An In-depth Analysis of Carbon Credits for Food Banks

 

Nourishing the Planet, Funding the Mission: An In-depth Analysis of Carbon Credits for Food Banks



Introduction

An article published by the news organisation Grist recently brought to light a compelling and complex development at the intersection of climate action and social welfare: food banks, long-established as pillars of community support, are exploring the controversial voluntary carbon market (VCM) as a new source of funding (Grist, 2025).1 These organisations, whose core mission is to alleviate hunger by rescuing and redistributing surplus food, have always generated a significant, albeit unintentional, climate co-benefit. By diverting millions of tons of organic waste from landfills, they prevent the emission of vast quantities of methane, a greenhouse gas far more potent in the short term than carbon dioxide. This has led them to the doorstep of the VCM, a multi-billion-dollar arena that promises to translate this environmental service into a tangible revenue stream, one that could help them expand their operations at a time of rising demand and shrinking traditional funding (Grist, 2025; Food Bank News, 2023).1

The proposition is undeniably attractive. It offers a market-based solution to fund a social good that also happens to be a climate good. However, this path is fraught with peril. The VCM is a market in crisis, plagued by systemic integrity issues, a history of "phantom credits" that represent no real emissions reductions, and persistent accusations of enabling corporate "greenwashing" (CSIS, 2024; Grist, 2025; Illuminem, 2024).1 For food banks, whose greatest asset is public trust, an association with such a market carries profound reputational and ethical risks.

This report argues that while monetising the climate benefits of food rescue is a concept worthy of exploration, the inherent structural flaws of the VCM—particularly around the foundational principle of "additionality" and the immense challenge of verifying "avoided emissions"—make it a hazardous and potentially inappropriate tool for mission-driven non-profits. The attempt to retrofit the complex, socially motivated work of food rescue into the rigid, and often compromised, framework of carbon offsetting creates a paradox that may be impossible to resolve without damaging the integrity of the food banks themselves. The analysis will conclude that a fundamental paradigm shift is necessary. Moving away from a flawed "offsetting" model towards a more transparent "contribution model"—where corporations fund the climate co-benefits of food banking as a direct contribution to climate action rather than as a tool to neutralise their own emissions—is essential for harnessing corporate climate finance without compromising the core mission and public trust of these vital organisations.

To build this argument, this report will first establish the scientific imperative for action by quantifying the immense climate impact of food waste. It will then provide a detailed primer on the architecture and systemic failings of the voluntary carbon market. The analysis will subsequently delve into the specific "additionality paradox" that confronts food banks, followed by a comparative assessment of the emerging carbon accounting methodologies designed for food rescue. Through a series of real-world case studies, the report will examine the practical challenges and alternative pathways being forged by pioneers in the field. Finally, it will culminate in a set of strategic, actionable recommendations for food banks, corporate credit buyers, and the standards bodies that govern this volatile market, outlining a critical path forward that protects the mission while genuinely nourishing both people and the planet.

Section 1: The Methane Imperative: Quantifying the Climate Impact of Food Waste

To fully appreciate the opportunity and the peril that carbon markets present to food banks, one must first grasp the sheer scale of the environmental problem their work addresses. Food waste is not a minor contributor to climate change; it is a primary driver, with an impact that is both global in scale and acute in its warming potential. The scientific case for diverting food waste from landfills is not merely compelling—it is one of the most urgent and effective levers available for near-term climate mitigation. This is due to the unique chemical properties of organic decomposition in an anaerobic environment and the outsized role of one particular greenhouse gas: methane. Understanding this scientific foundation is critical, as it forms the very basis upon which the value of a food rescue "carbon credit" is calculated and justified.

1.1 The Disproportionate Impact of Food Waste in Landfills

In the United States, municipal solid waste (MSW) landfills represent the third-largest source of human-related methane emissions (EPA, 2023; RMI, n.d.).5 Within this vast stream of discarded material, one component stands out for its volume and its environmental impact: food. According to the U.S. Environmental Protection Agency (EPA), food waste is the single most common material sent to landfills and incinerators, constituting approximately 24% of all landfilled MSW (EPA, 2021; EPA, 2023; ERG, n.d.).5 Over one-third of all food produced in the country is never eaten, and a significant portion of this surplus ends up in landfills (AP News, 2023; EPA, 2021; USDA, 2022).9

However, its contribution to the landfill problem goes far beyond its weight. The critical factor is its rapid rate of decay. Unlike more stable materials like wood or paper, food waste decomposes quickly in the oxygen-deprived (anaerobic) conditions of a landfill, a process that generates large quantities of methane. This biological reality means that food waste's climate impact is vastly disproportionate to its share of landfill volume. A landmark 2023 EPA report, the first peer-reviewed national analysis of its kind, quantified this disparity with startling clarity: while making up just 24% of the material in landfills, food waste is responsible for an estimated 58% of all fugitive methane emissions escaping from them (AP News, 2023; EPA, 2023; ERG, n.d.).5 This single statistic reframes the issue entirely. It demonstrates that tackling landfill methane is, to a very large extent, synonymous with tackling food waste. Any strategy aimed at mitigating emissions from the waste sector that does not prioritise the diversion of organic material is addressing less than half of the problem.

1.2 Methane: A Potent, Short-Lived Climate Pollutant

The focus on food waste is intensified by the nature of the gas it produces. Methane (CH4​) is a "super-pollutant," a greenhouse gas with a warming power far exceeding that of carbon dioxide (CO2​). Over a 20-year time horizon—a critical period for avoiding catastrophic climate tipping points—methane has more than 80 times the atmospheric warming power of CO2​ (RMI, n.d.).6 While its overall concentration in the atmosphere is lower than

CO2​, it is responsible for approximately 30% of the total global warming experienced since the Industrial Revolution (EPA & USDA, 2024).11

Crucially, methane is also a short-lived climate pollutant. It has an average atmospheric lifetime of only about 12 years, compared to the centuries that CO2​ can persist (ReFED, n.d.).12 This characteristic is of immense strategic importance. Because it is both highly potent and relatively short-lived, reducing methane emissions offers the most significant opportunity to slow the rate of global warming in the near term. Organisations like ReFED, a non-profit focused on food waste solutions, have characterised methane reduction as an "emergency brake" in the fight against climate change (ReFED, 2024).13 Actions taken today to cut methane can have a discernible impact on atmospheric concentrations and the rate of warming within a decade, buying invaluable time for longer-term decarbonization efforts to take effect (ReFED, 2024).13 This makes the methane generated by food waste a high-priority target for rapid climate mitigation.

1.3 The Global Scale: An IPCC and UNFCCC Perspective

The problem of food waste emissions is not confined to any single country; it is a global phenomenon of staggering proportions. Authoritative reports from the world's leading climate science and policy bodies, the Intergovernmental Panel on Climate Change (IPCC) and the United Nations Framework Convention on Climate Change (UNFCCC), place the issue at the center of the climate crisis. Globally, food loss and waste are responsible for an estimated 8% to 10% of all anthropogenic greenhouse gas emissions (Grist, 2025; UNFCCC, 2024; WRAP, n.d.).1

To put this figure in perspective, if global food loss and waste were a country, it would be the world's third-largest emitter, surpassed only by the entire economies of China and the United States (Carbon Brief, 2023; WRAP, n.d.).14 The emissions from wasted food are nearly five times greater than those from the entire global aviation sector, an industry that is often the subject of intense climate scrutiny (MDPI, n.d.; UNFCCC, 2024).17 This comparison underscores a critical disconnect in public and policy perception: a globally systemic source of emissions remains largely addressed by fragmented, localised efforts, while far smaller sectors receive disproportionate attention. The production of this wasted food also carries an immense environmental burden, consuming nearly a third of the world's agricultural land and costing the global economy an estimated

CO_2$-eq per year by 2050 if left unchecked (IPCC, n.d.).18

1.4 The Inefficiency of Landfill Gas Capture for Food Waste

The scientific rationale for diverting food waste becomes even more compelling when examining the operational realities of landfill management. Modern landfills are not simply open dumps; many are engineered facilities equipped with landfill gas (LFG) collection systems designed to capture methane and either flare it (converting it to less-potent CO2​) or use it to generate energy. While these systems can be effective for slowly decomposing materials, they are fundamentally ill-suited to the rapid decay profile of food waste (Advanced Waste Solutions, 2023; BioCycle, 2023).19

The core of the problem is a critical time lag. LFG collection systems are typically installed in landfill "cells" only after they have been filled and covered, a process that can take years. During this initial period, when there is no active gas collection, the waste begins to decompose (BioCycle, 2023).20 For food waste, this is the period of its most intense methane generation. An analysis cited in the EPA's 2023 report uses a decay rate constant (

k) of 0.19 for food waste, which translates to a half-life of just 3.6 years (BioCycle, 2023).20 This means that half of the food waste's methane-generating potential is exhausted before LFG systems are typically up and running at full efficiency. In the first four years a waste cell is active, LFG collection efficiency is effectively zero; for the next four, it might average 50% (BioCycle, 2023).20 Consequently, a large fraction of the methane from food waste escapes directly into the atmosphere as fugitive emissions before the engineered mitigation systems can capture it.

This technical detail is not incidental; it is the central scientific justification for why diversion is climatically superior to end-of-pipe mitigation for this specific waste stream. The very chemistry of food decomposition creates a direct causal link to the inefficiency of standard landfill management practices. This establishes a clear and scientifically robust hierarchy of solutions: preventing food from entering the landfill in the first place—the core activity of a food bank—is profoundly more effective at preventing methane emissions than attempting to capture them after the fact. This understanding is fundamental to constructing the "baseline scenario" in any carbon accounting methodology for food rescue, as it validates the assumption that, in the absence of diversion, a significant portion of the food's methane potential would indeed be released into the atmosphere. This reality reframes food banks not merely as social charities providing a secondary climate benefit, but as essential, front-line infrastructure for climate mitigation, performing a function that conventional waste management systems are structurally ill-equipped to handle. This re-evaluation justifies the exploration of new, climate-aligned funding mechanisms, even as it raises critical questions about whether the VCM is the appropriate instrument for the task.

MetricValue / StatisticSource(s)
Food Waste as % of U.S. Landfilled Municipal Solid Waste (MSW)24%

(EPA, 2023; ERG, n.d.) 5

Food Waste Contribution to U.S. Landfill Methane Emissions58%

(EPA, 2023; ERG, n.d.) 5

Global GHG Emissions from Food Loss & Waste8-10% of total anthropogenic emissions

(IPCC, n.d.; UNFCCC, 2024) 15

Comparison to Aviation Sector EmissionsNearly 5 times greater

(UNFCCC, 2024) 15

Methane's 20-Year Global Warming Potential (GWP) vs. CO2​~80 times more potent

(RMI, n.d.) 6

Lifecycle Methane Emissions from U.S. Surplus Food (% of U.S. Total)Nearly 14% (equivalent to 75 million cars)

(ReFED, 2024) 13

Section 2: The Voluntary Carbon Market: A Primer on Mechanisms and Integrity

The voluntary carbon market (VCM) is the arena where the climate benefits of activities like food rescue are translated into a tradable, financial asset. It operates on a simple premise: entities that cannot or have not yet fully eliminated their own greenhouse gas emissions can "offset" or compensate for them by purchasing "carbon credits" from projects elsewhere that are actively reducing or removing emissions from the atmosphere. In theory, this allows capital to flow to the most cost-effective climate solutions globally, accelerating decarbonization. However, the journey from this elegant theory to on-the-ground reality has been fraught with controversy. The VCM is not a mature, regulated financial market akin to a stock exchange. Instead, it is a complex and often opaque ecosystem of private actors, competing standards, and subjective judgments. For any organisation, particularly a non-profit whose reputation is its most valuable asset, a clear-eyed understanding of the market's architecture, its core principles, and its deep-seated integrity challenges is an absolute prerequisite to engagement.

2.1 Architecture of the VCM

The VCM exists parallel to "compliance markets," which are government-mandated systems (like the European Union's Emissions Trading System) where participation is compulsory for certain industries (Senken, n.d.).21 In the VCM, participation is entirely voluntary, driven by corporate social responsibility commitments, net-zero pledges, and consumer pressure (Global Witness, n.d.).22 The market's structure involves several key players:

  • Project Developers: These are the organisations that implement the emissions-reducing activities on the ground. This could be a renewable energy company building a wind farm, a conservation group protecting a forest, or, in the context of this report, a food bank rescuing surplus food.

  • Standards Bodies and Registries: These are the private, non-profit organisations that set the rules for the market. They develop the accounting methodologies, approve projects, and issue the carbon credits. The two most prominent standards in the VCM are Verra, which manages the Verified Carbon Standard (VCS), and Gold Standard (Aquila, n.d.).23 These bodies also operate public registries to track every credit issued and "retired" (used), preventing the same credit from being sold twice (Global Witness, n.d.).22

  • Validation and Verification Bodies (VVBs): These are independent, third-party auditors accredited by the standards bodies. Their role is to validate that a project's design meets the standard's requirements before it begins, and to periodically verify that the claimed emissions reductions have actually occurred (Medium, n.d.; Verra, n.d.).24

  • Buyers: These are the corporations, individuals, and other organisations that purchase the carbon credits to offset their own emissions. Their motivations range from fulfilling public climate pledges to marketing products as "carbon neutral" (Global Witness, n.d.; Senken, n.d.).22

The basic unit of exchange is the carbon credit, which represents one metric ton of carbon dioxide equivalent (tCO2​e) that has been either removed from or avoided being emitted into the atmosphere (CarbonCredits.com, n.d.).26

2.2 The Cornerstone of Credibility: Additionality

For a carbon credit to have any environmental integrity—that is, for it to represent a real climate benefit—it must be additional. This is the single most important and most contested principle in the carbon market. A project is considered additional only if the emissions reductions it generates would not have occurred in the absence of the incentive created by the revenue from selling carbon credits (Calyx Global, n.d.; Endangered Landscapes Programme, 2023; Sylvera, n.d.; UNDO, n.d.).27 If the project had happened anyway, then selling credits for it creates no new climate benefit; it simply allows a buyer to continue polluting while claiming to be "offsetting" their impact, resulting in a net increase in atmospheric GHGs.

To determine additionality, standards bodies have developed a series of tests that projects must pass. While the specifics vary, they generally fall into three categories:

  • Financial Additionality: This test seeks to prove that the project would not be financially viable or attractive without the income from carbon credits. This often involves an investment analysis showing that the project's internal rate of return (IRR) is below a standard benchmark, or that it faces significant financial barriers that only carbon revenue can overcome (Calyx Global, n.d.; UNDO, n.d.).29

  • Legal and Regulatory Additionality: This is a straightforward check to ensure that the project's activities are not already mandated by law or regulation. If a landfill is legally required to capture its methane, for example, it cannot sell carbon credits for doing so, because the action would have happened anyway (Calyx Global, n.d.).29

  • Common Practice Test: This test assesses whether the project's technology or practice is already common in the region. If similar projects are being implemented widely without carbon finance, it suggests that the activity is already standard practice and therefore not additional (Calyx Global, n.d.).29

Proving additionality is inherently difficult because it requires demonstrating a counterfactual—what would have happened in a hypothetical world without the project. This relies on assumptions, projections, and judgments that are susceptible to bias and what economists call "information asymmetry," where the project developer knows more about their own motivations and financial situation than an external auditor ever could (OffsetGuide.org, n.d.; Salzman and Weisbach, 2024).31

2.3 Avoided Emissions vs. Carbon Removal

A critical distinction within the VCM is between projects that generate credits through carbon removal and those that do so through avoided emissions.

  • Carbon Removal projects actively pull CO2​ out of the atmosphere and store it. Examples include afforestation and reforestation (planting trees), direct air capture (technological removal), and biochar (converting biomass into a stable form of carbon) (Grist, 2025).1 The quantity of removed carbon can, in principle, be directly measured.

  • Avoided Emissions projects prevent greenhouse gases from being released into the atmosphere in the first place. Examples include protecting a forest that was at risk of being logged (avoided deforestation), replacing wood-burning cookstoves with cleaner alternatives, or building a wind farm that displaces a coal-fired power plant (Grist, 2025).1 Food bank credits, which prevent methane emissions from landfills, fall squarely into this category (Grist, 2025).1

Credits from avoided emissions projects are often viewed with greater scepticism by experts and watchdog groups. This is because their entire claim to a climate benefit rests on the credibility of the counterfactual baseline. The number of credits issued is calculated as the difference between the baseline emissions (what would have happened) and the project emissions (what did happen). If the baseline is inflated—if the threat of deforestation was exaggerated, or if the assumption is made that all diverted food would have gone to a high-emitting landfill—then the project will be issued "phantom credits" for emissions reductions that were never truly at risk of occurring (Grist, 2025; OffsetGuide.org, n.d.).1 This reliance on a hypothetical scenario makes avoided emissions credits structurally more vulnerable to integrity failures than removal credits.

2.4 A Market in Crisis: Systemic Critiques and the "Greenwashing" Epidemic

In recent years, the theoretical promise of the VCM has collided with a harsh reality of market failure. A series of high-profile, data-driven investigations has exposed systemic flaws in the market, particularly within the category of avoided emissions projects that are most analogous to food rescue.

In January 2023, a joint investigation by The Guardian, Die Zeit, and SourceMaterial analysed a significant portion of the rainforest protection credits certified by Verra, the market's largest standard-setter. These projects, known as REDD+ (Reducing Emissions from Deforestation and Forest Degradation), are a cornerstone of the VCM. The investigation concluded that more than 90% of these credits were likely "phantom credits" that did not represent genuine emissions reductions, based on findings that the threats of deforestation were systematically overstated (CSIS, 2024).3 This was followed by an August 2023 study in the prestigious journal

Science came to a similar conclusion, finding that many forestry programs had significantly overestimated their climate impact (CSIS, 2024).3

These are not isolated incidents. The watchdog organisation Carbon Market Watch has documented similar patterns of over-crediting in other avoided emissions project types. An analysis of clean cookstove projects—which sell credits based on avoiding emissions from burning wood—found that their climate impact was "overstated significantly," in part due to flawed assumptions in their baseline calculations (Grist, 2025).1 These consistent failures are not random; they are concentrated in projects that rely on proving a counterfactual baseline, a process that is highly susceptible to biased assumptions and the financial incentive to maximize credit issuance. Because food bank credits are also based on avoiding emissions against a hypothetical baseline (landfill methane), they are structurally analogous to the project types with the worst track records for environmental integrity, placing them in a high-risk category from the outset.

These market failures have fueled a widespread "greenwashing" epidemic. Greenwashing occurs when a company uses environmental marketing to mislead the public into believing it is more sustainable than it actually is (Frontiers in Climate, 2021).33 In the context of the VCM, companies purchase cheap, low-quality carbon credits and use them to make high-profile claims of being "carbon neutral" or "Paris-aligned" (Global Witness, n.d.).22 This practice is doubly damaging: it deceives consumers and investors, and, more insidiously, it delays genuine corporate decarbonization by creating the illusion of climate action (CSIS, 2024; Global Witness, n.d.; Salzman and Weisbach, 2024).3 The growing number of "climate-washing" lawsuits, such as the class-action suit filed against Delta Air Lines over its carbon neutrality claims, highlights the increasing legal and reputational risks for companies relying on a flawed market (CSIS, 2024; Salzman and Weisbach, 2024).3

The VCM is not a well-regulated financial exchange but has been aptly described as a "Wild West"—a space where rules are fragmented and loosely enforced (CSIS, 2024).3 A fundamental conflict of interest is embedded in its structure: the project developers, who have a financial interest in maximising the number of credits they receive, are the ones who pay the third-party auditors (VVBs) who are supposed to be providing independent scrutiny (Medium, n.d.; OffsetGuide.org, n.d.).24 This creates a powerful, albeit often subtle, incentive for leniency, contributing to a "race to the bottom" on quality that has been documented by the widespread failure of credits to deliver their promised climate benefits (Carbon Market Watch, 2024).34 For any organisation like a food bank, whose primary asset is public trust built over decades, entering such a market without an acute awareness of these structural flaws represents an existential risk.

Section 3: The Additionality Paradox of Food Banking

The principle of additionality, while a challenge for all carbon projects, presents a unique and profound paradox for food banks. The very nature of their mission and operating model collides with the fundamental logic of the carbon market, creating a conundrum that is difficult, if not impossible, to resolve within the existing framework of carbon offsetting. This is not merely a technical accounting problem; it goes to the heart of the ethical and reputational questions surrounding the entry of mission-driven non-profits into a market mechanism designed to incentivize purely climate-driven actions. The debate over food bank additionality reveals a fundamental mismatch between the tool and the task, a category error that attempts to force a social good with a climate co-benefit into a system that struggles to value either with integrity.

3.1 The Central Conundrum: Mission vs. Mechanism

Food banks were not created to fight climate change. They were established, in some cases decades ago, with the singular social mission of alleviating hunger by rescuing surplus food and providing it to people in need (Grist, 2025).1 The fact that this core activity also prevents potent methane emissions is a significant and valuable co-benefit, but it is not, and has never been, the primary driver of their operations. This creates an immediate and obvious conflict with the principle of additionality.

The "business-as-usual" scenario for a food bank already involves diverting food from landfills. Therefore, the climate benefit they provide is part of their existing operational baseline. From a strict carbon accounting perspective, selling credits for this ongoing activity appears to be a textbook case of non-additionality. It would be rewarding an organization for something it was already doing for entirely different reasons. This is precisely the "free-rider" problem that additionality tests are designed to prevent (Kotchen, n.d.; Salzman and Weisbach, 2024).32 If credits are issued for non-additional activities, the market fails in its primary purpose: to incentivize

new climate action. Instead, it simply provides a windfall to existing actors while allowing buyers to claim offsets for emissions reductions that would have happened anyway, leading to a net increase in global emissions. This is the central paradox: how can an activity that is, by definition, part of an organisation's long-standing mission be considered "additional" in the context of the carbon market?

3.2 The "Funding for Expansion" Argument

Proponents of carbon credits for food banks, most notably the Global FoodBanking Network (GFN), have put forward a nuanced argument to address this conundrum. They contend that the revenue from carbon credits is not intended to fund the work that food banks are already doing, but rather the work that this new funding will enable them to do in the future (Grist, 2025).1

The argument is as follows: Food banks are chronically under-resourced and face limitations on their capacity. They may lack sufficient warehouse space, refrigerated trucks, or the logistical infrastructure needed to rescue all available surplus food in their communities. The revenue generated from selling carbon credits, they argue, would be earmarked specifically for capacity-building projects—buying a new truck, expanding a cold storage facility, or developing new partnerships with food donors. This marginal increase in their capacity to rescue food, which is directly enabled by the carbon finance, represents the "additional" climate benefit. In this framing, the carbon market is not rewarding past behavior but is instead catalysing future growth and, therefore, future emissions reductions that would not have otherwise occurred (Grist, 2025).1

3.3 The Verification Impasse: Fungibility and Intent

While elegant in theory, the "funding for expansion" argument encounters a nearly insurmountable verification impasse in practice. The core problems are the fungibility of money and the unobservability of institutional intent.

Food banks, like all non-profits, are in a constant state of fundraising. They actively seek funding for expansion from a diverse portfolio of sources, including philanthropic grants, corporate sponsorships, government support, and individual donations (Food Rescue Hero, 2025).36 Their operational and capital budgets are typically a blend of these various income streams. When a food bank does expand—for instance, by purchasing a new vehicle—it becomes practically impossible for a third-party auditor to prove with certainty that this specific investment would

not have happened without the revenue from carbon credits.

Consider a scenario where a food bank receives $50,000 from carbon credit sales and, in the same year, secures a $100,000 grant from a local foundation, both intended for capacity building. When a new $75,000 truck is purchased, which funding stream was the decisive cause? Was the carbon revenue truly the "but for" factor, or was it simply one contribution among many to a pre-existing strategic goal? Money is fungible; once it enters the organisation's accounts, its origin becomes irrelevant to its use. An auditor cannot definitively disentangle these funds to establish the clear, unambiguous causal link that the principle of additionality demands (OffsetGuide.org, n.d.; Salzman and Weisbach, 2024).31

This is not just a minor accounting hurdle; it is a fundamental failure to meet the standard of proof. Expert critics have pointed out that this represents poor carbon accounting because it relies on the unverifiable assertion of intent rather than on objective evidence of causality (Grist, 2025).1 The "funding for expansion" argument attempts to shift the focus of the additionality test away from the

activity itself (food rescue, which is not additional) and onto the financing of that activity. However, because food banks have multiple, overlapping funding streams all aimed at the same goal of expansion, the causal chain required for a credible additionality claim is effectively broken. At best, the carbon revenue can be described as a contributor to the expansion, but it cannot be proven to be its sole, decisive cause. This ambiguity falls far short of the rigorous standard required for a carbon credit that purports to represent a real and verifiable offset.

3.4 The Risk of Perverse Incentives

Beyond the verification challenges, a reliance on carbon finance could introduce subtle but significant perverse incentives that could ultimately conflict with a food bank's primary social mission. The strict requirements of additionality could create scenarios where a food bank's optimal fundraising strategy is at odds with its eligibility for carbon credits.

For example, imagine a food bank is in the process of applying for both a large philanthropic grant to fund a new warehouse and certification for a carbon credit project based on the "funding for expansion" argument. If the philanthropic grant is successful, it could render the carbon project non-additional, as it would demonstrate that the expansion was financially viable without the carbon revenue. This could create a perverse incentive for the food bank to either deprioritise the grant application or obscure its fundraising successes from carbon market auditors. It could pit the organisation's immediate social goal (securing the largest possible funding for expansion) against its climate financing model.

Furthermore, if a food bank becomes reliant on carbon revenue, its operational decisions could become influenced by the need to maximise credit generation rather than social impact. This could, for example, lead to prioritising the rescue of certain types of food that have a higher calculated methane potential over other foods that might have greater nutritional value for their clients. While this is a speculative risk, it highlights the potential for mission drift when a social service organisation becomes financially entangled in a market mechanism with a completely different set of objectives and performance indicators. The entire debate over food bank additionality is ultimately a symptom of a larger category error. It is an attempt to force-fit a mission-driven social enterprise into a market mechanism that was designed, however imperfectly, to incentivise purely financially-driven climate projects. The tools of carbon accounting, such as investment analysis and barrier assessments, are predicated on a logic of profit maximisation and return on investment that simply does not apply to an organisation motivated by a mandate to alleviate hunger. This fundamental mismatch suggests that a different financing model is required—one that honestly acknowledges and funds the immense climate co-benefit of their essential social work, rather than trying to construct an artificial and unverifiable narrative that their work is only happening because of the lure of climate finance.

Section 4: Methodologies in Focus: A Comparative Analysis

For any carbon credit to be considered legitimate, the emissions reductions it represents must be quantified according to a rigorous, transparent, and scientifically sound methodology. This "rulebook" is the technical heart of a carbon project, dictating everything from how to define the project's boundaries to how to calculate its impact and monitor its performance over time. The quality and integrity of the methodology are therefore paramount; a flawed methodology will inevitably produce flawed, low-quality credits, regardless of the project's good intentions. In the emerging space of food rescue carbon credits, several distinct methodologies have been developed, each with its own scope, approach, and set of assumptions. A comparative analysis of these frameworks—offered by the market's leading standards bodies, Verra and Gold Standard, as well as by industry stakeholders like the Global FoodBanking Network—is essential for understanding the nuances, strengths, and potential weaknesses of this new asset class.

4.1 The Need for a Standardised Rulebook

A methodology serves as the standardised procedure that all projects of a certain type must follow to ensure that their emissions reductions are calculated consistently and comparably (Norton Rose Fulbright, n.d.; SustainCERT, n.d.).37 It provides the detailed instructions for:

  • Defining the Baseline Scenario: Establishing what would have happened in the absence of the project.

  • Demonstrating Additionality: Proving that the project would not have occurred without carbon finance.

  • Quantifying Emissions Reductions: Calculating the net difference between baseline emissions and project emissions.

  • Monitoring, Reporting, and Verification (MRV): Setting out the requirements for ongoing data collection and third-party auditing to ensure the project performs as claimed.

The approval of a methodology by a major standards body like Verra or Gold Standard is a critical step that allows projects to begin the process of generating credits. The development of several methodologies for food loss and waste signals a growing interest in this area, but also necessitates careful scrutiny of their underlying assumptions.

4.2 Verra's VM0046: Methodology for Reducing Food Loss and Waste

Verra, the world's most widely used GHG crediting program, activated its framework for this sector in July 2023 with the release of VM0046, Methodology for Reducing Food Loss and Waste, v1.0 (Verra, 2023).39

  • Scope: The methodology is broadly applicable to a range of activities that prevent food loss and waste (FLW) by keeping food within the human supply chain. This explicitly includes food bank donations, as well as interventions at farms, processing facilities, retailers, and households, such as the use of apps to facilitate food sharing (Verra, 2023).39 A key requirement is that the rescued food must remain intended for human consumption; using it for animal feed or biogas production is not eligible under this specific methodology (Swiss Climate, n.d.). .41

  • Quantification: VM0046 provides detailed procedures to quantify the downstream emissions reductions that result from diverting food from a designated FLW destination. The core of the calculation involves comparing the emissions of the project scenario (where food is rescued, transported, stored, and distributed by the food bank) with the emissions of the baseline scenario (where the same food is sent to a specific waste destination, such as a landfill, incinerator, or composting facility) (Verra, 2023).39 The net climate benefit is the baseline emissions minus the project emissions.

  • Additionality: The methodology does not contain its own bespoke additionality test. Instead, it requires project developers to apply Verra's centralised and standardised additionality tools. These include VCS Tool VT0008 (Additionality Assessment) and VCS Tool VT0009 (Combined Baseline and Additionality Assessment) (ClearBlue Markets, 2024).42 These tools provide a structured process for conducting an investment analysis (to prove the project is not financially attractive on its own), a barrier analysis (to identify non-financial hurdles that carbon finance helps overcome), and a common practice analysis (ClearBlue Markets, 2024).42 The application of these generic tools to the unique, mission-driven context of a non-profit food bank is a key area of analytical tension, as discussed in the previous section.

4.3 Gold Standard's Reduction in Methane Emissions from Landfills Through Decentralised Organic Waste Processing

Gold Standard, known for its rigorous requirements and focus on sustainable development co-benefits, approved a relevant methodology in May 2024: Reduction in Methane Emissions from Landfills Through Decentralised Organic Waste Processing (Gold Standard, 2024).43

  • Scope: This methodology was developed in partnership with Lomi, the maker of a home food recycling appliance, and is therefore tailored for decentralised, on-site waste processing (Gold Standard, 2024; Medium, n.d.).47 It applies to activities at the household or commercial level where organic waste is treated through an aerobic decomposition process, avoiding the need to transport it to a central landfill (Gold Standard, 2024).45 While not designed specifically for food banks, its principles could potentially be adapted for food banks that also manage non-edible organic waste or operate community composting programs. It explicitly excludes animal waste and wastewater (Gold Standard, 2024).45

  • Quantification: The methodology focuses on calculating the avoided methane emissions from diverting specific organic waste streams (kitchen and vegetable waste) from a landfill baseline. It also accounts for the additional benefit of avoiding emissions from waste transportation (Gold Standard, 2024).45

  • Additionality and Safeguards: The methodology requires the project developer to demonstrate that, in the baseline scenario, the organic waste would have been sent to a landfill and that there is no legal mandate requiring its separate treatment (Gold Standard, 2024).45 True to the Gold Standard's approach, it includes robust safeguards. For example, projects must establish and monitor procedures to ensure that the end-product (e.g., compost) is handled properly and does not end up back in the landfill, which would negate the climate benefit (Gold Standard, 2024).45 Compared to Verra, Gold Standard places a much stronger, mandatory emphasis on projects demonstrating contributions to at least two additional Sustainable Development Goals (SDGs) and conducting thorough stakeholder consultations, which often results in a price premium for its credits (Aquila, n.d.; SustainCERT, n.d.).23

4.4 GFN's FRAME: Food Recovery to Avoid Methane Emissions

The Global FoodBanking Network (GFN), in partnership with the Global Methane Hub and the Carbon Trust, has developed its own specialised methodology, FRAME (Food Recovery to Avoid Methane Emissions), which is currently in the process of seeking certification from Gold Standard (GFN, 2024; GFN, n.d.; Grist, 2025).1

  • Scope: As its name suggests, FRAME is specifically and exclusively designed for food recovery and redistribution operations conducted by food banks (GFN, 2024).49 It is tailored to their specific operational realities.

  • Quantification: The methodology calculates avoided emissions by comparing the project scenario to a baseline scenario. The project emissions include those from transporting and refrigerating the rescued food. The baseline scenario assumes that the food, if not rescued, would be disposed of in a way that does not feed people—primarily by being sent to a landfill, but also potentially to composting or animal feed (Grist, 2025).1 The methodology only considers food that is donated to food banks, not purchased by them (Grist, 2025).1

  • Critique: While tailored to the sector, the FRAME methodology's baseline has drawn criticism from experts. Marc Roston, a scholar at the Stanford Doerr School of Sustainability, argues that the framework is flawed because it assumes that if food is not donated, it will inevitably go to waste (Grist, 2025).1 This ignores other plausible outcomes, such as the retailer selling the surplus food at a steep discount. This creates a logical inconsistency: if a food bank buys the discounted food, no credits are generated; if the store gives the same food to the food bank for free, credits are issued. Roston contends this is "not good carbon accounting" because the climate outcome is identical in both cases, yet only one is rewarded (Grist, 2025).1

A critical examination of these methodologies reveals a shared and potentially significant vulnerability: they all rely on a baseline assumption that, in the absence of the project activity, the diverted food would have been sent to a landfill. This is the highest-emission plausible outcome for food waste, and therefore, its use as the default baseline maximises the number of credits a project can claim. However, surplus food has multiple potential destinations, including animal feed, composting, or anaerobic digestion, all of which have different and often lower emissions profiles than landfilling, as shown in various Life Cycle Analyses (LCAs) (Frontiers, 2020; OSTI, n.d.; Open Access, n.d.; PubMed, 2023; ResearchGate, n.d.).50 By defaulting to the worst-case scenario as the baseline, the methodologies risk systematically over-crediting the emissions that are truly being avoided. This is a classic problem in the VCM and a key mechanism by which "phantom credits" are generated (OffsetGuide.org, n.d.). .31

This simplification highlights a fundamental tension. The development of these specific methodologies represents an attempt to "retrofit" the complex, dynamic, and socially-driven activity of food rescue into the rigid, quantitative, and standardised framework of carbon accounting. To make the activity "fit" the model, simplifying assumptions must be made. However, these very simplifications—particularly the choice of baseline—introduce a potential compromise to the environmental integrity of the resulting credits. This creates a difficult trade-off between creating a workable accounting system and accurately reflecting the complex reality of food supply chains.

FeatureVerra VM0046Gold Standard (Decentralised Waste)GFN FRAME (Seeking Gold Standard Certification)
Standard BodyVerraGold StandardSeeking Gold Standard
Scope of Eligible ActivitiesBroad: Food loss/waste reduction across the supply chain, including food banks. Must be for human consumption.Narrow: Decentralised, on-site aerobic processing of household/commercial organic waste (e.g., composting).Specific: Food recovery and redistribution by food banks.
Baseline Scenario DefinitionFood is sent to a specified FLW destination (e.g., landfill, incinerator, compost).Organic waste is sent to a landfill.Food is sent to a destination other than human consumption (e.g., landfill, compost, animal feed).
Approach to Additionality TestingApplication of Verra's standardised additionality tools (investment, barrier, common practice analysis).Must demonstrate that activity is not legally mandated and that landfilling is the baseline.Argues for additionality based on using carbon revenue to expand capacity.
Monitoring, Reporting, Verification (MRV)Rigorous MRV requirements as per VCS Program rules.Requires monitoring of end-product (compost) handling to prevent re-entry into the waste stream.Requires detailed tracking of food rescued, transported, and refrigerated.
Mandatory Co-Benefit (SDG) ReportingOptional (can be certified separately under Verra's CCB or SD VISta standards).Mandatory (must contribute to at least two SDGs beyond climate action).Aligns with SDG 2 (Zero Hunger) and SDG 12 (Responsible Consumption) as part of its core model.
Key Strengths & Potential WeaknessesStrength: Broad applicability, backed by the market's largest registry. Weakness: Generic additionality tools may not fit non-profits well.Strength: High integrity standard, mandatory SDG co-benefits. Weakness: Narrow scope may not apply directly to all food bank models.Strength: Tailor-made for food bank operations. Weakness: Baseline assumptions have been criticised as potentially flawed and oversimplistic.

Section 5: Pioneers in Practice: Case Studies from the Field

As the theoretical frameworks for food rescue carbon credits take shape, a handful of pioneering organisations are already navigating the practical realities of this new frontier. Their experiences offer invaluable, real-world insights into the opportunities, the immense operational challenges, and the strategic choices facing any food bank considering this path. These early case studies reveal that generating carbon credits is not a simple administrative task but a resource-intensive venture requiring specialised expertise and robust data systems. They also highlight a critical divergence in strategy: while some are embracing the VCM as a direct funding mechanism, others are leveraging the tools of carbon accounting for a different purpose altogether—to validate their impact and strengthen their case for traditional fundraising.

5.1 The First Mover: Mexican FoodBanking Network (BAMX)

In a landmark development for the sector, the Mexican FoodBanking Network (BAMX) became the first food banking organisation in the world to successfully earn carbon credits for its food rescue operations (Food Bank News, 2023).2 This pioneering effort provides a candid look at the process and its potential outcomes.

To achieve this, BAMX partnered with a Miami-based consultancy, CoreZero, which guided them through the complex process of quantifying their climate impact. This involved a comprehensive audit of all facets of their operations to measure the carbon dioxide emissions saved from the atmosphere and translate that impact into a verifiable, tradable asset (Food Bank News, 2023).2 The Executive Director of BAMX, Maria Teresa Garcia Plata, described the process as "not easy," underscoring the significant investment of time and resources required to meet the stringent demands of the carbon market (Food Bank News, 2023).2

The result of this intensive effort was that for every ton of food BAMX rescued over the preceding year, it was issued one carbon credit. Having become active on the voluntary market in early 2023, BAMX projected that its credits could fetch a price ranging from a low of $1.80 to $2.00 per ton, with a potential upside of $5.00 to $6.00 if the significant social co-benefits of their work—namely, feeding people—were factored into the price (Food Bank News, 2023).2 Climate technical consultants noted that while typical VCM prices ranged from $2 to $12 per ton, the novelty of food recovery credits could give them added value, as buyers are often attracted to projects with compelling social stories (Food Bank News, 2023).2

The BAMX experience demonstrates a critical reality: successfully entering the carbon market is likely beyond the reach of most food banks without significant external support from specialised technical consultants. The process is complex and requires a deep understanding of market mechanics and accounting methodologies. The relatively low initial price per credit also raises important questions about the economic viability of the model. When the substantial costs of consultancy, auditing, and ongoing monitoring are factored in, the net revenue for the food bank may be modest, especially in the early stages. This suggests that the decision to pursue carbon credits must be a strategic one, weighing the potential for a new, albeit potentially small, revenue stream against the significant upfront and ongoing resource commitment.

5.2 The Technology-Enabled Model: Food Rescue Hero & Brightly

A different approach to tackling the operational hurdles of the carbon market is being pioneered through a partnership between Food Rescue Hero, a technology platform used by food rescue organisations, and Brightly, a carbon project developer (Food Rescue Hero, 2025).36 This model positions technology as the key enabler for food banks to access carbon finance at scale.

The partnership leverages Verra's VM0046 methodology and is built on the premise that the rigorous data collection, tracking, and verification requirements of the carbon market are a major barrier for most non-profits (Food Rescue Hero, 2025).36 The Food Rescue Hero platform, which is already used to coordinate the logistics of food rescue, is uniquely positioned to solve this problem. It provides a standardised system for real-time data capture, enabling the precise tracking and verification of every pound of food rescued. This creates a seamless, auditable data trail that can be used to accurately calculate the associated emissions reductions and generate carbon credits (Food Rescue Hero, 2025).36

This technology-driven model attempts to address the additionality challenge head-on by focusing on the concept of "incrementality." The partnership claims that credits are generated based on verified, completed actions and the "incrementality of pounds of food rescued and emissions prevented" (Food Rescue Hero, 2025).36 This framing suggests that the platform can track growth in food rescue over time, attributing this incremental increase to the new incentives provided by the carbon finance program. By making the process more efficient and data-driven, the model aims to lower the barrier to entry for the food rescue organisations using the platform, allowing them to participate in the carbon market and create a new revenue stream to support their work (Food Rescue Hero, 2025).36 The credits generated through this partnership have received a preliminary 'AA' rating for additionality from the rating agency BeZero Carbon, placing them in the top tier of waste-related projects in the US and lending credibility to their approach (Brightly, n.d.).55

5.3 An Alternative Path: FareShare UK's Impact Reporting

The case of FareShare, one of the United Kingdom's largest food redistribution charities, presents a crucial and compelling alternative strategy. Rather than entering the VCM to sell offsets, FareShare undertook a rigorous carbon footprint analysis for a different purpose: to more powerfully communicate its social and environmental impact to its existing and potential funders (Food Bank News, 2023).2

Working with The Carbon Trust, a respected environmental consultancy, FareShare conducted a comprehensive assessment of its entire operation. They measured the carbon emissions associated with their warehouses, vehicle fleet, and refrigeration, as well as the embodied carbon in the food they distribute. They then compared this operational footprint to the emissions that were avoided by preventing that same food from going to waste. The results were striking and provided a powerful new metric for their fundraising and partnership efforts: for every one ton of carbon dioxide equivalent FareShare emits through its operations, it prevents nine tons from being unnecessarily wasted (Food Bank News, 2023).2

This approach represents a "third way" that may resolve the central paradox facing food banks. By using the language and rigour of carbon accounting as a tool for impact validation rather than offset generation, FareShare can leverage the powerful climate narrative to attract traditional funding—corporate donations, philanthropic grants, and government support—without inheriting the myriad reputational risks and integrity challenges of the VCM. They gain the primary benefit of the climate connection (a compelling, data-backed story of their value) while completely avoiding the primary risk (association with greenwashing, phantom credits, and the additionality debate).

This model suggests that the most valuable application of carbon accounting for food banks may not be in the direct sale of offsets, but in using the data to make a more sophisticated and compelling case to their traditional funding partners. It allows them to demonstrate their alignment with corporate sustainability goals and prove their efficiency as a solution that addresses both hunger and climate change simultaneously. This strategy protects their core asset—public trust—while still unlocking the value of their climate co-benefit, albeit through a different and arguably more stable financial channel.

Section 6: A Critical Path Forward: Recommendations and Conclusion

The intersection of food banking and carbon finance presents a landscape of immense opportunity and significant peril. The evidence is unequivocal: the work of food banks in diverting organic waste from landfills provides a profound and immediate climate benefit, targeting a potent greenhouse gas that conventional waste management systems struggle to control. Yet, the primary mechanism currently proposed for monetising this benefit—the voluntary carbon market—is a deeply flawed instrument, rife with integrity challenges that pose a direct threat to the public trust that is the lifeblood of any non-profit organisation. The path forward requires a clear-eyed assessment of these risks and a strategic approach that prioritises the long-term health of the mission over the lure of a volatile and controversial new funding stream. A shift in thinking is needed, away from the problematic logic of "offsetting" and towards a more honest and transparent model of corporate contribution to a vital social and climate solution.

6.1 Synthesising the Evidence

This report has established several key findings. First, the scale of the food waste problem is immense, accounting for 8-10% of global greenhouse gas emissions, with landfill methane being a particularly acute driver of near-term warming (IPCC, n.d.; UNFCCC, 2024).15 Second, the VCM, especially for "avoided emissions" projects, has a documented history of systemic failure, with a majority of credits from some major project types failing to represent real emissions reductions, thereby enabling corporate greenwashing (CSIS, 2024).3 Third, the principle of additionality presents a fundamental, perhaps insurmountable, paradox for food banks, whose climate-positive activities are an embedded co-benefit of a long-standing social mission, making the "but for" claim of carbon finance nearly impossible to verify (Grist, 2025; Salzman and Weisbach, 2024).1 Finally, while new methodologies are attempting to create a rulebook for this sector, they rely on simplifying assumptions, such as the choice of baseline, that may systematically overstate the climate impact (Grist, 2025; OffsetGuide.org, n.d.).1 The case studies reveal that while entry into the market is possible, it is resource-intensive and carries both financial and reputational risks, leading some organisations to pursue an alternative path of using carbon accounting for impact reporting rather than offset sales (Food Bank News, 2023; Food Rescue Hero, 2025).2

6.2 Strategic Recommendations for Stakeholders

Based on this comprehensive analysis, a set of strategic recommendations can be offered to the key actors in this emerging space.

For Food Banks:

  1. Prioritise Internal Accounting for Impact Reporting: Before considering the sale of carbon credits, food banks should first adopt the model pioneered by FareShare UK (Food Bank News, 2023).2 Invest in a robust internal carbon accounting framework, such as GFN's FRAME methodology, not to generate credits, but to measure, validate, and communicate their climate impact. This data is an incredibly powerful tool for traditional fundraising. It can be used to enhance grant proposals, strengthen corporate partnership pitches by demonstrating clear alignment with sustainability goals, and provide donors with a tangible, quantifiable return on their investment in both social and environmental terms. This strategy captures the upside of the climate narrative without inheriting the downside risk of the VCM.

  2. Approach the VCM with Extreme Caution and Transparency: If, after careful consideration, a food bank chooses to explore the sale of carbon credits, it must be treated as a high-risk venture, not a simple fundraising activity. This path should only be pursued with a clear understanding of the potential for public scrutiny and criticism. Key steps include partnering with highly reputable, expert consultants and project developers, demanding maximum transparency in all accounting and verification processes, and being prepared to publicly defend the project's additionality claims and baseline assumptions. The potential net revenue, after accounting for high transaction costs, must be carefully weighed against the significant and potentially irreversible risk to the organisation's public trust and reputation.

  3. Advocate for Systemic Policy Solutions: The VCM is, by its nature, a volatile and discretionary source of funding. A more sustainable and impactful long-term strategy is to advocate for public policy that creates systemic support for food rescue. This includes lobbying for policies modelled on California's SB 1383, which mandates organic waste diversion and requires edible food generators to donate surplus food (CalRecycle, n.d.).56 Such regulations create a stable, legally-backed framework for food rescue that is far more reliable than the fluctuating prices and questionable integrity of the voluntary market.

For Corporate Credit Buyers:

  1. Shift from an Offsetting to a Contribution Model: This is the single most important step corporations can take to engage with this sector responsibly. Companies should cease using food rescue credits to make claims of "carbon neutrality" or to "offset" their own unabated emissions. Such claims are not credible given the profound additionality challenges. Instead, they should adopt a "contribution model," an emerging best practice advocated by groups like Carbon Market Watch (Carbon Market Watch, n.d.).58 In this model, a company purchases credits and transparently reports this as a financial contribution to a high-impact project that delivers both social and climate benefits. This is an investment in climate action that occurs

    beyond the company's own value chain, not a substitute for it. This approach is honest, avoids greenwashing, and properly frames the purchase as a way of financing a vital community service with a climate co-benefit.

  2. Conduct Deep, Project-Level Due Diligence: Corporate buyers cannot and should not rely solely on a credit's certification by a standards body. The history of the VCM has shown that this is insufficient protection against low-quality credits. Buyers must conduct their own due diligence, scrutinising the specific project's documentation. They should critically question the additionality claims, interrogate the baseline scenario assumptions, and favour projects that offer high levels of transparency and utilise robust, technology-enabled, real-time data verification, such as the model proposed by Food Rescue Hero and Brightly (Food Rescue Hero, 2025).36

For Standards Bodies (Verra, Gold Standard):

  1. Acknowledge and Address the Unique Risk Profile: Standards bodies must formally recognise that projects involving mission-driven non-profits fall into a high-risk category for additionality. They should apply the most stringent possible verification standards to these projects and develop specific, rigorous guidance that addresses the unique challenges of applying financial additionality tests to organisations that are not profit-motivated. Projects with ambiguous or unverifiable additionality claims should be rejected.

  2. Actively Promote and Differentiate the Contribution Model: Verra, Gold Standard, and other market infrastructure players have a responsibility to educate the market. They should use their platforms to actively promote the integrity and value of contribution claims as a superior alternative to offsetting claims for certain project types. This could involve creating a distinct credit category or tag for projects intended for contribution claims, helping to detoxify the market and provide a credible pathway for corporate finance to support these projects without enabling greenwashing.

6.3 Conclusion: Funding the Co-Benefit, Protecting the Mission

The climate benefit generated by the global network of food banks is real, significant, and urgently needed. The question is not whether this climate service has value, but how to finance it with integrity. The voluntary carbon market, in its current form, is a deeply flawed and hazardous instrument for this task. Its foundational logic of offsetting, combined with its systemic integrity failures, creates a framework that risks corrupting the social mission of food banks and enabling a new and insidious form of corporate greenwashing. To force these vital community organisations to contort their mission to fit the broken logic of the offset market is to get the solution backward.

The path forward lies in a fundamental reframing of the relationship. The climate work of food banks should be recognised and funded for what it is: a powerful and measurable co-benefit of their primary social mission. The challenge for the climate finance community, for corporate sustainability leaders, and for standards bodies is not to bend food banks to the will of a dysfunctional market, but to design and champion new, more honest mechanisms that can support their work. The contribution model offers such a path. It allows corporations to fund this vital work transparently and honestly, celebrating it as a direct investment in community resilience and climate mitigation. This approach protects the invaluable public trust that food banks have earned over decades, ensuring that in their quest to nourish the planet, they do not compromise their sacred mission of nourishing its people.

Bibliography

Advanced Waste Solutions. (2023). Food Waste, Methane Gas, and the U.S. EPA. [Online]. Available at: https://advancedwastesolutions.ca/2023/10/28/food-waste-methane-gas-and-the-u-s-epa/. 19

AP News. (2023). Americans are still putting way too much food into landfills. Local officials seek EPA's help. [Online]. Available at: https://apnews.com/article/epa-food-waste-methane-landfills-f34ce9d1a8a58a95250f5f5883470ba0. 10

Aquila. (n.d.). Verra vs. Gold Standard: Which Certification is Right for Your Project? [Online]. Available at: https://aquila.is/knowledge-hub-article/verra-vs-gold-standard-which-certification-is-right-for-your-project/. 23

BioCycle. (2023). Connections: Food Waste And Landfill Methane Report — A Giant Step On A Long Road. [Online]. Available at: https://www.biocycle.net/connections-food-waste-and-landfill-methane-report-a-giant-step-on-a-long-road/. 20

Brightly. (n.d.). Solutions. [Online]. Available at: https://www.brightly.earth/solutions. 55

CalRecycle. (n.d.). California's Short-Lived Climate Pollutant Reduction Strategy (SB 1383). [Online]. Available at: https://www.calrecycle.ca.gov/organics/slcp. 56

Calyx Global. (n.d.). What is additionality in carbon credits? [Online]. Available at: https://calyxglobal.com/research-hub/research/when-are-carbon-credits-additional. 29

Carbon Brief. (2023). In-depth Q&A: What food waste means for climate change. [Online]. Available at: https://www.carbonbrief.org/in-depth-qa-what-food-waste-means-for-climate-change/. 16

Carbon Market Watch. (2024). Cooking the climate books: New peer-reviewed study finds carbon credit impact vastly overstated. [Online]. Available at: https://carbonmarketwatch.org/2024/11/14/cooking-the-climate-books-new-peer-reviewed-study-finds-carbon-credit-impact-vastly-overstated/. 34

Carbon Market Watch. (n.d.). Carbon offsetting. [Online]. Available at: https://carbonmarketwatch.org/carbon-offsetting/. 58

CarbonCredits.com. (n.d.). The Ultimate Guide to Understanding Carbon Credits. [Online]. Available at: https://carboncredits.com/the-ultimate-guide-to-understanding-carbon-credits/. 26

ClearBlue Markets. (2024). Verra's New Additionality Tools to Align with Core Carbon Principles. [Online]. Available at: https://www.clearbluemarkets.com/knowledge-base/verras-new-additionality-tools-to-align-with-core-carbon-principles. 42

CSIS. (2024). What’s Plaguing Voluntary Carbon Markets? [Online]. Available at: https://www.csis.org/analysis/whats-plaguing-voluntary-carbon-markets. 3

Endangered Landscapes Programme. (2023). Additionality in carbon market projects. [Online]. Available at: https://www.endangeredlandscapes.org/wp-content/uploads/2023/09/ELP_demonstrating_additionality_primer.pdf. 27

EPA. (2021). From Farm to Kitchen: The Environmental Impacts of U.S. Food Waste. [Online]. Available at: https://www.epa.gov/land-research/farm-kitchen-environmental-impacts-us-food-waste. 8

EPA. (2023). Quantifying Methane Emissions from Landfilled Food Waste. [Online]. Available at: https://www.epa.gov/land-research/quantifying-methane-emissions-landfilled-food-waste. 5

EPA & USDA. (2024). Methane and Food Waste. [Online]. Available at: https://www.epa.gov/system/files/documents/2024-06/epa_usda_methane_and_food_waste_fact_sheet.pdf. 11

ERG. (n.d.). Understanding Methane Emissions from U.S. Food Waste. [Online]. Available at: https://www.erg.com/project/understanding-methane-emissions-us-food-waste. 7

Food Bank News. (2023). Mexican Food Bank Earns World's First Carbon Credits for Food Rescue. [Online]. Available at: https://foodbanknews.org/mexican-food-bank-earns-first-carbon-credits-for-food-rescue/. 2

Food Rescue Hero. (2025). How Carbon Credits Can Fuel Food Rescue and Fight Climate Change. [Online]. Available at: https://foodrescuehero.org/how-carbon-credits-can-fuel-food-rescue-and-fight-climate-change/. 36

Frontiers. (2020). Life Cycle Assessment of an Innovative Food Waste Management System. [Online]. Available at: https://www.frontiersin.org/journals/sustainable-food-systems/articles/10.3389/fsufs.2020.00023/full. 50

Frontiers in Climate. (2021). Voluntary Carbon Markets: A Review of Global Initiatives and Evolving Models. [Online]. Available at: https://www.frontiersin.org/journals/climate/articles/10.3389/fclim.2021.686516/full. 33

GFN. (2024). FRAME Methodology: Food Recovery to Avoid Methane Emissions. [Online]. Available at: https://www.foodbanking.org/wp-content/uploads/2024/08/FRAME-Methodology_Food-Recovery-to-Avoid-Methane-Emissions_GFN.pdf. 49

GFN. (n.d.). Climate Financing for Food Banking: New Research Explores Opportunities to Scale Food Recovery. [Online]. Available at: https://www.foodbanking.org/news/climate-financing-for-food-banking-new-research-explores-opportunities-to-scale-food-recovery/. 48

Global Witness. (n.d.). Carbon trading continues: what's wrong with the voluntary market? [Online]. Available at: https://www.globalwitness.org/en/campaigns/greenwashing/carbon-trading-continues-whats-wrong-with-the-voluntary-market/. 22

Gold Standard. (2024). Reduction in methane emissions from landfills through decentralised organic waste processing. [Online]. Available at: https://globalgoals.goldstandard.org/documents/methodology/. 43

Grist. (2025). Food banks are eyeing carbon credits to fund their work. Critics are wary. [Online]. Available at: https://grist.org/food-and-agriculture/food-banks-carbon-credits-food-waste-methane-controversy/. 1

Illuminem. (2024). A Buyer's Guide to Carbon Credits: Between Criteria and Challenges. [Online]. Available at: https://illuminem.com/illuminemvoices/a-buyers-guide-to-carbon-credits-between-criteria-and-challenges. 4

IPCC. (n.d.). Chapter 5: Food Security. [Online]. Available at: https://www.ipcc.ch/srccl/chapter/chapter-5/. 18

Kotchen, M.J. (n.d.). Offsetting Guilt. [Online]. Available at: https://environment.yale.edu/kotchen/pubs/ssirfinal.pdf. 35

MDPI. (n.d.). Food Waste Reduction: A Systematic Literature Review on Integrating Policies, Consumer Behaviour, and Innovation. [Online]. Available at: https://www.mdpi.com/2071-1050/17/7/3236. 17

Medium. (n.d.).Revolutionising Food Waste: The First Home Food Recycling Methodology for Carbon Emissions. [Online]. Available at: https://medium.com/@tradefin101/revolutionizing-food-waste-the-first-home-food-recycling-methodology-for-carbon-emissions-0a01238dcada 47

Medium. (n.d.). Verification: The Critical Step for Voluntary Carbon Projects. [Online]. Available at: https://medium.com/@iskenderkokey/verification-the-critical-step-for-voluntary-carbon-projects-9b1cd95dc6da. 24

Norton Rose Fulbright. (n.d.). Creating carbon offset units on the voluntary market. [Online]. Available at: https://www.nortonrosefulbright.com/en-nl/knowledge/publications/6f326481/creating-carbon-offset-units-on-the-voluntary-market. 37

OffsetGuide.org. (n.d.). What Makes High-Quality Carbon Credits? [Online]. Available at: https://offsetguide.org/what-makes-high-quality-carbon-credits/. 31

Open Access City University. (n.d.). Environmental impact of different waste-to-food approaches. [Online]. Available at: https://openaccess.city.ac.uk/id/eprint/27924/1/Environmental%20impact%20of%20different%20waste%20to%20food%20approaches%20v6%20%28Recovered%29.pdf. 53

OSTI. (n.d.). Consequential life cycle assessment of food waste and sewage sludge management strategies. [Online]. Available at: https://www.osti.gov/pages/biblio/2352208. 52

PubMed. (2023). Consequential life cycle assessment of food waste and sewage sludge management strategies. [Online]. Available at: https://pubmed.ncbi.nlm.nih.gov/37244015/. 51

ReFED. (2024). Uneaten Food Is Responsible for 14 Per cent of U.S. Methane Emissions, According to New ReFED Study. [Online]. Available at: https://refed.org/articles/uneaten-food-is-responsible-for-14-percent-of-u-s-methane-emissions-according-to-new-refed-study/. 13

ReFED. (n.d.). Climate and Resources. [Online]. Available at: https://refed.org/food-waste/climate-and-resources/. 12

ResearchGate. (n.d.). Life cycle assessment of the food waste management with a focus on the collection bag. [Online]. Available at: https://www.researchgate.net/publication/354928652_Life_cycle_assessment_of_the_food_waste_management_with_a_focus_on_the_collection_bag 54

RMI. (n.d.). Waste Methane 101: Driving Emissions Reductions from Landfills. [Online]. Available at: https://rmi.org/waste-methane-101-driving-emissions-reductions-from-landfills/. 6

Salzman, J. and Weisbach, D.A. (2024). The Additionality Double Standard. Harvard Environmental Law Review, 48(1). [Online]. Available at: https://journals.law.harvard.edu/elr/wp-content/uploads/sites/79/2024/04/03_HLE_48_1_Salzman-Weisbach.pdf. 32

Senken. (n.d.). Voluntary Carbon Market: Issues and Opportunities. [Online]. Available at: https://www.senken.io/blog/voluntary-carbon-market-issues-and-opportunities. 21

SustainCERT. (n.d.). Carbon Credits 101: What is the Gold Standard? [Online]. Available at: https://sustain-cert.com/news/carbon-credits-101-what-is-the-gold-standard. 38

Swiss Climate. (n.d.). How climate protection projects influence Switzerland's food waste target. [Online]. Available at: https://www.swissclimate.ch/en/blog/how-climate-protection-projects-influence-switzerlands-food-waste-target. 41

Sylvera. (n.d.). Additionality in carbon offsets. [Online]. Available at: https://www.sylvera.com/blog/additionality-carbon-offsets. 28

UNDO. (n.d.). Understanding Additionality in Carbon Offsetting. [Online]. Available at: https://un-do.com/resources/blog/understanding-additionality-in-carbon-offsetting/. 30

UNFCCC. (2024). Food loss and waste account for 8-10% of annual global greenhouse gas emissions; cost USD 1 trillion annually. [Online]. Available at: https://unfccc.int/news/food-loss-and-waste-account-for-8-10-of-annual-global-greenhouse-gas-emissions-cost-usd-1-trillion. 15

USDA. (2022). Food Waste and Its Links to Greenhouse Gases and Climate Change. [Online]. Available at: https://www.usda.gov/about-usda/news/blog/food-waste-and-its-links-greenhouse-gases-and-climate-change. 9

Verra. (2023). Verra Releases Food Loss and Waste Methodology. [Online]. Available at: https://verra.org/verra-releases-food-loss-and-waste-methodology/. 39

Verra. (n.d.). Beyond the Headlines: A Constructive Response to Criticism of Validation and Verification in the VCM. [Online]. Available at: https://verra.org/verra-views/beyond-the-headlines-a-constructive-response-to-criticism-of-validation-and-verification-in-the-vcm/. 25

WRAP. (n.d.). Food waste contributes 10% to global emissions, but 9 out of 10 countries' NDCs fail to focus on food loss and waste. [Online]. Available at: https://www.wrap.ngo/media-centre/press-releases/food-waste-contributes-10-percent-global-emissions. 14

Comments

Popular posts from this blog

Beyond Incineration

Navigating the Global Energy Storm

Strategic Dialogues and Cambodian Excellence