2012
DOI: 10.1007/s11104-012-1478-y
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Land use effects on erosion and carbon storage of the Río Chimbo watershed, Ecuador

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Cited by 42 publications
(28 citation statements)
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“…The role of pine plantations in the land-use mosaic of the Chambo basin has been a dominating factor since the 1970s. The post-1960s land reforms and changes in economic policy [17,22,28,61,62] led to the establishment of tree plantations while simultaneously declaring native forests and other natural vegetation, such a páramo, vacant land [31]. Initially this led to significant land-use transitions from páramo and native forest to pine plantations and then, as economic and forestry policies evolved, led to plantations being converted to other uses.…”
Section: Post-1979 Drivers Of Land-use and Land-cover Change: Forestrmentioning
confidence: 99%
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“…The role of pine plantations in the land-use mosaic of the Chambo basin has been a dominating factor since the 1970s. The post-1960s land reforms and changes in economic policy [17,22,28,61,62] led to the establishment of tree plantations while simultaneously declaring native forests and other natural vegetation, such a páramo, vacant land [31]. Initially this led to significant land-use transitions from páramo and native forest to pine plantations and then, as economic and forestry policies evolved, led to plantations being converted to other uses.…”
Section: Post-1979 Drivers Of Land-use and Land-cover Change: Forestrmentioning
confidence: 99%
“…Between 1975 and 2001, the extent of pasture increased at the expense of páramo and there was considerable forest fragmentation in southern Ecuador [30]. These dramatic changes in native vegetation in the high Andes in the late 20th and early 21st Centuries have been attributed to changes in land-use practices after the 1954 land reform [31]. These changes have increased soil erosion rates and negatively impacted on the hydrological and carbon cycles [8,9,14,[31][32][33][34][35][36][37][38][39].…”
Section: Introductionmentioning
confidence: 99%
“…The phenotyping of RCS is not possible at the seedling stage, since it takes several weeks of plant growth for the phenotype and genetic differences to be visible. The identification of genetic markers controlling RCS would greatly facilitate their use in breeding programs (Lynch 2011;Henry et al 2012;York et al 2013). Advances in laser ablation tomography may enable the phenotyping of root anatomical traits on targeted root segments in a high-throughput manner (Chimungu et al 2014a;Saengwilai et al 2014;Chimungu et al 2014b).…”
Section: Research Prospectsmentioning
confidence: 99%
“…Soil erosion measurements based on fallout radionuclides for the Chimbo catchment (central Ecuadorian Andes) by Henry et al (2013) clearly illustrate that soil erosion rates highly depend on land cover and management: erosion rates in páramo grasslands are estimated at 9 t ha −1 yr −1 , and are significantly higher in forest plantations, pastures, and croplands with erosion rates of, respectively, 21, 24, and 150 t ha −1 yr −1 . The latter values are similar to soil erosion estimates for highly degraded Andean environments in southern Ecuador (Molina et al, 2008;Vanacker et al, 2014).…”
Section: Soil Hydrology Following Land Cover Conversionsmentioning
confidence: 99%