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EM-349: Ecosystem services reinforce Sumatran tiger conservation in land use plans
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EM-349 | |
Document Author
variable.detail.emDocumentAuthorHelp
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Bhagabati, N. K., Ricketts, T., Sulistyawan, T. B. S., Conte, M., Ennaanay, D., Hadian, O., McKenzie, E., Olwero, N., Rosenthal, A., Tallis, H., and Wolney, S. |
Document Year
variable.detail.emDocumentYearHelp
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2014 |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Variable ID
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6921 | 7039 | 6922 | 6923 | 6924 | 10847 | 7089 | 7052 | 6926 |
LULC | Not reported | Not reported | Not reported | Not reported | Not reported | Not reported | Not reported | Not reported | |
Qualitative-Quantitative
variable.detail.continuousCategoricalHelp
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Qualitative (Class, Rating or Ranking) | Qualitative (Class, Rating or Ranking) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) |
Cardinal-Ordinal
variable.detail.cardinalOrdinalHelp
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Non-Ordinal | Non-Ordinal | Cardinal | Cardinal | Cardinal | Cardinal | Cardinal | Cardinal | Cardinal |
Not applicable | Not applicable | tons ha^-1 | tons ha^-1 | tons ha^-1 | ton ha^-1 | % | % | Not reported |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Predictor-Intermediate-Response
variable.detail.displayVariableTypeHelp
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Predictor |
Predictor |
Predictor |
Predictor |
Predictor |
Predictor |
Response |
Response |
Response |
Predictor Variable Type
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Time- or Space-varying Variable |
Time- or Space-varying Variable |
Constant or Parameter | Constant or Parameter | Constant or Parameter | Constant or Parameter | Not applicable | Not applicable | Not applicable |
Response Variable Type
variable.detail.resClassHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Computed Variable |
Computed Variable |
Computed Variable |
Data Source/Type
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Map or database (e.g., wide coverage, wide availability, measured or modeled) | Derived as output of another model (and not found in a widely available database) | Transferred Values (e.g., from literature; transferred spatially, temporally or across scales) | Transferred Values (e.g., from literature; transferred spatially, temporally or across scales) | Transferred Values (e.g., from literature; transferred spatially, temporally or across scales) |
Transferred Values (e.g., from literature; transferred spatially, temporally or across scales) ?Comment:Peat values (Wahyunto et al., 2003, Uryu et al., 2008) |
Not applicable | Not applicable | Not applicable |
Variable Classification Hierarchy
variable.detail.vchLevel1Help
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2. Land Surface (or Water Body) Cover, Use, Substrate, or Metric |
2. Land Surface (or Water Body) Cover, Use, Substrate, or Metric |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
--Land use/land cover type or dominant habitat type |
--Demarcation of watershed, channel, floodplain, shore, coastline, flowline |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
--Chemical (C, N, P, sediment/particulate) characteristics of ecosystem components |
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----Other, multiple, unspecified or unclear |
----Watershed demarcation or dimension |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
----Carbon-related characteristics of ecosystem components |
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------Carbon presence (in terrestrial or aquatic ecosystem components) |
------Carbon presence (in terrestrial or aquatic ecosystem components) |
------Carbon presence (in terrestrial or aquatic ecosystem components) |
------Carbon presence (in terrestrial or aquatic ecosystem components) |
------Carbon accumulation by terrestrial or aquatic ecosystem components |
------Carbon accumulation by terrestrial or aquatic ecosystem components |
------Carbon presence (in terrestrial or aquatic ecosystem components) |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Spatial Extent Area
variable.detail.spExtentHelp
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100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | 100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 | 100,000-1,000,000 km^2 |
Spatially Distributed?
variable.detail.spDistributedHelp
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Yes | Yes | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | No | Yes | Yes |
Observations Spatially Patterned?
variable.detail.regularSpGrainHelp
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Yes | No | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | No | No |
Spatial Grain Type
variable.detail.spGrainTypeHelp
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area, for pixel or radial feature | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Spatial Grain Size
variable.detail.spGrainSizeHelp
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30 m x 30 m | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Spatial Density
variable.detail.spDensityHelp
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Not applicable | 6 watersheds divided into 68 sub-watersheds | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | aggregated to 68 sub-watersheds | aggregated to 68 sub-watersheds |
EnviroAtlas URL
variable.detail.enviroAtlasURLHelp
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The Watershed Boundary Dataset (WBD) |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Temporal Extent
variable.detail.tempExtentHelp
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2008-2020 | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | 2008-2020 | 2008-2020 | 2008-2020 |
Temporally Distributed?
variable.detail.tempDistributedHelp
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Regular Temporal Grain?
variable.detail.regularTempGrainHelp
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Temporal Grain Size Value
variable.detail.tempGrainSizeValHelp
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Temporal Grain Size Units
variable.detail.tempGrainSizeUnitHelp
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Temporal Density
variable.detail.tempDensityHelp
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Not applicable | Not applicable | tons ha^-1 | tons ha^-1 | tons ha^-1 | Not reported | Not reported |
% ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Not reported ?Comment:Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Min Value
variable.detail.minEstHelp
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Not applicable | Not applicable | 0 | 0 | 0 | Not reported | Not reported | >-20 | Not reported |
Max Value
variable.detail.estHelp
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Not applicable | Not applicable | 172.49 | 72.38 | 4.00 | Not reported | Not reported | >20 | Not reported |
Other Value Type
variable.detail.natureOtherEstHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | Parameter value | Not applicable | Not applicable |
Other Value
variable.detail.otherEstHelp
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Not applicable | Not applicable | Not reported | Not reported | Not reported | Not reported | Varies by Run; view Runs to see values | Not reported | Not reported |
Land use/land cover class ?Comment:A LULC map was obtained for the "baseline year of 2008 from WWF Indonesia, derived by manual classification of Landsat and IRS-P6 satellite imagery at 30 m resolution and validated through ground checks (Setiabudi and Budiman, 2008). The map contained 89 LULC classes (Appendix A)". "The Sumatra Ecosystem Vision scenario is based on the Sumatra 2020 Roadmap (Roosita et al., 2010), a vision for sustainable land use advanced by the Sumatra Spatial Planning Forum, a coalition of government officials, civil society representatives and academics. It delineates areas for conservation, restoration and development based on 9 spatial layers...The Government Spatial Plan scenario is based on zoning plans developed by the Indonesian Ministry of Public Works for the three provinces covering our study area (Riau, Jambi and West Sumatra) as mandated under Indonesia’s Spatial Planning law No. 26 / 2007 (Hudalah and Woltjer, 2007). These plans incorporate stakeholder input from the relevant provinces". Land use/land cover is a class driver variable that sets constant values for the variables; Above ground carbon pool per LULC, Below ground carbon pool per LULC, and Dead organic matter carbon pool per LULC, per land use/land cover type. |
Sub-watershed boundary |
Above ground carbon pool per LULC ?Comment:"For above-ground biomass (AGB), we used data provided in Uryu et al.’s (2008) assessment of CO2 emissions in Riau province, supplemented with estimates for Jambi province (SEAMEO-BIOTROP, 1999) where available for a given LULC type. Uryu et al. (2008) estimated biomass values (ton ha-1) as medians of published (when possible, region-specific) biomass values for different LULC classes extracted from a literature search. Most of the LULC classes in Uryu et al. (2008) are consistent with those in our scenario maps, and the values were directly transferred in those cases. When a LULC class in our map did not appear in Uryu et al. (2008), we took the median value of similar classes (e.g., generic “plantation” and “forest” classes in our scenario maps were assigned the median values of all plantations and mature forest classes, respectively). We multiplied AGB by a factor of 0.47 (Table 4.3 in IPCC, 2006, Vol. 4) to convert biomass to ton ha-1 of carbon." This variable has set constant values determined by class of Land use/land cover. |
Below ground carbon pool per LULC ?Comment:Below-ground biomass was calculated as a fraction of AGB, using root: shoot biomass ratios for tropical ecosystems provided in IPCC guidelines (Table 4.4. in IPCC, 2006, Vol. 4). This variable has set constant values determined by class of Land use/land cover. |
Dead organic matter carbon pool per LULC ?Comment:For carbon stored in dead organic matter, we used estimates of carbon in leaf litter provided in IPCC (2006) (Table 2.2 in Vol. 2) for tropical ecosystems, assigning zero or downscaled values for human-modified or bare land uses. This variable has set constant values determined by class of Land use/land cover. |
Soil carbon pool ?Comment:Soil carbon layer generated using the Harmonized World Soil Database (FAO/IIASA/ISRIC/ISSCAS/JRC, 2009). Where peat soils occur, the world soil layer was replaced with a peatland distribution layer from Wetlands International that includes spatially explicit estimates of peat carbon content (Wahyunto et al., 2003). |
Average percent change in total carbon ?Comment:Value is the average change from 2008 to 2020 for each scenario for the study area, across all sub-watersheds. |
Percent change in total carbon per sub-watershed ?Comment:Percent change was mapped by sub-watershed coded in increments of: >20%, 5-20%, +/-5%, (-)5-20%, >-20%. |
Total carbon per sub-watershed ?Comment:Sub-watersheds were the smallest spatial grain at which results were reported. Results were reported as relative spatial distribution across the landscape, and relative change to scenarios rather than precise quantification. Results were mapped at the sub-watershed level, with each sub-watershed assigned a shaded value based on quintile breaks. Specific modeled values were not reported. |
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Variability Expression Given?
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Not applicable | No | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | No | No | No |
Variability Metric
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None | None | None | None | None | None | None | None | None |
Variability Value
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None | None | None | None | None | None | None | None | None |
Variability Units
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None | None | None | None | None | None | None | None | None |
Resampling Used?
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Variability Expression Used in Modeling?
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Not applicable | Not applicable | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not recorded for Constant or Factor Variables | Not applicable | Not applicable | Not applicable |
Average percent change in total carbon | Percent change in total carbon per sub-watershed | Total carbon per sub-watershed | |
Variable ID
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7089 | 7052 | 6926 |
Validated?
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Not applicable | Not applicable | Not applicable |
Validation Approach (within, between, etc.)
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None | None | None |
Validation Quality (Qual/Quant)
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None | None | None |
Validation Method (Stat/Deviance)
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Validation Metric
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Validation Value
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Use of Measured Response Data
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None | None | None |