Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar.

Research output: Chapter in Book/Report/Conference proceedingChapter

Standard Standard

Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. / Mieja , Razafindrakoto; Andriamananjara, Andry; Razafimbelo, Tantely et al.
Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. ed. / María Muñoz; Raúl Zornoza. Academic Press, Elsevier, 2018. p. 25-37.

Research output: Chapter in Book/Report/Conference proceedingChapter

HarvardHarvard

Mieja , R, Andriamananjara, A, Razafimbelo, T, Hewson, J, Andrisoa, R, Jones, JPG, van Meerveld, I, Cameron, A, Ranaivoson, N, Ramifehiarivo, N, Ramboatiana, N, Razafinarivo, R, Ramananantoandro, T, Rasolohery, A, Razafimanantsoa, M, Jourdan, C, Saint-André, L, Rajoelison, G & Razakamanarivo, H 2018, Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. in M Muñoz & R Zornoza (eds), Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. Academic Press, Elsevier, pp. 25-37. https://doi.org/10.1016/B978-0-12-812128-3.00003-3

APA

Mieja , R., Andriamananjara, A., Razafimbelo, T., Hewson, J., Andrisoa, R., Jones, J. P. G., van Meerveld, I., Cameron, A., Ranaivoson, N., Ramifehiarivo, N., Ramboatiana, N., Razafinarivo, R., Ramananantoandro, T., Rasolohery, A., Razafimanantsoa, M., Jourdan, C., Saint-André, L., Rajoelison, G., & Razakamanarivo, H. (2018). Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. In M. Muñoz, & R. Zornoza (Eds.), Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions (pp. 25-37). Academic Press, Elsevier. https://doi.org/10.1016/B978-0-12-812128-3.00003-3

CBE

Mieja R, Andriamananjara A, Razafimbelo T, Hewson J, Andrisoa R, Jones JPG, van Meerveld I, Cameron A, Ranaivoson N, Ramifehiarivo N, et al. 2018. Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. Muñoz M, Zornoza R, editors. In Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. Academic Press, Elsevier. pp. 25-37. https://doi.org/10.1016/B978-0-12-812128-3.00003-3

MLA

Mieja , Razafindrakoto et al. "Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar.". and Muñoz, María Zornoza, Raúl (editors). Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. Chapter 3, Academic Press, Elsevier. 2018, 25-37. https://doi.org/10.1016/B978-0-12-812128-3.00003-3

VancouverVancouver

Mieja R, Andriamananjara A, Razafimbelo T, Hewson J, Andrisoa R, Jones JPG et al. Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. In Muñoz M, Zornoza R, editors, Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. Academic Press, Elsevier. 2018. p. 25-37 doi: 10.1016/B978-0-12-812128-3.00003-3

Author

Mieja , Razafindrakoto ; Andriamananjara, Andry ; Razafimbelo, Tantely et al. / Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar. Soil Management and Climate Change: Effects on Organic Carbon, Nitrogen Dynamics, and Greenhouse Gas Emissions. editor / María Muñoz ; Raúl Zornoza. Academic Press, Elsevier, 2018. pp. 25-37

RIS

TY - CHAP

T1 - Organic carbon stocks in all pools following land cover change in the rainforest of Madagascar.

AU - Mieja , Razafindrakoto

AU - Andriamananjara, Andry

AU - Razafimbelo, Tantely

AU - Hewson, Jennifer

AU - Andrisoa, Riana

AU - Jones, J.P.G.

AU - van Meerveld, Ilja

AU - Cameron, Alison

AU - Ranaivoson, Ntsoa

AU - Ramifehiarivo, Nandrianina

AU - Ramboatiana, Nantenaina

AU - Razafinarivo, Ravo

AU - Ramananantoandro, Tahiana

AU - Rasolohery, Andriambolantsoa

AU - Razafimanantsoa, Marie

AU - Jourdan, Christophe

AU - Saint-André, Laurent

AU - Rajoelison, Gabrielle

AU - Razakamanarivo, Herintsitohaina

PY - 2018

Y1 - 2018

N2 - Terrestrial ecosystems represent the most important carbon (C) sink with their capacity to store almost three times that of the atmosphere (Trumper et al., 2009). Further, approximately 40% of terrestrial C is stored in tropical forests, sequestering large amounts of carbon dioxide from the atmosphere (Beer et al., 2010; Pan et al., 2011). However, these forests are threatened by high rates of conversion to other land uses, constituting a major source of greenhouse gas (GHG) emissions and contributing to climate change (Fearnside, 2000; Houghton, 2005). The UN initiative, Reducing Emissions from Deforestation and Forest Degradation (REDD+), represents one path aimed at mitigating the impacts of climate change by conserving tropical forests threatened by deforestation or degradation (Day et al., 2013). It aims to reduce carbon dioxide emissions from developing countries through the sustainable management of forests, while providing co-benefits of biodiversity conservation and livelihood support (Danielsen et al., 2011). Accurate carbon stock quantification represents one important step in ensuring the successful implementation of REDD+, as such information is needed for validation and verification of emissions reductions. (Gibbs et al., 2007; Saatchi et al., 2011).In eastern Madagascar, deforestation is mainly due to slash-and-burn agriculture (Styger et al., 2007), which results in a mosaic of land use types where fallows are prevalent (Nambena, 2003). To address deforestation in one area of this region, many activities have been implemented, including the development of a REDD+ project initiated by the Government of Madagascar in 2008 (Conservation International, 2013). REDD+ demands a precise estimation of the amount of C stored in forest and other land use types in order to accurately calculate, for example, the emissions avoided due to the presence of a REDD+ project (Andriamananjara et al., 2016). This is needed because the contribution of the C pools may vary across the landscape. The majorityof studies to date on C accounting in different forest ecosystems in Madagascar considered separately the C pools, while studies of the estimation of C stock that consider all five C pools are scarce (Andriamananjara et al., 2016; Grinand et al., 2017; Razakamanarivo et al., 2011, 2012). In this chapter, we firstly review a recent study that accounted C stocks in all five pools recognized by the IPCC (2003), including AGB, BGB, litter, deadwood (DW), and SOC. Afterwards, we identify their dynamics across land uses following deforestation.

AB - Terrestrial ecosystems represent the most important carbon (C) sink with their capacity to store almost three times that of the atmosphere (Trumper et al., 2009). Further, approximately 40% of terrestrial C is stored in tropical forests, sequestering large amounts of carbon dioxide from the atmosphere (Beer et al., 2010; Pan et al., 2011). However, these forests are threatened by high rates of conversion to other land uses, constituting a major source of greenhouse gas (GHG) emissions and contributing to climate change (Fearnside, 2000; Houghton, 2005). The UN initiative, Reducing Emissions from Deforestation and Forest Degradation (REDD+), represents one path aimed at mitigating the impacts of climate change by conserving tropical forests threatened by deforestation or degradation (Day et al., 2013). It aims to reduce carbon dioxide emissions from developing countries through the sustainable management of forests, while providing co-benefits of biodiversity conservation and livelihood support (Danielsen et al., 2011). Accurate carbon stock quantification represents one important step in ensuring the successful implementation of REDD+, as such information is needed for validation and verification of emissions reductions. (Gibbs et al., 2007; Saatchi et al., 2011).In eastern Madagascar, deforestation is mainly due to slash-and-burn agriculture (Styger et al., 2007), which results in a mosaic of land use types where fallows are prevalent (Nambena, 2003). To address deforestation in one area of this region, many activities have been implemented, including the development of a REDD+ project initiated by the Government of Madagascar in 2008 (Conservation International, 2013). REDD+ demands a precise estimation of the amount of C stored in forest and other land use types in order to accurately calculate, for example, the emissions avoided due to the presence of a REDD+ project (Andriamananjara et al., 2016). This is needed because the contribution of the C pools may vary across the landscape. The majorityof studies to date on C accounting in different forest ecosystems in Madagascar considered separately the C pools, while studies of the estimation of C stock that consider all five C pools are scarce (Andriamananjara et al., 2016; Grinand et al., 2017; Razakamanarivo et al., 2011, 2012). In this chapter, we firstly review a recent study that accounted C stocks in all five pools recognized by the IPCC (2003), including AGB, BGB, litter, deadwood (DW), and SOC. Afterwards, we identify their dynamics across land uses following deforestation.

KW - Soil

KW - carbon stocks

KW - Madagascar

KW - Rainforest

KW - land use change

U2 - 10.1016/B978-0-12-812128-3.00003-3

DO - 10.1016/B978-0-12-812128-3.00003-3

M3 - Chapter

SP - 25

EP - 37

BT - Soil Management and Climate Change

A2 - Muñoz, María

A2 - Zornoza, Raúl

PB - Academic Press, Elsevier

ER -