The US Department of Energy (DOE) has outlined its research and development (R&D) priorities to achieve the ambitious cost targets for clean hydrogen set by the Biden administration. Renewable hydrogen production and storage, as well as technology for trucking applications, are among the key focus areas identified by the DOE’s Hydrogen and Fuel Cell Technologies Office in its Multiyear Program Plan.
Sunita Satyapal, director of the said Office, stated in a forward to the program plan:
“While the progress in clean hydrogen today is encouraging, it is also clear that more is needed… and the actions taken must be well-planned, deliberate, carefully executed with measurable outcomes, and they must come without delay.”
DOE’s Clean Hydrogen Roadmap
The Inflation Reduction Act, enacted in August 2022, introduced tax credits of up to $3/kg for clean hydrogen producers over the initial decade of a project’s lifespan, depending on its carbon emissions lifecycle. This incentivizes clean or green hydrogen production, positioning it competitively against grey hydrogen from fossil fuels.
The U.S. leads in green hydrogen production due to these tax credits and a $9.5 billion subsidy from the Infrastructure Investment and Jobs Act. The subsidy includes $8 billion to establish at least 4 regional clean hydrogen hubs.
Projections anticipate the cost of green hydrogen to decrease significantly by 2050, signaling its long-term viability, and encouraging further investment.

The DOE aims to significantly reduce the cost of zero-emission hydrogen by targeting a price of $1/kilogram by 2031. This price includes production, delivery, and dispensation at fueling stations. An interim target of $2 per kilogram by 2026 has been set.
The agency’s plan centers around the DOE’s “Hydrogen Shot” objective. It also seeks to decrease the cost of electrolyzer systems to $250-500/kW, lower the cost of fuel cell systems for heavy-duty transportation to $80/kW, and achieve a final dispensed cost of hydrogen fuel below $7/kg.
Currently, hydrogen produced by electrolysis can cost at least $5 per kilogram, or up to $12 per kilogram when accounting for delivery and fueling station costs. Conventional hydrogen production from natural gas costs about $1.50 per kilogram but comes with a significant carbon footprint.
The near-term priorities outlined by the DOE include improving electrolyzer technology to achieve lower systemwide costs and increased durability. Additionally, research and development efforts will focus on hydrogen storage and transportation for heavy-duty vehicle applications, aiming to reduce costs and minimize leakage.
DOE Clean Hydrogen Production Pathways in the RD&D Portfolio

In the long term, the DOE sees opportunities in advanced hydrogen production methods that require minimal or no electricity input. These include solar photoelectrical chemical production and biological conversion. Materials-based hydrogen storage, utilizing absorbents or chemical carriers, is also a focus area for long-term research and development.
Toyota’s Renewable Hydrogen System
Over in California, FuelCell Energy and Toyota Motor North America recently celebrated the inauguration of the groundbreaking “Tri-gen” system at the Port of Long Beach. This innovative system uses biogas to generate renewable electricity, renewable hydrogen, and usable water.
The Tri-gen system was specifically constructed to support the vehicle processing and distribution center for Toyota at Long Beach. The facility is Toyota’s largest in North America, receiving about 200,000 new Toyota and Lexus vehicles annually.
The system showcases scalable hydrogen-based technology that reduces emissions and minimizes reliance on natural resources. Tri-gen’s fuel cell technology converts renewable biogas into electricity, hydrogen, and usable water with high efficiency and minimal pollution.
Moreover, Tri-gen produces up to 1,200 kg/day of hydrogen to fuel Toyota’s incoming light-duty fuel cell electric vehicle (FCEV) Mirai. It also supplies hydrogen to the adjacent heavy-duty hydrogen refueling station, supporting TLS logistics and drayage operations at the port.
California’s Advanced Clean Fleet Regulation mandates zero-emission trucks for newly registered drayage trucks. And Tri-gen is well-positioned to support the transition to zero-emission trucks, including FCEV Class 8 trucks. The system’s hydrogen production can be adjusted based on demand, facilitating the migration to zero-emission vehicles by 2035.
Generating 2.3 megawatts of renewable electricity, Tri-gen also supplies excess electricity to the local utility, Southern California Edison. As such, it will contribute to the renewable energy grid under the California Bioenergy Market Adjustment Tariff (BioMAT) program.
Pioneering Innovative Carbon Reduction Solutions
Overall, Tri-gen is expected to help reduce more than 9,000 tons of CO₂ emissions annually from the power grid. It can also avoid over 6 tons of grid nitrogen oxide emissions, while potentially reducing diesel consumption by 420,000 gallons/year. This aligns with both Toyota’s carbon reduction goals and the Port of Long Beach’s commitment to innovative CO2 reduction solutions.
In summary, the DOE’s plan underscores the importance of continued innovation and investment in clean hydrogen technologies to accelerate the transition toward a low-carbon economy.
The collaboration between FuelCell Energy and Toyota is an example of how innovative and sustainable solutions through hydrogen can help reduce carbon emissions in business operations while promoting renewable energy sources.
The post DOE Sets Eyes on Cutting Clean Hydrogen Cost, $1/Kilo by 2031 appeared first on Carbon Credits.
Carbon Footprint
The Strategic Case for Nature-Based Carbon Investments
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.
Carbon Footprint
How to buy plastic credits, and what to check before you do
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.
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Carbon Footprint
EU carbon credit claims after 27 September 2026
EU carbon credit claims changed on 27 September 2026, the day the Directive (EU) 2024/825 began to apply across the European Union. The change is narrow. It changes how a company can talk about the credits it buys. A product can no longer be called neutral on the strength of compensation alone; however, every specific, evidenced statement about what a company measured, reduced, and funded stays fully available.
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