Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia

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Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia. / Murray, J.P.; Grenyer, R.; Wunder, S. et al.
In: Conservation Biology, Vol. 29, No. 5, 10.04.2015, p. 1434-1445.

Research output: Contribution to journalArticlepeer-review

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Murray, JP, Grenyer, R, Wunder, S, Raes, N & Jones, JPG 2015, 'Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia', Conservation Biology, vol. 29, no. 5, pp. 1434-1445. https://doi.org/10.1111/cobi.12500

APA

Murray, J. P., Grenyer, R., Wunder, S., Raes, N., & Jones, J. P. G. (2015). Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia. Conservation Biology, 29(5), 1434-1445. https://doi.org/10.1111/cobi.12500

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VancouverVancouver

Murray JP, Grenyer R, Wunder S, Raes N, Jones JPG. Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia. Conservation Biology. 2015 Apr 10;29(5):1434-1445. doi: 10.1111/cobi.12500

Author

Murray, J.P. ; Grenyer, R. ; Wunder, S. et al. / Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia. In: Conservation Biology. 2015 ; Vol. 29, No. 5. pp. 1434-1445.

RIS

TY - JOUR

T1 - Spatial patterns of carbon, biodiversity, deforestation threat, and REDD+ projects in Indonesia

AU - Murray, J.P.

AU - Grenyer, R.

AU - Wunder, S.

AU - Raes, N.

AU - Jones, J.P.G.

PY - 2015/4/10

Y1 - 2015/4/10

N2 - There are concerns that Reduced Emissions from Deforestation and forest Degradation (REDD+) may fail to deliver potential biodiversity cobenefits if it is focused on high carbon areas. We explored the spatial overlaps between carbon stocks, biodiversity, projected deforestation threats, and the location of REDD+ projects in Indonesia, a tropical country at the forefront of REDD+ development. For biodiversity, we assembled data on the distribution of terrestrial vertebrates (ranges of amphibians, mammals, birds, reptiles) and plants (species distribution models for 8 families). We then investigated congruence between different measures of biodiversity richness and carbon stocks at the national and subnational scales. Finally, we mapped active REDD+ projects and investigated the carbon density and potential biodiversity richness and modeled deforestation pressures within these forests relative to protected areas and unprotected forests. There was little internal overlap among the different hotspots (richest 10% of cells) of species richness. There was also no consistent spatial congruence between carbon stocks and the biodiversity measures: a weak negative correlation at the national scale masked highly variable and nonlinear relationships island by island. Current REDD+ projects were preferentially located in areas with higher total species richness and threatened species richness but lower carbon densities than protected areas and unprotected forests. Although a quarter of the total area of these REDD+ projects is under relatively high deforestation pressure, the majority of the REDD+ area is not. In Indonesia at least, first-generation REDD+ projects are located where they are likely to deliver biodiversity benefits. However, if REDD+ is to deliver additional gains for climate and biodiversity, projects will need to focus on forests with the highest threat to deforestation, which will have cost implications for future REDD+ implementation.

AB - There are concerns that Reduced Emissions from Deforestation and forest Degradation (REDD+) may fail to deliver potential biodiversity cobenefits if it is focused on high carbon areas. We explored the spatial overlaps between carbon stocks, biodiversity, projected deforestation threats, and the location of REDD+ projects in Indonesia, a tropical country at the forefront of REDD+ development. For biodiversity, we assembled data on the distribution of terrestrial vertebrates (ranges of amphibians, mammals, birds, reptiles) and plants (species distribution models for 8 families). We then investigated congruence between different measures of biodiversity richness and carbon stocks at the national and subnational scales. Finally, we mapped active REDD+ projects and investigated the carbon density and potential biodiversity richness and modeled deforestation pressures within these forests relative to protected areas and unprotected forests. There was little internal overlap among the different hotspots (richest 10% of cells) of species richness. There was also no consistent spatial congruence between carbon stocks and the biodiversity measures: a weak negative correlation at the national scale masked highly variable and nonlinear relationships island by island. Current REDD+ projects were preferentially located in areas with higher total species richness and threatened species richness but lower carbon densities than protected areas and unprotected forests. Although a quarter of the total area of these REDD+ projects is under relatively high deforestation pressure, the majority of the REDD+ area is not. In Indonesia at least, first-generation REDD+ projects are located where they are likely to deliver biodiversity benefits. However, if REDD+ is to deliver additional gains for climate and biodiversity, projects will need to focus on forests with the highest threat to deforestation, which will have cost implications for future REDD+ implementation.

U2 - 10.1111/cobi.12500

DO - 10.1111/cobi.12500

M3 - Article

VL - 29

SP - 1434

EP - 1445

JO - Conservation Biology

JF - Conservation Biology

SN - 0888-8892

IS - 5

ER -