Native forest replacement by exotic plantations in southern Chile (1985–2011) and partial compensation by natural regeneration
Autores
Zamorano Elgueta, Carlos; Rey Benayas, José María; Cayuela Delgado, Luis; Hantson, Stijn; Armenteras, DolorsIdentificadores
Enlace permanente (URI): http://hdl.handle.net/10017/21353DOI: 10.1016/j.foreco.2015.02.025
ISSN: 0378-1127
Editor
Elsevier
Fecha de publicación
2015Patrocinadores
Comunidad de Madrid
Comisión Europea
Ministerio de Ciencia e Innovación
Cita bibliográfica
Forest Ecology & Management, 2015, n. 345, p. 10-20
Palabras clave
Deforestation
Fragmentation
Land cover change
Temperate forest
Spatial patterns
Proyectos
info:eu-repo/grantAgreement/MICINN//CGL2010-18312/ES/RESTAURACION DE LA BIODIVERSIDAD Y LOS SERVICIOS ECOSISTEMICOS EN SISTEMAS AGRARIOS. UN ENFOQUE MULTI-ESCALA/
info:eu-repo/grantAgreement/CAM//S2009%2FAMB-1783/ES/Restauración y conservación de los ecosistemas madrileños: respuesta frente al cambio global/
info:eu-repo/grantAgreement/EC/DCI-ENV%2F2010%2F222-412/ES//
Tipo de documento
info:eu-repo/semantics/article
Versión
info:eu-repo/semantics/acceptedVersion
Versión del editor
http://dx.doi.org/10.1016/j.foreco.2015.02.025Derechos
(c) Elsevier, 2015
Derechos de acceso
info:eu-repo/semantics/openAccess
Resumen
Although several studies have reported rates of deforestation and spatial patterns of native forest fragmentation, few have focused on the role of natural forest regeneration and exotic tree plantations on landscape dynamics. The objective of this study was to analyze the dynamics of land cover change in order to test the hypothesis that exotic tree plantations have caused a major transformation of temperate forest cover in southern Chile during the last three decades. We used three Landsat satellite images taken in 1985 (TM), 1999 (ETM+), and 2011 (TM) to quantify land cover change, together with a set of landscape indicators to describe the spatial configuration of land cover. Our results showed that the major changes were dynamic conversion among forest, exotic tree plantation and shrubland. During the study period,
the area covered by exotic tree plantations increased by 168% (20,896–56,010 ha), at an annual rate of
3.8%, mostly at the expense of native forest and shrubland. There was a total gross loss of native forest
of 30% (54,304 ha), but a net loss of initial cover of only 5.1% (9130 ha), at an annual net deforestation
rate of 0.2%. The difference between gross and net loss of native forest was mostly the result of conversion
of shrubland and agricultural and pasture land to secondary forest following natural regeneration. Over
the course of the study period, exotic tree plantations showed a constant increase in patch density, total
edge length, nearest-neighbor distance, and largest patch index; maximum mean patch size occurred in
the middle of the study period. Native forest exhibited an increase and then a decrease in patch density
and total edge length, whereas mean patch size and largest patch index were lowest in the middle of the
period. Overall, the observed trends indicate expansion of exotic tree plantations and increase in native
forest loss and fragmentation, particularly between 1985 and 1999. Forest loss included both old-growth
and secondary forests, while native forest established after secondary succession differed in diversity,
structure, and functionality from old-growth and old growth/secondary forests. Since different successional
stages influence the provision of ecosystem services, the changes observed in our study are likely
to have consequences for humans that extend beyond immediate changes in land use patterns.
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