CDR Policy Roads Less Traveled

Paths to focus on for carbon removal policy in the wake of a US election

Photo by James Wheeler: https://www.pexels.com/photo/photo-of-pathway-surrounded-by-fir-trees-1578750/

“When we are no longer able to change a situation, we are challenged to change ourselves” – Viktor Frankl

I wrote at the start of this Substack that it would be a series about carbon removal covering insights about carbon markets, workforce and policy. Today in the wake of the US election outcome, I am going to take on that third topic – policy – with some quick takes on what the US election in November 2024 might mean for CDR Federal and State policy efforts. As much as I’ll write about policy in this post, I can’t avoid the politics of the moment. My instinct is that while US Federal climate policy per se will likely take a step back or two (or three…) in the incoming administration, a reframing of policies that advance carbon removal specifically as an economic driver would be a path forward.

First, some first impressions of what’s possible at the Federal level in the United States. I’ll keep this as specific as I can to carbon removal since there are many, many platforms better equipped than I am to speak to broader policy impacts.

The clearest risk to support for carbon removal comes in how the Trump administration might restructure the Department of Energy, specifically the office of Fossil Energy and Carbon Management (FECM) which has been administering the DAC Hubs and other carbon removal programs. Notably, the DAC Hubs in particular were authorized and funded by the Bipartisan Infrastructure Law (BIL), rather than the Inflation Reduction Act (IRA) which passed on a partisan vote. So it is possible that the bipartisan nature of the BIL funding would insulate programs it supports from being scaled down. The tax provisions of the IRA – in particular 45Q – might be subject to repeal, under a scenario of unified Republican Presidency, House, and Senate.

Beyond the Direct Air Capture programs at FECM efforts the department has recently taken action on marine carbon removal (mCDR), enhanced rock weathering (ERW), and biochar might be subject to change as well. Look additionally to new appointments at USDA – which administers US Forest Service and Natural Resources Conservation Service, as well as Commerce – NOAA and National Institutes for Standards and Technology – which impact these methods of CDR as well.

For Congressional action, the upcoming Congress at the time of this writing (November 11th 2024), appears to have a thin Republican majority in the House, while Republicans will take control of the Senate. While a comprehensive climate bill (‘IRA2’) is off the table, other policy avenues are open which would require bipartisan support. For instance, the 2018 Farm Bill will be up for renewal, with US Congressman Don Bacon (R-Nebraska) having supported bipartisan climate friendly agriculture legislation in the past likely playing a key role. Biochar, ERW, and soil carbon sequestration advocates would take note. 

For DAC advocates, permitting and the intersection of DAC and energy policy would be areas to watch. Any efforts to reform carbon dioxide pipeline permitting (more on this below) would be a start. Also, the re-election of Michelle Steel (R-California), who has supported bipartisan geothermal energy legislation, suggests that advancing projects using a geothermal Fervo Energy’s new project will harness the earth’s heat to capture…energy source for DAC could have support.

Since Federal CDR policy may have to be meted out piecemeal, carbon removal policy advocates could then look to state governments as areas to advance policy ideas. I will recap some of the election results here, outlining particular actions to take in specific cases.

Washington State: Ballot Initiative 2117 failed resoundingly, with 62% voting “No”, thus preserving the state’s Cap-and-invest system for selling emissions allowances and reinvesting the proceeds into the State’s economy. A wide variety of organizations contributed to the “No on 2117” campaign, including corporations such as Amazon, Microsoft, REI, and British Petroleum (!) aligned with several unions and climate affiliated civic organizations. Key to the messaging was the economic benefit to the state in retaining the cap-and-invest system; additionally, there is evidence that the fiscal impact of the state losing $3.8 billion in revenue from 2025 to 2029 was persuasive to voters.

What it means: Revenues from the cap-and-invest system will continue apace to flow to the state’s accounts, which are set up to collect and disburse auction proceeds to advance the clean energy economy. For Carbon removal, this includes state grants that CDR companies are eligible for under the Clean Energy Fund.

Going forward, Washington can now pursue linkage in its Cap-and-invest system with California and Quebec’s cap-and-trade systems, as directed by the state legislature in the spring of 2024. How carbon removal credits integrate into this remains to be seen, however. First steps include the Department of Ecology writing a study – slated for completion and release in June 2025 – covering “the extent to which carbon dioxide removal is needed to meet Washington’s emissions reduction targets”.

South Dakota: Carbon removal pipeline enabling Referendum 21 failed, with 60% of South Dakota voters rejecting a measure that would have made constructing carbon dioxide pipelines easier in the state. Opponents had argued that passing the referendum would have canceled local governance and removed protections for landowners. 

What it means: Envisioned as a CO2 transportation pipeline for ethanol-based CO2 capture, DAC developers should take heed to consider local community concerns surrounding possible similar CO2 pipeline efforts.

California: California voters approved Proposition 4: a $10B state bond to be distributed to counties, local governments, and Native American tribes to support a wide variety of projects,including clean water security, reducing risk of flood and wildfires, and also improving marine ecosystem regeneration in aid of climate resilience.

CDR angle: With $1.5B slated for wildfire risk reduction, including forest thinning, California biochar producers could see a greater abundance of feedstock for pyrolyzing operations. It might also improve offtake for the biochar itself, which has uses for wastewater remediation. For marine CDR companies, $890M of the $10B is marked for coastal projects; a project that improves water quality and promotes coastal resilience that also removes atmospheric carbon dioxide might benefit. 

Louisiana: 73% of voters approved a constitutional amendment that revenue from state renewable energy projects, such as wind power, can be diverted to coastal resilience measures

Implication: Similar to California, to the degree that marine CDR projects – particularly in a coastal location – can add to the state’s ability to buffet against hurricanes, floods, and sea level rise, this would be a benefit.

Massachusetts: This is not directly election related, but noting that the state legislature will consider an Economic Development package in a special session, which contains many climate and clean energy provisions which would be important for CDR. The House and Senate had each separately passed their own bill and to agree on a common bill to send to Governor Healy for signature before the current session ends on December 31st. 

So what kind of pathways are best for policies to support carbon removal?

In my view, reframing the discussion of carbon removal policy in the United States as an economic development measure and not a climate measure could lead the way to successful growth of the industry.

Why? For one thing there is motivation to do something about climate. Voters – and surprisingly a high percentage (~40%) of Trump voters – at least somewhat agree that climate change is a problem:

But – even among some Harris supporters (~35%) – American voters are not willing to pay for measures to counteract its effects:

Carbon removal projects that show an economic benefit beyond the action of removing excess atmospheric greenhouse gas will be a winner in the policy environment that will likely emerge from the 2024 US election season. The ability to show tangible benefits to people in communities, in the form of providing valuable products or services, or well paying careers – not just project-based jobs – for people who are struggling in an economy that they (fairly or unfairly) perceive to be still ridden with inflation or unemployment. And that might affect how C-suite and corporate sustainability managers perceive the need for climate action, and by extension carbon removal, as investor Susan Su mentions here. The perception of the state of the US economy among Americans has diverged from how the actual economy is performing since the COVID pandemic. This suggests that policies that underscore the economic benefit to voters would find a favorable reception among government leaders at any level.

While there may be limited pathways forward at the Federal level, State and local efforts at CDR policy offer a potentially meaningful way to support the industry. Even if policies are not specifically titled ‘carbon removal’, policymakers can include CDR alongside general economic development efforts – and make a difference in their state, county, or municipality. Respecting the interests of those communities – particularly at a local level – is paramount, as evidenced by the South Dakota measure above. Project developers who are in touch with the communities where they operate can consider how to meet the needs of those where they operate. And that’s important: especially in this environment, building political support starts at the local level. 

This can move the conversation away from carbon removal being perceived as an expense imposed from outsiders, and rather as a source of revenue generating activities integrated into the economy and society, and coincidentally happen to draw excess greenhouse gasses out of the atmosphere. 

Venture capitalist Vinod Khosla wrote over a decade ago that for ‘cleantech’ to succeed it has to be perceived as ‘maintech’ – that it integrates within the industrial base as a natural progression of technology in the minds of customers. Reframing the conversation about carbon removal from a climate technology dependent on specific climate policy to a ‘maintech’ solution that integrates with economic policy is a step forward in an otherwise daunting national political environment for climate in the United States.

Jason Grillo is a Co-Founder of AirMiners. The opinions expressed in this writing are the author’s own and do not reflect the position of any employer.

Introducing a new tool for monitoring, reporting and verifying CO2 removals

Today marks the launch of a new interactive visualisation of the landscape for monitoring, reporting and verification of carbon dioxide removal methods, a joint project between the Grantham Research Institute and AlliedOffsets. Josh Burke, our Senior Visiting Fellow and Leo Mercer and Anton Root describe the purpose and benefits of the tool for policy practitioners, CDR developers and purchasers – who can use it to understand the market at a glance.

Why is monitoring, reporting and verification of CO2 removal so important?

Alongside actions to rapidly reduce greenhouse gas emissions, carbon dioxide will need to be removed from the atmosphere if the world is to meet the Paris Agreement climate goals. The Intergovernmental Panel on Climate Change (IPCC) suggests carbon dioxide removal will need to be scaled up from a current base of around 2 Gt (billion tonnes) CO₂ removed per annum to at least 10 Gt by 2030 and 100-1,000 Gt over the remainder of the century to counterbalance residual emissions.

The proliferation of net zero targets, and by extension the use – or planned use – of carbon dioxide removal (CDR) has led to increased attention on the governance of CDR. A key component of this governance architecture is monitoring, reporting and verification (MRV), which is the multi-step process to measure the amount of greenhouse gases removed by a specific removal project and reported to an accredited third party.

Robust MRV can help governments and private sector actors overcome information gaps and asymmetries that may make it difficult for them to make investment or regulatory decisions. This is critical as the current crisis of confidence in the voluntary carbon market (VCM) has the potential to erode trust and confidence in CDR, halt capital investments and slow the integration of CDR into climate policy. Successful industries rely on standards and certification to ensure activities meet expectations. The CDR industry is no different.

Furthermore, owing to the absence of internationally agreed minimum quality standards, multiple regulatory efforts (such as the EU Carbon Removals and Carbon Farming/CRCF Regulation) are developing in parallel to fast-moving technical developments in the VCM. This results in overlapping protocols for some CDR methods and incomplete MRV coverage for others. Consequently, the MRV landscape has become ever more confusing. This makes comparison and oversight of CDR difficult for investors and governments alike. Greater transparency is sorely needed.

From mapping the MRV ecosystem to launching a new interactive tool

With new protocols constantly emerging, the challenge for policymakers, researchers and investors is to maintain a systematic overview of activity and use this to improve policy. To shed light on this, as a first step in 2023 the Grantham Research Institute conducted an MRV ecosystem mapping exercise to help identify the number of, and interrelationships between, regulations, certifying entities and MRV protocols across the spectrum of CDR methods.

To qualify for inclusion, protocols had to provide guidance for CDR activities that lead to net CO2 removals from the atmosphere and carbon capture and storage (CCS). Protocols on the latter were included because CCS facilitates certain CDR methods like direct air carbon capture and storage (DACCS) and bioenergy with carbon capture and storage (BECCS).

In partnership with AlliedOffsets, we are launching today the next iteration of this work: Transparent Reporting and Certification for CDR or the TRACEcdr tool. This has digitalised our original research to create a new interactive tool for policy practitioners, CDR developers and purchasers. TRACEcdr combines the mapping efforts of the Grantham Research Institute with AlliedOffsets’ data-gathering on activity happening in the VCM.

What does the tool do?

The TRACEcdr tool responds to the challenges set out above by creating the first interactive digital tool to provide transparency and oversight to the CDR market. It involves three initial steps, two of which we can present today in the beta version.

  • The first systematically maps and digitalises the MRV ecosystem for all CDR methods, providing an interactive digital MRV ecosystem.
  • The second step illustrates the activity within the system by providing information on the number of projects and the volume of issued credits for each CDR method and MRV protocol. Data is provided on project registrations and issuances of credits from the AlliedOffsets database of over 32,000 projects globally, from 25 registries plus hundreds of unregistered projects.
  • The third step, due for completion in 2025, will overlay the results of a systematic evaluation of MRV quality by assigning scores to the MRV protocols that underpin credit issuance.

The outcome is an interactive visualisation of the CDR MRV landscape. The tool has been created with an eye towards understanding the market at a glance, allowing policymakers and investors to grasp the complexity and activity within the ecosystem such as risks and benefits of current market activity, where activity is happening, by what methods and eventually, how rigorous and credible underlying MRV protocols are.

How to interact with TRACEcdr

Upon opening the TRACEcdr tool, four levels of the MRV system are visible:

  • Level 1 is organised according to CDR method.
  • Level 2 is the entity that provides the removal standard for a given CDR method.
  • Level 3 details the MRV protocol and denotes whether a protocol is applicable in a national or international context and for voluntary or compliance purposes.
  • Level 4 visualises credit issuance projects per protocol. The larger the node, the larger the credit issuance. Clicking on nodes in the fourth tier enables the user to isolate and trace the connected nodes in each tier below.

Users of the tool can filter for different options such as whether the protocol is nationally or internationally focussed and whether it is for use in compliance or voluntary carbon markets. CDR methods or protocols can be isolated such that all activity can be seen more easily. Some protocols do not connect to the fourth tier of the ecosystem map either because they do not have any registered projects associated with them, or because AlliedOffsets has been unable to access data on those protocols at the time of publication (this is mainly for compliance issuance due to data protection regulations).

Key insights

A major trend exemplified by the tool is the dominance of ‘land-based biological’ methods. Although methods like DACCS have dominated CDR discussion and funding, the overwhelming activity within removals today – by the sum of MRV protocols, project number and credit issuance – are projects planting trees or restoring natural carbon sinks like peatlands and soils. Indeed, of the 117 MRV protocols that have been recorded in total (between 2005 and mid-October 2024), 29% are attributable to afforestation, reforestation and forest management (A/R), 18% to soil carbon sequestration (SCS), 9% to peatland and wetland restoration and a further 5% to BECCS. In terms of credit issuance, A/R accounts for 77% of all issued credits, with peatland restoration projects constituting another 19%.

The ecosystem is currently in a rapid state of development. In 2023, 22 MRV protocols were published, which was a small increase on the total of 19 in 2022. Protocol development in 2023 skewed towards biological methods with seven protocols, and SCS with three. Data from 2024 indicate more balanced MRV development, with 15 protocols to date including two for ocean alkalinity enhancement, two for biomass carbon removal and storage (BiCRS) and two for CCS but also including single protocols for enhanced rock weathering, direct ocean capture and DACCS. 2024 may yet surpass 2023 in terms of the total number of MRV protocols published.

Although we observe a complex system with duplication and year-on-year increases in MRV protocol development, the majority of issuance is occurring through a few select protocols. For example, for peatland and coastal wetland restoration, Verra’s VM0033 protocol is responsible for 99% of issuance. For soil carbon sequestration, four protocols account for 97% of all issued credits, with Verra’s VM0032 and VM0026 respectively accounting for 31% and 30% of total issuance. For A/R, 90% of issued credits stem from just four protocols, with the California Air Resources Board’s Compliance Offset Protocol U.S. Forest Projects (compliance) issuing 64% of all credits (114 million).

This coalescence in the market has benefits and risks. On the one hand, it suggests that improvements to the dominant protocols could ripple through most of the system. On the other, it may indicate systemic risks if in the future new evidence indicates problems with these dominant protocols. For this reason, it is important that there are independent assessments of the quality and rigour of MRV underpinning CDR issuance.

Table 1. Overview of system activity

The numbers in brackets for the CDR method column indicate the total number of protocols per method, but we only illustrate the most popular

CDR method Registry Protocols with greatest issuance No. of projects No. of issued or sold credits % of total
Afforestation, reforestation, agroforestry, forest management (34) American Carbon Registry Compliance Offset Protocol U.S. Forest Projects 113 114,065,156 64%
Improved Forest Management (IFM) on Non-Federal U.S. Forestlands 150 26,243,535 15%
Gold Standard Impact Registry Afforestation/ Reforestation (A/R) GHG Emissions Reduction and Sequestration Methodology 62 11,389,778 6%
Woodland Carbon Code WCC Standard v2.2 2,118 8,955,223 5%
Soil carbon sequestration in croplands and grasslands (21) Verra VM0032 Methodology for the Adoption of Sustainable Grasslands Through Adjustment of Fire and Grazing v1.0 11 6,098,086 31%
VM0026 Methodology for Sustainable Grassland Management v1.0 48 5,786,488 30%
Plan Vivo PU001 Estimation of Baseline and Project GHG Removals by Carbon Pools in Plan Vivo Projects 10 5,209,137 27%
BioCarbon BCR0001 Quantification of GHG Emission Reductions from GHG removal activities 20 1,863,323 10%
Peatland and coastal wetland restoration (10) Verra VM0033 Methodology for Tidal Wetland and Seagrass Restoration, v2.0 30 4,802,658 78%
Peatland Code Peatland Code v1.2 295 1,268,675 21%
American Carbon Registry Restoration of California Deltaic and Coastal Wetlands 1.1 2 52,405 1%
Verra VM0036 Methodology for Rewetting Drained Temperate Peatlands v1.014 2 0 0%
Biochar (5) Puro.earth Puro.earth Biochar Methodology Version 2.4.1 44 295,827 100%
Verra VM0044 Methodology for Biochar Utilisation in soil and non-soil applications v4.0 8 0 0%
DACCS (2) Climeworks Carbon Dioxide Removal by Direct Air Capture 10 175,836 100%
BECCS (6) Puro.earth Geologically Stored Carbon Methodology v2.2 1 157,592 100%
Bio-oil storage (2) Charm Industrial Bio-oil Sequestration Prototype Protocol for Measurement, Reporting, & Verification 1 154,063 99.997%
Isometric Bio-oil Geological Storage 1 5 0.003%
Direct ocean carbon capture and storage (2) Equatic Methodology for Measurement, Reporting, and Verification of Electrolytic Oceanic Carbon Dioxide Removal 4 63,221 99.2%
Captura Carbon Dioxide Removal Pathway: Ocean Health and MRV 2 508 0.8%
Biomass sinking (1) Running Tide Framework Protocol for Multipathway Biological And Chemical Carbon Removal in the Ocean 2 18,398 100%
Enhanced rock weathering (5) Puro.earth Enhanced Rock Weathering in Soil Methodology 1 12,276 100%
Carbfix Permanent and Secure Geological Storage of CO2 By In-Situ Carbon Mineralization 8 0 0%
Ocean alkalinity enhancement (4) Planetary Ocean Alkalinity Enhancement MRV Protocol 0 8,684 97%
Ebb Carbon Measurement, Reporting and Verification for Safe and Effective Carbon Dioxide Removal 1 256 3%
BiCRS (2) Isometric Biomass Geological Storage 1 4,403 100%
Geological storage (1) Puro.earth Geologically Stored Carbon Methodology v2.2 1 587 100%
Mineral products (2) Gold Standard Impact Registry Carbon Sequestration Through Accelerated Carbonation of Concrete Aggregate 15 149 100%
Marine biomass sinking (1) Rewind Marine Terrestrial Biomass Storage 3 0 0%
CO2 capture, transport and storage (9) Australian Carbon Credit Units Carbon Credits (Carbon Farming Initiative—Carbon Capture and Storage) Methodology Determination 2021 1 0 0%

 

One more surprising insight, given that MRV development for CDR methods is primarily happening in the VCM, is the major role of compliance markets. Just under 60% of credits issued can be used in compliance markets, most significantly within California’s Air Resources Board programme. However, outside of California and in terms of novel durable CDR, there is no virtually issuance in compliance markets yet.

Note that the data are derived only from those projects that are registered on a registry adhering to a protocol included in our analysis. Many novel companies and projects are in the pilot phase, meaning they are not adhering to any protocol when selling credits. This carries risk for buyers, but it also allows the suppliers to launch and sell credits quickly, without needing to develop a protocol and certify against it, a process that can take years. We can expect this to continue over the next decade, as pilot projects begin to issue credits and more projects come online.

Future plans for TRACEcdr

The release of the beta version of the TRACEcdr tool today is an early step in promoting openness and transparency in CDR markets. We are using this release to product-test and gain insights and feedback from user experience. The data will be updated on a regular basis. Further iterations will include more visualisations, and more data added for each of the protocols and a second release in the second quarter of 2025.

Access the TRACEcdr tool at https://www.lse.ac.uk/granthaminstitute/tracecdr/. We welcome user feedback – please send to l.w.mercer@lse.ac.uk / j.burke2@lse.ac.uk.

Josh Burke is a Senior Visiting Fellow at the Institute for Responsible Carbon Removal and a Senior Policy Fellow at the Grantham Research Institute; Leo Mercer is a Policy Analyst at the Grantham Research Institute; Anton Root is the Co-Founder of AlliedOffsets. The opinions expressed in this writing are the authors’ own and do not reflect the position of any employer.

The Price is… Wrong? – Climagination with Jason Grillo

Carbon removal prices are going to reflect value to the customer rather than cost of production. Here’s how.

Photo by Eva Bronzini: https://www.pexels.com/photo/blank-tags-in-close-up-photography-8058803/

 

“The purpose of a business is to create a customer … The customer never buys a product. By definition the customer buys the satisfaction of a want. He buys value. … But price is only part of value. There is a whole range of quality considerations which are not expressed in price” 

– Peter Drucker, Management: Tasks, Responsibilities, Practices

 

One of the questions I hear (frequently!) is “what’s a good price per ton for carbon removal?” Or a variant “What price is carbon removal converging on?” While it sounds like a shrewd question to ask, this assumes that all carbon removal tons are equal – that this is a commoditized market in 2024. Nothing could be further from the case. 

My argument in this post is not only that the attributes of projects and methods of carbon removal are highly variable, but that different customer segments perceive different benefits from carbon removal credits. I’m going to suggest a pricing analysis tool below which addresses these customer segment needs from a couple different angles – stay tuned! 

But before addressing these customer segments, let’s level-set with some terminology points.

 

First, Cost vs Price: These are different terms. A ‘Cost’ usually refers to the internal expenses needed for a supplier of a good or service to produce a unit for sale – in this case a voluntary market credit representing one ton of CO2 removed. (FOOTNOTE: Not talking about methane or nitrous oxide equivalents). These take into account labor, cost of the physical resources for production, energy, transportation, and cost of capital.

A ‘Price’ refers to what a producer of a good or service charges to a customer at exchange. The difference between Price charged to the customer, and Cost to the supplier is the Profit margin.

To illustrate, here’s a chart from a conference presentation I recently gave:

 

Second, Price vs Value: What a supplier charges to a customer for one carbon removal ton is NOT the sum total of the entire value that the customer derives from the purchase. The buyer of a carbon removal ton realizes a value beyond what the market price is that the seller charged for that ton – otherwise they would not have purchased it to begin with.

State of pricing today: A wide variety of value propositions to a customer lead to a wide variation of prices, especially since customers are in 2024 starting to figure out what the value to their organization is of the durable CDR credits purchased. 

Indeed, this is exactly what we are seeing in the 2023 State of CDR report (2nd Ed.) prices based on 2023 market conditions:

What price is the “right” price? They all are! Customers are not irrational, even though there is a high degree of variability in these CDR prices. For example, a customer believed that for Direct Ocean Capture CDR $1,402 per ton is a valuable ton to buy: they wanted to see the exchange happen. Another customer believed that for biochar a $131 ton of CDR is a valuable ton to buy. For each of these customers the price was justified by what they used the durable CDR ton to achieve.

Different customers had different rationales underlying their purchasing decision, value propositions, and thus different price points. The reason for purchasing could have been to neutralize Scope 1, 2, or Scope 3 emissions directly, could have been for branding purposes of being perceived as good stewards of the earth, or perhaps to lock in relationships with suppliers for future credits, or simply to signal support for early stage innovation. SBTi’s Beyond Value Chain Mitigation work offers examples of these reasons. 

 

My takeaway: the rationale for purchasing credits drives the perception of value, and thus the price a supplier is able to charge to cover their costs of supporting their business.

Evidence: These self-reported motivational customer segments are evident in the NASDAQ Global Net Zero Pulse report chart below (Sept 2024):

Granted these are for carbon credit markets writ large – i.e. traditional offsets and less durable nature-based solutions, not only for durable carbon removal – but I would offer that the structure stands, regardless of the type of carbon credit, be it avoidance, less durable CDR (<100 years), or higher durability CDR (>100 years). There is no monolithic rationale for buying durable carbon removal today. When a potential buyer reports that “prices of credits are too high”, the lesson is not that buyers think “you should find a way to lower your costs”, rather “prices are too high for what you are offering to meet what the customer views as valuable now”. The options for a startup to take, therefore, are either:

A) figure out a way to improve the value of the durable CDR credit delivered to the type of customer you are trying to address or 

B) Find a different customer who will find what you are delivering to be valuable.

Which leaves carbon removal suppliers at a standstill: if all prices are valid, then what should I charge?

One answer lies in a powerful survey tool that may be helpful: a Van Westendorp model. This technique can yield an acceptable price range for a given set of potential customers.

The four very specific questions asked in Van Westendorp analysis are:

      • At what price would you consider the product to be so inexpensive that you would feel the quality couldn’t be very good?
      • At what price would you consider the product to be priced so low that you would feel it’s a bargain?
      • At what price would you say the product is starting to get expensive, but you still might consider it?
      • At what price would you consider the product to be so expensive that you would not consider buying it?

The result, a chart that looks something like this example, with one line tracking each of the four questions, price points on the X-axis, and % of respondents who accept the price for that line description on the Y-axis (e.g. 80% of respondents consider $20 ‘Acceptably cheap’):

Source: sawtoothsoftware.com

And there are several ways of segmenting the data, assuming a large enough set of respondents. For instance, a survey team could segment by industry and see the different ranges represented there. Or ask intake questions (like in the NASDAQ survey example above) to divide up the respondent pool by motivations. Or conduct two sets of questions and change the delivery to be in 2025 vs 2030.

Additionally, you can ask these sets of questions twice, once for lower durability carbon removal, and another time for high durability carbon removal. Charts like the one above would have different price ranges for different purchase types. 

This would yield price ranges that offer a quantitative look at how much the value that a customer feels derives into a specific price that a supplier would charge. Then, suppliers would be able to focus on cost targets to become profitable and support their growth – and ability to satisfy the wants of new customers for their products.

The move from cost-based pricing to value-based pricing for CDR credits is just in its infancy, as many early stage technologies are just now starting to move down the internal cost curve. As internal costs decline in future years, startups can drive value by discovering a price point in line with what the customer’s willingness to pay will be, rather than purely to break even on operational costs. Even in the current market, CDR credit supply companies can learn a wealth of knowledge about building a value proposition story that unlocks a customer through offering additional benefits or driving home the message about the quality of carbon removal credits. And in doing so build sustainable businesses that use voluntary carbon markets to drive impact for the customers they serve as well as for the climate.

What do you think? Let me know here

Jason Grillo is a Co-Founder of AirMiners. The opinions expressed in this writing are the author’s own and do not reflect the position of any employer.

Free CDR Career Advice! – Climagination with Jason Grillo

TL;DR working to find a job in carbon removal can be hard work itself – some advice below on how to find the right team fit.

Photo by fauxels: https://www.pexels.com/photo/photo-of-people-holding-each-other-s-hands-3184433/

“Knowing yourself is the beginning of all wisdom” – Aristotle

Part of my dream for the carbon removal industry is a future where many thousands of people find gainful, meaningful employment for work to remove the legacy of excess greenhouse gas. For that vision to become reality – removing the first one billion tons before we believe it is possible today – requires a workforce that is educated, trained, and well-matched for the CDR jobs of the future.

To that end, through the people I’ve been lucky to meet in the carbon removal industry, I’ve been asked quite a bit about how to find a job in CDR. When welcoming new folks into AirMiners, the question of how to find a job is probably the topic most on the minds of those who are new to our community. That’s why in AirMiners we’ve done  two  events ( about this topic – Heidi Lim in particular has some excellent (and oft-cited advice) here.

One pillar of this is: how much can I expect to earn in carbon removal? And that data has been difficult to find. That is, until today with the release of an excellent global salary report created by the CDRJobs.earth team led by Sebastian Manhart.

Building on that hope for finding a job that inspires the best of you is why I’m writing this for you as a CDR job-seeking reader: to help you save time by asking three questions of yourself, about what makes you most effective to direct your efforts to fruitful career goals. 

Please note that these self-revealing questions constitute my own personal advice, and your own results may vary.

First, what is your one functional superpower that you bring to the table when approaching a carbon removal company? To be blunt: what is the one thing that you could do immediately in a new role without any on-the-job training? 

‘Functional expertise’ could be marketing campaign creation, operations or program management, corporate financial expertise, or any one of a wide variety of technical skills. And what concrete results have you driven in executing on this skill? In business school my classmates and I practiced the STAR framework to handle interviews: Situations,Tasks, Actions, and Results. What was the Situation you found yourself in, what Tasks were before you to achieve, what were your Actions to attain that goal, and what were the Results you ultimately arrived at. Quantifying those results is especially important: “I developed R or Python to research and analyze X number of deep datasets” “Our marketing campaigns achieved a 200% ROI!” / “We delivered this $5M project ahead of schedule and below budget” marks the success that attracts interest.

Not to discount passion – which is important – but a Grade ‘A’ record of performance plus passion is a compelling story. At the time of this writing, our industry is still in an early enough stage that top functional expertise from different industries will find a ready-made home. Not many have been in CDR for more than five years (myself included!), so bringing a strong transferable set of skills is by far the best way to build a compelling narrative to land a new role.

Second, what type of carbon removal do you like best? 

There are a wide – and I mean wide – variety of CDR methods on offer in these early years of the carbon removal industry. The trick is to figure  out which type of CDR suits your skills and interests – as soon as you can – which makes career searching in CDR  much easier. That way as a job seeker you can home in on how the superpower identified above can be useful in, say, marine CDR, Direct Air Capture, biochar, enhanced rock weathering, Measurement/Reporting/Verification, or any other type of carbon removal technology that provides meaning to you.¹

Carbon removal is a new enough industry that you as a job seeker can ask yourself what sparks your interest in a particular method of carbon removal. What is it about that method that makes you like it more than others, at a high level? If you don’t have that perspective, fortunately AirMiners own BootUp program² provides such an entry point, offering a broad overview of state-of-the-art CDR methods over the course of several weeks.

Most importantly get out and talk to people who are starting up these organizations! Find them on LinkedIn, at networking events, even (gasp) in our main AirMiners community or elsewhere. Ask yourself whether you can envision you working at the type of jobs for people in that method of CDR is a good fit.

Third question: what size organization would you like to work at? The landscape of carbon removal is very much the landscape of startups, though the term ‘startup’ covers a lot of ground in terms of risk and reward. Maybe you are a founder of a company. Maybe you are Employee Number 5, or Number 25, or Number 125 – all of those are new, small STARTUP businesses, with a high degree of risk around technological approach or business model. 

The real introspection to work on is: “in what environment am I most effective at driving results?” Will your 1 or 2 skills from Question 1 above be best unleashed with structure and resources? Or with freedom and latitude without as much to fall back on? Every person has different preferences – and prefers things at different points of their career, especially when factoring for personal and family needs.

The larger a company, even along the more differentiated a role tends to be, and possibly the more hierarchical. Smaller organizations tend to be flatter, favoring those who consider themselves generalists. Plus, compensation – especially for pre-revenue companies – would be more for equity rather than cash. 

Different people in a similar situation could pursue widely varied pathways. For example a recent graduate might want to develop the one functional skill that they know they want to fulfill throughout the next several years of their career, then climb a career ladder or switch companies. Or another recent graduate would say ‘nah, I need my space’ and found a startup or two (or three) in their first years in industry. Knowing yourself and where your talents may best take root – that’s the essence of how to start a job search.

And an added bonus question: How effective might you be in a remote vs. hybrid vs. in-office work environment? The COVID pandemic led to the rise of remote work, with some reversal of that trend in recent years. Fortunately many CDR companies – including small startups – are willing to take a risk and seek talent from a truly global pool rather than limit themselves to a particular geography. 

This post started off with the goal of developing a professional workforce in carbon removal; my hope is that you as a job seeking reader find the career journey a bit easier by asking questions of yourself to guide your job search in a new and growing field. 

Thanks for reading, and wishing you good job hunting!

 

Jason Grillo is a Co-Founder of AirMiners. The opinions expressed in this writing are the author’s own and do not reflect the position of any employer.

Mind the CDR Gap – Climagination with Jason Grillo

 

TL;DR: A gap exists between where we are and where we need to be in carbon removal by 2030, but with the right factors in play we can overcome it sooner than anyone thinks is possible today.

Hi there! 

Summertime travels are wonderful – the result of oftentimes weeks of planning for where you’re going and how to get there. In the carbon removal industry, we’re moving forward to a destination where gigatons of excess greenhouse gases are removed from the atmosphere.  “NetZero by 2050” is certainly an admirable target – we need to understand where the industry needs to get to by midcentury.

As much as future projections focus on 2050 goals, they can seem, well, a bit distant: nowhere near as much emphasis has been placed on what an interim 2030 goal might look like. And that’s an important goal because we can know now whether or not we are on track, and take actions if needed to meet an end-of-2030 target. A specific, measurable, achievable, relevant, and time-bound goal – 6 years away at the time of this writing – can inspire action today which can make that midcentury vision a reality.

That’s why I’m writing today about what might be 2030 interim CDR milestones for climate goals, a gap in where we might be, and a path forward to tackle that. 

To do this I’m going to outline a target, then use publicly available data sources of leading novel CDR methods to extrapolate a portfolio of projections to 2030. As defined in the State of CDR 2nd Edition report, “Novel” CDR includes DAC, BECCS, Biochar, Enhanced Rock Weathering, and marine CDR methods. 

Fair warning: this analysis includes many assumptions about future growth of various CDR sectors – and I very much welcome your scrutiny and constructive critical eyes. So please, comment away using the link at the end of this post!

 

What does a 2030 target look like?

To start off, let’s characterize the 2030 destination.

Fortunately, the aforementioned State of CDR report, 2nd Edition offers an excellent starting point. I’m presenting two scenarios outlined in Chapter 3 of that report: one where our climate settles on 1.5 degrees C without overshoot, and one with overshoot. The data for this comes from the data resources accompanying the report – again, publicly available, and free of charge!

The State of CDR team made multiple estimates, with a median of 260 Megatons of atmospheric CO2 to be removed in the year 2030 for the climate to be on track with the scenario of 1.5 degrees of warming without overshoot, and 70 Megatons with overshoot. 

Data sourced from State of CDR report, 2nd Ed, June 2024

Others have speculated that the 1.5C number requires as low as 190 Megatons; additionally or as high as 285 megatons. For the purposes of our gap conversation, I’m comfortable to stay with 260 megatons for a 1.5 degrees Celsius result without overshoot.

 

Where will the 2030 Megatons come from?

The short answer: everywhere! All solutions are on the table; a portfolio of approaches – some of which are not delivering tonnage yet – are going to contribute to getting to the result. To forecast what a 2030 scenario might look like I’m going to use some existing estimates here from citable sources, and also create some projections of my own based on growth assumptions.

 

Contributions by DAC and BECCS in 2030 

know that Microsoft and Frontier in particular have gone quite deep in funding new BECCS projects, particularly in Scandinavia. The State of CDR Report Chapter 3 has an excellent chart (below) based on companies’ announced plans to build and deploy BECCS and DAC capacity through 2030. BECCS in particular is indicated to have a capacity of ~20 MT in 2025, rising to ~60 MT by 2030; DAC in 2030 is also projected to be 60 MT, for a 120 MT total between these two methods.

 

Some caveats: this likely reflects the facilities’ nameplate capacity, so actual tonnage removed – might not perform as well. 

Second, as with all company estimates, delayed and canceled project deployments may diminish future results. 

Contributions by Biochar in 2030  

Per CDR.FYI we know that Biochar is delivering the vast majority of CDR tonnage today and is selling well now, and is poised to grow in future years. By how much is an open question. For the 2030 estimate, I am going to assume linear growth of tons of biochar produced based on the 2023 Market estimates from the International Biochar Initiative/US Biochar Initiative 2023 Global Market report

Growing from ~96,000 tons to ~352,000 tons represents a 3.6x increase in physical char produced over two years from 2021 to 2023. Assuming this trend of linear growth continues, then in the year 2030, 31 million tons of biochar worldwide would be produced. And since one ton of biochar contains ~2.8 tons of CO2 (source: 2023/24 European Biochar Market report), that figure represents approximately 87 million tons of CO2 stored in the year 2030.

Note that this figure is the tons of physical biochar produced rather than the quantity of registered carbon credits from them – regardless of whether a biochar producer is selling credits, the physical char stores embodied carbon and represents carbon removed from the atmosphere. Adapting a phrase, if a tree gets pyrolyzed in a forest, and nobody registers the credit, it still does reflect removed carbon (and yes will probably make a sound 😉).

Contributions by Enhanced Rock Weathering in 2030

For ERW, the data are a bit more scant, though the Boston Consulting Group offers insights from their 2023 report on carbon removal. With a forecast that 33 megatons will be removed by the entire CDR industry in 2030, 9% of which is ERW, BCG’s result is that ~3 Megatons of CDR will be achieved by enhanced weathering in that year.

That said, I offer that there could be some upside to this – weathering rates and CO2 uptake rates are still under research. And it is possible that deployments may outpace estimates as of now.

The estimated gap

The sum total of those four methods that we have credible 2030 estimates for is 204 megatons to be removed in that year, leaving a gap of 56 megatons to be fulfilled by other methods or by outpacing the projected trajectories of the methods mentioned above.

How to make up a gap? 

  1. Bring additional methods to scale.

Marine CDR in 2030 could contribute to reducing the gap mentioned above, however it is challenging to estimate since most startups are not (yet!) reaching volume at the time of this writing. However, I agree that a suite of marine solutions could be enough to fill the gap (and more on that below) however, projecting into the future is a challenge.

Fundamental research now in mCDR would set the stage for significant deliveries to take place in the year 2030 – particularly for Ocean Alkalinity Enhancement, or macroalgae sinking. BCG suggests a 100Mt in 2050 figure across all ocean methods, rather than offer a 2030 estimate.

Biomass burial and storage is also just now starting to gain a foothold, with over 180,000 tons sold and over 3,000 tons delivered at the time of this writing per CDR.FYI. This solution is scaling rapidly. Assuming that 75% of the 180k tons sold to date are delivered in 2024, and this grows at the same rate as biochar 3.6x every two years (yes, a big IF), then burial solutions would contribute 3M in 2030. 

 

2. Keep pushing to outpace the estimate of the four methods that I included above (BECCS, DAC, Biochar, and ERW). Growing any field of carbon removal is not inevitable, but rather the result of people researching, deploying, and learning how to efficiently advance the practice of removing excess atmospheric greenhouse gas. The ability to advance faster than forecasts is not fanciful – but happening for key climate technologies already. 

It is my belief that carbon removal can model the systemic adaptations present in these industries – innovations in financing, policy advancements, improved social license to operate through awareness and endorsement – leading to deployment and expansion beyond linear estimates. 

In other words, we can close the carbon removal gap – and despite the many challenges that carbon removal faces, that can happen sooner than anyone thinks today.

 

-Jason Grillo is a Co-Founder of AirMiners. Opinions expressed here are the author’s own and do not represent the position of any employer.

Engaging Communities on Ocean Alkalinity Enhancement: Insights from Two Workshops in Sequim, Washington

Authored by Giulia Belotti, Research Fellow at the Institute for Responsible Carbon Removal and Sara Nawaz, Director of Research at the Institute for Responsible Carbon Removal

Hurricane Ridge, Olympic National Park. Credits: Doug Kerr/Flickr

Marine carbon dioxide removal is moving from the lab into the world. Now, the enterprise is no longer an abstraction, but is becoming real for the communities where field tests are being conducted and larger deployments are being planned. Against this backdrop, the need for meaningful, robust, and replicable mechanisms for community engagement and input are becoming more pressing and urgent.

We report here on a recent set of workshops that we designed and hosted in Sequim, in Washington State. We describe an innovative approach to engaging community members in (m)CDR, designed to showcase best practices for future engagement efforts. Additionally, we outline the key questions and actionable insights that emerged from the meetings. Most notably, community members expressed a strong willingness to learn more about the technology and its implications for development in the region. However, they also raised significant concerns and reservations across various aspects of (m)CDR, including but not limited to social, ecological, and political dimensions. These concerns underscore the importance of engaging local communities in ongoing (m)CDR research and future deployment efforts.  

Our team at the Institute for Responsible Carbon Removal is leading on other community engagement efforts in Washington State and elsewhere. We welcome feedback on our process and findings. Please be in touch with Sara Nawaz [snawaz@american.edu] and Giulia Belotti [gbelotti@mail.ubc.ca] with any feedback. 

The Setting

Located on the northern edge of Washington State’s Olympic Peninsula, Port Angeles is nestled between the Pacific Ocean and the wilderness of Olympic National Park. Home to about 20,000 residents, it is the largest town on the Peninsula.

Port Angeles sunrise. Credit: Anupam Ts/Flickr

In this unique setting, California startup Ebb Carbon is proposing “Project Macoma.” Project Macoma will use ocean alkalinity enhancement (OAE), a marine carbon dioxide removal (m)CDR) process, to draw CO2 from the atmosphere. OAE involves adding alkalinity to the ocean, which triggers chemical reactions that convert dissolved CO2 into bicarbonate and carbonate molecules, ultimately allowing the ocean to absorb more CO2 from the atmosphere. Alkalinity can be added either by spreading ground minerals like olivine or lime into the ocean, or through an electrochemical process that splits seawater into acidic and alkaline streams. Project Macoma will use the latter method. Seawater will be pumped into a series of tanks, treated to become less acidic, and then returned to the ocean, where it will combine with CO2 to form bicarbonate.

This isn’t Ebb Carbon’s first project in the region. The startup is already testing the technology at the Pacific Northwest National Laboratory (PNNL) in nearby Sequim, though on a smaller and more contained scale. Partnering with the Pacific Marine Environmental Laboratory, PNNL, and the University of Washington, Ebb Carbon is drawing water from Sequim Bay, splitting it into acidic and alkaline streams, and using most of it for further experiments before releasing it back into the Bay. Project Macoma aims to take this process a step further, by testing the process at a larger scale.

Community engagement: the missing piece of CDR research

Interest in novel mCDR approaches like OAE is rapidly growing among the scientific community and policymakers. However, so far focus has largely been on technical feasibility and natural science aspects of the technology, with community engagement sidelined or delayed.

Yet, social engagement is essential at every stage of a CDR initiative, especially since this field is still emerging. Involving communities early on should not be aimed at gaining public buy-in – it is a vital step toward ensuring equity and justice. Understanding who stands to benefit and who might be adversely affected by mCDR must be a primary goal of any engagement effort. Moreover, a well-informed community is better equipped to make decisions about how, or even if, CDR technologies should be implemented in their region. Ultimately, this approach shifts the process from being a top-down imposition to one where communities actively co-produce knowledge and help shape the development of these technologies. This can help engender community support for projects and often contributes to more thoughtful design.

In other words, meaningful social engagement goes beyond simply presenting a project to the public and asking for feedback. For mCDR initiatives, engagement must fully capture the complexity of the technology and ensure that community concerns and priorities are genuinely integrated into its development. Even well-meaning stakeholders can struggle with how to achieve this.

Recognizing this challenge, our research team at the Institute for Responsible Carbon Removal at American University is committed to fostering more participatory and deliberative approaches in (m)CDR research. As part of this broader commitment, we organized two engagement workshops in the Sequim region. These workshops aimed to showcase best practices for initiating meaningful community engagement on mCDR, with a particular focus on OAE. Dr. Sara Nawaz, the Institute’s Director of Research, received funding for this research from ClimateWorks Foundation.

What did we do?

On June 4 and 5, 2024, we hosted two day-long community engagement workshops on mCDR in Sequim, Washington. With the trial projects discussed above on the horizon, this region could become a significant site for large-scale OAE deployment in the future, by Ebb and other companies looking to leverage the favorable local environmental conditions. Engaging communities at this early stage is essential to ensuring that local voices are heard and considered.

Over the course of these two days, 38 participants representing a diverse range of affiliations joined the workshops. Attendees included staff from environmental non-governmental organizations, Tribes, recreational groups, shellfish farms, marine resource management committees, local government, and educational institutions.

The workshops began with a foundational introduction to CDR, aimed at helping participants become more familiar with the existing landscape of these technologies. Following this, we introduced information about OAE, offering insights into the current state and potential of this particular approach. After each presentation, we made sure to give participants plenty of time to ask questions, share their curiosities, and voice any comments. We also encouraged them to share the first things that came to mind – whether images, thoughts, or associations – when thinking about CDR and OAE. A colleague from Ocean Networks Canada, Dr. Kohen Bauer, served as the technical expert for the workshops, providing detailed information on mCDR and OAE and answering participants’ numerous questions.

Throughout the discussions, we maintained transparency about the state of knowledge of OAE, including its potential unintended consequences and broader implications. Importantly, we were clear about our role as independent researchers, emphasizing that this work is not being conducted on behalf of Ebb Carbon or any other CDR company.

Following the presentations, participants were guided through two interactive activities designed to deepen their understanding of the complexities associated with OAE. The first was a “best-case and worst-case scenario” exercise, where participants were prompted to write down their hopes and concerns about OAE deployment in the region. Using sticky notes, they captured their thoughts, ranging from environmental benefits to potential social impacts, which were then shared and discussed collectively.

The second activity was a scenario-based exercise that divided participants into four groups. Each group was assigned a unique scenario, presenting different contexts for OAE deployment, including variations in political climate, climate change status, governance and funding structures, and potential ecosystem and community impacts. Groups rotated to explore all scenarios, discussing the elements they found most promising, the challenges they foresaw, and how realistic they considered each scenario. This dynamic process allowed participants, many of whom were new to OAE and, more in general, CDR technologies, to engage critically with the issues, fostering informed opinions and preferences about the future of these technologies.

What did we find?

Our initial observations from the workshops reveal that participants are generally open to learning more about (m)CDR and are eager to be involved from the early stages. However, while participants appreciated the information shared, many expressed a need to better visualize the scale of mCDR efforts to fully grasp how much CO2 removal is required to meet climate goals and what this entails in practice. For instance, many confessed that it was difficult for them to picture how their region would look if mCDR were implemented on a large scale. Therefore, they suggested the incorporation of slides that visually demonstrate such impacts in future presentations, or using metaphors to better convey specific quantities. This aspect was especially crucial for participants, especially when it came to understanding the operational chain of OAE. Concerns were raised regarding the potential creation of a new industry, as well as the amount of resources extracted, energy consumed, and emissions associated with these efforts.

How mCDR is implemented emerged as a key concern. Participants stressed the importance of involving communities throughout the process and showed a clear preference for government- and community-owned projects. There was significant skepticism about private corporations, particularly those connected to the fossil fuel industry, due to fears that these entities might use carbon removal technologies as a way to avoid more ambitious emissions reductions. Linked to this, the status of climate change mitigation emerged as a crucial consideration. Participants emphasized that mitigation efforts should be prioritized, viewing mCDR as a complementary component within a broader array of solutions. Discussions frequently centered on the potential trade-offs that communities would inevitably have to face in a future characterized by climate change. There was a strong recognition that decisions about what can be sacrificed or justified in the context of climate action will likely evolve as the crisis progresses.

Participants also highlighted the necessity for a transparent and open Monitoring, Reporting, and Verification (MRV) process, ideally managed by an independent entity, but potentially supported by local groups of citizen scientists. This underscores the importance of keeping communities actively involved as these technologies are scaled up, ensuring that their evolving concerns and insights are integrated throughout the process.

Moving CDR research and development towards more participation and deliberation

The workshops conducted in Sequim mark an important first step in establishing best practices for community engagement in mCDR research and development. More importantly, they represent the beginning of what we hope will be an ongoing relationship and collaboration with the local community. As OAE technology progresses from trial phases to larger-scale deployment, our goal as a research Institute is to continue deepening this engagement, fostering not only broader participation but also moving towards meaningful deliberation.

Carbon Removal in California: Striving Toward Environmental Justice in the Central Valley

Authored by Jake Ferrell, Carbon Justice Fellow at the National Wildlife  Federation & Audrey Alonso, Digital Organizer at Our Climate

Orchard in California's Central Valley.

Orchard in California’s Central Valley. Credit: Ian Abbott/Flickr

Crops, cattle farms, and oil wells. Look out over the landscapes of Kern County, California, and you can find the physical infrastructure of various industries. The latest industry poised to shape Kern County landscapes is carbon dioxide removal.

California appears set to become a national leader in carbon dioxide removal (CDR)a climate strategy that removes CO2 directly from the ambient air and sequesters it in a form where it is prevented from re-entering the atmosphere. CDR addresses the climate crisis by targeting excess atmospheric CO2, a result of societal industrialization, and can range from natural solutions like reforestation to more technological processes like direct air capture (DAC).

Carbon Removal Projects in California Receive Federal Support

When the Department of Energy (DOE) announced the first round of awardees for its $3.5 billion Direct Air Capture Hubs (DAC Hubs) program in August 2023, no fewer than four projects in California were selected, the most of any one state. The most advanced project, led by a subsidiary of fossil fuel company California Resources Corporation, will receive up to $11.8 million to conduct a Front End Engineering Design (FEED) study to explore the potential for a DAC hub in Kern County, California.

The other threeled by Aera Energy, Chevron, and the University of Californiawill receive up to $3 million each to explore the feasibility of their proposed projects. All projects are located in the southern part of California’s Central Valley, in and around Bakersfield and Kern County.

What Goes On in the Central Valley?

Oil and gas production in California. Credit: John Ciccarelli, BLM

The Central Valley is no stranger to economic sectors of national importance. According to the U.S. Geological Survey, the Central Valley is among the main agricultural regions in the U.S., producing a quarter of the nation’s food, including 40% of the fruits and nuts consumed. Alongside agriculture, fossil fuel extraction dominates the landscape.

In 2019, Kern County was the leading oil producing county in the state, and the seventh largest in the country. While these industries helped build a city like Bakersfield into what it is today, participants at a carbon removal workshop convened earlier this year in Bakersfield, were quick to point out the environmental degradation and human health consequences those same industries have brought with them.

Though these consequences impact nearly all residents of Bakersfield and the broader Central Valley, the burden falls especially on low-income communities and communities of color. Bakersfield, a city of over 400,000 people, is located 100 miles northeast of Los Angeles. Census data shows around half of the residents identify as Latinx, 7% Black, 7% Asian, and around 30% as white (these numbers may not be fully representative of the population, due to Kern’s large population of undocumented people). More than 16% of county residents live below the poverty line.

The CDR spotlight shines so brightly on the Central Valley because its landscape fits the criteria set forth by Congress guiding DOE’s selection process, including: access to geological storage reservoirs for CO2ongoing economic reliance on the fossil fuel industry, proximity to low-carbon electricity sources, and location as an economic opportunity zone.

However, given the ongoing history of this region, the characteristics that make the Central Valley an attractive site for DAC in the federal government’s eyes are the same characteristics that may make communities in the area skeptical of DAC.

Indeed, “economic opportunity zones” refer to areas identified by the Internal Revenue Service (IRS) where developers are offered tax benefits to “spur economic growth and job creation in low-income communities” but the environmental degradation and public health consequences of the fossil industry’s boon in particular, are frequently centered by Kern residents, even if they also acknowledge the jobs that come with the industry’s presence.

Given DOE’s mandate to prioritize applications for these areas, and the mandate’s demographic overlap with vulnerable groups, it is likely that most or all of the DAC Hub locations will have large shares of BIPOC populations, along with those of low socioeconomic status. This is true of Kern County, where nearly 70% of residents are BIPOC and the average income is one third of the state’s average.

The long history of unjust infrastructure siting and legacies of environmental injustice in the United States may bolster and inform skepticism and resistance to further projects, particularly in the communities that have borne the brunt of hosting extractive industries.

Hope & Skepticism

So, how are different groups and actors in California approaching the prospect of a new carbon removal industry blossoming in the state? At the state level, California has positioned itself as a leader in developing CDR policyit is the first US state to incorporate specific quantitative targets for CDR with its latest Scoping Plan for reaching carbon neutrality, and there have been a flurry of state bills recently passed supporting CDR.

Local government officials are leading calls to bring the burgeoning carbon management industry to the Central Valley with the announcement of a Carbon Management Business Park in Kern County. Lorelai Oviatt, the director of Kern County’s Planning and Natural Resources Department, has stated that the vision is to build a massive solar farm to power DAC plants, so as to replace the county’s declining agricultural revenues due to droughts continuing to plague the Southwest. For Kern alone “at the top end this could produce $68 million a year in county property tax revenue to the county, $25 million to surrounding cities, and 23,000 jobs,” Oviatt noted. “That is hope!”

But it is not so simple. Local residents have expressed opposition to carbon capture and storage (CCS) projects in the past. Part of that opposition is centered around the fact that captured CO2 would have been used to extract more oil in a process known as enhanced oil recovery (EOR).

Today, the California Resources Corporation FEED study has expressly stated that its DAC Hub would not utilize CO2 for EOR, however Chevron and Aera Energy have not yet made statements either way. Some participants in a Bakersfield community DAC workshop signaled that Chevron or Aera Energy involvement in a project would be a red line for them.

“Chevron and Aera Energy own this town,” stated one participant, and other participants agreed that they did not always trust local elected officials to support the needs of the community over industry. Workshop participants were frustrated that fenceline communities like theirs always seemed to be the first choice for new industrial projects, and voiced skepticism over whether DAC would be any different from past projects that did not pursue a caring relationship with the community.

Climate Change in the Central Valley

California’s Central Valley is experiencing extreme heat in the summer months. Credit: Flickr/Eric Sonstroem

Anyone who lives in or has experienced the summer months in the Central Valley likely knows firsthand the extreme heat faced by residents every year, and how it is only projected to get hotter. “By midcentury, the Central Valley is projected to experience average heat-health events that are two weeks longer” states a Summary of Projected Climate Change Impacts on California.

Experiencing 90° F October days is already a common event for those living in the Valley. Alongside extreme heat, there is also the aforementioned drought. Audrey Alonso, an NWF-American University Carbon Removal Justice Fellow was born and raised in the Central Valley, and personally remembers learning how to deal with drought as a kid and has maintained those water-conserving lessons to this day.

The Central Valley depends on a functioning irrigation system to maintain arable land, and droughts have put a massive strain on many households and farms in the area. The 2021 drought caused communities to incur $1.7 billion in costs, and led to the loss of over 14,000 jobs. These issues, exacerbated by climate change, are a growing problem that continue to affect the region’s agricultural production and the livelihoods that support it.

Climate change is bringing increasingly severe and frequent heat waves and droughts to Kern County; creating dusty conditionsexacerbating air quality issues, as the region consistently ranks as one of the worst in the U.S.; and threatening human health, especially that of vulnerable populations like the elderly and those who labor outside, including farmworkers.

It is important that any Kern County DAC projects acknowledge this context and refrain from becoming a burden to communities as well as limited resources they might share, like water. If they are able to do this, some argue there may be a way forward.

What if We Centered Equity and Environmental Justice?

In the community DAC workshop conducted in Bakersfield “to understand community needs, concerns, and support or opposition for a potential DAC hub in their community,” participants laid out pathways toward an equitable vision for DAC Hubs deployment.

Such a vision, they said, would need to emerge from ongoing discussions across the community, and would require rooting decision-making power firmly with community groups and local small businesses, include active involvement and oversight from the community, and work with trusted experts. Accountability, transparency, local job guarantees, and integration with the existing local economy would be paramount, and the DAC technology must be renewably powered and sensitive to the region’s water conditions.

Of all workshop participants, 75% would either strongly support or somewhat support a DAC Hub project in their community if it aligned with their equitable vision by addressing the concerns and needs they outlined, 20% of participants remained indifferent or unsure, and only 5% would oppose such a project.

This hypothetical buy-in was uniquely high across all four DAC workshops conducted, and signals a real opportunity to pursue a responsible buildout of CDR in California centering equity and environmental justice principles.

This blog is the second installment in an ongoing series examining the intersections of carbon dioxide removal and environmental justice.

The Oil & Gas Industry’s Role in CCS and CDR: International Energy Agency Conclusions

Authored by Wil Burns, Co-Director, Institute for Carbon Removal Law & Policy, American University

As part of its World Energy Outlook Special Report Series, the International Energy Agency (IEA) last week released a report that focuses on what the Agency believes the fossil fuel industry should do “to align with the Paris Agreement and with the 1.5°C goal.” Pertinent to the Institute’s work, the report includes a section (2.3.1) discussing the potential role of carbon capture and storage (CCS) within the fossil fuel sector, as well as direct air capture (DAC). While CCS is not squarely in the purview of the Institute’s work, it plays an integral role in one carbon dioxide removal approach, bioenergy and carbon capture with storage (BECCS), and the technology’s deployment will contribute to the development of conveyance and storage infrastructure relevant to the development of the direct air capture (DAC) sector.

The report contends that neither CCS or DAC can be viewed by the industry as mechanisms to “retain the status quo.” Under a business-as-usual scenario, the study concludes that oil and natural gas consumption would require an “inconceivable” 32 billion tons of CCS/DAC, including 23 billion tons of DAC to be Paris-compliant. Moreover, the study projected that this would require 26,000 terawatts of electricity generation in 2050, which would be greater than electricity demand in 2022, and $3.5 trillion in annual investments through mid-century, commensurate with the fossil fuel industry’s annual average revenue in recent years.

However, the report also emphasizes the important role that the fossil fuel industry can play in achieving Paris Agreement objectives through responsible deployment and investment in these approaches. The IEA’s World Energy Outlook 2023 study outlines a number of scenarios that reflect future potential global conditions. These include the Stated Policies Scenario (STEPS), premised on current climate policy, and commitments, the Announced Pledges Scenarios (APS), premised on the assumption that governments meet all national energy and climate targets made to date, and the Net Zero Emissions by 2050 (NZE) Scenario, which limits warming to 1.5°C.

In the APS, carbon dioxide capture grows from 45 Mt CO2 in 2022 to 440 Mt CO2 in 2030, with early action through large-scale deployment of CCS in the fossil fuel sector providing the foundation for subsequent use in other sectors where abatement is critical after 2030. This is projected to result in the global capture of 3.5 GtCO2 by 2050.

The NZE scenario requires much more aggressive carbon capture to contribute to the goal of holding temperatures to 1.5°C: 1 GtCO2 by 2030, and 6 GtCO2 by 2050, half of which is from DAC and heavy industry. This requires a whopping $500 billion of investment just through 2030. The study concludes that this daunting task requires the fossil fuel industry to go beyond conceiving carbon capture as a “social license to operate,” focusing merely on reducing Scope 1 and Scope 2 emissions from the sector. Rather, the IEA argues that the fossil fuel sector could use its “sizeable balance sheets” to leverage a competitive advantage across the broader energy economy, helping further the industry’s diversification strategies while facilitating requisite levels of CCS and CDR.

Section 2.3.1 of the report also includes an extensive analysis of the specific role of, and limitations to, deployment of DAC. On the one hand, the IEA emphasizes that countries with low-cost energy resources and ample CO2 carbon capacity could reap $60-150 billion per year if certificates for DAC sequestration are traded between $100-250 per ton/CO2. However, the study concludes that the cost of deployment, energy constraints, competition for DAC CO2 from synthetic fuel production, and constraints on annual CO2 storage capacity will limit DAC deployment. It projects that under the NZE scenario, atmospheric removal of CO2 will reach 1.7 Gt/yr. by 2050, with one-third of this achieved by DAC. The study finds this will require about $70 billion in annual investment for DAC in 2050 and approximately 500 TWh of annual electricity generation in 2050.

As is often the case with IEA reports, this one is short on specific policy prescriptions to drive the kind of investment by the fossil fuel industry that is contemplated in the study. While the study discusses some specific roles that governments are, and can, play in incentivizing CCS/CDR, it is by no means clear these will be sufficient to substantially move the needle. The suboptimal levels of investment of the fossil fuel industry to date in these technologies, given the sector’s massive contribution to greenhouse gas emissions, suggests that it may not fulfill the role contemplated by the IEA without far most aggressive demand-pull mechanisms, such as a carbon take back obligation. Hopefully, the IEA’s future reports on this sector will consider a wider array of policy options to foster a more responsible role by the fossil fuel industry.

Reershemium, et al., Initial Validation of a Soil-Based Mass-Balance Approach for Empirical Monitoring of Enhanced Rock Weathering Rates, Environmental Science & Technology (2023)

Literature Review Series

Authored by Wil Burns, Co-Director, Institute for Carbon Removal Law & Policy, American University

There is growing interest in enhanced rock weathering (ERW) as a potentially important component of a carbon dioxide removal portfolio. Recent studies project that large-scale application of pulverized silicate rocks, such as olivine, basalt, or wollastonite, to croplands could effectuate atmospheric carbon dioxide removal of 0.5-4 gigatons annually by 2100. However, one of the most imposing barriers to scaling ERW as a climate response mechanism is the difficulty of monitoring and verifying carbon sequestration.

A new study in the journal Environmental Science & Technology tries to help address this issue. The study introduces a new tool to monitor and verify ERW sequestration. The approach seeks to measure differences in concentrations of ERW feedstock pre- and post-weathering by comparing concentrations of mineral-bound metal cations before and after feedstock deployment. More specifically, the approach, which is referred to as “TiCAT,” seeks to estimate the total loss of cations from the solid phase of soil samples vis-à-vis a titanium tracer. The researchers contend that this mass-balance approach can help us estimate the time-integrated amount of weathering of a silicate mineral, basalt in this study, within a given soil profile. The TiCAT approach was initially assessed through a laboratory mesocosm experiment that measured the concentration of reaction products in soils and leachate solution pools.

The researchers concluded that the TiCAT process accurately estimated initial CDR within the standard error or means of results from the more conventional method used to calculate weathering and initial CDR in mesocosm experiments. This suggests that “it can yield an accurate and robust estimate of initial CDR in enhanced weathering systems.” This could be a significant breakthrough, because prior methods of estimating ERW, especially those reliant on measuring quantities and transport of weathering reaction products, pose barriers to scaling given their time and labor intensiveness. Moreover, this approach could “directly integrate into existing agronomic practices,” as samples from the uppermost layer of soils are routinely taken for nutrient and soil pH analysis.

However, the authors of the study also proffer a number of caveats in terms of their findings, including the following:

    • The estimates from this approach are only an initial value, subject to potential leakage of initially captured carbon as it’s transported an alkalinity and dissolved inorganic carbon from soil to the oceans;
    • The variable lag time between feedstock dissolution and the capture of carbon dioxide needs to be taken into account in accurately assessing CDR;
    • As a next step, it needs to be established the approach can scale weathering rates from discrete sampling points to larger systems;
    • There may be site-specific conditions in some settings that would preclude accurate use of this approach, such as areas with high levels of physical erosion or where feedstocks with chemical conditions similar to those in the soils are applied.

As Mercer recently noted, robust monitoring, reporting and verification (MRV) of greenhouse gas removal approaches is a “market shaper” that can address a market failure that may preclude scaling of many options. Moreover, it’s critical to engender public acceptance and trust. While not as sexy as images of the construction of new CDR facilities, research of this nature needs to be front and center in our consideration.

DOE FECM should fund public and community organizations to lead on responsible carbon management

Authored by Dr. Sara Nawaz, Celina Scott-Buechler and Dr. Holly Caggiano

In August 2023, the Department of Energy’s Office of Fossil Energy and Carbon Management (DOE FECM) unveiled its Notice of Intent (NOI) and Request for Information (RFI) regarding the launch of a Responsible Carbon Management Initiative. The primary purpose of this announcement was to notify interested parties of the department’s intentions and to encourage project developers and industry stakeholders to prioritize safety, environmental stewardship, accountability, community engagement, and societal benefits in carbon management projects.

To engage stakeholders and gather input, DOE FECM sought responses to a set of questions, particularly focusing on the draft Principles for Responsible Carbon Management Projects and the broader initiative. Responding to this call for input, Dr. Sara Nawaz, the Institute’s Director of Research, collaborated with Dr. Holly Caggiano from the University of British Columbia and Celina Scott-Buechler from Stanford University to share feedback on the draft Principles.

Their response highlighted the need for an important reconfiguration of DOE’s approach to responsible carbon management. Instead of treating ‘responsibility’ as something that individual developers should lead on and be supported in, the response argued for the need for DOE to support and fund democratic institutions and communities to better participate in decision-making about carbon removal.

Moreover, the response suggests the need for an autonomous, publicly funded entity to lead public engagement and participation processes. This entity would ensure that public and community views, concerns, and values are central to national, regional, and local planning for carbon management. These kind of independent public engagement processes have been demonstrated to improve public acceptance and social license, and to help in planning low-carbon transitions.

The response recommended a two-fold approach for DOE FECM:

    1. It suggests identifying and allocating funding to community organizations that are beginning to address issues of environmental justice, Tribal consultation, and more in carbon management. These funds would support community-led exploration of socially viable pathways for carbon management at the regional level.
    2. It proposes funding the scoping of an independent agency to lead governance and public co-creation of carbon management initiatives, with a focus on community participatory methods.

You can find a version of their full response below:

We commend the Department of Energy’s Office of Fossil Energy and Carbon Management (DOE FECM) for its commitment to exploring responsible carbon management. Approaching this topic via a set of Principles is a useful starting point, but as we will assert in this response, the current formulation of this RFI and these Principles offers only limited potential to meet the goal of responsible management. As we understand the RFI, it suggests that DOE FECM’s goal with a Responsible Carbon Management Initiative is to support [private] project developers in adequately meeting the Principles; it suggests that, in Phase 2, there will be a FOA that “would provide resources to support project developers seeking to meet the Principles or other aspects of this effort (including increasing transparency or third-party verification)”.

As written, the Principles appear to empower the private sector to lead emerging carbon management efforts. We urge that FECM reconsider this approach to carbon management. A socially and environmentally responsible carbon management regime is best led by our democratic institutions and the communities that have been, and will continue to be, most impacted by carbon-intensive industries.

Public and community leadership and ownership must be at the heart of DOE efforts on carbon management—and this initiative provides a unique opportunity to do so. If retooled to imagine carbon management as a public good, this flagship approach would empower government and community organizations to develop strategies tailored to local needs while developing ambitious long-term goals and the institutions necessary to meet them. A handful of local governments are already doing this through the 4 Corners Carbon Coalition. Another example of community-centered, and ultimately community-owned, carbon management project is the CALDAC DAC Hubs application. While we recognize the appeal of a private enterprise that can move faster and more nimbly than the government is sometimes able to do, we as social scientists must stress the importance of building social license and effective governance in any new industry. Given carbon management’s growing importance to meeting global climate goals—and the many examples of misuse of carbon management as a greenwashing tactic—the societal stakes of a successful industry are high. Like other forms of waste management in the U.S., carbon management should primarily be treated as a public project. This is further justified by the significant public funds that have been allocated to carbon management to date. Treating carbon removal as a public project

In addition to conceptualizing the carbon management industry as a public undertaking necessitating public control, we would further argue that a community-driven approach is needed over the proponent-led model implicit in this RFI. Developers of carbon management projects certainly need support in working towards more responsible deployment at the project level, but they are not the only group that do, nor are they the group with the greatest need for support. In fact, there are limits to what ‘developers’ alone can accomplish in working towards the goal of responsible deployment. To ensure adequate attention to the Principles (particularly on community engagement, environmental justice, Tribal consultation, workforce development and quality jobs, but also others), it will be crucial that community groups (e.g., Tribal, environmental justice, labor, and general public community groups) are supported in engaging with developers regarding potential projects and broader carbon management initiatives in their local areas.

There are a few reasons why these groups are well-positioned to support the implementation of responsible carbon management initiatives, and why DOE FECM should actively focus its attention and support on these important public and community groups. Despite holding crucial local knowledge, these groups often lack access to the conversations, options, and technical understandings of trade-offs that would help them make informed decisions about if, how, when, and where potential carbon management projects might benefit their communities. When developers lead the agenda on these topics, communities tend to enter the conversation later—yet, early participation is essential for effective community engagement and positive outcomes for environmental justice communities, workforces, and overall project acceptance and success. Beginning the conversation early means that communities can shape priorities from a project’s inception, rather than responsively negotiating at a table that has already been laid. When developers lead the conversation, communities are less likely to be offered the full range of possible options available to them, as developers tend to focus on options that they hope to implement, excluding other options (for decarbonization, community benefits, etc.) that might also exist.

As such, there is an urgent need for public engagement and participation processes that are shepherded and led by independent groups separate from developers—both to determine the scope and governance of carbon management nationally as well as to determine mechanisms for empowering communities to lead carbon management projects. DOE FECM should take steps towards establishing such an autonomous public entity that can ensure that public and community views, concerns and values are centered in national planning for carbon management and the production and ownership of individual projects.

 A key value of such a group would be the impartiality that such independent third-party actors bring. Precedents for such independent public participation bodies have been developed for environment and megaproject sectors in the Netherlands, Denmark, Canada, Italy, the UK, and France, with the most long-standing in Quebec and France. In France, a public entity that does public engagement (the National Commission for Public Debate, or Commission Nationale du Débat Public, CNDP) is designed to facilitate early public participation in potential environmental projects, so that participation occurs when it is still possible to substantially modify terms of projects. As such, the CNDP has the potential to meaningfully improve projects and generate social acceptance; of 101 public debates, 296 consultations, and 31 consultancy and expertise missions that the CNDP has facilitated in the last 25 years, only 3 projects were abandoned following public debate, 58% of projects saw design modifications, and all saw changes to their governance procedures.

Germany’s regional coal workforce transition also offers insights into how to ensure that carbon management is developed to facilitate a just transition. Beginning in the 1980s, Germany began a multi-decade community engagement process, acknowledging that a just transition away from coal must be a participatory process involving workers, industry and governments.” Since then, municipal governments have implemented a regional-level approach that relies heavily on participation—an approach that has been much more successful than its previous top-down approach with minimal public participation. Forms of engagement and participation used have included multi-stakeholder commissions (to advise on intervention design and oversee implementation), and multi-stakeholder conferences (to create local dialogues about regional needs and possibilities), and grant committees (to select projects for funding). Much of this has occurred at the local level, where the federal government transferred resources to local governments for them to oversee these participatory processes; such a transfer of resources to local governments was found to reduce coordination problems across policy levels, facilitating the efficacy of this transition away from coal.

From the German coal transition example, we see (1) the importance of conducting participation not just in relation to specific projects, but on broader sectoral transition and how it should unfold. We also see (2) that government-facilitated participation processes enable solutions that are targeted and adapted to local contexts and generate higher levels of acceptance. Both of these lessons will be relevant for carbon removal and carbon management, which needs to grow exponentially as a sector in the coming years and decades, and which will vary in form depending on the geographic regions in which they are conducted.

How can DOE FECM begin to incorporate these insights into its work? We propose that, instead of funneling its limited resources to developers, a better approach to responsible development by DOE FECM might involve the following:

    1. Identifying and allocating funding to a set of community organizations that are beginning to give attention to issues of environmental justice, Tribal consultation (and consent), etc. on carbon management. Funding would support these groups in leading initial exploration of socially viable pathways for carbon management at the regional level while considering the broader role and scope of carbon management in climate action. Redirecting resources directly to community organizations and facilitating these groups in leading on engagement activities would provide a strong pathway for DOE FECM to work towards its goals of “the highest levels of safety, environmental stewardship, accountability, community engagement, and societal benefits in carbon management projects”.
    2. Funding the scoping of an independent agency that might be chartered to lead governance of and public co-creation of carbon management (with attention to the many other issues covered in these Principles). Such a body might be deployed at regional levels to provide independent insights into community carbon management priorities through community participatory methods and inform the development of carbon management initiatives. Given the existing precedent for autonomous public entities to facilitate robust and sustained community engagement, we suggest that such an entity would be well-positioned to equitably and effectively facilitate the development of a Responsible Carbon Management Initiative.