Integrated Information System · BAPPEDA South Kalimantan 2025 · FOLU Carbon Inventory
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Statistics & Distribution — BAPPEDA 2025
Estimate offset potential & revenue — REDD+ · Restoration · Agroforestry
Protected area size
Tropical avg. 150–250 tC/ha
Without project intervention
After REDD+ implementation
VCS standard: 20–30 yrs
Voluntary market: $5–$50
Target area
Peat: 3–5, Forest: 6–12
Long-term restoration
Restoration premium
Agroforestry area
Typical: 200–600
Mature fruit: 30–80 kg C
Tree growth cycle
CO₂ Emission Methodology Analysis from Forest Loss
6.6 Mt (GFW) vs 143 Mt (MODIS) — due to definition & coverage differences:
| Aspect | GFW (6.6 Mt CO₂) | MODIS (143 Mt CO₂) |
|---|---|---|
| Definition | Permanent forest loss | All detected fire emissions |
| Coverage | Deforestation only | Peat, farmland, shrubland |
| Decomposition | Gradual (50% immediate) | Immediate at fire event |
| Peatland | ❌ Not included | ✅ Included (major contributor) |
GFW Calculation Formula
Peatland contributes 녲72% of total FOLU emissions in South Kalimantan. GFW excludes peat decomposition (not classified as forest loss). Drained peatland emission potential: 213.8 Mt C or Mt CO₂e.
GFW Hansen — South Kalimantan
Avg. South Kalimantan forest
Proportion burned vs cleared
Typical: 0.3–0.5
50% released year 1
| Method | Emissions | Coverage | Peatland | Best Use |
|---|---|---|---|---|
| GFW (Hansen) | 6.6 Mt CO₂/yr | Forest loss only | ❌ | REDD+ reporting |
| MODIS FIRMS | 143 Mt CO₂/yr | All fire emissions | ✅ | Fire monitoring |
| FOLU (IPCC) | Mt CO₂/yr | All land use change | ✅ | NDC reporting |
| This System | 618.4 Mt C stock | 5 regencies | ✅ | Stock management |
Use FOLU methodology (IPCC Tier 2) for comprehensive emission accounting including peatland. GFW suits deforestation monitoring; MODIS for fire detection. This carbon stock system is best used as a planning tool for conservation priority areas.