The voluntary carbon market is changing. Buyers are no longer focused only on large volumes of cheap credits. Instead, they want projects with strong science, long-term monitoring, and clear proof that carbon has truly been removed from the atmosphere. That shift is drawing more attention to high-integrity, nature-based projects.
One project now gaining that spotlight is the Sabah INFAPRO rainforest rehabilitation project in Malaysia. Climate Impact Partners announced that the project is now issuing verified carbon removal credits, opening access to one of the highest-quality nature-based removals currently available in the global market.
Restoring One of the World’s Richest Rainforest Ecosystems
The project is located in Sabah, Malaysia, on the island of Borneo. This region is home to tropical dipterocarp rainforest, one of the richest forest ecosystems on Earth. These forests store huge amounts of carbon and support extraordinary biodiversity. Some dipterocarp trees can grow up to 70 meters tall, creating habitat for orangutans, pygmy elephants, gibbons, sun bears, and the critically endangered Sumatran rhino.
However, the forest within the INFAPRO project area was not intact. In the 1980s, selective logging removed many of the most valuable tree species, especially large dipterocarps. That caused serious ecological damage. Once the key mother trees were gone, natural regeneration became much harder. Young seedlings also had to compete with dense vines and shrubs, which slowed the forest’s recovery.
To repair that damage, the INFAPRO project was launched in the Ulu-Segama forestry management unit in eastern Sabah.
- The project has restored more than 25,000 hectares of logged-over rainforest.
- It was developed by Face the Future in cooperation with Yayasan Sabah, while Climate Impact Partners has supported the project and helped bring its credits to market.
Why Sabah’s Carbon Removals are Attracting Attention
What makes Sabah INFAPRO different is not only the size of the restoration effort. It is also the way the project measured carbon gains.
Many forest carbon projects issue credits in annual vintages based on year-by-year growth estimates. Sabah INFAPRO followed a different path. It used a landscape-scale monitoring system and waited until the forest moved through its strongest natural growth period before issuing removal credits.
- This approach gives the credits more weight. Rather than relying mainly on short-term annual estimates, the project measured carbon sequestration over a longer period. That helps show that the forest delivered real, sustained, and measurable carbon removal.
The scientific backing is also unusually strong. Since 2007, the project has maintained nearly 400 permanent monitoring plots. These plots have allowed researchers, independent auditors, and technical specialists to observe the full growth cycle of dipterocarp forest recovery. The result is a large body of field data that supports carbon calculations and strengthens confidence in the credits.
In simple terms, buyers are not just being asked to trust a model. They are being shown years of direct forest monitoring across the project landscape.
Strong Ratings Support Market Confidence
Independent assessment has also lifted the project’s profile. BeZero awarded Sabah INFAPRO an A.pre overall rating and an AA score for permanence. That places the project among the highest-rated Improved Forest Management, or IFM, projects in the world.
The rating reflects several important strengths. First, the project has very low exposure to reversal risk. Second, it has a long and stable operating history. Third, its measured carbon gains align well with peer-reviewed ecological research and independent analysis.
These points matter in today’s market. Buyers have become more cautious after years of debate over the quality of some forest carbon credits. As a result, they now look more closely at durability, transparency, and third-party validation. Sabah INFAPRO’s rating helps answer those concerns and makes the project more attractive to companies looking for credible carbon removal.
The project is also registered with Verra’s Verified Carbon Standard under the name INFAPRO Rehabilitation of Logged-over Dipterocarp Forest in Sabah, Malaysia. That adds another level of market recognition and verification.
A Wider Model for Rainforest Recovery
Sabah INFAPRO also shows why high-quality nature-based projects are about more than carbon alone. The restoration effort supports broader ecological recovery in one of the world’s most important rainforest regions.
Climate Impact Partners said it has worked with project partners to restore degraded areas, run local training programs, carry out monthly forest patrols, and distribute seedlings to support rainforest recovery beyond the project boundary. These efforts help strengthen the wider landscape and expand the project’s environmental impact.
That broader value is becoming more important for buyers. Companies increasingly want projects that support biodiversity, ecosystem health, and local engagement, along with carbon removal. Sabah INFAPRO offers that mix, making it a stronger fit for the market’s shift toward higher-integrity credits.
Why IFM is Getting More Attention in the Carbon Market
The project’s launch also fits a wider shift in the voluntary carbon market. Improved Forest Management refers to practices that help existing forests store more carbon or avoid emissions through better stewardship. Unlike afforestation or reforestation, which involve creating or replanting forests, IFM focuses on improving the way current forests are managed.
These practices can help forests grow older, become more diverse, and stay healthier under climate stress. They can also support timber production in some cases by improving harvest cycles rather than stopping forest use altogether.
Because IFM projects often operate over very long periods, sometimes 100 years or more, they can generate lasting climate benefits. Still, buyers must be careful. Quality varies widely across projects, and strong due diligence remains essential.
That is why Sabah INFAPRO is drawing attention. Although IFM supply has grown in recent years, truly high-quality carbon removal credits within the category remain limited.
Nature-Based Carbon Removal Still Leads the Market
Nature-based carbon removal continues to dominate the spot market, as reported by Carbon Direct. In 2025, about 95% of all carbon dioxide removal credits issued in the voluntary carbon market came from nature-based pathways. Only 5% came from higher-durability pathways such as biochar or BECCS.
This shows two things at once. First, nature-based carbon removal still plays the leading role in today’s market. Second, high-durability removal technologies are still at an early stage of deployment.
Demand Side:
Within nature-based credits, supply conditions differ sharply by project type.
- Afforestation, reforestation, and revegetation, known as ARR, have remained tight. Over the past four years, ARR issuances and retirements have stayed close to a 1:1 ratio, while annual issuance has held nearly flat at around 7 million to 8 million metric tons. That has left limited ARR inventory available for spot buyers.
- IFM has followed a different path. Issuances have grown about 2.5 times since 2023, making it one of the biggest growth areas in nature-based carbon credits. Even so, the supply of top-tier IFM carbon removal credits remains much smaller than headline volumes suggest.
Supply Side:
At the same time, buyer behavior is shifting. Demand has moved away from many older REDD+ projects and toward IFM, ARR, agriculture-based projects, and other credit types viewed as more credible or better aligned with corporate climate goals.
Retirements have dipped slightly, but that does not necessarily mean interest is fading. Buyer participation has remained steady. What changed is the purchasing strategy. Companies are becoming more selective about what they buy, when they buy, and how much they are willing to pay for quality.
Meanwhile, long-term nature-based offtakes and purchase commitments have risen above 90 million tons of future delivery. Most of those commitments are concentrated in ARR projects. That trend shows both how tight ARR supply is today and how seriously buyers are trying to secure future volume.
Against that backdrop, Sabah INFAPRO enters the market at the right time. It offers a rare mix of long-term monitoring, strong scientific backing, high biodiversity value, and verified removals. For buyers looking for high-quality nature-based carbon removal, this Malaysian rainforest project may become an important benchmark.
The post Climate Impact Partners Unveils High-Quality Carbon Credits from Sabah Rainforest in Malaysia appeared first on Carbon Credits.
Insetting program design starts with your supplier map. The carbon claim comes much later.
Consider a coffee procurement team that funds a farm intervention before checking its sourcing data. The supplier aggregates coffee lots from several regions. The buyer lacks farm-level traceability. Another purchaser expects to report the same outcome. A more attractive project brochure solves none of these problems.
If the distinction between a value-chain intervention and a purchased credit is still open, read CCC’s Insetting vs Offsetting guide before you set the brief.
Insetting program design begins with the purchasing relationship and works outward. You need to decide 1) where an intervention belongs, 2) what business problem it addresses, 3) who pays for it, 4) how results will be measured, and 5) what the evidence will let you say about them. This five-step playbook turns that sequence into a procurement plan.
Step 1: Insetting program design starts with supplier mapping
Start with the commodities that matter most to your Scope 3 inventory and sourcing continuity. Ask finance for spend by supplier, sustainability for the emissions baseline, and category managers for origin and volume records. Then identify which suppliers can trace material to a jurisdiction, sourcing region, producer group, or individual land-management unit.
The level of traceability affects what you can account for. Under the GHG Protocol Land Sector and Removals Standard, the spatial boundary for purchased land-based products depends on the traceability associated with each volume. Farm-specific factors or removals require physical traceability through an acceptable chain-of-custody model. A contract with a tier-one trader, by itself, does not establish a link to the farms behind its deliveries.[1]
Build a first-pass table with five columns: commodity and annual volume; supplier and origin; current traceability level; land-use and production risks; and the business owner who can change the purchasing terms. Mark missing data plainly. A blank cell is cheaper to fix before a program starts than after a claim is drafted.
If your company sets an SBTi Forest, Land and Agriculture target (FLAG), keep its land-related target boundary separate from energy and industry emissions. The current FLAG guidance also requires relevant companies to assess primary deforestation-linked commodities in their value chains.[2]
Step 2: Choose a commodity and jurisdiction for a pilot
Select one supply corridor where the sourcing connection can be established and procurement has a reason to stay. A useful pilot has repeat purchases, suppliers willing to share records, an intervention matched to a diagnosed problem, and a defined plan to measure the result. Carbon potential alone is a poor selection rule if the supplier cannot deliver the crop your business needs.
Compare candidate regions on land-use risk, supplier concentration, local rights and tenure, the availability of baseline data, and exposure to drought, erosion, or forest conversion. Check the relevant legal requirements separately. A nature project does not satisfy a due-diligence obligation merely because it has a carbon method attached.
Consider a coffee buyer sourcing from two districts. In the first, producer-group records identify the farms, while recent dry seasons have increased rejected green coffee lots. In the second, deliveries pass through several intermediaries and farm origins are unknown. Pilot shade management in the first district, with local agronomic advice and quality checks built into the plan. The buyer can trace purchases there and test the intervention against a defined sourcing problem.
Use a short decision memo to record why the selected corridor beats the alternatives, what remains uncertain, and what would stop the pilot. That memo is the first control against a project drifting toward whatever happens to photograph well.
Step 3: Design the supplier engagement and commercial model
The intervention needs an owner on each side of the contract. Decide who supplies planting material or training, who maintains the practice, who bears the cost if a harvest disappoints, and how long the buyer expects to purchase from participating suppliers. Where smallholders participate, budget cash flow and technical support for practices that offer a later return.
Put these terms in a supplier agreement or pilot addendum. It should cover eligible farms and volumes, consent to data collection, access for monitoring, any land or carbon rights that matter, benefit sharing, and what happens if the purchasing relationship ends. Ask local counsel and producer representatives to review the arrangement. The Accountability Framework is a useful reference for supply-chain work involving forests, ecosystems, and human rights.[3]
Avoid assigning an automatic carbon benefit to the buyer. The contract should say which party has the right to report each outcome, how overlapping claims will be checked, and how any issued credits will be handled. A reduction reported in a buyer’s inventory cannot simply be sold for someone else’s offset claim without an accounting review. SBTi FLAG guidance excludes purchased credits used as offsets from near-term FLAG target achievement.[2]
Set commercial measures beside environmental ones: delivered volume, rejection rate, supplier retention, and procurement cost. They tell you whether the program works as a supply-chain investment, even if carbon accounting takes longer to resolve.
Step 4: Build monitoring, reporting, and verification before rollout
Agree on the baseline and data flow before paying for a full rollout. Identify the land units or sourcing regions in scope, the practices that change, the records suppliers already keep, and the additional measurements the program requires. Decide which data can come from field visits, transaction records, or remote sensing, and who checks each source.
For carbon, separate three questions. Did the practice happen? Did emissions or removals change under an applicable method? Can the buyer attribute a defensible share to its purchased goods without double counting? The GHG Protocol’s 2026 guidance includes dedicated chapters on spatial boundaries, data and methods, evaluating actions, credited outcomes, and assurance.[1] These are distinct jobs. A photograph of a planted tree answers only part of the first.
CCC’s MRV and Additionality article explains the separate evidence questions a project reviewer will ask.
Create an evidence file for every reporting period: dated supplier and farm records, purchase volumes, methods and emission factors, uncertainty, quality checks, and changes from the baseline. Specify who can challenge the data and how corrections are recorded. If a project also seeks credit certification, keep project accounting and corporate inventory accounting separate. The GHG Protocol says its land standard focuses on entity-level inventories and does not set the rules for credit certification.[4]
Start with the minimum viable measurement design that can survive review. Add complexity when the pilot tells you which data actually changes a decision.
Step 5: Decide what can be reported and claimed
Insetting program design needs reporting rules before the marketing copy. Procurement, sustainability, finance, and legal should agree on four distinct outputs: operational performance; observed land or nature outcomes; inventory effects, if the accounting criteria are met; and any separately issued credits. One dashboard can display them, but they should not share a single unqualified headline.
SBTi FLAG guidance allows certain land-based removals within a company’s operations or supply chain to contribute to FLAG pathways, subject to criteria including permanence, traceability, data quality, and allocation. It does not allow purchased offsets to meet near-term FLAG targets.[2] Eligibility therefore depends on evidence and the applicable target rules, not on calling an activity “insetting.”
Draft a claims register. For each proposed sentence, record the period, boundary, data owner, calculation method, reviewer, and whether the result is measured, estimated, or still a goal. If the evidence supports only “we funded a pilot with 200 farms,” say that. Do not turn a funding fact into a verified emissions reduction.
What good looks like by year three
Treat year three as a review point, not a promised payback date. A mature pilot should have mapped participating supply volumes, a stable supplier agreement, a repeatable data collection process, and a comparison of commercial and environmental results against the baseline. It should also have a documented answer for outcomes that cannot be included in the buyer’s inventory.
Scale only where the pilot improves a sourcing decision and the evidence can follow the product. If neither condition holds, redesign the intervention or change the corridor. A disciplined program can conclude that a site is unsuitable. That is useful procurement intelligence.
Discuss your insetting program with CCC
Carbon Credit Capital designs nature-based supply chain investments around sourcing needs and measurable sustainability outcomes. Schedule a consultation with our carbon and sustainability experts to map your tier-one supplier network, FLAG exposure, and first pilot decision.
Sources
[1] GHG Protocol, Land Sector and Removals Standard, version 1.1, and companion Guidance, June 2026: https://ghgprotocol.org/land-sector-and-removals-standard ; https://ghgprotocol.org/land-sector-and-removals-guidance
[2] Science Based Targets initiative, Forest, Land and Agriculture Science-Based Target-Setting Guidance, version 1.2, March 2026, especially pp. 16–17, 37, and 41: https://sciencebasedtargets.org/resources/files/SBTiFLAGGuidance.pdf
[3] Accountability Framework initiative, Accountability Framework and guidance for companies: https://accountability-framework.org/
[4] GHG Protocol, Frequently Asked Questions: Land Sector and Removals Standard, questions 10 and 18: https://ghgprotocol.org/blog/frequently-asked-questions-land-sector-and-removals-lsr-standard
Nature-based carbon investments deserve consideration when they address a specific business dependency and produce outcomes you can measure. Imagine Moonbucks, a global coffee roaster planning next season’s espresso blend. It is considering natural Grade 4 coffee from Jimma, in southwestern Oromia, Ethiopia. Its sourcing decisions affect the roasting schedule and the cash tied up in coffee purchases. Moonbucks needs to understand which measures could protect that supply, what they would cost and how it would judge the results.
1. Define the sourcing problem before choosing a project
Moonbucks needs a dependable component for its espresso blend. Its procurement team wants continuity of volume and an agreed cup profile. Replacing a shipment at short notice could require new sample approval and changes to the blend, and given the schedules for cultivation, processing, and freight delivery, is practically impossible. Moonbucks needs to get this right, and its initial concern is inconsistent deliveries. It commissions an assessment of the supplying farms and post-harvest chain. The questions cover land condition, harvest availability and whether drying or storage problems are affecting saleable lots.
This distinction changes the investment brief. A tree-planting proposal cannot be assumed to fix drying problems. Better storage cannot restore eroded land. The team must establish which problem exists before selecting the response.
CCC’s guide to finding nature-based solutions in your supply chain explains where to look. Here, the next task is to turn a broad concern into a testable proposal.
2. Develop nature-based carbon investments around the actual supply chain
The assessment would trace Moonbucks’ purchases back through the exporter and supplying producer groups. Which farms supply the contracted lots? Who controls land-management decisions? How long does the buyer expect to maintain the purchasing relationship?
Furthermore, Jimma natural Grade 4 cannot be treated as interchangeable with every Ethiopian coffee. Moonbucks would need to test any substitute against its own blend and quality requirements.
Suppose Moonbucks’ assessment identifies an opportunity to maintain shade trees and restore vegetation along exposed streambanks. The IPCC describes agroforestry as a way to store carbon in vegetation and soil, with potential benefits for erosion control and water quality.1 Moonbucks would need local advice on species, growing conditions and maintenance before deciding how these measures fit its sourcing plan.
The proposal now has a defined sourcing connection and a candidate intervention. The next steps are to test its effect on production, assess carbon eligibility and build the financial case.
3. Compare the proposal with other ways to protect supply
WBCSD’s Nature-based Solutions Blueprint recommends comparing nature-based options with other responses across their benefits and costs.2 For Moonbucks, that means evaluating the landscape proposal alongside drying improvements, storage controls and alternative sourcing arrangements.
The product’s natural-process designation matters. Moonbucks should examine the drying and dry-milling chain alongside land conditions. Its team would check storage practices, contamination risks and incoming-lot quality to see whether problems arise before or after the coffee leaves the farms.
The revised proposal might combine land stewardship with separate post-harvest controls. Each component needs its own purpose and budget. A sustainability label should not obscure which activity is expected to solve which problem.
The project develops as the evidence improves. Its scope should follow the diagnosis rather than preserve the first idea unchanged.
4. Establish what the carbon outcome could count toward
Moonbucks’ sustainability team now tests the proposed carbon case separately from the sourcing case. Is the objective a measurable change in Moonbucks’ value-chain emissions, verified credits for separate voluntary use, or distinct outcomes under carefully defined arrangements?
Scope 3 covers value-chain emissions. A purchasing relationship alone does not prove that a farm intervention can be included in Moonbucks’ inventory. The team needs an applicable accounting method, defensible boundaries and evidence supporting attribution.
SBTi’s FLAG Guidance (forest, land and agriculture), version 1.2, says purchased credits used as offsets cannot meet near-term FLAG or energy and industry targets. Eligible land-based removals are subject to accounting requirements.3 Moonbucks needs to test its proposal against those rules before including an outcome in its targets.
For Moonbucks’ Jimma proposal, maintaining existing trees and establishing new vegetation could involve different carbon questions. Specialists must examine the baseline and additionality, meaning what changes because the project proceeds. They must also assess measurement and the risk that stored carbon is lost. CCC’s MRV and additionality article introduces those tests.
Until that work is complete, Moonbucks should not budget an assumed Scope 3 reduction or credit-sale receipt. Direct emissions reductions remain the priority.
5. Build a financial case that survives weaker assumptions
Moonbucks’ finance team would now build a multi-year budget. UNEP’s State of Finance for Nature 2023 compares current finance with the investment needed to meet climate, biodiversity and land-restoration goals.4 The company would cost its proposed activities, farmer participation and ongoing monitoring. Verification, where required, is a separate expense. Maintenance and responsibility for replacing failed plantings must remain visible after the initial establishment budget ends.
Operational benefits need equally careful treatment. If fewer rejected lots reduce emergency purchasing, count that saving once. Do not add “supply resilience” as another financial benefit when it represents the same avoided cost.
Moonbucks should compare a base case with slower benefits, higher implementation costs and no carbon revenue. It should also distinguish production outcomes from quality and shipment outcomes. A single good harvest would not prove that the landscape intervention caused better delivery performance.
A project can remain worth funding even when its carbon case needs more work. That decision must rest on the operational evidence and the company’s objectives, without unsupported environmental claims.
6. Fund a pilot with a clear expansion decision
Moonbucks’ first approval would fund a bounded pilot, rather than commit the entire sourcing program. Before spending, Moonbucks would agree on participating farms, responsibilities and the evidence needed at review.
Its scorecard could track farmer participation, implementation costs and plant survival, alongside accepted coffee volumes and lot-quality results. Carbon measurements would follow the selected method. Farm-level traceability must connect the intervention to the actual sourcing relationship.
Suppose Moonbucks’ review later finds that storage changes explain most quality improvements, while the land measures need longer observation. Those findings would shape the next decision: expand the proven component, adjust the landscape work or pause further spending. They would not justify crediting all improvements to tree planting.
This gives nature-based carbon investments a practical place in a multi-year strategy. Funding increases as the evidence supports it, and the project can change direction before a larger commitment.
Discuss a sourcing opportunity with CCC
Carbon Credit Capital’s nature-based supply-chain investment service uses its Dual-Value Model to examine supply-chain economics alongside potential sustainability outcomes.
Schedule a consultation to discuss your sourcing exposure and the questions to resolve before allocating capital.
Sources
- Intergovernmental Panel on Climate Change (IPCC), Climate Change 2022: Mitigation of Climate Change, Chapter 7, Agriculture, Forestry and Other Land Uses, section 7.4.3.3 (Agroforestry).
- World Business Council for Sustainable Development (WBCSD), Nature-based Solutions Blueprint, 5 June 2024.
- Science Based Targets initiative (SBTi), Forest, Land and Agriculture Science-Based Target-Setting Guidance, version 1.2, March 2026, section 3.1.4, pp. 37–38.
- United Nations Environment Programme (UNEP),