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Verra

Verra, a leading non-profit VCM registry in the US has recently released its Verified Carbon Standard (VCS) modular methodology VM0049 for carbon capture and storage (CCS). Carbon dioxide removals play a crucial role in corporate net-zero strategies. Thus, VM0049 is a global framework for tech-based CCS activities that generate carbon dioxide removals (CDRs) and emission reductions.

Unlocking the Future of Carbon Capture: VM0049’s Modular Approach

CCS involves CO2 capture directly from the atmosphere or from high-emission industrial sources. It is then transported or permanently stored underground. CCS is a highly efficient technique to combat CO2 emissions in tough sectors like industrial manufacturing (e.g., cement), oil and natural gas, and power generation.

VM0049 underscores the key requirements essential for CCS projects. Verra’s press release describes that these projects can choose from various modules for CO2 capture, transport, and storage activities to quantify their CDRs and emission reductions. Furthermore, the modules are customizable to fit a project’s design and technological needs. The unique modular format adapts to project expansions, shared infrastructure development, and future innovations.

Verra is set to launch the initial modules in the upcoming months, encompassing the following activities:

  • Direct air capture
  • CO2 transportation
  • CO2 storage in saline aquifers and depleted oil and gas reservoirs

At present, multiple additional modules are under development to encompass a wide range of activities supported by VM0049.

Image: An overview of Verra’s CCS and Transport Model

Verra

Pre-requisites for Carbon Capture from Ambient Air

This module governs projects that capture CO2 from ambient air using the latest VM00XX Methodology for Carbon Capture and Storage. Verra’s draft highlights that these projects must meet the following conditions:

  1. Capture activities must extract atmospheric CO2, potentially alongside CO2 from on-site point sources such as oxy-fuel combustion. Methods may include chemical or physical absorption/adsorption with solvents or sorbents (e.g., amines), membrane processes, electrochemical processes, or cryogenic processes.
  2. The primary capture fluid or media must be regenerated to prevent one-time use. It should yield a concentrated CO2 stream available for subsequent transport and storage.
  3. Capture facilities must either be new, expand existing ones, or refurbish those that would otherwise be decommissioned at the project’s start.
  4. Both existing and new capture facilities can share auxiliary equipment like utilities.

Notably, this framework ensures that CO2 capture from ambient air meets rigorous standards, facilitating effective carbon storage and utilization. The draft is yet to be finalized.

Milestones for Geologic Carbon Storage (GCS)

The methodology is evolving in stages using a modular approach. The initial phase will emphasize storing carbon in saline aquifers and depleted oil and natural gas reservoirs. Later phases will focus on using captured carbon, storing it, and carbon mineralization in geological formations. Each type of GCS project (CCS, GCM, or CCUS) will have specific requirements. Verra has outlined all the rules applicable to GCS projects under the VCS Program.

Verra examines two approaches to managing risks in GCS projects. Regulatory measures establish eligibility criteria, operational requirements, and closure obligations outlined in the VCS Standard and GCS Requirements. The Geologic Carbon Storage Non-Permanence Risk Tool assesses project risks. It allocates funds to the GCS pooled buffer account to protect the validity of all issued Verified Carbon Units (VCUs) from possible reversals.

CO2 Transport Module Boundary

The CO2 transport module covers all processes in the CO2 transport value chain. Key processes include CO2 conditioning (like dehydration and cooling), compression, and loading/unloading from ships, trains, and trucks. It also provides for the propulsion of these transport modes, maintaining CO2 conditions in pressure vessels, and reconditioning CO2 for different transport modes or delivery conditions.

Verra signifies defining module and segment boundaries crucial for projects with diverse ownership. For now, the activities are divided into intermediate storage sites and transport segments within the transport module. Intermediate storage sites handle temporary CO2 storage during transfer, while transport segments involve equipment and processes for moving CO2 through a consistent transportation system. All documents are currently in their draft stage.

Figure: Verra’s Module boundary for CO2 transport (for public consultation)

Verrasource: Verra

Overall, Verra’s framework supports various capture, transport, and storage technologies. They ensure real, additional, and high-integrity emission reductions and removals (ERRs) globally. Deploying CCS and engineered CDR technologies is crucial to limit global warming to 1.5℃. These technologies complement emission reduction efforts, offset residual emissions, and provide a net negative CO2 option.

Disclaimer: Information in the content has been sourced from Verra

The post What’s New in Verra’s Latest CCS Methodology Update? Find Out! appeared first on Carbon Credits.

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Carbon Footprint

Insetting vs Offsetting: Which Actually Counts Toward Your Scope 3 Targets

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The accounting differences that decide whether your nature investment shows up in inventory, in BVCM, or nowhere at all.

The question reaches a procurement team about three weeks before the next sustainability committee meeting. Someone has read about insetting. Someone else has just signed off on an offset purchase. The CSO wants to know if the two are interchangeable. The answer is no, and the GHG Protocol Land Sector and Removals Standard is the reason why.

This article walks through what each term means at audit-grade specificity, what the standards actually say about how each gets counted, and how to decide which tool fits which target. The insetting vs offsetting question is one of the most-searched in corporate climate strategy, and one of the most poorly answered. By the end of this piece, you should be able to brief a committee on the difference without notes.

The two definitions, in plain English

Offsetting means buying carbon credits generated outside your value chain and retiring them against your residual emissions. The reduction happens somewhere else, financed by you, and the credit is the receipt.

Insetting means investing in emission reductions or removals inside your own value chain, typically with suppliers, where the reduction is directly linked to the products and services you buy. The reduction happens inside the boundary of your Scope 3 inventory, and the accounting treatment is fundamentally different.

The shorthand from the University of Oxford’s Nature-based Insetting Initiative is useful: insetting is what you do with the supply chain you have; offsetting is what you do with the supply chain you do not have.

What the GHG Protocol Land Sector Standard actually says

The GHG Protocol Land Sector and Removals Standard, finalised in 2024 after a multi-year pilot, sets the rules for how land-based emission reductions and removals enter corporate inventories. The Standard distinguishes between inventory accounting (Scope 1, 2, and 3) and project or intervention accounting (a separate methodology for crediting).

For insetting, the practical implication is that supplier-level interventions, when properly measured and attributed, can reduce your Scope 3 category 1 (purchased goods and services) emissions in your inventory. The reduction is not a credit retired against the inventory; it is a lower inventory number, period.

For offsetting, the credit is retired separately. It can be reported as a contribution toward a net-zero claim under the SBTi Beyond Value Chain Mitigation framework or as part of a VCMI Carbon Integrity claim, but it does not lower the inventory number.

A practical consequence: if your Science Based Target requires a 50% absolute reduction in Scope 3 emissions by 2030, insetting moves you toward the target. Offsetting does not. This single point of difference reshapes the procurement decision.

When insetting counts toward Scope 3 (and when it does not)

Insetting counts toward Scope 3 only when several conditions are met:

  • The intervention must occur with an entity in your value chain.
  • The emissions reduction or removal must be measured against a defensible baseline.
  • The reduction must be attributed to your share of that supplier’s output, not double-counted with other buyers.
  • It must follow the inventory accounting rules in the GHG Protocol Land Sector Standard, not the project accounting rules used to generate credits.

The most common failure mode is double counting. If your supplier sells the same reduction as a credit on the voluntary market and also reports it to you as a Scope 3 reduction, the math breaks. The Standard requires you to address this risk, typically by purchasing and retiring the supplier-issued credit as part of your inventory or by contractual provisions that prevent the supplier from selling the reduction twice.

When insetting does not count toward Scope 3: when the intervention sits with a supplier you do not buy from, when the baseline is not defensible, when the attribution is unclear, or when the documentation does not survive audit. Those cases default to Beyond Value Chain Mitigation, which is still useful but operates on a different ledger.

The procurement and supplier engagement question

Insetting is harder than offsetting. That is the unfashionable truth most buyers eventually confront. Offsetting is a transaction; insetting is a relationship.

To run an insetting program, you need supplier mapping precise enough to know which farms or facilities sit at which Scope 3 boundary. You need an engagement model that gets suppliers to participate, which usually requires multi-year commitments and shared economics. You need an MRV architecture that measures the right things and produces audit-ready documentation. And you need a contractual structure that prevents double counting and protects both sides.

The trade-off you receive in return is significant. Reductions count against your inventory rather than your residual. Supplier relationships deepen, which protects sourcing continuity. Yield and quality improvements often follow regenerative interventions, which reduces your input cost over time. And the regulatory file, under CSRD, CSDDD, EUDR, and the SBTi FLAG Guidance, is materially stronger.

Choosing the right tool for the right target

A practical decision rule. If your target is a science-based Scope 3 reduction and you operate in a FLAG sector or source FLAG commodities, insetting is the structurally correct tool. If your target is a net-zero claim that includes neutralising hard-to-abate residual emissions outside your value chain, BVCM via high-integrity offsets is the structurally correct tool. Most companies with material Scope 3 exposure need both, in different proportions, sequenced over time.

The sequencing matters. Insetting takes longer to stand up but produces a permanent reduction in the inventory. Offsetting can be transacted faster but does not change the inventory and now sits under tighter claim restrictions. Treat them as complementary tools with different jobs, not as substitutes. The Accountability Framework Initiative and the IUCN Global Standard for Nature-based Solutions both provide useful guardrails for the insetting side, with biodiversity, human rights, and benefit-sharing requirements that go beyond carbon math.

If you are mapping a Scope 3 reduction roadmap and need to scope which interventions count toward your inventory versus which sit in Beyond Value Chain Mitigation, the carbon and sustainability experts at Carbon Credit Capital can help you structure a nature-based supply chain investment program that fits your FLAG exposure, your target architecture, and your audit horizon. Schedule a consultation.

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Carbon Footprint

Net zero needs nature: a carbon credit guide

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Net zero is often described as a balancing act: cut what you can, account for the rest, and reach zero on the ledger. That framing is useful, but it leaves something out. It treats every tonne of carbon as interchangeable and every route to zero as equally sound, while the science tells a more specific story.

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Carbon Footprint

Deforestation in Malawi: causes and solutions

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Malawi has lost a striking share of its forests over the past three decades. Woodlands that once covered well over a third of the country now cover less than a quarter, and the pressure on what remains is increasing. Behind those figures sit two practical questions: what is driving the loss, and what reverses it?

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