- Enhanced Rock Weathering (ERW) is gaining attention as a scalable carbon removal solution. A recent study suggests the method could remove up to 350 million tonnes of CO₂ per year by 2050 if widely deployed.
What is Enhanced Rock Weathering?
Enhanced Rock Weathering is a carbon removal method that speeds up a natural geological process. Rocks such as basalt and silicates naturally react with carbon dioxide (CO₂) over thousands of years.
ERW involves crushing these rocks into fine powder and spreading them on the soil. The larger surface area makes the rocks react faster with CO₂ in the air and soil. Scientists believe this could permanently capture and store carbon as stable minerals or ocean carbon pools.
This carbon removal has emerged as a promising part of the climate toolkit to help lower atmospheric CO₂ levels.
How ERW Removes Carbon
Natural rock weathering already captures about 1.1 billion tonnes of CO₂ per year from the atmosphere. ERW accelerates this process by increasing the rock’s contact with CO₂.
When rainwater dissolves CO₂, it forms carbonic acid, which reacts with silicate rocks. This reaction locks carbon into bicarbonate ions. Some of the ions wash into rivers and reach the ocean, where they can stay for thousands of years. Because the carbon is stored this way, it is unlikely to return to the atmosphere soon.
In agriculture, ground rocks applied to the soil enhance this process. The rocks react with CO₂ around plant roots and soil microbes. Some companies source rock dust from quarries. They use industrial byproducts instead of new mining.
350 Million Tonnes: The Mid-Century Potential
New research shows that ERW could make a major contribution to climate goals by mid-century. Scaling ERW on suitable agricultural land and other surfaces worldwide could remove an estimated 350 million tonnes of CO₂ per year by 2050. This would come from fast-tracking the natural weathering process across large areas of cropland.
Global modelling studies also suggest even bigger potential. ERW could cut hundreds of millions to billions of tonnes of CO₂ each year by 2050. This depends on widespread use, strong policy support, and proper infrastructure.
Some studies focused on the United States have reported similar potential. Research shows that ERW in U.S. agriculture could cut CO₂ by 160 to 300 million tonnes each year by 2050. If expanded, this number could reach 250 to 490 million tonnes by 2070.
This 350 million-tonne figure sits within a broader picture of potential CDR capacity. Some analyses suggest that ERW could remove billions of tonnes every year. This would occur if the method is used widely across continents with big agricultural sectors.
Why ERW Stands Out in the Carbon Removal Race
One key reason ERW attracts attention is its durability. Carbon captured through rock weathering is stored in stable forms that can last thousands to millions of years. This permanence can make ERW more durable than some nature-based solutions that store carbon only for the lifetime of trees or plants.
ERW also builds on existing farming and mining systems. The technology uses known equipment and methods for crushing and spreading rock. This means ERW is likely easier to use widely than complex methods like direct air capture (DAC). DAC needs big new facilities and a lot of energy.
Enhanced rock weathering has additional benefits beyond carbon capture. When applied to agricultural soils, silicate rock dust can improve soil nutrition and structure. This can enhance crop yields and reduce the need for some fertilizers. Some research has even shown that certain enhanced weathering practices can improve crop performance while removing CO₂.
ERW Carbon Removal Credits Snapshot
ERW has begun to enter this market with real, verified credits. In early 2025, InPlanet and Isometric issued the first independently verified ERW carbon removal credits. These credits show long-lasting CO₂ removal. They are certified with strict monitoring, reporting, and verification (MRV) protocols.
While ERW still makes up a very small share of total credits traded in 2025, its emergence marks a milestone for carbon removal markets. Early tracking shows that nearly one million ERW credits have been sold, and the total investment in ERW projects is about US$121 million. This reflects increasing interest from companies and offset buyers.
ERW carbon credit prices now range from $200–$500 per tonne. This spread comes from differences in project size, location, and how mature each method is.
Early ERW credits add variety to the carbon market. They focus on carbon removal, which is attracting buyers like Google and Microsoft. They want long-term, verified removal credits along with avoidance credits.
- SEE MORE: Microsoft Backs InPlanet’s Enhanced Rock Weathering Push to Remove 28,500 Tons of CO₂ in Brazil
Scaling Up: Verification, Logistics, and Adoption Hurdles
Despite its promise, ERW faces several challenges before it can deliver on its full potential by 2050.
- Monitoring and verification: Measuring exactly how much CO₂ ERW removes is complex. The process occurs over time and involves soil chemistry, water movement, and geological cycles. Accurate monitoring, reporting, and verification (MRV) systems are needed to ensure that carbon removal amounts are real and not overstated.
- Deployment logistics: Scaling ERW globally would require vast amounts of crushed rock. This means expanded quarrying, crushing, transport, and spreading infrastructure. These steps must be done efficiently to avoid high emissions from transport and machinery.
- Agronomic adoption: Farmers and landowners would need incentives and support to adopt ERW. Also, the use of rock dust must align with soil types, crops, and local farming practices. Long-term studies are ongoing to determine the best application rates and conditions for different regions.
- Environmental questions: While ERW can benefit soil fertility, some uncertainties remain about long-term ecosystem impacts and potential side effects. Careful planning and studies are needed before very large-scale deployments can occur.
A Key Piece in the Net-Zero Puzzle
Climate models show that reducing emissions alone won’t be enough to meet the Paris Agreement’s goals. Many experts argue that carbon dioxide removal (CDR) must play a role in keeping the temperature rise below 1.5°C. ERW is one of several CDR methods being considered.
Other CDR approaches include direct air capture (DAC) and bioenergy with carbon capture and storage (BECCS). DAC uses machines to pull CO₂ directly from the air, but it is still expensive and energy-intensive.
BECCS captures CO₂ from biomass energy but depends on large dedicated biomass supplies. ERW, by contrast, can leverage natural soil processes and agricultural lands for scalable removal.
Policy makers and climate planners see enhanced rock weathering as one piece of a broader carbon removal portfolio. ERW, along with strong emissions cuts, nature-based solutions like reforestation, and new technologies, can help balance hard-to-abate emissions in sectors such as industry and agriculture.
To reach 350 million tonnes of CO₂ removal per year by 2050, ERW must scale rapidly. This will require stronger global commitment from governments, research institutions, and private investors.
Moreover, investment in field trials and pilot programs will help refine practices and decrease uncertainty. As more data becomes available, ERW techniques can be optimized for different soils, climates, and crop systems.
Public policy support will also be key. Carbon markets, incentives, and crediting systems that recognize verified removal could help fund large-scale ERW deployment. If aligned with broader climate goals, ERW could become a major contributor to meeting global net-zero targets.
The post Rocking the Carbon Clock: ERW Could Cut 350 Million Tonnes of CO₂ Annually by 2050 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), State of Finance for Nature 2023, 2023.
A plastic credit funds the collection of plastic waste in places where no formal system exists to collect it. Each credit represents a measured, independently audited quantity of plastic taken out of the environment or returned to use, tracked on a public registry.
