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Improving the profits from 
peatland without exacerbating 
the environmental impacts 
Fahmuddin Agus, Neneng L. Nurida, Wahyunto, et al. 
Indonesian Agency for Agricultural Research and Development 
F_agus@litbang.pertanian.co.id 
Side Event IAARD-ICRAF COP 20 
Lima, Peru , 5 December 2014 
www.litbang.deptan.go.id
Multifunctional roles of peatland 
• Environmental services: 
-Water storage and regulator 
- Carbon storage 
- Niche of peatland-specific biodiversity 
• Agricultural production. Agricultural land is 
expanding rapidly on peatland, despite its sub-optimal 
inherent fertility 
Need to balance the two roles, although 
sometimes they are mutually exclusive
Distribution of Indonesian Peatland 
Island Area (ha) 
Sumatra 6.436.649 
Kalimantan 4.778.004 
Papua 3.690.921 
Total 14.905.594
Research objectives 
(ICCTF Phase II Program) 
• Analyze GHG emissions and sequestration as 
well as the costs and benefits under different 
LULUC 
• Policy recommendations for the sustainable 
peatland management 
• Capacity building 
• Strengthening networks for scientific 
exchange
Activities 
• Mapping and recommendations of the use and management of 
degraded peatland, 
• Evaluation of: 
- crop responses, 
- hydrology, 
- GHG Emissions, 
- carbon stock 
- Costs – benefits 
Terhubung ke komputer 
Atau data logger 
Terhubung ke baterei 
Outlet 
Inlet 
Infrared gas analyzer (IRGA) 
Gas chromatography
Research sites 
Riau 
W. Kalimantan 
Jambi C. Kalimantan 
Papua
Research Results
Districts with dominant peatland 
District 
Total area 
(million ha) 
Peatland area 
(million ha, %) 
Pelalawan/Riau 1.39 0.70 (50%) 
Muaro Jambi/Jambi 0.54 0.20 (37%) 
Kubu Raya/Kalbar 0.70 0.52 (76%) 
Pulang Pisau/Kalteng 0.98 0.62 (63%) 
Mimika/Papua 1.78 0.24 (13%) 
Little flexibility of there district to use mineral land
Land cover of peatland as of 2011 
(Mha, %) 
Peat Shrub: 
• Unproductive 
• Emission sources 
• Fire subscribers 
Data uncertainty: 
Other plantation 
& Multistrata ?
How good is Ag. productivity on 
peatland 
Treatments 
FFB, Jambi; 
6 yr old oil 
palm 
plantation 
(t/ha/yr) 
FFB, Riau; 6 yr 
old oil palm 
pantation) 
(t/ha/yr) 
Crumb rubber; 
Central 
Kalimantan, 5 
yr old rubber 
plantation 
(t/ha/5 months) 
Maize, West 
Kalimantan, 
(t/ha/season) 
Base fertilizer 11.4 a 18.5 a 1.6 a 2.7 a 
Peat fertilizer 17.4 ab 19.3 a 1.9 a 3.8 a 
Manure 18.8 b 19.6 a 1.8 a 3.0 a 
EFB/Mineral soil 17.7 ab1) 20.1 a1) 1.2 a2) 
Dolomite 3.5 a 
Dolomite 
+manure 
+Trichoderma 
3.4 a
Sawah pada lahan 
gambut di Kaltim 
Ex PLG Sejuta Ha 
(Rice Mega Project) 
Crop performance varies depending on the management level
Is peat farming profitable? 
Analysis using 10% df 
Land use Location NPV 
(USD/ha/yr) 
B/C 
Oil palm Jambi 896 1.09 
Oil palm Riau 2,421 1.21 
Rubber C. Kalimantan 4,421 1.60 
Maize-pineapple W. Kalimantan 315 1.44 
Sago palm Papua 478 1.40 
Oil palm is the main driver of LUC, 
despite the higher NPV for rubber: 
• Easy marketing 
• Low labor requirement compared to 
rubber
NPV (USD/ha/yr), Net emission, Emission 
redxn cost USD/t CO2, 10% df 
Land use 
Oil palm, 
Jambi 
Oil palm, 
Riau 
Rubber, C. 
Kalimantan 
Maize, W. 
Kalimantan Sago, Papua 
NPV (USD/ha/yr) 
Agriculture 1) 896 2,421 4,421 315 478 
Initial land uses 
Difference in net emissions from biomass carbon loss and 
gain and peat decomposition (t CO2/ha/tahun) 
Shrub 19.6 22.8 30.8 -3.3 -15.4 
Secondary peat forest 37.9 62.5 49.1 48.9 3.0 
Primary peat forest 63.3 87.9 74.5 74.3 28.4 
Emission reduction cost (USD/t CO2) 
Shrub 45.8 106.4 143.7 -104 -34 
Secondary peat forest 23.6 38.8 90.0 7 175 
Primary peat forest 14.1 27.5 59.3 5 18
Opportunity costs (USD/t CO2) at different 
discount factors and different LUCs 
Discount factor 
Oil palm, Jambi 
Oil Palm, 
Riau 
Rubber, C. 
Kalimantan 
Shrub - Agriculture 
10% 45.8 106.4 143.7 
12.50% 19.5 58.0 87.3 
15% 0.9 24.3 49.4 
Secondary peat forest to Agric. 
10% 23.6 38.8 90.0 
12.50% 10.1 21.1 54.7 
15% 0.4 8.9 30.9 
Primary peat forest to Agric. 
10% 14.1 27.5 59.3 
12.50% 6.0 15.0 36.0 
15% 0.3 6.3 20.4 
Low input, smallholder
Degraded peatland is a subscriber of 
peat fire 
60 cm deep burn scar from 6 days event in Oct 2014, 
emitting about 300 ton CO2-C ha-1 or 1101 CO2 ha-1 
Photo: Maswar, 8 Oct 2014 
60 cm layer burnt 
in 6 days 
Photo: Maswar, 8 Oct 2014
Farmers safeguarded their land 
from fire 
ICCTF site in Jabiren, Central Kalimantan, surrounded by peat forest fire. 8 Oct. 2014: 
Photo: Maswar
What kind of incentives required by 
smallholder for rehabilitating 
degraded peatland? 
• Secure and (semi) permanent land tenure 
• Subsidies for initial investment, especially for 
smallholder rubber plantation 
• Infrastructure, including drainage canals and 
water table control system 
• High quality planting materials and fertilizers 
• Technical guidance
Land swap 
Peat forest Degraded peatland 
Hutan lindung/protection forest jur. 
APL: production area jur. 
APL: production area jur. 
Protection forest jur.
Conclusions 
• Emission reduction from peatland is not a low hanging 
fruit. Combination of incentives, carbon market 
mechanism and regulatory measures are needed to 
reduce emissions from peatland. 
• Being an important source of emission from 
decomposition and fire, degraded peatland should be 
rehabilitated for (smallholder) livelihood and reduce 
peat fire risk. 
• A land swap mechanism to protect natural forest is 
plausible, although very challenging. It requires an 
agrarian reform.

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  • 1. Improving the profits from peatland without exacerbating the environmental impacts Fahmuddin Agus, Neneng L. Nurida, Wahyunto, et al. Indonesian Agency for Agricultural Research and Development F_agus@litbang.pertanian.co.id Side Event IAARD-ICRAF COP 20 Lima, Peru , 5 December 2014 www.litbang.deptan.go.id
  • 2. Multifunctional roles of peatland • Environmental services: -Water storage and regulator - Carbon storage - Niche of peatland-specific biodiversity • Agricultural production. Agricultural land is expanding rapidly on peatland, despite its sub-optimal inherent fertility Need to balance the two roles, although sometimes they are mutually exclusive
  • 3. Distribution of Indonesian Peatland Island Area (ha) Sumatra 6.436.649 Kalimantan 4.778.004 Papua 3.690.921 Total 14.905.594
  • 4. Research objectives (ICCTF Phase II Program) • Analyze GHG emissions and sequestration as well as the costs and benefits under different LULUC • Policy recommendations for the sustainable peatland management • Capacity building • Strengthening networks for scientific exchange
  • 5. Activities • Mapping and recommendations of the use and management of degraded peatland, • Evaluation of: - crop responses, - hydrology, - GHG Emissions, - carbon stock - Costs – benefits Terhubung ke komputer Atau data logger Terhubung ke baterei Outlet Inlet Infrared gas analyzer (IRGA) Gas chromatography
  • 6. Research sites Riau W. Kalimantan Jambi C. Kalimantan Papua
  • 8. Districts with dominant peatland District Total area (million ha) Peatland area (million ha, %) Pelalawan/Riau 1.39 0.70 (50%) Muaro Jambi/Jambi 0.54 0.20 (37%) Kubu Raya/Kalbar 0.70 0.52 (76%) Pulang Pisau/Kalteng 0.98 0.62 (63%) Mimika/Papua 1.78 0.24 (13%) Little flexibility of there district to use mineral land
  • 9. Land cover of peatland as of 2011 (Mha, %) Peat Shrub: • Unproductive • Emission sources • Fire subscribers Data uncertainty: Other plantation & Multistrata ?
  • 10. How good is Ag. productivity on peatland Treatments FFB, Jambi; 6 yr old oil palm plantation (t/ha/yr) FFB, Riau; 6 yr old oil palm pantation) (t/ha/yr) Crumb rubber; Central Kalimantan, 5 yr old rubber plantation (t/ha/5 months) Maize, West Kalimantan, (t/ha/season) Base fertilizer 11.4 a 18.5 a 1.6 a 2.7 a Peat fertilizer 17.4 ab 19.3 a 1.9 a 3.8 a Manure 18.8 b 19.6 a 1.8 a 3.0 a EFB/Mineral soil 17.7 ab1) 20.1 a1) 1.2 a2) Dolomite 3.5 a Dolomite +manure +Trichoderma 3.4 a
  • 11. Sawah pada lahan gambut di Kaltim Ex PLG Sejuta Ha (Rice Mega Project) Crop performance varies depending on the management level
  • 12. Is peat farming profitable? Analysis using 10% df Land use Location NPV (USD/ha/yr) B/C Oil palm Jambi 896 1.09 Oil palm Riau 2,421 1.21 Rubber C. Kalimantan 4,421 1.60 Maize-pineapple W. Kalimantan 315 1.44 Sago palm Papua 478 1.40 Oil palm is the main driver of LUC, despite the higher NPV for rubber: • Easy marketing • Low labor requirement compared to rubber
  • 13. NPV (USD/ha/yr), Net emission, Emission redxn cost USD/t CO2, 10% df Land use Oil palm, Jambi Oil palm, Riau Rubber, C. Kalimantan Maize, W. Kalimantan Sago, Papua NPV (USD/ha/yr) Agriculture 1) 896 2,421 4,421 315 478 Initial land uses Difference in net emissions from biomass carbon loss and gain and peat decomposition (t CO2/ha/tahun) Shrub 19.6 22.8 30.8 -3.3 -15.4 Secondary peat forest 37.9 62.5 49.1 48.9 3.0 Primary peat forest 63.3 87.9 74.5 74.3 28.4 Emission reduction cost (USD/t CO2) Shrub 45.8 106.4 143.7 -104 -34 Secondary peat forest 23.6 38.8 90.0 7 175 Primary peat forest 14.1 27.5 59.3 5 18
  • 14. Opportunity costs (USD/t CO2) at different discount factors and different LUCs Discount factor Oil palm, Jambi Oil Palm, Riau Rubber, C. Kalimantan Shrub - Agriculture 10% 45.8 106.4 143.7 12.50% 19.5 58.0 87.3 15% 0.9 24.3 49.4 Secondary peat forest to Agric. 10% 23.6 38.8 90.0 12.50% 10.1 21.1 54.7 15% 0.4 8.9 30.9 Primary peat forest to Agric. 10% 14.1 27.5 59.3 12.50% 6.0 15.0 36.0 15% 0.3 6.3 20.4 Low input, smallholder
  • 15. Degraded peatland is a subscriber of peat fire 60 cm deep burn scar from 6 days event in Oct 2014, emitting about 300 ton CO2-C ha-1 or 1101 CO2 ha-1 Photo: Maswar, 8 Oct 2014 60 cm layer burnt in 6 days Photo: Maswar, 8 Oct 2014
  • 16. Farmers safeguarded their land from fire ICCTF site in Jabiren, Central Kalimantan, surrounded by peat forest fire. 8 Oct. 2014: Photo: Maswar
  • 17. What kind of incentives required by smallholder for rehabilitating degraded peatland? • Secure and (semi) permanent land tenure • Subsidies for initial investment, especially for smallholder rubber plantation • Infrastructure, including drainage canals and water table control system • High quality planting materials and fertilizers • Technical guidance
  • 18. Land swap Peat forest Degraded peatland Hutan lindung/protection forest jur. APL: production area jur. APL: production area jur. Protection forest jur.
  • 19. Conclusions • Emission reduction from peatland is not a low hanging fruit. Combination of incentives, carbon market mechanism and regulatory measures are needed to reduce emissions from peatland. • Being an important source of emission from decomposition and fire, degraded peatland should be rehabilitated for (smallholder) livelihood and reduce peat fire risk. • A land swap mechanism to protect natural forest is plausible, although very challenging. It requires an agrarian reform.

Editor's Notes

  1. Peatlands have very important environment functions, among others as water storage, carbon storage and conservation of peatland-specific fauna and flora, above and below ground. Although these lands are considered as sub-optimal agronomically, but its role as agricultural land is increasingly important because of the limitations of optimal land for agricultural expansion. It’s our responsibility to keep the balance between environmental and economic roles. Winning one role and sacrificing the other is not the way to go.
  2. Recent study which are supported by field surveys indicated that the best estimate of Indonesian peat land area is about 14.9 million ha. These lands are distributed primarily on the East coast of Sumatra, especially in Riau, Jambi and South Sumatra provinces; Kalimantan, especially Central and West Kalimantan and the southern coast of Papua and West Papua.
  3. Recent study which are supported by field surveys indicated that the best estimate of Indonesian peat land area is about 14.9 million ha. These lands are distributed primarily on the East coast of Sumatra, especially in Riau, Jambi and South Sumatra provinces; Kalimantan, especially Central and West Kalimantan and the southern coast of Papua and West Papua.
  4. In some districts, the peatland area exceeds 50% of the total land area. As a result, landholders and local governments have no choice but to utilize the peatland, although the land is considered sub-optimal for economic purposes.
  5. Our study has demonstrated that, when properly managed, crop production on peatland is comparable to that of mineral land, but the initial investment to build the drainage network and increase soil fertility could be impeding for smallholders.
  6. Various economic indicators such as net present value (NPV) and benefit cost ratio (B/C ratio) showed satisfactory profitability of agriculture on peatlands. NPV from peatland are relatively high, ranging from USD 315 to 4421 per hectare per year.
  7. The opportunity costs or emission reduction costs is very high in general that may hardly be attainable by the carbon market. Therefore, using peat shrub is an outlet to high land pressure.
  8. Degraded peatland is a subscriber of peat fire as shown by this short-duration video, taken by one of our researcher on 8 October 2014 in Jebiren, Central Kalimantan. Fires or arson causes high amount of CO2 emissions in addition to pollution caused by smog and carbon monoxide. These causes various respiratory and lung problems, especially the upper respiratory infection syndrome or better known as ISPA in Indonesia.
  9. At the study site of ICCTF, where the land is covered by rubber and pineapple, farmers safeguarded their land so that it was safer from fire. Maintenance of shallow water table, for instance by using flap gate system, reduces fire risks even better.
  10. Most farmers can not afford to rehabilitate the degraded peatland by themselves. They need incentives for doing so. The main forms of incentives required include: Secure and preferably semi permanent tenure Subsidies for initial investment Development of infrastructure, including drainage canals and water table control system High quality planting materials and fertilizers Technical guidance from extension agents The investments needed for such incentives is much cheaper compared to emissions reduction schemes through carbon trading.
  11. “Land swap” is a mechanism in which forest land on production area (APL) is conserved and allocated as protection forest, while peat shrubs, regardless of their status (APL or forest areas) is allocated for APL. This mechanism requires coordination among ministries. The challenge is whether we are ready to reform the legal systems related to land allocations.