Over the weekend the Washington Spectator published my essay, Diary of a Transit Miracle, recounting the arduous march of NYC congestion pricing from a gleam in a trio of prominent New Yorkers’ eyes at the end of the 1960s, to the verge of startup at the upcoming stroke of midnight June 30, the startup time announced by the MTA last Friday.
Landing page for this post’s original version.
I’m cross-posting it here — the third post on the subject in this space in the past 12 months (following this in December and this post last June) — because the advent of congestion pricing in the U.S. is “a really big deal,” as a number of friends and colleagues have told me in recent weeks. As my new essay makes clear, charging motorists to drive into the heart of Manhattan isn’t just a rejection of unconstrained motordom, it’s a new beachhead in “externality pricing” — social-cost surcharging — of which carbon taxes are the ultimate form.
The essay features two governors, two mayors — one of whom I served a half-century ago as a lowly but admiring data cruncher — a civic “Walter Cronkite,” a Nobel economist, raucous transit activists, a gridlock guru and yours truly, plus a cameo appearance by Robert Moses. It includes footage of the historic 1969 press conference in which Mayor John Lindsay and two distinguished associates enunciated the core idea of using externality pricing to better balance automobiles and mass transit that animated the arduous but ultimately triumphant congestion pricing campaign.
— C.K., April 29, 2024
Diary of a Transit Miracle
A miracle is coming to New York City. Beginning on July 1, and barring a last-minute hitch, motorists will soon pay a hefty $15 to enter the southern half of Manhattan — the area bounded by the Hudson River, the East River and 60th Street.
An anticipated 15 percent or so of drivers will switch to transit, unsnarling roads within the “congestion zone” and routes leading to it. The other 80 or 90 percent will grumble but continue driving. That is by design. The toll bounty, a billion dollars a year, will finance subway enhancements like station elevators and digital signals that will increase train throughput and lure more car trips onto trains.
The result will be faster, smoother commutes, especially for car drivers and taxicab and Uber passengers, who will pay a modest surcharge of $1.25 to $2.50 per trip. Drivers of for-hire vehicles will benefit as well, as lesser gridlock leads to more fares.1
The miracle is three-fold: Winners will vastly outnumber losers; New York will be made healthier, calmer and more prosperous; and that this salutary measure is happening at all, after a half-century of setbacks.
Obstacles to congestion pricing
Congestion pricing, as the policy is known, faced formidable obstacles even beyond the difficulty inherent in asking a group of people to start forking over a billion dollars a year for something that’s always been free.
Congestion pricing also had to contend with: an ingrained pro-motoring ideology that casts any restraint on driving as a betrayal of the American Dream; a general aversion to social-cost surcharges (what economists call “externality pricing”); exasperation over the region’s balkanized and convoluted toll and transit regimes; and, of late, a decline in social solidarity and appeals to the common good.
The advent of congestion pricing in New York is, thus, cause not just for celebration but wonderment. How did this wonky yet radical idea advance to the verge of enactment?
Origins
The trail begins in the waning days of 1969, when newly re-elected mayor John Lindsay recruited two well-regarded New Yorkers to devise a plan to fend off a 50 percent rise in subway and bus fares.
William Vickrey, a Canadian transplant teaching at Columbia and a future Nobel economics laureate, was a protean theorist of externality pricing. New York-bred mediator Theodore Kheel was admired as a civic Walter Cronkite for his plain-spoken common sense.
Lindsay, too often dismissed as a lightweight, understood mass transit as key to loosening automobiles’ spreading chokehold over the city. He had made combating air pollution a pillar of his first term and was fast becoming an exemplar of urban environmentalism. From his municipal engineers, Lindsay knew that technology to clean up tailpipes still lay in the future. A transit fare hike that would add yet more vehicles to city streets imperiled his clean-air agenda.
The triumvirate proposed a suite of motorist fees to preserve the fare. Their program ― higher registration fees and gasoline taxes, a parking garage tax, doubled tolls ― though mild in today’s terms, threatened powerful bureaucracies and their auto allies. Newly dethroned “master-builder” Robert Moses opined that Kheel, in his zeal to save the fare, had “gone berserk over bridge and tunnel tolls.”2 The program went nowhere.
L to R: Kheel, Lindsay, Vickrey. Click arrow to view (please excuse two brief garbled passages toward end).
Moses was right to be alarmed. From a City Hall podium on Dec. 16, 1969, Mayor Lindsay showcased Kheel’s and Vickrey’s respective reports, “A Balanced System of Transportation is a Must” and “A Transit Fare Increase is Costly Revenue.” (Click link in still photo above to view 27-minute video.) The trio propounded a new urban doctrine rebalancing automobiles and public transportation: “Automobiles are strangling our cities… Starving mass transit imposes costs that are difficult to measure, yet real… Correcting the fiscal imbalance between transit and the automobile is key to enhancing our environment and quality of life…”
Their remarks set generations of urbanists on course toward congestion pricing.
Setbacks
Quantifying those precepts became my research agenda 40 years later. In the interim, two creditable attempts to enact congestion pricing crashed and burned.
The central element of Lindsay’s 1973 “transportation control plan” was tolls on the city’s East River bridges, a measure designed to eliminate enough traffic to satisfy federal clean-air standards. Though the plan’s formal demise didn’t come until 1977, in legislation written by liberal lawmakers from Brooklyn and Queens, the toll idea never stood a chance. Electronic tolling was 20 years away, and adding stop-and-go toll booths seemed more likely to compound vehicular exhaust than to cut it.
Three decades later, in 2007, Mayor Michael Bloomberg asked Albany to toll not just the same East River bridges but also the more-trafficked 60th Street “portal” to mid-Manhattan. Predictably, faux-populist legislators saw Bloomberg’s billionaire wealth as an invitation to denounce the congestion fee as an affront to the little guy.
The mayor may have hurt his cause by presenting congestion pricing primarily as a climate and pollution measure. The pollution rationale was no longer compelling in the way it had been in Lindsay’s day, as automotive engineers had slashed rates of toxic vehicle exhaust ten-fold. Appeals tied to global warming also fell flat; remember, congestion pricing contemplated that most drivers would stay in their fossil-fuel burning cars.
This isn’t to say that congestion pricing confers no climate benefits. Rather, the benefits are subtler ones that can be hard to convey to voters, such as making climate-friendly urban living more attractive. A further benefit may come as congestion pricing demonstrates the unique power of externality pricing, as explained below.
From the Rubble
Even as Bloomberg’s toll plan was faltering in Albany, new loci of support were germinating in the city.
Changing times demanded not just the intellectual leadership of think-tanks like the Regional Plan Association and the good-government Straphangers Campaign, but gritty, grassroots transit organizing. Enter the newly-minted Riders Alliance.
2017 subway handbill exemplified new militancy targeting Gov. Andrew Cuomo for failing transit.
As subway service began cratering in 2015, the inevitable result of budget-raiding by a skein of governors, the Alliance posted crowd-sourced photos of stalled trains and jammed platforms alongside demands for improved service from “#CuomosMTA.” Before long, the papers were pointing the finger at the governor not just in “Why Your Commute Is Bad” explainers but in tear-jerkers like the Times’ May 2017 classic, “Money Out of Your Pocket”: New Yorkers Tell of Subway Delay Woes.
The drumbeat was deafening. Cuomo finally blinked. On a Sunday in August 2017, he phoned the Times’ Albany bureau chief and handed him a scoop for the next day’s front page: Cuomo Calls Manhattan Traffic Plan an Idea ‘Whose Time Has Come’.
The “traffic plan” was congestion pricing.
Data Cruncher
Two months later, Cuomo’s staff summoned me to the midtown office of the consulting firm they had retained to “scope” congestion pricing ― essentially, to compute how much revenue tolls could generate. They wanted to see if an Excel spreadsheet model I had constructed and refined over the prior decade could aid their scoping process.
The model was called the Balanced Transportation Analyzer, a name bestowed in 2007 by Ted Kheel.
Ted, in his nineties, had recruited me to determine whether a large enough congestion toll could pay to make city transit free. The idea worked on paper but foundered politically. Nevertheless, Ted saw in my Excel modeling a way to capture phenomena like “rebound effects” (motorists driving more as road space frees up) and “mode switching” between cars, trains, buses and taxicabs, that he and Prof. Vickrey had identified in their 1969 work but lacked the computing ability to quantify.
Ted’s philanthropy enabled me over the next decade to expand, test and update my transportation modeling. With a hundred “tabs” and 160,000 equations, the “BTA” can instantly answer almost any conceivable question about New York congestion pricing, as well as these two central ones: how much revenue it will yield, and how much time will travelers save in lightened traffic and better transit.3
The BTA model aced its 2017 audition and became the computational engine for the congestion pricing legislation the governor’s team enacted into law in 2019. Its impact has been even broader.4 “Having the model helped make the case with the public, journalists, elected officials and others,” Eric McClure, director of the livable-streets advocacy group StreetsPAC, wrote recently, in part by helping congestion pricing proponents push back on opponents’ exaggerated claims of disastrous outcomes and their incessant demands for special treatment. The model may also have influenced the detailed toll design adopted by the MTA board earlier this year, which hewed close to the toll design I had recommended last summer.5
The BTA also provided sustenance during congestion pricing’s seven lean years ― the 2009-2016 period in which the torch was kept lit by a new triumvirate known as “Move NY” ― traffic guru “Gridlock” Sam Schwartz, the very able campaign strategist Alex Matthiessen, and myself. The model helped our team evangelize congestion pricing’s transformative benefits to elected officials and the public. This, I believe, was a key element in mustering the critical mass of support that ultimately swayed not one but two governors.
The Hochul Factor
New York Lieutenant Governor Kathy Hochul’s ascension to governor in August 2021 could have been congestion pricing’s death knell. The toll plan was adrift in the federal bureaucracy, and its latter-day champion Andrew Cuomo had exited in “me-too” disgrace. His successor, from distant Buffalo, wasn’t beholden to New York or congestion pricing.
Hochul, who as governor controls city and regional transit, could have disowned congestion pricing as convoluted, bureaucratic and tainted. Instead, she became a resolute and enthusiastic backer. Her spirited support, both in public and behind the scenes, became the decisive ingredient in shepherding congestion pricing to safety.
Why the new governor went all-in on congestion pricing awaits a future journalist or historian. Had she spurned it, the opprobrium from downstate transit advocates would have been intense; but there doubtless would have been cries of “good riddance” as well. Vickrey, Kheel and Riders Alliance notwithstanding, it’s not clear how closely New Yorkers — including transit users — connect congestion tolls to improved travel and a better city.
What makes Hochul’s embrace especially impressive is that congestion pricing is, in a real sense, an attack on a jealously guarded entitlement: the right to inconvenience others by usurping public space for one’s vehicle. The classic lament about entitlements’ iron grip is that “losers cry louder than winners sing.”6 Yet in this case, it seems, potential losers — actual and aspiring zone-bound drivers — are being out-sung by transit interests seeking, in Kheel’s 1969 words, a better balance between public transportation and automobiles.
Credits and Prospects
Let us now praise Andrew Cuomo’s crafting of the legislation that teed up congestion pricing’s successful run.
Rather than specifying a dollar price for the tolls, or a precise traffic reduction, his 2019 bill established a revenue target: sufficient earnings to bond $15 billion in transit investment — which equates to $1 billion a year to cover debt service. This device trained the public’s focus on the gain from congestion pricing (better transit) instead of the pain (the toll). Equally important, with this deft stroke, any toll exemption that a vocal minority might seek would mathematically trigger higher tolls for everyone else. The effect was vastly heightened scrutiny of requests for carve-outs.
Which cities will follow on New York’s heels? No U.S. urban area comes close to our trifecta of gridlock, transit and wealth. Sprawling Los Angeles or Houston, or even Chicago for that matter, might be better served by more granulated traffic tolls than New York’s all-or-none model.
Perhaps Asia’s megalopolises will be swept up in our wake. In the meantime, my focus will be on the holy grail of externality pricing: taxing carbon emissions. Every economist knows that the surest and fastest way to cut down on a “bad” is by taxing it rather than subsidizing possible alternatives. Yet that approach remains counter-intuitive and even anathema to nearly everyone else.
A huge and important legacy that New York congestion pricing could provide is to prove that intelligently taxing societal harms need not be electoral suicide. This proof could help unlock a treasure-trove of prosperity-enhancing pricing reforms including, most prominently, robust carbon taxing.
The author, a policy analyst based in New York City, worked in Mayor Lindsay’s Environmental Protection Administration in 1972-1974. He met Bill Vickrey in 1991 and worked closely with Ted Kheel from 2007 to 2010.
Endnotes
- The new passenger surcharges of $1.25 for taxicabs and $2.50 for “ride-hails” (principally Ubers) apply to trips touching the congestion zone. These will be partially offset by lower fares owing to shorter wait-time charges due to faster travel speeds.
- Quote is from Moses’ August 23, 1969 guest essay in Newsday, “Is Rubber to Pay for Rails?” (not digitally available).
- The current version of the BTA is publicly available at this link: (18 MB Excel file).
- See Fix NYC Advisory Panel Report, Appendix B, 2019.
- A Congestion Toll New York Can Live With, July 2023, by Charles Komanoff, co-authored with Columbia Business School economist Gernot Wagner.
- As pronounced by University of Michigan economist Joel Slemrod, in Goodbye, My Sweet Deduction, New York Times, by Eduardo Porter and David Leonhardt, Nov. 3, 2005.
Carbon Footprint
Designing an Insetting Program: A Step-by-Step Playbook for Procurement
Insetting program design starts with your supplier map. The carbon claim comes much later.
Consider a coffee procurement team that funds a farm intervention before checking its sourcing data. The supplier aggregates coffee lots from several regions. The buyer lacks farm-level traceability. Another purchaser expects to report the same outcome. A more attractive project brochure solves none of these problems.
If the distinction between a value-chain intervention and a purchased credit is still open, read CCC’s Insetting vs Offsetting guide before you set the brief.
Insetting program design begins with the purchasing relationship and works outward. You need to decide 1) where an intervention belongs, 2) what business problem it addresses, 3) who pays for it, 4) how results will be measured, and 5) what the evidence will let you say about them. This five-step playbook turns that sequence into a procurement plan.
Step 1: Insetting program design starts with supplier mapping
Start with the commodities that matter most to your Scope 3 inventory and sourcing continuity. Ask finance for spend by supplier, sustainability for the emissions baseline, and category managers for origin and volume records. Then identify which suppliers can trace material to a jurisdiction, sourcing region, producer group, or individual land-management unit.
The level of traceability affects what you can account for. Under the GHG Protocol Land Sector and Removals Standard, the spatial boundary for purchased land-based products depends on the traceability associated with each volume. Farm-specific factors or removals require physical traceability through an acceptable chain-of-custody model. A contract with a tier-one trader, by itself, does not establish a link to the farms behind its deliveries.[1]
Build a first-pass table with five columns: commodity and annual volume; supplier and origin; current traceability level; land-use and production risks; and the business owner who can change the purchasing terms. Mark missing data plainly. A blank cell is cheaper to fix before a program starts than after a claim is drafted.
If your company sets an SBTi Forest, Land and Agriculture target (FLAG), keep its land-related target boundary separate from energy and industry emissions. The current FLAG guidance also requires relevant companies to assess primary deforestation-linked commodities in their value chains.[2]
Step 2: Choose a commodity and jurisdiction for a pilot
Select one supply corridor where the sourcing connection can be established and procurement has a reason to stay. A useful pilot has repeat purchases, suppliers willing to share records, an intervention matched to a diagnosed problem, and a defined plan to measure the result. Carbon potential alone is a poor selection rule if the supplier cannot deliver the crop your business needs.
Compare candidate regions on land-use risk, supplier concentration, local rights and tenure, the availability of baseline data, and exposure to drought, erosion, or forest conversion. Check the relevant legal requirements separately. A nature project does not satisfy a due-diligence obligation merely because it has a carbon method attached.
Consider a coffee buyer sourcing from two districts. In the first, producer-group records identify the farms, while recent dry seasons have increased rejected green coffee lots. In the second, deliveries pass through several intermediaries and farm origins are unknown. Pilot shade management in the first district, with local agronomic advice and quality checks built into the plan. The buyer can trace purchases there and test the intervention against a defined sourcing problem.
Use a short decision memo to record why the selected corridor beats the alternatives, what remains uncertain, and what would stop the pilot. That memo is the first control against a project drifting toward whatever happens to photograph well.
Step 3: Design the supplier engagement and commercial model
The intervention needs an owner on each side of the contract. Decide who supplies planting material or training, who maintains the practice, who bears the cost if a harvest disappoints, and how long the buyer expects to purchase from participating suppliers. Where smallholders participate, budget cash flow and technical support for practices that offer a later return.
Put these terms in a supplier agreement or pilot addendum. It should cover eligible farms and volumes, consent to data collection, access for monitoring, any land or carbon rights that matter, benefit sharing, and what happens if the purchasing relationship ends. Ask local counsel and producer representatives to review the arrangement. The Accountability Framework is a useful reference for supply-chain work involving forests, ecosystems, and human rights.[3]
Avoid assigning an automatic carbon benefit to the buyer. The contract should say which party has the right to report each outcome, how overlapping claims will be checked, and how any issued credits will be handled. A reduction reported in a buyer’s inventory cannot simply be sold for someone else’s offset claim without an accounting review. SBTi FLAG guidance excludes purchased credits used as offsets from near-term FLAG target achievement.[2]
Set commercial measures beside environmental ones: delivered volume, rejection rate, supplier retention, and procurement cost. They tell you whether the program works as a supply-chain investment, even if carbon accounting takes longer to resolve.
Step 4: Build monitoring, reporting, and verification before rollout
Agree on the baseline and data flow before paying for a full rollout. Identify the land units or sourcing regions in scope, the practices that change, the records suppliers already keep, and the additional measurements the program requires. Decide which data can come from field visits, transaction records, or remote sensing, and who checks each source.
For carbon, separate three questions. Did the practice happen? Did emissions or removals change under an applicable method? Can the buyer attribute a defensible share to its purchased goods without double counting? The GHG Protocol’s 2026 guidance includes dedicated chapters on spatial boundaries, data and methods, evaluating actions, credited outcomes, and assurance.[1] These are distinct jobs. A photograph of a planted tree answers only part of the first.
CCC’s MRV and Additionality article explains the separate evidence questions a project reviewer will ask.
Create an evidence file for every reporting period: dated supplier and farm records, purchase volumes, methods and emission factors, uncertainty, quality checks, and changes from the baseline. Specify who can challenge the data and how corrections are recorded. If a project also seeks credit certification, keep project accounting and corporate inventory accounting separate. The GHG Protocol says its land standard focuses on entity-level inventories and does not set the rules for credit certification.[4]
Start with the minimum viable measurement design that can survive review. Add complexity when the pilot tells you which data actually changes a decision.
Step 5: Decide what can be reported and claimed
Insetting program design needs reporting rules before the marketing copy. Procurement, sustainability, finance, and legal should agree on four distinct outputs: operational performance; observed land or nature outcomes; inventory effects, if the accounting criteria are met; and any separately issued credits. One dashboard can display them, but they should not share a single unqualified headline.
SBTi FLAG guidance allows certain land-based removals within a company’s operations or supply chain to contribute to FLAG pathways, subject to criteria including permanence, traceability, data quality, and allocation. It does not allow purchased offsets to meet near-term FLAG targets.[2] Eligibility therefore depends on evidence and the applicable target rules, not on calling an activity “insetting.”
Draft a claims register. For each proposed sentence, record the period, boundary, data owner, calculation method, reviewer, and whether the result is measured, estimated, or still a goal. If the evidence supports only “we funded a pilot with 200 farms,” say that. Do not turn a funding fact into a verified emissions reduction.
What good looks like by year three
Treat year three as a review point, not a promised payback date. A mature pilot should have mapped participating supply volumes, a stable supplier agreement, a repeatable data collection process, and a comparison of commercial and environmental results against the baseline. It should also have a documented answer for outcomes that cannot be included in the buyer’s inventory.
Scale only where the pilot improves a sourcing decision and the evidence can follow the product. If neither condition holds, redesign the intervention or change the corridor. A disciplined program can conclude that a site is unsuitable. That is useful procurement intelligence.
Discuss your insetting program with CCC
Carbon Credit Capital designs nature-based supply chain investments around sourcing needs and measurable sustainability outcomes. Schedule a consultation with our carbon and sustainability experts to map your tier-one supplier network, FLAG exposure, and first pilot decision.
Sources
[1] GHG Protocol, Land Sector and Removals Standard, version 1.1, and companion Guidance, June 2026: https://ghgprotocol.org/land-sector-and-removals-standard ; https://ghgprotocol.org/land-sector-and-removals-guidance
[2] Science Based Targets initiative, Forest, Land and Agriculture Science-Based Target-Setting Guidance, version 1.2, March 2026, especially pp. 16–17, 37, and 41: https://sciencebasedtargets.org/resources/files/SBTiFLAGGuidance.pdf
[3] Accountability Framework initiative, Accountability Framework and guidance for companies: https://accountability-framework.org/
[4] GHG Protocol, Frequently Asked Questions: Land Sector and Removals Standard, questions 10 and 18: https://ghgprotocol.org/blog/frequently-asked-questions-land-sector-and-removals-lsr-standard
Carbon Footprint
The Strategic Case for Nature-Based Carbon Investments
Nature-based carbon investments deserve consideration when they address a specific business dependency and produce outcomes you can measure. Imagine Moonbucks, a global coffee roaster planning next season’s espresso blend. It is considering natural Grade 4 coffee from Jimma, in southwestern Oromia, Ethiopia. Its sourcing decisions affect the roasting schedule and the cash tied up in coffee purchases. Moonbucks needs to understand which measures could protect that supply, what they would cost and how it would judge the results.
1. Define the sourcing problem before choosing a project
Moonbucks needs a dependable component for its espresso blend. Its procurement team wants continuity of volume and an agreed cup profile. Replacing a shipment at short notice could require new sample approval and changes to the blend, and given the schedules for cultivation, processing, and freight delivery, is practically impossible. Moonbucks needs to get this right, and its initial concern is inconsistent deliveries. It commissions an assessment of the supplying farms and post-harvest chain. The questions cover land condition, harvest availability and whether drying or storage problems are affecting saleable lots.
This distinction changes the investment brief. A tree-planting proposal cannot be assumed to fix drying problems. Better storage cannot restore eroded land. The team must establish which problem exists before selecting the response.
CCC’s guide to finding nature-based solutions in your supply chain explains where to look. Here, the next task is to turn a broad concern into a testable proposal.
2. Develop nature-based carbon investments around the actual supply chain
The assessment would trace Moonbucks’ purchases back through the exporter and supplying producer groups. Which farms supply the contracted lots? Who controls land-management decisions? How long does the buyer expect to maintain the purchasing relationship?
Furthermore, Jimma natural Grade 4 cannot be treated as interchangeable with every Ethiopian coffee. Moonbucks would need to test any substitute against its own blend and quality requirements.
Suppose Moonbucks’ assessment identifies an opportunity to maintain shade trees and restore vegetation along exposed streambanks. The IPCC describes agroforestry as a way to store carbon in vegetation and soil, with potential benefits for erosion control and water quality.1 Moonbucks would need local advice on species, growing conditions and maintenance before deciding how these measures fit its sourcing plan.
The proposal now has a defined sourcing connection and a candidate intervention. The next steps are to test its effect on production, assess carbon eligibility and build the financial case.
3. Compare the proposal with other ways to protect supply
WBCSD’s Nature-based Solutions Blueprint recommends comparing nature-based options with other responses across their benefits and costs.2 For Moonbucks, that means evaluating the landscape proposal alongside drying improvements, storage controls and alternative sourcing arrangements.
The product’s natural-process designation matters. Moonbucks should examine the drying and dry-milling chain alongside land conditions. Its team would check storage practices, contamination risks and incoming-lot quality to see whether problems arise before or after the coffee leaves the farms.
The revised proposal might combine land stewardship with separate post-harvest controls. Each component needs its own purpose and budget. A sustainability label should not obscure which activity is expected to solve which problem.
The project develops as the evidence improves. Its scope should follow the diagnosis rather than preserve the first idea unchanged.
4. Establish what the carbon outcome could count toward
Moonbucks’ sustainability team now tests the proposed carbon case separately from the sourcing case. Is the objective a measurable change in Moonbucks’ value-chain emissions, verified credits for separate voluntary use, or distinct outcomes under carefully defined arrangements?
Scope 3 covers value-chain emissions. A purchasing relationship alone does not prove that a farm intervention can be included in Moonbucks’ inventory. The team needs an applicable accounting method, defensible boundaries and evidence supporting attribution.
SBTi’s FLAG Guidance (forest, land and agriculture), version 1.2, says purchased credits used as offsets cannot meet near-term FLAG or energy and industry targets. Eligible land-based removals are subject to accounting requirements.3 Moonbucks needs to test its proposal against those rules before including an outcome in its targets.
For Moonbucks’ Jimma proposal, maintaining existing trees and establishing new vegetation could involve different carbon questions. Specialists must examine the baseline and additionality, meaning what changes because the project proceeds. They must also assess measurement and the risk that stored carbon is lost. CCC’s MRV and additionality article introduces those tests.
Until that work is complete, Moonbucks should not budget an assumed Scope 3 reduction or credit-sale receipt. Direct emissions reductions remain the priority.
5. Build a financial case that survives weaker assumptions
Moonbucks’ finance team would now build a multi-year budget. UNEP’s State of Finance for Nature 2023 compares current finance with the investment needed to meet climate, biodiversity and land-restoration goals.4 The company would cost its proposed activities, farmer participation and ongoing monitoring. Verification, where required, is a separate expense. Maintenance and responsibility for replacing failed plantings must remain visible after the initial establishment budget ends.
Operational benefits need equally careful treatment. If fewer rejected lots reduce emergency purchasing, count that saving once. Do not add “supply resilience” as another financial benefit when it represents the same avoided cost.
Moonbucks should compare a base case with slower benefits, higher implementation costs and no carbon revenue. It should also distinguish production outcomes from quality and shipment outcomes. A single good harvest would not prove that the landscape intervention caused better delivery performance.
A project can remain worth funding even when its carbon case needs more work. That decision must rest on the operational evidence and the company’s objectives, without unsupported environmental claims.
6. Fund a pilot with a clear expansion decision
Moonbucks’ first approval would fund a bounded pilot, rather than commit the entire sourcing program. Before spending, Moonbucks would agree on participating farms, responsibilities and the evidence neede
