SelvaFlux
Spatial bankability · The tropics

Modeled Bankability of Tropical Reforestation and Forest Protection

We modeled a forest-carbon project for each eligible square-kilometre grid cell across the tropics. For each cell, we calculated the lowest carbon price that produces a 12% return. These prices form a supply curve for bankable land and carbon. We then added prospective revenue from bark methane uptake to each project cash flow. No registry credits bark methane yet. The full analysis is available to partners and investors under NDA.

Two credit types: reforestation & forest protection Cost basis: mapped net agricultural income Co-product: bark methane uptake
01

Modeled Effects on Reforestation Finance and Delivery

The spatial model estimates changes in bankable area and peak funding need. A separate completion scenario applies an assumed response to land that is already bankable. The response has not been fitted to observed project completion data. These results answer different questions and are reported separately.

+1.7 Mha
newly bankable at $50 · GWP100
Methane Revenue Lowers the Bankability Threshold
+6.5 Mha in the GWP* scenario
−1.3%
peak funding need · GWP100
The Spatial Cash-Flow Model Applies a One-Year Payment Lag
−4.5% in the GWP* scenario
+0.3 to 0.5 Mha
completion scenario · GWP100
The Scenario Applies an Assumed Completion Response
+1.2 to 1.9 Mha in the GWP* scenario
Advance Purchases Are Outside the Model
The model does not estimate it. An advance purchase can provide funding before planting and affect whether a project proceeds. The current cash-flow model begins methane-credit payments after a one-year lag. An additional restoration claim requires evidence that the purchase affected the project decision. The host project's baseline and additionality must also qualify, and the project must be eligible under the eventual methane methodology.
02

What the Supply Curve Shows

The supply curve reports the lowest carbon price at which a project in each eligible tropical grid cell would produce a 12% return.

Reforestation · how much, at what price

Most Modeled Reforestation Land Becomes Bankable Between $50 and $75

At low carbon prices, almost none of the eligible land is bankable. The bankable area rises steeply between about $50 and $75 per tonne of CO₂, then flattens, because by $75 most of the modeled plantable land is already bankable. Whether a given site is bankable depends mostly on tree growth and forgone farm income.

Bark methane · bankable area

At $50, Methane Revenue Makes More Reforestation Land Bankable

The carbon-only model estimates 32.0 Mha of bankable reforestation land at $50 per tonne. Prospective methane revenue increases that area by 1.7 Mha under GWP100 and 6.5 Mha in the GWP* scenario. These are changes in modeled bankability. They do not show how much land will be financed or planted.

Demand scenario · purchase-price assumptions

Demand Weighting Produces a Range of Bankable Area

We weighted the supply-curve results using assumed distributions of carbon purchase prices. Across those assumptions, prospective methane revenue adds 0.8 to 1.7 Mha under GWP100 and 3.1 to 6.3 Mha in the GWP* scenario. These results depend on the assumed price distributions. Observed purchase volumes were not used.

Cost basis · the cost of forgone farming

The Cost Uses Mapped Net Agricultural Income

A major cost of a reforestation project is the farm income the land would give up. We take that from a published map of net farm income across the tropics, and check it against two independent maps of farm value. The model also includes establishment, monitoring, verification, and project costs.

03

The Geographic Pattern

The same pricing method applies across the tropical study area, so the analysis shows where reforestation is more or less readily bankable. The public map uses three broad tiers and contains no site-level detail. The precise maps are part of the full analysis.

A coarse three-tier map of the tropics showing where reforestation clears a lower break-even carbon price. Central and South America, central Africa, and parts of South and Southeast Asia and the Pacific hold the most readily bankable land.
Where reforestation is more readily bankable. The darker regions clear a lower break-even carbon price, mostly where trees grow fast and the farm income given up is low. The public map uses a coarse three-tier resolution and shows no numbers. The detailed maps are shared under NDA.
04

What Each Result Measures

The model separates effects on the bankability threshold, peak funding need, and project completion. It also separates spatial model outputs from scenarios that have not been fitted to project data.

Spatial model

Methane Revenue Expands the Modeled Frontier

Fixed price

The Model Applies a $50 Carbon Price

The model compares carbon-only and methane-inclusive project cash flows for each tropical grid cell.

GWP100 adds 1.7 Mha; GWP* adds 6.5 Mha
Demand weighting

Price Assumptions Produce an Area Range

The model weights the supply-curve shift using assumed distributions of carbon purchase prices.

GWP100 adds 0.8 to 1.7 Mha; GWP* adds 3.1 to 6.3 Mha
Spatial cash flow

Methane Revenue Reduces Peak Funding Need

Issued-credit timing

The Model Uses a One-Year Payment Lag

The peak cumulative funding need is calculated across the same grid cells used for the bankability result.

GWP100 reduces it 1.3%; GWP* reduces it 4.5%
Before planting

Advance Purchases Require Project Evidence

An advance purchase can affect a project before its investment decision. A restoration claim requires evidence of that causal effect and eligibility under the host and methane methods.

The spatial model does not estimate this effect
Unfitted scenario

Added Revenue Could Improve Completion

Completion response

The Scenario Applies an Assumed Response

The response has not been fitted to observed project completions. It shows one possible effect of added revenue.

GWP100 adds 0.3 to 0.5 Mha; GWP* adds 1.2 to 1.9 Mha
Scope

The Scenario Uses Land That Is Already Bankable

The completion areas are conditional estimates. They do not represent newly bankable land and are not added to the frontier result.

No combined delivery result is reported

Early measurement may preserve records that an eventual methodology requires. The analysis does not assign a land-area result to early adoption or retrospective eligibility. Any value depends on the final methodology and on whether earlier measurements qualify.

05

How to Read a Supply Curve

Each eligible grid cell has a break-even price: the lowest carbon price at which its modeled project clears a 12% return. At a given carbon price, bankable land includes each grid cell with a break-even price at or below it. Adding methane revenue lowers each break-even price, so more land becomes bankable at the same carbon price.

The Shape of the Reforestation Supply Curve

The chart is illustrative, showing the shape only. As the carbon price rises, more land becomes worth replanting, and methane revenue shifts the curve.
$20 $50 $75 Carbon revenue With bark methane Carbon price → Land worth replanting →
This chart shows the shape of the supply curve. At a given carbon price, prospective methane revenue makes additional land bankable. The GWP* scenario produces a larger shift. Quantitative results are reported above and in the full analysis.
06

GWP* Is a New-Sink Scenario

No registry credits bark methane yet. The model applies GWP100, the metric registries currently use for methane, and a separate GWP* scenario. GWP* represents the warming-equivalent effect of a change in the methane removal rate. The model uses it to examine a newly established sink. It is not a current crediting basis.

Two panels show modeled annual methane value per hectare over 30 years. The reforestation GWP* line is a new-sink scenario that assumes full mature-forest uptake from the first modeled year. The protection line develops with modeled avoided deforestation.
The model values methane over a 30-year project. The reforestation GWP* line assumes that full mature-forest bark uptake begins in the first modeled year. Uptake development in restored forests has not been measured, so this timing is a scenario assumption. Under GWP*, the value of establishing the sink is high for about 20 years and then falls. Under this calculation, measurement that begins after sink formation does not create a new flux change at the measurement date. The protection line develops with the modeled avoided loss of forest. The panels use different vertical scales.
For partners and investors

The Full Analysis Is Available Under NDA

The full spatial bankability analysis includes the method, per-price results for both credit types, cost and bankability maps, sensitivity tests, and the decision record. We share it with partners and investors under a mutual NDA.

These modeled results depend on stated assumptions. They do not forecast SelvaFlux delivery. Bark-methane crediting is not yet approved, so the model prices it as a prospective credit.