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Welcome to the Riverse Documentation Hub—your go-to resource for everything related to our carbon registry: standard rules, procedures, and methodologies. Whether you are a project developer, partner, or carbon credit buyer, this platform is designed to provide you with all relevant information you might look in a efficient navigation system.
Why this documentation?
At Riverse, we believe that consistency, transparency, and adherence to well-defined standards are the cornerstones of trustful and success Voluntary Carbon Markets.
Our documentation is providing detailed guidance, rules and structured approaches to all processes of our carbon standard and registry.
Our Riverse Standards Document section covers the essential rules and guidelines that govern our standard and registry across all methodologies and project types.
Each methodology gives specific requirements and quantification methods per project types.
It should be used together with the latest versions of the , , , and all other documentation found on this site.
Download any page as a PDF by clicking the Export as PDF button to the right
Riverse is a simplified joint-stock company ("société par actions simplifiée") with its headquarters situated at 28 Avenue des Pépinières, 94260 Fresnes, France, and is registered in the Créteil Companies and Trade Register with the number 908 082 332.
As a mission-driven entity ("Société à Mission"), Riverse has a defined purpose pursuant to Article 1835 of the French Civil Code.
The company's mission is to create significant and positive environmental or social impact through its commercial and operational activities, and to conduct its business with exemplary professionalism in the pursuit of the collective interest. In alignment with its mission, the company is dedicated to:
Advancing solutions that contribute a net environmental or social benefit to both the community and the planet;
Engaging with partners and customers who share the company's values and objectives;
Delivering significant value and impact through its partnerships and client interactions;
Ensuring the dignity of individuals and promoting a healthy work-life balance for its employees.
Building upon its core mission, the simplified joint-stock company Riverse operates two entities:
The Riverse Standard: A European crediting program within the voluntary carbon market, tailored for industrial projects that demonstrate the potential for significant reductions or sequestration of greenhouse gas (GHG) emissions. The Riverse Standard prescribes exacting certification criteria, rooted in stringent scientific methodology and designed to align with the principal frameworks dedicated to fostering transparency and integrity in the voluntary carbon market.
The Riverse Tech Infrastructure: Serving as the operational backbone for the Riverse Standard, this infrastructure comprises two principal components:
The Riverse Registry: Ensuring traceability and transparency, it maintains detailed records of Riverse Carbon Credits from issuance to retirement, thereby preventing double counting and adhering to the protocols recommended by carbon market integrity organizations.
The Impact Certification Platform: This platform streamlines the RCCs certification (validation and verification) process for Project Developers by offering tools for environmental impact assessment, documentation assembly, and simplifying validation and verification procedures. With features designed for third-party Validation and Verification Bodies (VVB), it promotes a transparent and efficient pathway for project auditing and RCC management.
Both entities are managed by the Riverse Executive Team and supported by the internal teams within Riverse.
Overview of the Riverse Organization:
The Riverse Standard's governance architecture is designed to ensure scientific rigor, independence and efficiency.
It is spearheaded by two principal independent entities: the Standard Advisory Board and the Technical Advisory Committee.
Standard Advisory Board (SAB)
Ensures Riverse’s activity is continuously in line with its foundational mission. Provides strategic direction, endorses or vetoes amendments to the standard rules and methodologies, and recommends enhancements.
Technical Advisory Committee (TAC)
Composed of independent experts, provides technical expertise and reviews on specific methodological aspects or project certification.
In addition to these independent governance entities, four specialized Riverse teams are dedicated to the standard's operational execution:
Executive Team
Manages the organization's day-to-day operations
Secretariat
Compiles and synthesizes feedback and updates on standard documents, and conveys these to the Standard Advisory Board for deliberation and approval.
Certification team
Primary point of contact for Project Developers navigating the standard processes, provides technical assistance, process guidance, feedback, and performs the final validation review.
Climate team
Oversees the scientific approach and choices behind Riverse Standard Rules and methodologies. As GHG quantification and climate solution experts, they assist the Certification team in case of technical inquiries.
All Riverse ecosystem stakeholders are contractually linked with Riverse. The following stakeholders are publicly disclosed:
The following is the minimum list of stakeholders who must sign the policy:
Members of the Executive board
Members of the Secretariat, Standard Advisory Board
Members of the Climate, Certification, R&D and Partnerships teams
Members the Technical Advisory Board
VVBs
Project information, including documentation, detailed calculations, audit/verification/monitoring statements, as well as reports and legal representations
Transparent issuance tracking, transfer and retirement/cancellation of units
Individually identified units through unique serial numbers containing sufficient information to avoid double counting (type, geography, vintage)
Unit status (issued, verified, retired, canceled), with full traceability of the chain of custody
6.3 Improve water quality by reducing pollution, eliminating dumping and minimizing release of hazardous chemicals and materials
6.4 Increase water-use efficiency
6.5 Protect and restore water-related ecosystems
7.2 Increase substantially the share of renewable energy in the global energy mix
7.3 Double the global rate of improvement in energy efficiency
7.4 Facilitate access to clean energy research and technology
8.2 Achieve higher levels of economic productivity through diversification, technological upgrading and innovation
8.3 Support decent job creation and innovation, and encourage micro-, small- and medium-sized enterprises
8.4 Improve global resource efficiency in consumption and production
8.5 Achieve full and productive employment and decent work for all women and men, including for young people and persons with disabilities
9.4 Upgrade infrastructure and retrofit industries to make them sustainable, with increased resource-use efficiency and greater adoption of clean and environmentally sound technologies and industrial processes
11.6 Reduce the adverse per capita environmental impact of cities, including air quality and municipal and other waste management
11.a Support positive economic, social and environmental links between urban, peri-urban and rural areas
12.2 Achieve the sustainable management and efficient use of natural resources
12.4 Achieve the environmentally sound management of chemicals and all wastes throughout their life cycle
12.5 Reduce waste generation through prevention, reduction, recycling and reuse
13.2: Integrate climate change measures into national policies, strategies and planning (note that only GHG reduction measures beyond what is considered for carbon credit issuance may be considered as a co-benefit)
14.1 Prevent and significantly reduce marine pollution of all kinds, in particular from land-based activities, including marine debris and nutrient pollution
14.3 Minimize and address the impacts of ocean acidification
15.1 Ensure the conservation, restoration and sustainable use of terrestrial and inland freshwater ecosystems and their services
15.5 Reduce the degradation of natural habitats, halt the loss of biodiversity and, by 2020, protect and prevent the extinction of threatened species
GHG emissions and reductions shall be calculated using the following IPCC Global Warming Potential (GWP) values for a 100 year horizon according to . The GWPs for the main greenhouse gasses are summarized below, and the full list of GWPs can be found in the , Table 7.SM.7.
1
29.8
27
273
HFC-32
771
HFC-134a
1526
CFC-11
6226
PFC-14
7380
The following security measures are the minimum requirements for the Riverse Registry, and ensure confidentiality, integrity, and data availability:
Data transfers shall always use industry-standard encryption technology (SSL/TLS/HTTPS).
Application authentication shall be enabled and verified by a third-party provider that meets industry best practice, is internationally recognized, and is ISO27001 certified.
Backend service and database hosting shall be enabled by a third-party provider that enables encryption.
Administrative tools shall be provided 2FA for admin authentication and sign-in.
The Riverse Secretariat shall verify at least twice per calendar year that the IT security requirements are met, and summarize the findings in a report made publicly available on the Riverse website. The following elements shall be verified:
Verify compliance with the above requirements
Verify security vulnerability status and upgrade all JavaScript dependencies with npm.
Review Authentication provider access
Review Cloud provider IAM accounts and access
Rotate database passwords, API keys (internal and external)
Review Database connection allowlist
Review repository history for leaked secrets
Verify application authorization rules
Some projects have particularly high environmental impacts in their first year(s) of operation. This can be caused by inefficiency in early stages of operations while ramping up their processes. For example, at the beginning of a project, there may be very high consumption of inputs for a rather low production of outputs. This does not include emissions of construction and infrastructure, which are amortized over many years.
In some cases, this ramp-up effect may lead the project to emit more GHGs than the baseline scenario in the first year of the crediting period. In this case, the project’s validation and verification of the first two years will be bundled. This way, the project’s net induced emissions from the first year are subtracted from the avoided emissions of the second year.
If the project is still a net emitter and does not avoid any emissions at the end of the second year of the crediting period, the project will be dropped from the Riverse certification process.
When RCCs are bundled for the first two years of a crediting period, the vintage is the second year.
Note that this ramp-up effect only relates to high volume or frequent use of consumables in the first year, not to fixed inputs such as machinery and buildings. This is because according to the LCA approach, the emissions of these long-lived inputs are distributed annually over their usable lifespan. Fixed inputs refer to products where the lifespan is more than 1 year, and includes objects such as machinery, tanks, pipelines, building materials, and concrete slabs. Consumables refer to inputs that are taken up by the process and consumed in order to create the product. Their use is usually recurring and ongoing, and include inputs such as electricity, water, fuel for transportation, feedstock inputs (for biogas), and replacement screens (for electronics reconditioning).
There are two types of avoided emissions: those that lead to an absolute decrease in emissions, and those that lead to a smaller increase in emissions.
Absolute decrease: there is a real absolute decrease in emissions compared to the baseline scenario.
Smaller increase: there is a relative decrease in emissions compared to the baseline scenario, but still an absolute increase in emissions. This may happen when a project intervenes in a sector with growing demand, where overall production increases, so emissions increase over time.
Moreover, any stakeholder of Riverse’s ecosystem is under .
Finally, Riverse implements a robust that sets out how the Riverse organization identifies, manages, prevents, and discloses potential or real conflicts of interest to comply with the applicable regulatory requirements and code of practices.
Contractors to the Riverse Standard involved in at least one of the procedures described in the .
The Riverse Registry is openly accessible through Riverse’s website , and displays the following information to ensure maximum transparency and traceability of Riverse Carbon Credits:
The Riverse Registry IT security requirements are detailed in the Appendix 6.5.
Below is a selection of co-benefits that are particularly aligned with Riverse’s program objectives. They are taken from the .
CO
CH fossil
CH biogenic
NO
For example, if Project A launches in Year 1 and is found to emit 300 tCOeq more than the baseline scenario, no RCCs are issued for Year 1.
In Year 2, Project A avoids 4,000 tCOeq compared to the baseline scenario. After verification at the end of Year 2, Project A is issued 4,000 - 300 = 3,700 RCCs.
For example, if a machine is installed in Year 1, and its life cycle carbon footprint is 50 tCOeq, and it has a 25 year service life, its impacts included in the Year 1 calculations are 50/25= 2 tCOeq. For every year of operation, 2 tCOeq are counted from the machine. There is no ramp-up effect because the impacts of the machine are the same in Year 1 as all other years.
Both types of avoided emissions can be eligible for RCCs, as long as they meet the for their sector.
All Riverse Carbon Credits are issued ex post, after the verification process.
Removal RCCs are issued on Riverse’s registry under the mechanism label “removal”. They represent one tonne of carbon dioxide equivalent captured and stored: 1 removal RCC = 1 .
Avoidance RCCs are calculated by comparing GHG emissions of the project to the ones of a reference or baseline scenario that would have occurred without the project.
Avoidance RCCs are classified on Riverse’s registry under the mechanism label “avoidance”. They represent one avoided tonne of carbon dioxide equivalent: 1 avoidance RCC = 1 .
Credit pools are defined as a group of Riverse Carbon Credits from the same project, mechanism and vintage year. Each transaction in the Riverse Registry may cover credits from one credit pool. For example, separate transactions are required to retire credits from two different credit pools.
A project is uniquely described on the registry by:
Project registry ID
Project name
Name of the Project Developer
Location
Host country
Type of mechanism (avoidance and/or removal)
Crediting period
Validation body
Other labels where relevant (e.g. CORSIA, Article 6, CCP…)
Each RCC is uniquely described on the registry by:
unique identifier
Project registry ID
Vintage year (year of verified activity in verification)
Type of mechanism (avoidance or removal)
Methodology ID
Riverse Standard Rules version number
Host country (inherited from Project)
Other labels where relevant (e.g. CORSIA, Article 6, CCP…)
Riverse Carbon Credits and provisional credits can have different statuses on the Riverse Registry:
Provisional
Provisional credits are estimated credits from projects that are validated but not yet verified. They give visibility on the volume of expected credits, which enables pre-purchase agreements. They may result from:
Validated projects that are still in the planning phase, and have completed a validation audit, and ex-ante estimates of avoided/removed emissions.
Verified
Canceled
Riverse Carbon Credits can be “canceled” if the verification audit demonstrates that the previous ex-post credits were not legitimate, or if a reversal event is reported (for removal RCCs).
Retired
Riverse Carbon Credits are “retired” when a buyer claims them, they can’t be transacted anymore and are considered permanently used. They still appear on the Riverse Registry for traceability, with the label “retired”.
Verified RCCs may have labels, which are supplementary information and do not change the inherent status of a verified avoidance or removal RCC. Labels may cover, for example:
Permanence horizons: e.g. 100 or 1000 year permanence for removal RCCs
Compliance with trading schemes: e.g. CORSIA eligible, Article 6 eligible
Accredited: e.g. ICROA accredited, ICVCM accredited
Provisional credits are estimated upon project validation for the projected volume of emission avoidance/removal over the project’s crediting period. They are conservatively calculated.
Pre-purchase agreements are signed agreements between the PD and a buyer with defined volumes and prices of Riverse Carbon Credits. These can be made once provisional credits have been estimated and the project has been validated.
Provisional credits are only used to track pre-purchase agreements for buyers. Their property rights can not be transferred to the buyer until the mitigation activity occurs and they are verified (hence become RCCs).
The Riverse Standard Documentation is the set of documents that describes requirements and procedures for all projects and methodologies under the Riverse Standard.
The revision of the Procedures Manual follows the same process.
Major revisions are tracked through the first number after the standard document name (e.g. Riverse Standard Rules V1). Major revisions include three phases: submission, review, and approval.
Open feedback: All the latest versions of the Riverse Standard Rules and methodologies documentation are published on Riverse’s website. This allows any interested party to be able to comment on every document at any time—not only during dedicated public consultations.
To ensure the relevance and rigor of the Riverse Standard Documentation, the Climate team and the Secretariat actively monitor all references, and propose changes from referenced standards and tools (IPCC, ISO…).
Compilation of feedback: The Secretariat compiles feedback into a document called the 'Standard Revision Request'.
Formulation of Revision Proposal: After analyzing each feedback, the Secretariat drafts a 'Revision Proposal'. This proposal outlines the changes deemed necessary to the Riverse Standard Documentation based on the feedback received.
Submission to SAB and deliberation: the Revision Proposal is presented to the SAB for their critical evaluation. If the Revision Proposal is validated, the SAB decides whether the proposed revision is of a nature that demands public input.
Integration of Public Feedback: the Secretariat integrates feedback from the public consultation into the existing 'Revision Proposal'. The outcome of this integration is a 'Final Standard Revision Proposition'.
SAB Review and Approval: The 'Final Standard Revision Proposition' is then presented to the SAB for their final approval. The SAB ensures that feedback from the public consultation phase has been genuinely and appropriately integrated.
After the revision procedure is completed, each contributor receives an update on how their remark has been treated.
Project compliance: Projects that are already validated must become compliant with revised rules upon their next verification. They do not need to undergo a new validation process. The VVB shall check for gaps and compliance during the verification audit. If projects are incompatible with revised rules, no new RCCs will be issued for that project, but their verified RCCs will remain valid on the Riverse registry.
Correct typographical or formatting errors that do not affect the meaning or application of the standard.
Update references to external documents, tools, or standards without changing the core methodology.
Adjust procedural steps or timelines to improve clarity or efficiency without altering the overall process.
Add or update examples or case studies to aid understanding, without introducing new requirements.
Simplify or streamline documentation language to improve accessibility, without affecting the technical content.
Formalize processes that are already implemented in practice.
Procedure and document development:
Internal process setting: All Riverse Standard Documentation is initially drafted internally by the Climate team.
Basis of standards: procedures are tailored to Riverse’s operations, but should draw inspiration and guidance from established standards such as ISO 9001 and ISO 31000, ensuring global compliance and recognition.
Instead of a Revision Proposal as described in the previous section, a creation proposal is submitted to the Standard Advisory Board for validation.
A public consultation is conducted for the creation of any new Riverse Standard Documentation.
The Methodology Creation Proposal is reviewed first by the Riverse Climate team, and if approved then it is reviewed by the SAB for final approval.
The reviews consider factors such as:
Maturity of the technology
Number of existing projects
Scientific consensus of substantial carbon reduction potential
Feasibility of carbon reduction measurement
Degree of circularity
If the proposal is rejected by the SAB, it then decides whether to earmark it for reworking or, based on the gravity of the concerns, abandon it altogether.
Members of the technical working group shall be selected based on
expertise related to e.g. the scientific foundations, sustainability issues, LCA/GHG quantification, policy, or operations of the methodology's subject.
representation from diverse stakeholders from e.g. researchers/academics, project developers, independent experts, or NGOs.
To research and develop the methodology, the Climate team will gather the working group and consult the TAC members on a regular basis. The first step of methodology development shall always be a literature review. Following steps depend on the needs of each methodology.
The minimum requirements for a Riverse methodology include the following:
Eligible technologies and activities
Scope/delineation of a project (e.g. how many sites can be included in one project?)
Minimum requirements for a monitoring plan
Justification of the baseline scenario (pre-defined or guidance for baseline scenario selection), and frequency of updating the baseline scenario
Glossary with definitions of technical terms
Methodology-specific instructions for:
no double counting
co-benefits
substitution (for avoidance RCCs)
permanence (for removal RCCs)
ESDNH risks
leakage
targets alignment
Risk assessment template
Methodology-specific instructions for:
assumptions
data sources
description of processes to include in the project and baseline scenario
all equations needed to calculate avoided and/or removed emissions
uncertainty assessment
Once a first version of the methodology has been drafted, the Secretariat organizes a 30-day public consultation by publishing a Call for Consultation. The Secretariat and Climate team integrates feedback into a new Final Methodology Creation Proposition.
The Final Methodology Creation Proposal is then validated by the SAB, which ensures that the feedback from the TAC, experts, and the public consultation was integrated.
Methodologies are adaptable to ensure their relevance and robustness. To streamline updates and maintain transparency, the Climate team implements:
At a minimum, methodologies shall be reviewed and undergo public consultation every 3 years.
A methodology may be discontinued if:
shifts in scientific consensus indicate it no longer aligns with best practices
it fails to achieve measurable carbon reductions
it is no longer additional
it overestimates credits and cannot be revised to ensure conservativeness
Methodologies are evaluated against these criteria at least once every three years during the mandatory major revision process, though they can also be reviewed and discontinued at any time if necessary.
Projects already validated under a discontinued methodology may continue using it until their next verification. After that, they must transition to a new methodology or become ineligible for new RCCs. Previously issued RCCs remain valid and tradable.
Decision by the SAB: Public consultations are mandatory for all major revisions of the Riverse Standard Documents and methodologies. For other revisions, the Standard Advisory Board (SAB) decides, based on their judgment and complexity of the topic at hand, whether to launch a public consultation.
Publishing the Call for Consultation: the Secretariat initiates the public consultation with the publication of a Call for Consultation. This call is widely broadcasted through relevant channels to ensure maximum outreach, inviting Project Developers, carbon credit resellers / brokers / marketplaces, Net Zero engaged corporates, Validation and Verification bodies, greentech experts, climate and environmental scientists and the general public to provide their insights and feedback on the topic. The minimum duration of the consultation is 30 days.
For all new methodologies, the Secretariat should organize a webinar to explain the rationale of the methodology and an overview of its requirements.
Integration into Final Proposition: the Secretariat then integrates this feedback into the existing proposal. This revised document, now termed the Final Standard Revision Proposition, harmonizes both the initial proposal and the feedback from the public consultation.
The general GHG reduction quantification approach and components are outlined below. Detailed instructions and requirements can be found in Riverse methodologies.
Riverse Carbon Credits shall be calculated by subtracting the GHG emissions and removals of the project scenario from the emissions and removals of a baseline scenario, or reference scenario, that would have occurred without the implementation of the project.
Functional units shall include characteristics such as:
Type of product/service
Amount
Functional units may include characteristics such as:
Performance specifications
Geographic location
Duration
The system boundary shall cover the project scope, and include:
all processes under direct control of the project and
the key upstream and downstream processes.
Processes may include raw material extraction, delivery of supplies, processing, manufacturing, distribution, use, retail, distribution, and waste treatment.
Processes with the lowest contributions to impacts, which each account for less than 1% of total impacts, may be excluded from the GHG quantification. These processes shall be transparently identified and justified.
Due to the comparative measurement approach, processes that are identical in the project and baseline scenario may be excluded, since they will not affect the comparative results.
The by the World Business Council for Sustainable Development (WBCSD) shall be followed to select the baseline scenario (see figure below).
According to the from the WBCSD, average market solutions shall be assumed by default for the baseline scenario. Only when a project solution is known to substitute one specific technology (e.g. the best available technology, or a product from one specific manufacturer), may the specific technology be used as a baseline.
Conservative assumptions, values, and processes shall be chosen when selecting a baseline scenario, to avoid overestimation of GHG emission reductions. Average market solutions shall be determined based on practices in the country/region of the project, and statistically relevant historical information.
If the project activity is multifunctional, the baseline scenario shall cover all functions of the project.
When the average market solution is represented by a market mix of solutions, the market mix shall include the portion of the project solution that is already used in the market.
The duration of validity of the baseline scenario selection shall be defined in methodologies.
Project GHG emissions and removals shall be quantified using primary data from project operations for operating projects, or estimated data for planned projects. The estimated data shall be used for project validation, and shall be replaced with actual data once the project begins operations for the verification of emission reductions.
All measurements from the project must be verifiable and based on recent conditions (no more than 1 year old). These measurements include quantities (volume, mass, number) and type of products and inputs.
All background data (for example, emission factors, rates of recycling, composition of national electricity grid) shall be derived from traceable, transparent, unbiased, and reputable sources.
All assumptions and estimates shall be conservative, transparently presented and justified.
For geographic accuracy and consistency across projects, national-level background data should be prioritized. Local (region, state, city-scale) or global sources may be used if justified.
Qualitative estimates of uncertainty shall be justified ranging from none, low, medium, to high. A choice of “None” is only applicable for measurements of primary data that have strong, immutable sources of proof.
Project Developers shall assess uncertainty for the following areas at the project-level:
assumptions
selection of the specific baseline scenario
measurements
estimates or secondary data used for the project assessment
Methodologies shall include assessments of uncertainty for the following areas at the methodology-level:
assumptions
baseline scenario selection guidance
equations and models
estimates or secondary data used for all projects under the given methodology
All practical steps must be taken to achieve a low level of uncertainty for each area.
Areas that have high levels of uncertainty shall use the most conservative reasonable option, to avoid overestimation of GHG emission reductions.
Based on the uncertainty levels estimated for the above individual areas, Project Developers shall justify an overall uncertainty estimate of low, medium or high for the project’s GHG emission reductions.
The uncertainty estimate shall account for the sensitivity of the total GHG emission reductions to each assessed area. This way, for example, an area might have high uncertainty, but if that area has a small effect on the total GHG emission reduction calculations, then the level of uncertainty is acceptable and can be considered lower.
The overall uncertainty estimate shall be translated into the discount factor, representing the percent of credits that will not be issued, using the following:
Low uncertainty: 3%
Medium uncertainty: 6%
High uncertainty: 9% or higher
GHG emission reduction measurements shall aim for completeness, accuracy, transparency, and conservativeness.
If no Riverse methodology exists for a given project, documented scientific research can be proposed to establish a measurement method. This method shall be evaluated and validated by the Riverse Climate team and the VVB.
Upstream and downstream actors in the supply chain are not counted as project sites.
purpose
relationship to the project
street address or, if not available, GPS coordinates
reference person
contact information
host country
Projects shall undergo an in-person or remote site audit within two years of the project’s crediting period start date and/or before the second verification audit. The purpose of this site audit is to confirm that:
The project exists and is functional
The scale of the project is in line with the description
Key processes operate as described in the project PDD
Projects that are in the planning phase and seeking carbon finance to fund investments shall prove that the project will actually occur, and will begin operations within 2 years of certification. Proof may include contracts with suppliers of key inputs or receipts from purchase of key machinery.
After beginning operations, the Project Developer shall comply with the requirement in 4.2.5.
Project developers must define the scope of the project, i.e. the mitigation activities that are under consideration for RCC issuance. The scope specifies the geographic, temporal (i.e. project start date), site, and operation limits of the project.
For example, a company operating in multiple countries, that has existed for many years, with several operating sites, and multiple activities must define the scope of their operations that is defined as the project. A company’s annual operations are not a sufficient definition of a project.
The project must have started operating within the last three years.
The crediting period shall start when the mitigation activities begin, provided the project is already registered with Riverse at that time. The crediting period shall be no longer than five years.
If the project is already underway, the crediting period may start up to 18 months prior to its registration date with Riverse.
📎 Supporting documents:
Site registration certificate
Site audit certificate and report
[conditional] If the project is under development, proof that it will actually occur
The Project Developer shall submit a Monitoring Plan during the validation step that defines the list of Key Impact Indicators (KII).
For each KII in the Monitoring Plan, the Project Developer shall specify the update frequency and auditable source.
For each verification and issuance of RCCs, the Project Developer shall upload each KII with proof to the Impact Certification Platform.
📎 Supporting documents:
During validation: Monitoring Plan defining the Key Impact Indicators (KIIs) with examples of proof, source of the proof and update frequency.
During verification: values of KIIs with proof, uploaded to the Riverse certification platform.
Regulatory surplus analysis: Mitigation activities must go beyond what is required by regulations.
Projects shall prove that:
there is no law, regulation, statute, legal ruling or other regulatory framework that makes the implementation of the project compulsory, and
if there is a regulation, their mitigation activities allow for more GHG emission reductions than what is required by regulations. In this case, only the project activities that surpass the mandated amount are eligible for RCCs.
📎 Supporting documents:
Description of the regulatory environment concerning the project’s mitigation activity.
Description of current and confirmed upcoming regulations or incentives that promote the project’s solution.
Investment analysis: Project Developers may use investment analysis to prove that revenue from carbon finance is necessary to make the project investment a financially viable and interesting option.
Projects shall prove that revenue from carbon finance is necessary for investments to launch or expand the project.
Note that for investments in expansion, only the additional carbon reductions enabled by the expansion shall be eligible for Riverse Carbon Credits.
📎 Supporting documents:
Annual updates of predicted financial indicators.
Barrier analysis: Barriers may exist that prevent the mitigation activity from continuing or expanding. These may be financial, institutional, or technological barriers. Project Developers must demonstrate how revenue from carbon finance is necessary to allow projects to overcome these barriers.
Examples of barriers include but are not limited to:
Financial: high upfront costs, uncertain or low returns on investment, long payback periods
Institutional: complex or costly regulatory requirements, limited access to financing, lack of supportive infrastructure, limited market demand, resistance from incumbents
Technological: cost competitiveness and economic viability, scale and manufacturing challenges
Project Developers shall identify, describe and where possible, quantify the barrier, with verifiable proof.
Project Developers shall demonstrate that revenue from carbon finance is decisive in overcoming this barrier, including justification that:
the magnitude of revenue from carbon finance is similar to the amount of funding needed to overcome the barrier, and
the project could not have provided the funding itself.
Project Developers shall demonstrate that at least one alternative to the project activity does not face significant barriers, including the barriers faced by the project.
Note that for overcoming barriers to expansion, only the additional carbon reductions enabled by the expansion shall be eligible for Riverse Carbon Credits.
📎 Supporting documents:
Description and, where possible, quantification of the barrier. Demonstration that revenue from carbon finance is decisive in overcoming this barrier.
Projects eligible for removal RCCs are subject to the Permanence and risk of reversal criteria. Permanence and reversal risks are not evaluated for avoidance RCCs, because they are considered to have little to no material reversal risks.
By default, at least 3% of all verified removal RCCs shall be transferred to the buffer pool upon issuance.
Project Developers shall complete the Risk Assessment Template tailored to their specific project type, which is provided in the methodology documentation. This template guides Project Developers in evaluating the likelihood and severity of each risk type.
For each reversal risk type with a high or very high risk score, Project Developers shall develop a risk mitigation plan, or incur an additional 3% contribution of verified removal RCCs to the buffer pool.
If no methodology exists, the Project Developer shall suggest risks to consider in the PDD, which must be approved by the Riverse Certification team and the VVB. Documentation and proof must be provided to justify that the identification of risks was performed with a similar level of rigor, scientific accuracy, and conservativeness that is required for methodology development.
📎Supporting documents:
Project Developer’s responses to the Risk Assessment Template evaluating reversal risks.
[conditional] If a risk has a high or very high risk of reversal, a risk mitigation plan, or signed agreement to contribute an extra 3% of verified removal RCCs to the buffer pool.
Double use shall be prevented by the Riverse Registry, where each project is automatically assigned a unique identifier, with project ID, location, and Project Developer name and contact information. An immutable certificate is generated upon retirement.
Project Developers shall not use another program to issue carbon credits for the given mitigation activity, for the same year. Project Developers shall disclose any issuance of carbon credits for the same project prior to the crediting period, or with a different project scope.
Project Developers shall ensure that specified upstream and downstream actors in the supply chain have not and will not issue carbon credits for their role in the mitigation activity. Specific requirements on this topic may be made in methodologies.
Double claiming with NDCs shall be prevented by signed agreements with host countries and confirmation of corresponding adjustments. Such agreements will be made publicly available with the project documentation, and updated as needed.
Double claiming with national climate policies and emissions trading schemes shall be prevented by proof that the mitigation activity is outside the scope of such policies and schemes. If this is not the case, Project Developers must obtain proof of an accounting adjustment or cancellation in the emissions trading scheme.
For purposes of voluntary climate pledges and reporting (e.g. GHG protocol), Project Developers must inform upstream and downstream supply chain entities of claimed project/intervention/insetting emission reductions, report them to Riverse, document any transfer of emission reduction units, and seek guidance in cases of conflicting claims from reporting bodies like the GHG Protocol.
📎 Supporting documents:
Proof that carbon credits will not be issued by specified actors within the same value chain for the same mitigation activity (specific proof requirements depending on the methodology).
[conditional] Any other requirements specified in the methodology document.
[conditional] Letters of authorization from host country and proof of corresponding adjustments.
Projects shall support between two and four quantifiable and verifiable environmental or social co-benefits. These must be in addition to their climate benefits that are already accounted for in the issuance of RCCs.
Co-benefits must be positive environmental or social impacts that are substantial, and would not have occurred without the intervention of the project.
Other relevant UN SDG sub-objectives or sustainability indicators may be suggested by Project Developers, and accepted at the discretion of the Riverse Certification team and the VVB.
Co-benefits shall be quantified and proven using the project’s GHG quantification results, primary data collection from the project, an LCA of the project or similar technology, or other reputable scientific documents. The tool, method, approach, and/or equations used for assessing co-benefits shall be described in methodology documents and/or DPDs.
📎 Supporting documents:
Identification of two to four UN SGDs that the project contributes to substantially as co-benefits, with:
quantified indicators for each co-benefit
source/proof for each co-benefit
Projects shall prove that their project outputs have similar performance metrics to the baseline scenario and deliver equivalent functions.
Project Developers shall identify and quantify performance metrics to compare between the baseline and the project scenario. Specific metrics to consider are detailed in methodologies.
📎 Supporting documents:
Proof that the project output has sufficiently similar technical and performance specifications to substitute for the baseline scenario.
If the project already has a legal permit (for example, construction permit, operation approval from authorities) that required similar stakeholder consultation or environmental and social impact assessments, Project Developers shall provide any documents related to those processes, and may be deemed exempt from the Riverse stakeholder consultation by the VVB and the Riverse Certification team.
Certain methodologies may define strict rules and cutoffs that may disqualify projects based on their environmental and social risk assessment results.
The Riverse Certification team or VVB may require annual monitoring of an environmental or social risk if they determine that the risk could lead to the project causing net harm.
Risk assessments shall assess at least the following risks, which should be avoided and minimized:
📎 Supporting documents:
Results of the stakeholder consultation
[conditional] Legal permits, or results of previous stakeholder consultations or environmental and social impact studies
Project Developer’s responses to the Risk Assessment Template evaluating environmental and social risks
Project Developers shall follow the relevant methodology requirements for identifying, assessing and mitigating leakage. Potential risks and detailed instructions are identified at the methodology level.
Methodologies provide instructions on how to assess leakage and manage and, if necessary, deduct leakage emissions. Any project-specific leakage risk may incur additional leakage emission deduction, up to the discretion of the Project Developer, the VVB and the Riverse Certification team.
📎 Supporting documents:
Project Developer’s responses to the leakage risks identified in the methodology.
Projects shall at minimum reach TRL 6, which is described in the table above.
📎 Supporting documents:
Proof of technological progress and/or production capacities either in an operational environment or lab.
📎 Supporting documents:
GHG quantification results showing that the project’s GHG reduction efficiency is aligned with the sector target emission reductions.
To renew certification at the end of the crediting period, projects may re-conduct a complete validation process using the current Riverse Standard Rules and methodology requirements.
For renewed projects, the crediting period shall be the total length of the combined crediting periods.
📎 Supporting documents:
All parties involved must sign the policy. The following is the minimum list of stakeholders who must be included:
Members of the Executive board
Members of the Secretariat, Standard Advisory Board
Members of the Climate, Certification, R&D and Partnerships teams
Members the Technical Advisory Board
VVBs
Contractors to the Riverse Standard involved in at least one of the procedures
Procedures to identify and mitigate conflicts of interest are detailed in the policy document.
This document presents guidelines for Validation and Verification Bodies (VVBs) for conducting evaluations of greenhouse gas emission avoidance and/or removals of project developers.
The aim of this document is to present guidelines for Validation and Verification Bodies (VVBs) for conducting comprehensive evaluations of greenhouse gas emission avoidance and/or removals of Project Developers under the Riverse Standard.
Validation Audits
Verification Audits
This guidance is part of the larger framework of the Riverse Standard system, which encompasses the Riverse Standard Rules and the methodologies. Moreover, it complements the Riverse Procedures Manual that delineates project registration and supervision This document offers targeted guidance for auditors performing validation and verification audits within the specialized scope of Project Developers.
The guidelines detailed in this document become binding upon its formal release. Post this date, any VVB that meets the requirements can contribute to the validation and verification of Riverse Standard Projects.
Existing VVBs must reapply and provide the necessary documentation outlined in this text before continuing validation or verification tasks.
For VVBs who have an existing formalized agreement with Project Developers before the activation date of this guidance, a grace period of twelve months is given to apply again and comply with the new requirements.
Henceforth, Project Developers can only collaborate with VVBs officially recognized by Riverse, based on the requirements and processes defined herein. Projects already registered that haven't transitioned to the Riverse Standard Rules might be subjected to different review templates than those mentioned here.
I hereby acknowledge that I have read and understand the above requirements.
Company name:____________________
Name:_________________
Signature: ____________________________________ Date:_____________
The Standard Advisory Board (SAB) is independent from Riverse SAS. It is responsible for reviewing suggested changes to the Riverse Standard Rules, Procedures Manual, and the Riverse Registry procedures.
The SAB shall:
Ensure Riverse’s activity is in line with its foundational mission, delineated in its statutes
Accept or reject changes to the Riverse Standard Rules, Procedure Manual, and Riverse Registry Procedures, specifying written reasons for the decisions
Provide strategic guidance for the Standard and make recommendations to align Riverse processes and rules with relevant regulations and integrity frameworks.
The SAB shall be appointed following the process bellow:
The inaugural SAB was selected by the Riverse Executive Team, following interviews with candidates who were distinguished by their expertise in areas relevant to the board's focus.
New SAB members are nominated by the Riverse Executive Team and confirmed through a decision made by the current SAB members.
The Chair of the SAB is elected by its members from among themselves by a simple majority vote for a one-year term
The mandate for SAB members is tacitly renewed every year
Only SAB members and the Chair have the right to vote on decision items during SAB meetings. When the Chair calls for a vote on any issue, decisions will be made by a simple majority. In the event of a tie, the Chair will cast the deciding vote to determine the outcome.
The Riverse Technical Advisory Committee (TAC) is an external entity from the Riverse organization. Its mission is to bring in-depth expertise on each sector covered by Riverse.
The Riverse Executive and Climate teams will establish the TAC’s missions as necessary. Typical missions may include the following:
Review a specific project application and deliver a Technical Analysis report
Review a new methodology, or its revision
Review a specific methodological aspect on their domain of expertise
Conduct solutions-based scientific research on their domain of expertise
Members of the TAC should be knowledgeable in at least one specialized area relating to the Riverse Standard focus (such as, but not limited to, refurbishment and recycling processes, bioenergy, biobased construction materials, biomass carbon removal and storage, or carbon markets).
TAC members should prove the following skills:
Expertise in an area covered by the Riverse Standard Rules, existing methodologies, or a sector considered for future methodology development
Deep understanding of environmental topics
The TAC serves as an expert consultative committee for the Riverse Standard, without decision-making authority. Should a technical issue arise necessitating a decision, the SAB may seek a recommendation from a TAC member. However, the final decision will be made by the SAB.
The Riverse Executive Team is tasked with operational and strategic functions within the organization. Their key responsibilities include:
Overseeing daily operations to ensure efficiency and alignment with organizational goals
Determining the long-term strategy and direction
Making essential decisions for Riverse.
Reporting to and integrating advice from the SAB into the company's operations and strategy
The Executive Team of Riverse is appointed by a collective decision of the Riverse SAS partners, in accordance with the constitutive statutes of Riverse.
Decisions for which the executive team is responsible are made by a simple majority vote within the executive team.
The Secretariat of Riverse holds a fundamental administrative and coordinating role within the organization's structure.
The Secretariat’s main responsibilities are outlined as follows:
Collecting and synthesizing feedback on the Riverse Standard Rules and methodologies, preparing them for review and validation by the governing bodies.
Serving as a communicative bridge, it conveys information between the Executive Team, the Certification and Climate Teams, and the SAB
Organizing and documenting public consultations.
The Climate team is responsible for the climate science and integrity of the Riverse Standard Rules.
The Climate team’s main tasks are the following:
Regularly revise and improve the Riverse Standard Rules
Monitor relevant references and scientific progress to integrate into the Riverse methods
Develop new methodologies, and regularly revise and improve existing ones
Coordinate with the TAC for methodologies creation and revision
Certification team and VVB trainings
The Certification team’s main tasks are the following:
Improve the validation process to make it as rigorous, transparent and practical as possible
Review Project Applications
Accompany Project Developers in the certification process of their project
Coordinate with VVBs for outputs of validation/verification audits
Run VVB performance oversight
Manage the Riverse Registry: register projects, deregister projects, process the issuance/verification/cancellation of credits.
Version history and changes to the Riverse Procedures Manual
By accepting the audit assignment, the accredited VVB agrees to:
declare whether impartiality and independence are compromised (this may be the case if the auditor is already in a relationship with the Project Developer)
comply with and sign a copy of Requirements for VVB
allow Riverse to disclose the results of the audit, the name of the firm, and the names of the people involved in the audit
respect confidentiality clauses with Project Developers (on processes, materials, quantities)
Remote audits (those that do not include a physical site visit by an auditor) can optimize audit efficiency while maintaining the integrity of the audit process. The objective of a remote audit is to establish confidence in the VVB certification process by direct observations carried out through an electronic medium:
Videographic evidence is required for remote audits. The video should allow the VVB to confirm that each component is true, and will typically consist of a tour of the site with commentary.
Formats may include video calls with the auditors or pre-recorded videos.
The use of remote assessments by VVB of a given project may be requested in site validation assessment. Additional remote audits for verification are at the discretion of the VVB, who is entitled to reject any request from PDs.
If the remote audit does not allow the VVB to to audit all elements deemed necessary, the remaining issues should be recorded and documented.
To maintain impartiality and credibility, and reduce complacency and bias, a single VVB may conduct a maximum of three (3) sequential verifications for a specific project.
Upon reaching the sequential verification limit with a VVB, the PD shall be granted a transition period of six (6) months to engage a new VVB for the subsequent verification.
PDs must maintain comprehensive records of all verifications, including the VVBs involved, to demonstrate compliance with this rule.
Regular audits will be conducted to ensure PDs adhere to this rule. Non-compliance may result in penalties or suspension of the project's validation status.
The following metrics will be employed to evaluate a VVB's performance:
Timeliness: Adherence to stipulated timelines for project verification.
Accuracy: Correctness of verification processes, calculations, and conclusions.
Consistency: Uniform application of standards and methodologies across different projects.
Communication: Effectiveness and clarity in communication with PDs and other stakeholders.
Integrity: Adherence to ethical guidelines, including conflict of interest declarations
Each VVB is required to submit an annual Performance Report that details its activities, challenges, and areas of improvement relating to its work with the Riverse validation and verification process. This report should provide insights into the VVB's verification approach, methodologies employed, and training undertaken.
Project Developers are asked to provide feedback on the VVB's performance after each validation and verification process, as part of the Riverse satisfaction survey. This feedback is considered in the VVB performance review.
The Standard Secretariat annually reviews the annual Performance Reports and assess VVBs based on the established performance metrics. VVBs are encouraged to continually enhance their skills, methodologies, and processes. Training resources, workshops, and seminars specific to the Riverse Standard will be provided to support this endeavor.
Policy
The purpose of this document is to:
Inform Project Developers and carbon credit buyers to avoid making misleading claims about the greenhouse gas emission reductions their activities enable
Double use occurs when a single carbon credit is used and/or retired twice (by two entities, or two times by the same entity). This is prevented on the Riverse registry, where Riverse carbon credits are traced with a unique identification number from issuance to retirement.
An immutable certificate is generated upon retirement, available to the public on the Riverse Registry, with the following information:
Entity that retired the carbon credit
Vintage year
Mechanism (avoidance or removal)
Date of retirement
Credit IDs
Credit source (project name and information)
Any applicable credit labels (e.g. CORSIA)
Refer to the Riverse Procedures Manual Section 9.7 RCC management- Retirement for more detailed information.
There are no project-specific requirements related to double use.
Double issuance occurs when multiple carbon credits are issued for one greenhouse gas (GHG) reduction or removal activity. This can occur in two ways:
Two carbon credits are issued for the same amount of emission reductions or removals that actually occurs
Two different entities (e.g., the manufacturer of the material/equipment and the user), both claim the same GHG avoidance or removal and request carbon credit issuance for it, to the same or two different crediting standards.
Where there exists a risk of overlapping claims of GHG avoidance and removal between actors in the same supply chain, projects shall clearly delineate the GHG accounting boundary of the GHG avoidance and removal activity. The Riverse Standard shall only issue one carbon credit for the GHG avoidance or removals that occur within the project’s GHG accounting boundary, and not to any overlapping activities.
Methodologies may specify requirements for projects to reduce risk of double issuance between actors in the same supply chain by, for example:
Obtaining signed agreements from upstream suppliers or downstream users
Adding relevant clauses in sales contracts
Providing information to users via marketing, packaging, or other outreach
Projects shall not be eligible for Riverse Carbon Credits if the Certification team identifies overlaps of GHG accounting boundaries with another project’s GHG accounting boundaries, within the same or any other crediting program.
If the project is already registered under another crediting program, and intends to register and/or issue credits under the Riverse Standard, the project must prove that the same emission avoidance and removals will not be issued under both crediting programs. The project shall provide the following information related to the project status under the other crediting program to Riverse:
Project unique identifier
Vintage period(s) and corresponding volumes
Signed letter from the Project Developer that it has informed the other crediting program representative about its intention to register to the Riverse Standard and requesting the deactivation or putting on hold the project with this other crediting program.
If the project has already issued credits under another crediting program, the project may be permitted to be certified under the Riverse Standard after deactivating registration with the other crediting program. Only GHG avoidance and removal units of a different vintage and/or scope, that have not already been issued under the other crediting program, shall be eligible for Riverse Carbon Credits.
Double claiming occurs when the same GHG emission avoidance or removal is claimed by two different entities towards their mitigation targets, inventories, or pledges. The following sections outline requirements to prevent double claiming across several scenarios.
If one of the following conditions are met, Project Developers shall follow requirements in 3.2.2 through 3.2.5.
the project issues carbon credits for use towards a nationally determined contribution (NDC), or
the project issues carbon credits for a domestic climate mitigation target of a jurisdiction or nation other than the host country, or
the project issues RCC to be used under CORSIA.
Obtain an authorisation by the project’s host country, to use the project carbon credits for the intended purpose. This authorization will be made publicly available with the project documentation, and updated as needed.
Obtain confirmation from the project’s host country, that the corresponding carbon credits will be granted a corresponding adjustment. This written confirmation will be made publicly available with the project documentation, and updated as needed.
Ensure the project’s compliance with host country regulations/guidance relating to the voluntary use of carbon credits that are also accounted towards a country’s NDC.
If the following conditions are met, Project Developers shall follow requirements in 3.3.3.
the host country has a regulated domestic climate mitigation target and/or national emissions trading scheme, and
the project’s GHG removal/avoidance units fall within the scope of the host country’s domestic climate mitigation target and/or national emissions trading scheme, and
the GHG avoidance or removal units may also be claimed by another country, jurisdiction, or entity
Obtain a letter from the host country/regional regulator stating that the GHG removal or avoidance unit is not accounted for under the host country’s domestic mitigation target and/or national emissions trading scheme, or that an accounting adjustment or cancellation has been made.
If the Project Developer seeks to issue credits with another GHG-related environmental credit framework for a different time period than GHG avoidance and removal units sought under the Riverse Standard, the Project Developer shall provide evidence that the other GHG-related environmental credits will not be issued for the same time period as the impact credited under the Riverse Standard.
Where the Project Developer is a buyer or seller of a product within a supply chain, and implements a project that generates a GHG avoidance/removal that changes the GHG inventory of another entity within the supply chain (e.g. through insetting), there is a risk that the other entity upstream or downstream within the supply chain could double claim the GHG avoidance/removal.
The Project Developer shall
inform entities throughout the supply chain that they are claiming and reporting the emission reductions from the associated intervention,
retire the associated Riverse Carbon Credits on the registry on their own behalf,
and inform Riverse of the associated change in their product's emission footprint through an issued statement.
Any transfer of GHG removal/avoidance units from one entity to another within the supply chain must be documented through an authorized project representative issuing a signed statement detailing the transfer that has occurred.
Situations may arise where two end users seek different types of claims (e.g. contributory vs. offsetting claims) from GHG avoidance/removal units issued by the same Project Developer from the same project. Under such circumstances, the company shall seek guidance from reporting companies, the GHG Protocol, and other accounting tracking mechanisms that emerge.
Projects that aim to issue RCCs that meet the requirements of Article 6 of the Paris Agreement, or other Paris Agreement-related programs such as CORSIA, must be differentiated from RCCs that are only eligible to be used for voluntary carbon market purposes. This is to prevent double counting between the host country’s NDC and the buyer or airline’s own climate targets, accounting and claims. As such, unique Riverse Standard labels can be issued to avoidance or removal credits that meet the requirements of Article 6 and CORSIA.
The Riverse Standard mainly covers projects based in Europe. In the context of Article 6, sellers of Internationally Transferred Mitigation Outcomes (ITMOs) are most likely to be low-income countries, while high-income countries, such as European countries are more likely to be the buyers. This is due to greater financial need, higher emission reduction potential at a lower cost, and the ability for ITMOs to facilitate technology transfer and capacity building in lower-income countries. Furthermore, high-income countries are more likely to purchase ITMOs to take responsibility for historical emissions and meet emission reduction targets.
Therefore, while the Riverse Standard has introduced the use of Riverse Standard labels to enable the use of credits under Article 6, at least in the short term, projects located in Europe are unlikely to become sellers of ITMOs under Article 6. However, seeking the labeling of Riverse Carbon Credits remains an option for Project Developers, since ITMOs may be used for other purposes.
Any project that intends to issue Riverse Carbon Credits for use under Article 6 or CORSIA shall meet any necessary established requirements specifically recognised under Article 6 of the Paris Agreement and CORSIA mechanisms. Projects that meet these requirements, including those relating to double counting and corresponding adjustments, may receive the relevant Riverse Standard labels. These credits will be labeled accordingly and be made available within the Riverse Registry.
Riverse labeled credits may also be used for voluntary carbon market purposes that do not require Article 6 or CORSIA labels but not vice versa.
The Project Developer applying these requirements shall provide evidence to Riverse that the Host Country has applied relevant corresponding adjustments in accordance with Article 6 of the Paris Agreement and its Letter of Authorisation. It shall also provide evidence that the Host Country is and continues to fulfill its obligations required under the relevant Paris Requirements.
The Project Developer shall provide evidence of the appropriate application of a corresponding adjustment within two years of the required application of corresponding adjustments pursuant to Article 6 of the Paris Agreement.
If the Project Developer is unable to provide evidence of the appropriate application of a corresponding adjustment as per 4.2.5 above, Riverse upholds the right to withdraw the Riverse Standard label from carbon credits in the registry and inform all account holders.
Riverse shall prepare and publish regular annual reports prior to April 1st of each calendar year, on the status of Riverse Carbon Credits associated with Article 6 authorisations on its website. The report will provide information relating to Riverse Carbon Credits authorized for use as ITMOs and categorize this data by host country, project activity type, and vintage. This will provide information to fulfill their reporting obligations in accordance with the Paris Agreement.
The Riverse Certification team may eliminate a fraction of a project’s estimated RCCs using the uncertainty discount factor to mitigate carbon credit overestimation. These verified avoided/removed emissions are never issued as RCCs.
Application of a discount factor may occur when material uncertainty is identified, for example, in the project’s measured data, assumptions, or the selection of the baseline scenario.
When faced with high uncertainty, steps should be taken to reduce uncertainty, and conservative choices should be made. If uncertainty remains, a discount factor shall be applied. Requirements are described in the Uncertainty Assessment section of the Riverse Standard Rules.
RCCs that are eliminated with the discount factor are not issued and will not appear on the registry. This discount factor may vary from 0% to more than 10% of estimated RCCs. The amount is evaluated individually for each project.
All projects that issue removal RCCs must allocate a portion of their verified removal RCCs to the buffer pool. This pool acts as an insurance mechanism, shared across all removal projects, against the risk of reversal of sequestered carbon before the agreed upon commitment period (at least 100 years, for removal RCCs). This may occur due to, for example, natural disaster (fires, drought, pests) or project mismanagement. These RCCs cannot be retired by buyers.
The buffer pool is supplied with RCCs via two paths:
Default: Each removal project allocates by default at least 3% of its verified removal RCCs to the buffer pool.
As a result of the verification phase, provisional credits either are issued as verified RCCs or are canceled.
Upon verification, three situations are possible: exact estimation, overestimation and under-estimation. Below is an example for 100 estimated provisional removal credits. Note that the actual portion of RCCs going to the buffer pool may vary by project.
The name of the Riverse Registry operator, from the Certification team, who operates the issuance is registered in the process.
When removal RCCs are issued, a contribution will automatically be transferred from Project accounts to the Riverse Buffer Pool account. The amount of removal credits to be added to the buffer pool is defined for each project, and displayed on the project page on the registry. The contribution shall equal the percentage confirmed during project validation, and shall be rounded up to the nearest whole RCC (3% by default).
Provisional credits may be canceled on the registry for several reasons:
lack of measurement source for a KII
change in KII or overall process, so that the project no longer avoids/removes carbon as expected
change in external factors causing the project to lose its additional status (i.e. change in regulation that makes the project activities required)
If pre-purchase agreements were made between buyers and PDs, the buffer pool will not be used to replace canceled provisional credits.
Riverse Certification team shall cancel RCCs from the buffer pool of a similar type as the removal RCCs that were reversed.
Verified RCCs may be deemed erroneously issued due to, for example, calculation errors, use of wrong input data, or inaccurate proof. While the comprehensive audit process renders this highly unlikely, a procedure is prepared out of an abundance of caution.
Erroneous issuance may be signaled by the PD, the VBB, the Riverse Certification team, or any stakeholder. The Riverse Certification team shall investigate the incident, determine the number of excess credits issued, and take the following remediating action:
Credits already transferred or retired: the above procedure shall be applied, and an equivalent amount of excess credits will be transferred to the credit user at no cost from the project's next verification and issuance. If no additional credits are available, Riverse will work with the credit user on a case-by-case basis to agree upon compensation, with Riverse taking financial responsibility to ensure the credit user incurs no loss.
An Cancelation Report will be generated and attached to the cancelation event in the Registry that states the amount of excess credits erroneously issued and the remediating action.
To retire RCCs, the user must log in with their username and password to the Riverse Registry and click on the option “retirement”. There they must enter the following information:
Project name and registry ID from which RCCs are to be removed
Vintage year
Number of RCCs to be retired
Reason for retirement: voluntary offset, carbon tax, or another specific offset scheme
End-user information: country of location, name, document type, and document number
Taxpayer information, if applicable: country of location, name, document type, and document number
Once retired, RCCs can not be transacted, retired or canceled.
Two main types of RCCs are issued by Riverse: removal RCCs and avoidance RCCs. Both types are measured by calculating the difference in GHG emissions of the project scenario compared to the baseline scenario, following the approach outlined in ISO 14064-2:2019. See details in the section.
Removal RCCs are calculated by evaluating the removal projects’ net GHG emissions (i.e. carbon removal and emissions) compared to the baseline scenario’s (i.e. what would have occurred in the absence of the project). See more details on choosing a baseline scenario in the .
projects that continuously upload data to the Impact Certification Platform to estimate credit volumes frequently (e.g. monthly, weekly), but only undergo verification audits e.g. annually.
Riverse Carbon Credits are issued ex-post as after the verification audit at the end of the monitoring period if the project meets the expected KII, with the production and emissions as estimated. See for more details. They appear as “verified” on the registry.
This manual describes the rules and procedures for registering and operating Riverse projects and issuing Riverse Carbon Credits (RCCs). It should be used together with the latest versions of the , , , .
See for full versions of previous documents
The Riverse Standard Rules undergoes regular revision to ensure it reflects up-to-date science and best practice in the voluntary carbon market. The complete diagram of these procedures can be found on the website .
All interested parties, irrespective of their background or involvement, are encouraged to continuously provide their feedback on the current Riverse Standard Documentation. They can do so by email at , or .
Public Consultation: the Secretariat organizes a public consultation of the proposed revisions (see section).
Implementation: The Climate team implements the approved revisions into the Riverse Standard Documentation and any affiliated documents. All changes are documented in the , and .
Minor revisions may be made by the Riverse Climate team when they are deemed necessary. All changes are documented in the , and . Minor revisions are tracked through the second number after the standard document name (e.g. Riverse Standard Rules V1.1). Revisions are considered minor if they:
The creation of new Riverse Standard Documentation follows the Review and Approval phases described in the section, with the following differences:
All public consultations are accessible on the website under the Standard Documentation section .
The complete diagram of these procedures can be found on the website .
Anyone may submit a request for a new methodology at any time. The requests are summarized by the Secretariat into a Methodology Creation Proposal (template ).
If the proposal is validated by the SAB, a Methodology Creation Mandate is granted to the Secretariat and the Riverse Climate team. This mandate assigns the designated teams to research, develop, and finalize the methodology. The are presented below.
The Secretariat gathers a technical working group composed of at least 3 members from the (TAC) and/or external experts. The technical working group collaborates with the Riverse Climate team to develop the methodology.
Major updates: substantive alterations are subject to a thorough vetting process and follow the , plus the technical working group requirements described the section. Major updates are tracked through the first number after the methodology name (e.g. BiCRS methodology V1).
Minor updates and clarifications: Minor modifications to the methodologies are regularly published and continuously open for public feedback on the , ensuring constant engagement with stakeholders. Minor updates are tracked through the second number after the methodology name (e.g. BiCRS methodology V1.1).
Feedback integration: continuous feedbacks are integrated into the , promoting a feedback-driven refinement approach.
Eligibility criteria changes that could lead to discontinuing previously validated projects (same project compliance procedures apply as in the )
projects under that methodology consistently fail to meet the outlined in the Riverse Standard Rules
Compilation of feedback: After the conclusion of the public consultation period, the Secretariat compiles all feedback, suggestions, and perspectives collected. This collective feedback is then structured and summarized into a document known as the 'Consultation Report’. The report serves as a comprehensive repository of public opinion, ensuring that every suggestion is captured. The consultation reports are made available on the website under Standard Documentation .
See the criteria for more general guidance on calculations.
See the section for more information.
Indirect processes, such as market changes or physical displacement, shall be evaluated in the criteria, and included in the GHG reduction quantification when relevant and feasible. Methodologies provide instructions on how to assess leakage and manage and, if necessary, deduct leakage emissions.
All projects must meet the 12 general eligibility criteria described below. Detailed instructions and examples are presented in .
Project Developers shall follow the approach outlined in the section, based on , to measure GHG emissions reduction, avoidance and/or removal.
Project Developers shall specify the Riverse they follow to measure GHG emission reductions.
Supporting documents:
GHG emission reduction measurements that meet the requirements and follow a Riverse-approved sector-specific methodology (if available)
All sites where the project operates shall be registered during the certification process. This includes all factories, facilities, or operations under direct control of the Project Developer, whose activities are involved in RCCs verification and issuance. Sites registration procedures are detailed in Section 4.3 of the .
shall include the site’s:
Only activities that are shall be considered in the project scope.
The project scope should not be confused with the , which is used for GHG reduction quantification. The system boundary defines the project scope plus upstream and downstream activities that count towards the project’s GHG emissions and removals.
KIIs are parameters that are important in the GHG reduction quantification calculations, are important in determining project eligibility, are subject to change, and are measurable using project data. More details on KIIs are available in the .
KIIs shall meet the minimum requirements for Monitoring Plans detailed in the Methodology, if applicable, and meet KII requirements described in the .
Project Developers shall fill in the to demonstrate their additionality. In the template, they must provide project-specific justifications and verifiable evidence.
Note that Riverse Carbon Credits are only issued for GHG reductions that are additional to business as usual. This is described more in the requirements for setting a
Investment analysis, business plan, or completed of the UNFCCC Clean Development Mechanism “Investment Analysis”, with accompanying spreadsheet and calculations, showing that funding from carbon finance is necessary for the project investment.
Permanent carbon removals mean that carbon removal is ensured for the committed-upon duration (at least 100 years for ). This duration is the commitment period, and represents the number of years for which the Project Developer can prove that carbon will likely remain sequestered. The minimum commitment period duration for RCCs is 100 years.
Contribution to the buffer pool: projects eligible for removal RCCs must contribute a default 3% of their verified removal RCCs to the buffer pool. This covers a minimum inherent reversal risk of all removal RCCs. More details on the buffer pool are available in the .
Risk assessment: projects eligible for removal RCCs must evaluate the risk of reversal during the validation step using the Reversal Risk Evaluation section of . Details on how to fill in the template, and how to use the results, are in the section below.
The consequences of a carbon removal reversal are outlined in the Cancelation section of the .
The Reversal Risk Evaluation section covers carbon reversal risks, and responds to the criteria. This is evaluated to ensure that carbon removal is long-term, and to provide transparency. Reversal risks may include social, economic, natural, and delivery risks.
The Environmental and Social Evaluation section covers risk of environmental and social damages, and responds to the criteria, described below. This is evaluated to transparently identify environmental and social damages, and if necessary, to put in place safeguards against high-risk damages.
For reversal risks, mitigation plans aim to manage the identified risks of carbon reversal, to ensure that carbon is removed from the atmosphere for at least the commitment period duration, which is at least 100 years. A reversal risk mitigation plan shall cover at least 40 years. In case reversal risks are realized, and more than 1 tonne of CO2eq is estimated to have been re-emitted, compensation measures shall follow the procedures outlined in the Cancelation section of the .
Double use of credits within the Riverse Registry: RCCs are traced with a unique identification number from issuance to retirement (see more in at Chapter 9 RCC Management). An immutable certificate is generated upon retirement.
Riverse’s provides full explanations and requirements regarding this eligibility criteria. Key points are summarized here.
Double issuance is prevented by the signing of the , where all Project Developers agree to follow the requirements outlined in the present document.
Double claiming with other GHG-related environmental credit frameworks is not allowed. This is prevented by the signing of the , where all Project Developers agree to follow the requirements outlined in the present document.
Signed agreeing to follow the requirements outlined in the present document, including those related to double counting.
Project Developers shall use the SDGs outlined in the as the basis for identifying co-benefits, which are deemed most relevant to Riverse’s program focus.
The GHG quantification method shall use an appropriate functional unit that reflects the equivalent functions delivered by the project and baseline scenarios (see more details in the ).
Stakeholder consultation: Project Developers must conduct a comprehensive and documented stakeholder consultation to provide insights into unintended outcomes and foster collaboration. Stakeholder feedback is collected online through the Riverse Registry for one month during the validation phase. The methods to conduct this consultation is detailed in the .
Risk assessment: Project Developers must evaluate the risk of environmental and social damage during the validation step using the Environmental and Social Damage evaluation section of Risk Assessment Templates. Details on how to fill in the template, and how to use the results, are in the section.
Project Developers shall conduct a stakeholder consultation gathering feedback on the environmental and social impacts of their project, among other feedback. The stakeholder consultation shall take place during the project's validation process, addressed to local stakeholders and communities. The feedback is reviewed by the Riverse Certification team during the final project validation review, and they may require the Project Developer to take corrective action to address the concerns. The feedback shall be made publicly available in an appendix of the PDD. More details are included in the .
Project Developers shall fill in the methodology’s Template for their project type, evaluating the likelihood and severity of each environmental and social risk.
If no methodology exists for the given project type, the requirement outlined at the end of the shall apply.
If no methodology exists for the given project type, the requirement outlined at the end of the shall apply.
The reduction efficiency of the project is calculated as following:
Projects’ reduction efficiency shall be higher than the targeted emission reduction targets for the project’s sector, presented in the :
The project must justify a minimum emission reduction of 1000 tCOeq over the crediting period of the project.
Projects shall justify a minimum emission reduction of 1000 tCOeq over the crediting period of the project.
GHG quantification results showing that the project’s GHG emission reductions over the crediting period are projected to be at least 1000 tCOeq.
The Conflict of Interest Policy (available ) is a separate document that must be signed by all individuals or parties identified as being at potential risk of a conflict of interest. For a detailed outline of the parties involved, please refer to the diagram found in the section.
This document delineates the requirements and procedures necessary for ensuring compliance with the and . It pertains to the following types of audits:
Please refer to the for a detailed description of the Standard Advisory Board’s responsibilities and organization.
Please refer to the for a detailed description of the Technical Advisory Committee’s responsibilities and organization.
TAC members are nominated by the Riverse , with the approval of the SAB.
The Certification team is responsible for delivering the ongoing tasks required by the .
See for full versions of previous documents
All requirements for VVB application and accredited VVBs can be found in the .
Comply with and sign a copy of Riverse's .
Regular performance reviews ensure that VVBs consistently uphold their responsibilities, for accurate and impartial verification, as detailed in the .
Outline the requirements set by the Riverse Standard to ensure that carbon credits are unique, following the No Double Counting criteria in the .
Projects shall not seek credit issuance for the same GHG avoidance or removal under the Riverse Standard and another crediting program. Project Developers commit to this by signing the .
Riverse shall complete regular spot checks to ensure that the same project, and different projects with overlapping project scopes and mitigation activities, are not also included on other registries under other carbon credit programs. Spot checks are conducted for each project based on geographies, similar processes types, and other standards/methodologies. Projects found to be non-compliant will face penalties outlined in the .
Project Developers shall not seek issuance of credits for GHG avoidance and removal units under the Riverse Standard at the same time as another GHG-related environmental credit for the same project activity and time period. Project Developers commit to this by signing the .
To obtain the Riverse Standard labels on Riverse Carbon Credits, the Project Developer must provide an official Letter of Authorisation from the Host Country. The Letter of Authorisation shall be made public on the Riverse Registry. A template letter is made available .
Conditional: If the project has high or very high risks of reversal (according to the project evaluation’s Risk Assessment Template), the Project Developer may choose to develop a risk mitigation plan, or contribute an extra 3% of their verified RCCs to the buffer pool. More details are available in the section on Risk Assessment.
RCCs are withdrawn from the buffer pool if there is a reversal event (see details in the section).
The issuance of RCCs is operated by the Certification team once the is fully conducted and all audit certificates are available.
Verified removal RCCs may be canceled/withdrawn from the buffer pool if the Project Developer notifies Riverse of an event that re-emits at least 1 tonne of COeq of the carbon stored in the removal solution, before the commitment period ends. The amount of RCCs withdrawn from the buffer pool equals the tonnes of COeq estimated to have been released as a result of the reversal event. The Project Developer must notify Riverse within 30 calendar days of becoming aware of the reversal event.
Credits not yet transferred: an amount of credits corresponding to the number of excess credits issued for the given project's shall be frozen during the investigation, and canceled.
A retirement certificate can be downloaded from the Riverse Registry. Additionally, all retirement transactions are publicly available on the registry (see example ).