilian government, which suggests that these policies are not effectively reducing the number of small clearings in primary forest, whether these are caused by large landholders or smallholders, but have been more effective at reducing the frequency of larger clearings. Diferentes agentes de deforestación, como campesinos y negocios agrícolas, crean diferentes patrones espaciales de deforestación. Analizamos la proporción de deforestación asociada con claros de diferentes tamaños en la Amazonía brasileña entre 2002 y 2009. Utilizamos mapas de deforestación anual para determinar el área total deforestada y la distribución de tamaños de parches deforestados por año. La distribución de tamaños de áreas deforestadas cambió de manera consistente y direccional. Los claros extensos (> 1000 ha) progresivamente abarcaron cantidades menores de deforestación anual total. El número de claros pequeños (6.25—50.00ha) permanecieron |
doi_str_mv | 10.1111/j.1523-1739.2012.01901.x |
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D. ; SOUZA, CARLOS ; EWERS, ROBERT M.</creator><creatorcontrib>ROSA, ISABEL M. D. ; SOUZA, CARLOS ; EWERS, ROBERT M.</creatorcontrib><description>Different deforestation agents, such as small farmers and large agricultural businesses, create different spatial patterns of deforestation. We analyzed the proportion of deforestation associated with different-sized clearings in the Brazilian Amazon from 2002 through 2009. We used annual deforestation maps to determine total area deforested and the size distribution of deforested patches per year. The size distribution of deforested areas changed over time in a consistent, directional manner. Large clearings (> 1000 ha) comprised progressively smaller amounts of total annual deforestation. The number of smaller clearings (6.25—50.00 ha) remained unchanged over time. Small clearings accounted for 73% of all deforestation in 2009, up from 30% in 2002, whereas the proportion of deforestation attributable to large clearings decreased from 13% to 3% between 2002 and 2009. Large clearings were concentrated in Mato Grosso, but also occurred in eastern Pará and in Rondônia. In 2002 large clearings accounted for 17%, 15%, and 10% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. Even in these states, where there is a highly developed agricultural business dominated by soybean production and cattle ranching, the proportional contribution of large clearings to total deforestation declined. By 2009 large clearings accounted for 2.5%, 3.5%, and 1% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. These changes in deforestation patch size are coincident with the implementation of new conservation policies by the Brazilian government, which suggests that these policies are not effectively reducing the number of small clearings in primary forest, whether these are caused by large landholders or smallholders, but have been more effective at reducing the frequency of larger clearings. Diferentes agentes de deforestación, como campesinos y negocios agrícolas, crean diferentes patrones espaciales de deforestación. Analizamos la proporción de deforestación asociada con claros de diferentes tamaños en la Amazonía brasileña entre 2002 y 2009. Utilizamos mapas de deforestación anual para determinar el área total deforestada y la distribución de tamaños de parches deforestados por año. La distribución de tamaños de áreas deforestadas cambió de manera consistente y direccional. Los claros extensos (> 1000 ha) progresivamente abarcaron cantidades menores de deforestación anual total. El número de claros pequeños (6.25—50.00ha) permanecieron sin cambios en el tiempo. Los claros pequeños correspondieron a 73% de toda la deforestación en 2009, un incremento de 20% desde 2002, mientras que la proporción de deforestación atribuible a claros extensos decreció de 13% a 3% entre 2002 y 2009. Los claros extensos se concentraron en Mato Grosso, pero también ocurrieron en el Pará oriental y en Rondônia. En 2002, los claros extensos correspondieron a 17%, 15% y 10% de toda la deforestación en Mato Grosso, Pará y Rondônia, respectivamente. Estos cambios en el tamaño de parches deforestados coinciden con la implementación de nuevas políticas de conservación del gobierno brasileño, lo que sugiere que estas políticas no están reduciendo el número de claros pequeños en el bosque primario, sean provocados por terratenientes o pequeños propietarios, pero han sido efectivas en la reducción de claros extensos.</description><identifier>ISSN: 0888-8892</identifier><identifier>EISSN: 1523-1739</identifier><identifier>DOI: 10.1111/j.1523-1739.2012.01901.x</identifier><identifier>PMID: 22827325</identifier><identifier>CODEN: CBIOEF</identifier><language>eng</language><publisher>Malden, USA: Blackwell Publishing Inc</publisher><subject>Agriculture - classification ; Animal, plant and microbial ecology ; Applied ecology ; Biological and medical sciences ; Brazil ; Cattle ranching ; Conservation biology ; conservation effectiveness ; Conservation of Natural Resources - methods ; Conservation, protection and management of environment and wildlife ; deforestación tropical ; Deforestation ; dinámica espacial ; dinámica temporal ; distribución de tamaños ; efectividad de la conservación ; Environment ; Environmental Policy ; Forest conservation ; Fundamental and applied biological sciences. Psychology ; General aspects ; Geographic Mapping ; Government Regulation ; Land management ; Land ownership ; Old growth forests ; Parks, reserves, wildlife conservation. 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D.</creatorcontrib><creatorcontrib>SOUZA, CARLOS</creatorcontrib><creatorcontrib>EWERS, ROBERT M.</creatorcontrib><title>Changes in Size of Deforested Patches in the Brazilian Amazon</title><title>Conservation biology</title><addtitle>Conserv Biol</addtitle><description>Different deforestation agents, such as small farmers and large agricultural businesses, create different spatial patterns of deforestation. We analyzed the proportion of deforestation associated with different-sized clearings in the Brazilian Amazon from 2002 through 2009. We used annual deforestation maps to determine total area deforested and the size distribution of deforested patches per year. The size distribution of deforested areas changed over time in a consistent, directional manner. Large clearings (> 1000 ha) comprised progressively smaller amounts of total annual deforestation. The number of smaller clearings (6.25—50.00 ha) remained unchanged over time. Small clearings accounted for 73% of all deforestation in 2009, up from 30% in 2002, whereas the proportion of deforestation attributable to large clearings decreased from 13% to 3% between 2002 and 2009. Large clearings were concentrated in Mato Grosso, but also occurred in eastern Pará and in Rondônia. In 2002 large clearings accounted for 17%, 15%, and 10% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. Even in these states, where there is a highly developed agricultural business dominated by soybean production and cattle ranching, the proportional contribution of large clearings to total deforestation declined. By 2009 large clearings accounted for 2.5%, 3.5%, and 1% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. These changes in deforestation patch size are coincident with the implementation of new conservation policies by the Brazilian government, which suggests that these policies are not effectively reducing the number of small clearings in primary forest, whether these are caused by large landholders or smallholders, but have been more effective at reducing the frequency of larger clearings. Diferentes agentes de deforestación, como campesinos y negocios agrícolas, crean diferentes patrones espaciales de deforestación. Analizamos la proporción de deforestación asociada con claros de diferentes tamaños en la Amazonía brasileña entre 2002 y 2009. Utilizamos mapas de deforestación anual para determinar el área total deforestada y la distribución de tamaños de parches deforestados por año. La distribución de tamaños de áreas deforestadas cambió de manera consistente y direccional. Los claros extensos (> 1000 ha) progresivamente abarcaron cantidades menores de deforestación anual total. El número de claros pequeños (6.25—50.00ha) permanecieron sin cambios en el tiempo. Los claros pequeños correspondieron a 73% de toda la deforestación en 2009, un incremento de 20% desde 2002, mientras que la proporción de deforestación atribuible a claros extensos decreció de 13% a 3% entre 2002 y 2009. Los claros extensos se concentraron en Mato Grosso, pero también ocurrieron en el Pará oriental y en Rondônia. En 2002, los claros extensos correspondieron a 17%, 15% y 10% de toda la deforestación en Mato Grosso, Pará y Rondônia, respectivamente. Estos cambios en el tamaño de parches deforestados coinciden con la implementación de nuevas políticas de conservación del gobierno brasileño, lo que sugiere que estas políticas no están reduciendo el número de claros pequeños en el bosque primario, sean provocados por terratenientes o pequeños propietarios, pero han sido efectivas en la reducción de claros extensos.</description><subject>Agriculture - classification</subject><subject>Animal, plant and microbial ecology</subject><subject>Applied ecology</subject><subject>Biological and medical sciences</subject><subject>Brazil</subject><subject>Cattle ranching</subject><subject>Conservation biology</subject><subject>conservation effectiveness</subject><subject>Conservation of Natural Resources - methods</subject><subject>Conservation, protection and management of environment and wildlife</subject><subject>deforestación tropical</subject><subject>Deforestation</subject><subject>dinámica espacial</subject><subject>dinámica temporal</subject><subject>distribución de tamaños</subject><subject>efectividad de la conservación</subject><subject>Environment</subject><subject>Environmental Policy</subject><subject>Forest conservation</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Geographic Mapping</subject><subject>Government Regulation</subject><subject>Land management</subject><subject>Land ownership</subject><subject>Old growth forests</subject><subject>Parks, reserves, wildlife conservation. Endangered species: population survey and restocking</subject><subject>Property rights</subject><subject>Research Note</subject><subject>Seasons</subject><subject>Size distribution</subject><subject>Spacecraft</subject><subject>spatial dynamics</subject><subject>temporal dynamics</subject><subject>tropical deforestation</subject><subject>Tropical rain forests</subject><issn>0888-8892</issn><issn>1523-1739</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><recordid>eNqNkV9P2zAUxS0Egg74CKC8IO0lmf_EjvOwSbQbXSVUQDDt0XKd69VdmjC71Uo__ZyllFf8Ykvnd--59xihhOCMxPNpkRFOWUoKVmYUE5phUmKSbQ7QYC8cogGWUqZSlvQEfQhhgTEuOcmP0QmlkhaM8gH6PJrr5heExDXJo9tC0trkK9jWQ1hBldzrlZn36moOydDrraudbpLrpd62zRk6sroOcL67T9GPm29Po-_p7d14Mrq-TU0uMEkLy6llTOiKiTzPmcScAXCwksLMzqhgVBJuQBqhSVUZkudSMmys5mVVCsNO0ce-77Nv_6zjaGrpgoG61g2066AIoUJgLgscUdmjxrcheLDq2bul9i-KYNWFpxaqy0h1GakuPPU_PLWJpZc7l_VsCdW-8DWtCFztAB2Mrq3XjXHhjROsxHHNyH3pub-uhpd3D6BGd8NJ94wNLvoGi7Bq_ZtBHIKzvDNIe93FX9rsde1_K1Gwgquf07EaPk0f2PThUd2wf0CQoUI</recordid><startdate>201210</startdate><enddate>201210</enddate><creator>ROSA, ISABEL M. D.</creator><creator>SOUZA, CARLOS</creator><creator>EWERS, ROBERT M.</creator><general>Blackwell Publishing Inc</general><general>Wiley-Blackwell</general><scope>BSCLL</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope></search><sort><creationdate>201210</creationdate><title>Changes in Size of Deforested Patches in the Brazilian Amazon</title><author>ROSA, ISABEL M. D. ; SOUZA, CARLOS ; EWERS, ROBERT M.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4601-7f52f336ad3644438053ee5ef82ebfb2632815ce8c6a1ddc1448830cfa59d96c3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>Agriculture - classification</topic><topic>Animal, plant and microbial ecology</topic><topic>Applied ecology</topic><topic>Biological and medical sciences</topic><topic>Brazil</topic><topic>Cattle ranching</topic><topic>Conservation biology</topic><topic>conservation effectiveness</topic><topic>Conservation of Natural Resources - methods</topic><topic>Conservation, protection and management of environment and wildlife</topic><topic>deforestación tropical</topic><topic>Deforestation</topic><topic>dinámica espacial</topic><topic>dinámica temporal</topic><topic>distribución de tamaños</topic><topic>efectividad de la conservación</topic><topic>Environment</topic><topic>Environmental Policy</topic><topic>Forest conservation</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Geographic Mapping</topic><topic>Government Regulation</topic><topic>Land management</topic><topic>Land ownership</topic><topic>Old growth forests</topic><topic>Parks, reserves, wildlife conservation. Endangered species: population survey and restocking</topic><topic>Property rights</topic><topic>Research Note</topic><topic>Seasons</topic><topic>Size distribution</topic><topic>Spacecraft</topic><topic>spatial dynamics</topic><topic>temporal dynamics</topic><topic>tropical deforestation</topic><topic>Tropical rain forests</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>ROSA, ISABEL M. D.</creatorcontrib><creatorcontrib>SOUZA, CARLOS</creatorcontrib><creatorcontrib>EWERS, ROBERT M.</creatorcontrib><collection>Istex</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Conservation biology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>ROSA, ISABEL M. D.</au><au>SOUZA, CARLOS</au><au>EWERS, ROBERT M.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Changes in Size of Deforested Patches in the Brazilian Amazon</atitle><jtitle>Conservation biology</jtitle><addtitle>Conserv Biol</addtitle><date>2012-10</date><risdate>2012</risdate><volume>26</volume><issue>5</issue><spage>932</spage><epage>937</epage><pages>932-937</pages><issn>0888-8892</issn><eissn>1523-1739</eissn><coden>CBIOEF</coden><abstract>Different deforestation agents, such as small farmers and large agricultural businesses, create different spatial patterns of deforestation. We analyzed the proportion of deforestation associated with different-sized clearings in the Brazilian Amazon from 2002 through 2009. We used annual deforestation maps to determine total area deforested and the size distribution of deforested patches per year. The size distribution of deforested areas changed over time in a consistent, directional manner. Large clearings (> 1000 ha) comprised progressively smaller amounts of total annual deforestation. The number of smaller clearings (6.25—50.00 ha) remained unchanged over time. Small clearings accounted for 73% of all deforestation in 2009, up from 30% in 2002, whereas the proportion of deforestation attributable to large clearings decreased from 13% to 3% between 2002 and 2009. Large clearings were concentrated in Mato Grosso, but also occurred in eastern Pará and in Rondônia. In 2002 large clearings accounted for 17%, 15%, and 10% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. Even in these states, where there is a highly developed agricultural business dominated by soybean production and cattle ranching, the proportional contribution of large clearings to total deforestation declined. By 2009 large clearings accounted for 2.5%, 3.5%, and 1% of all deforestation in Mato Grosso, Pará, and Rondônia, respectively. These changes in deforestation patch size are coincident with the implementation of new conservation policies by the Brazilian government, which suggests that these policies are not effectively reducing the number of small clearings in primary forest, whether these are caused by large landholders or smallholders, but have been more effective at reducing the frequency of larger clearings. Diferentes agentes de deforestación, como campesinos y negocios agrícolas, crean diferentes patrones espaciales de deforestación. Analizamos la proporción de deforestación asociada con claros de diferentes tamaños en la Amazonía brasileña entre 2002 y 2009. Utilizamos mapas de deforestación anual para determinar el área total deforestada y la distribución de tamaños de parches deforestados por año. La distribución de tamaños de áreas deforestadas cambió de manera consistente y direccional. Los claros extensos (> 1000 ha) progresivamente abarcaron cantidades menores de deforestación anual total. El número de claros pequeños (6.25—50.00ha) permanecieron sin cambios en el tiempo. Los claros pequeños correspondieron a 73% de toda la deforestación en 2009, un incremento de 20% desde 2002, mientras que la proporción de deforestación atribuible a claros extensos decreció de 13% a 3% entre 2002 y 2009. Los claros extensos se concentraron en Mato Grosso, pero también ocurrieron en el Pará oriental y en Rondônia. En 2002, los claros extensos correspondieron a 17%, 15% y 10% de toda la deforestación en Mato Grosso, Pará y Rondônia, respectivamente. Estos cambios en el tamaño de parches deforestados coinciden con la implementación de nuevas políticas de conservación del gobierno brasileño, lo que sugiere que estas políticas no están reduciendo el número de claros pequeños en el bosque primario, sean provocados por terratenientes o pequeños propietarios, pero han sido efectivas en la reducción de claros extensos.</abstract><cop>Malden, USA</cop><pub>Blackwell Publishing Inc</pub><pmid>22827325</pmid><doi>10.1111/j.1523-1739.2012.01901.x</doi><tpages>6</tpages></addata></record> |
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subjects | Agriculture - classification Animal, plant and microbial ecology Applied ecology Biological and medical sciences Brazil Cattle ranching Conservation biology conservation effectiveness Conservation of Natural Resources - methods Conservation, protection and management of environment and wildlife deforestación tropical Deforestation dinámica espacial dinámica temporal distribución de tamaños efectividad de la conservación Environment Environmental Policy Forest conservation Fundamental and applied biological sciences. Psychology General aspects Geographic Mapping Government Regulation Land management Land ownership Old growth forests Parks, reserves, wildlife conservation. Endangered species: population survey and restocking Property rights Research Note Seasons Size distribution Spacecraft spatial dynamics temporal dynamics tropical deforestation Tropical rain forests |
title | Changes in Size of Deforested Patches in the Brazilian Amazon |
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