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Global Ocean Accounts Partnership Technical Guidance

Traditional Knowledge

Circular ID TG-3.6
Version 7.0
Badge Emerging
Status Draft
Last Updated May 2026

1. Outcome

1After completing this Circular, readers will be able to incorporate traditional knowledge into ocean accounts, applying principles for respectful engagement with Indigenous Peoples and Local Communities (IPLCs), approaches for integrating traditional knowledge with scientific data, and the ethical frameworks that must govern such integration. The guidance recognises that methods for incorporating traditional knowledge into statistical frameworks are still developing and require particular sensitivity to cultural protocols, intellectual property rights, and the self-determination of knowledge holders.

2Important Note: This Circular addresses an emerging and sensitive area of ocean accounting practice. Traditional knowledge systems are diverse, context-specific, and embedded in cultural frameworks that may not align neatly with standardised accounting approaches. The guidance provided here should be understood as provisional principles rather than prescriptive methods, and practitioners should expect that approaches will continue to evolve as experience accumulates and as Indigenous Peoples and Local Communities articulate their own frameworks for knowledge sharing. Each engagement with traditional knowledge holders must be tailored to the specific cultural context and conducted with respect for the rights and protocols of knowledge-holding communities. No single set of guidelines can substitute for the sustained, context-sensitive relationship building that ethical traditional knowledge work demands.

1.1 Why traditional knowledge matters for ocean accounting

1Ocean accountants need to engage with traditional knowledge for three principal reasons:

2First, gap-filling in data-sparse regions. Many coastal and marine areas lack adequate scientific monitoring infrastructure, particularly in remote islands, polar seas, and developing coastal states. Traditional knowledge holders who have sustained relationships with these environments over generations hold observational knowledge that can inform ecosystem condition assessments, document historical baselines, and identify environmental changes not captured by sparse monitoring networks. For example, Indigenous observations of sea ice dynamics in Arctic marine areas have extended observational records by decades, whilst Pacific Island community knowledge of reef condition provides spatially detailed information unavailable from satellite remote sensing alone1. This gap-filling function is particularly relevant to ecosystem condition accounts (TG-2.3 Ocean Condition Accounts) and biophysical indicator selection (TG-2.1 Aggregate Biophysical Indicators of Environmental State).

3Second, validation and contextualisation of scientific data. Traditional knowledge provides independent lines of evidence that can validate or contextualise remote sensing classifications, model outputs, and short-term field surveys. When traditional ecological knowledge converges with scientific monitoring, confidence in both knowledge systems is strengthened. Divergence identifies areas that warrant further investigation and may reveal phenomena not captured by conventional monitoring2. Cross-validation is particularly valuable for ecosystem extent accounts where benthic habitat classifications must be validated against on-water observations.

4Third, spatial unit delineation informed by tenure systems. Indigenous marine tenure systems often reflect ecologically meaningful boundaries developed through generations of resource management practice. In some contexts, customary marine areas provide more ecologically coherent spatial units for ecosystem accounting than administrative boundaries or uniform grid cells. Documentation of customary tenure also supports governance accounts (TG-3.7 Governance Accounts), which record the de facto management arrangements that shape ecosystem outcomes.

5The Kunming-Montreal Global Biodiversity Framework (GBF) Target 21 calls for ensuring that “the best available data, information and knowledge are accessible to decision makers, practitioners and the public to guide effective and equitable governance, integrated and participatory management of biodiversity”3. Traditional knowledge is explicitly recognised as essential to achieving this target. The 2030 Agenda for Sustainable Development similarly recognises the role of Indigenous peoples in sustainable development, including SDG Target 2.3 which calls for doubling “the agricultural productivity and incomes of small-scale food producers, in particular women, indigenous peoples, family farmers, pastoralists and fishers”4. For ocean accounting, Target 14.b emphasises providing “access for small-scale artisanal fishers to marine resources and markets,” an objective that requires understanding the traditional knowledge and customary practices that underpin small-scale fisheries.

6This Circular builds upon the broader framework for social accounting established in TG-3.5 Social Accounts, which addresses wellbeing, equity, and qualitative approaches for documenting human dimensions of ocean-society relationships. The governance dimensions of traditional knowledge systems connect to the institutional documentation frameworks in TG-3.7 Governance Accounts. Data collection methods involving community participation are addressed in TG-4.4 Citizen Science and Community-Based Monitoring, which provides complementary guidance on working with non-official data sources. The accounts developed using this guidance may inform thematic accounts for coral reefs (TG-6.1 Coral Reef Ecosystem Accounting), mangroves (TG-6.2 Mangrove and Coastal Wetland Accounting), and seagrass ecosystems (TG-6.3 Seagrass Ecosystem Accounting), where traditional knowledge of ecosystem condition and change can complement scientific monitoring.

2. Requirements

1Essential prerequisites:

3. Guidance Material

3.1 Principles for Engagement

1Engagement with Indigenous Peoples and Local Communities (IPLCs) for the purpose of incorporating traditional knowledge into ocean accounts must be grounded in respect for human rights, recognition of Indigenous peoples’ self-determination, and adherence to established international principles. The guidance in this section draws on frameworks established by the United Nations Declaration on the Rights of Indigenous Peoples (UNDRIP), the Convention on Biological Diversity (CBD), the Biodiversity Beyond National Jurisdiction (BBNJ) Agreement, and the Taskforce on Nature-related Financial Disclosures (TNFD). It is supplemented by guidance from the statistical community, including the United Nations Fundamental Principles of Official Statistics, which affirm that statistical agencies should coordinate with other agencies to achieve consistency and efficiency in the statistical system5, and the UNSD guidance on strengthening the integration of diverse knowledge systems in official statistics6.

3.1.1 The significance of traditional knowledge holders

1Traditional knowledge encompasses7:

  • 2Observational knowledge of species, habitats, and ecological relationships accumulated over generations
  • 3Understanding of seasonal patterns, environmental change, and ecosystem dynamics
  • 4Practices for sustainable resource use developed through long experience
  • 5Governance systems for managing common resources and resolving conflicts
  • 6Spiritual and cultural relationships with marine environments
  • 7Oral histories documenting environmental change over time

8This knowledge can provide insights not available from short-term scientific monitoring, particularly regarding long-term baselines, rare events, and relationships that require sustained local observation to understand. For ocean accounting, traditional knowledge may inform ecosystem condition assessments (see TG-2.3 Ocean Condition Accounts), ecosystem service identification (see TG-2.4 Ecosystem Goods and Services), and understanding of human-ocean relationships that are not captured in standard economic or environmental data.

9Experience from multiple regions demonstrates the practical value of traditional knowledge for marine ecosystem assessment. In the Pacific Islands, customary marine tenure systems have long provided the basis for community-based fisheries management, and traditional ecological knowledge of reef systems has informed both national conservation strategies and regional environmental monitoring8. In the Arctic, Indigenous observations of sea ice dynamics, marine mammal behaviour, and shifting species distributions have contributed to understanding environmental change in ways that complement satellite-based monitoring9. In Southeast Asia and the Indian Ocean, local fisher knowledge of spawning aggregations, seasonal current patterns, and habitat changes has contributed to marine spatial planning and stock assessments10. In each case, traditional knowledge has yielded practical contributions where institutional arrangements supported respectful engagement.

3.1.2 International frameworks for engagement

1Several international instruments establish the framework for engagement with traditional knowledge holders:

2United Nations Declaration on the Rights of Indigenous Peoples (UNDRIP): Adopted in 2007, UNDRIP affirms Indigenous peoples’ rights to self-determination, to maintain their cultural practices and institutions, and to control their traditional knowledge. Article 31 states that “Indigenous peoples have the right to maintain, control, protect and develop their cultural heritage, traditional knowledge and traditional cultural expressions”11. Article 26 recognises Indigenous peoples’ rights to “the lands, territories and resources which they have traditionally owned, occupied or otherwise used or acquired”12.

3Convention on Biological Diversity (CBD): Article 8(j) requires parties to “respect, preserve and maintain knowledge, innovations and practices of indigenous and local communities embodying traditional lifestyles relevant for the conservation and sustainable use of biological diversity”13. The Nagoya Protocol on Access and Benefit Sharing establishes specific requirements for access to traditional knowledge associated with genetic resources, including requirements for prior informed consent and fair and equitable benefit sharing14.

4Kunming-Montreal Global Biodiversity Framework: Target 21 specifically calls for ensuring “the full, equitable, inclusive, effective and gender-responsive representation and participation in decision-making, and access to justice and information related to biodiversity by indigenous peoples and local communities, respecting their cultures and their rights over lands, territories, resources, and traditional knowledge”15. Target 3 calls for conserving at least 30% of marine and coastal areas “recognizing indigenous and traditional territories, where applicable”16. Target 5 calls for ensuring sustainable use of wild species “while respecting and protecting customary sustainable use by indigenous peoples and local communities”17.

5ILO Convention 169: The Indigenous and Tribal Peoples Convention establishes that governments shall “consult the peoples concerned, through appropriate procedures and in particular through their representative institutions, whenever consideration is being given to legislative or administrative measures which may affect them directly”18.

6Agreement on Biodiversity Beyond National Jurisdiction (BBNJ Agreement): The 2023 BBNJ Agreement, adopted under the United Nations Convention on the Law of the Sea, includes provisions specifically relevant to traditional knowledge in areas beyond national jurisdiction. Article 7 provides that the agreement shall be interpreted and applied in a manner that “does not undermine relevant legal instruments and frameworks and relevant global, regional and sectoral bodies” and recognises the “relevant traditional knowledge of Indigenous Peoples and local communities.” Part II of the agreement, on marine genetic resources and benefit sharing, establishes that “the collection of marine genetic resources of areas beyond national jurisdiction shall be … with due regard for the interests and rights of … Indigenous Peoples and local communities”19. For ocean accounting that extends to high seas areas, these provisions establish the principle that traditional knowledge must be respected even in areas beyond national jurisdiction.

1Free, Prior and Informed Consent (FPIC) is the foundational principle for engagement with Indigenous Peoples and Local Communities regarding the use of their traditional knowledge. The TNFD recommends that organisations describe “whether engagement has been based on free, prior and informed consultation and participation and how Free Prior and Informed Consent (FPIC) has been obtained”20.

2FPIC requires that consent be:

  • 3Free: Given voluntarily, without coercion, intimidation, or manipulation
  • 4Prior: Sought sufficiently in advance of any activities, allowing adequate time for consultation and decision-making according to the community’s own processes
  • 5Informed: Based on full disclosure of the purpose, nature, and implications of the proposed engagement, including potential risks and benefits
  • 6Consent: Documented agreement from the appropriate decision-making bodies according to the community’s own governance structures

7For ocean accounting purposes, FPIC should be sought before:

  • 8Collecting traditional knowledge for use in accounts
  • 9Integrating traditional knowledge with scientific data
  • 10Publishing or sharing information derived from traditional knowledge
  • 11Making decisions that affect marine areas of cultural significance

12FPIC is an ongoing process rather than a single event at the outset. Communities may withdraw consent, and continued engagement requires continued communication and agreement.

13The process for obtaining FPIC should be documented and included in the metadata for any accounts that incorporate traditional knowledge. This documentation supports the transparency requirements that apply across all ocean accounting work, as described in TG-0.7 Quality Assurance Principles.

3.1.4 Principles for respectful engagement

1Building on the international frameworks, practitioners should adhere to the following principles when engaging with traditional knowledge holders:

2Recognise community protocols: Each community has its own protocols for sharing knowledge, including who may speak on behalf of the community, what knowledge may be shared, and under what conditions. Practitioners must invest time in understanding and respecting these protocols before seeking to access traditional knowledge21.

3Build long-term relationships: Meaningful engagement with traditional knowledge holders cannot be achieved through brief consultations or one-time data collection exercises. Practitioners should invest in building sustained relationships based on trust and mutual benefit22. This principle of sustained engagement distinguishes traditional knowledge work from standard data collection and has implications for resource allocation and institutional commitment.

4Respect knowledge ownership: Traditional knowledge belongs to the communities that hold it, not to researchers or agencies that document it. Even when knowledge is shared, intellectual property rights remain with the knowledge holders23. This principle applies regardless of whether knowledge has been formally registered or protected under intellectual property law.

5Ensure equitable benefit sharing: Communities should benefit from the use of their knowledge, whether through direct compensation, capacity building, access to results, or other forms of reciprocity24. The TNFD recommends describing “how equitable Access and Benefit Sharing has been attained, particularly as it relates to Indigenous Peoples and Local Communities”25. Benefit sharing connects to the broader equity considerations addressed in TG-3.5 Social Accounts, Section 3.2.

6Support community priorities: Engagement should respond to community priorities and concerns, not solely to the data needs of accounting agencies. Where possible, accounting efforts should be designed to serve community information needs as well as national statistical requirements.

3.2 Knowledge Integration Approaches

1The integration of traditional knowledge with scientific data and accounting frameworks presents methodological challenges. Traditional knowledge is typically embedded in integrated worldviews, transmitted orally, and expressed in languages and concepts that may not have direct equivalents in Western scientific frameworks. Integration approaches must respect the integrity of traditional knowledge whilst enabling meaningful contribution to ocean accounts.

2Experience to date suggests that successful integration has been achieved through iterative, relationship-based approaches rather than through standardised data collection protocols. In Fiji, community-based ecosystem assessments have combined traditional indicators of reef health (e.g., presence of particular species, water clarity at specific times of year) with scientific monitoring data to produce fuller condition accounts26. In the Torres Strait, collaborative mapping of sea country has combined Indigenous spatial knowledge with satellite-derived habitat maps to improve the accuracy of ecosystem extent accounts27. These examples indicate the potential for traditional knowledge to contribute practically to ocean accounting compilations, whilst also demonstrating that integration methods must be adapted to each context. The GOAP Secretariat may wish to facilitate documentation of additional case studies as implementation experience accumulates.

3.2.1 Complementary rather than supplementary

1Traditional knowledge does more than fill gaps in scientific monitoring, and treating it solely as a gap-filling data source understates its contribution. The SEEA Ecosystem Accounting framework recognises that cultural services involve “experiential and intangible services related to the perceived or actual qualities of ecosystems whose existence and functioning contribute to a range of cultural benefits”28. Traditional knowledge can inform understanding of these experiential and intangible dimensions that may not be captured by conventional measurement approaches.

2Approaches to integration include:

3Parallel documentation: Traditional knowledge and scientific data can be documented in parallel, each using methods appropriate to its nature, with explicit acknowledgement of their different epistemological foundations (the different ways each knowledge system establishes what counts as valid knowledge). This approach respects the integrity of each knowledge system whilst enabling comparison and synthesis.

4Cross-validation: Where traditional knowledge and scientific monitoring address similar questions (e.g., species abundance, environmental change), cross-validation can strengthen confidence in findings. Convergent results from different knowledge systems provide stronger evidence than either alone. Divergent results may indicate important phenomena that warrant further investigation29.

5Gap identification: Traditional knowledge can help identify phenomena, relationships, or changes that are not captured by existing monitoring, prompting development of new scientific approaches. Traditional knowledge holders often have long-term observational baselines that extend well beyond the period of scientific record. The SEEA biophysical modelling guidance notes that “using a more recent reference condition (e.g. 1990) is another option” but acknowledges that this “fails to recognize the management of indigenous peoples”30. Traditional knowledge can extend baselines to pre-industrial or pre-colonial conditions, though such historical reconstruction requires careful methodological consideration. This is particularly relevant for ecosystem condition accounts, where understanding of historical baselines is essential (see TG-2.1 Aggregate Biophysical Indicators of Environmental State).

6Contextualisation: Traditional knowledge can provide essential context for interpreting scientific data, including understanding of historical conditions, ecosystem variability, and local factors that affect observations.

7Table 3.6.1: Traditional knowledge integration principles

TK Integration StageConsiderationsExample Applications
EngagementFree, prior, informed consentCommunity consultation protocols
Data collectionRespect for cultural protocolsSeasonal calendars, species knowledge
ValidationTK as complementary evidenceCorroboration of scientific observations
AttributionRecognition of knowledge holdersDocumentation, co-authorship
Benefit sharingFair distribution of benefitsCapacity building, data sovereignty

3.2.2 Co-production approaches

1Knowledge co-production involves the collaborative generation of knowledge by scientists and traditional knowledge holders working together as partners. Co-production goes beyond consultation or data extraction to involve Indigenous Peoples and Local Communities in all stages of the research process, from question formulation to interpretation of results31.

2Table 3.2.2 below summarises four elements of co-production.

ElementDescription
Joint problem definitionResearch questions and accounting priorities are developed collaboratively, reflecting both scientific interests and community priorities; communities may identify questions that would not occur to outside researchers.
Multiple ways of knowingTraditional knowledge and scientific knowledge represent different but equally valid ways of understanding the world; neither is simply validated by the other, and both contribute distinct insights.
Shared governanceDecision-making about research design, data management, and dissemination is shared between scientific and community partners, often formalised through research agreements or memoranda of understanding.
Two-way capacity buildingCapacity building flows in both directions, with scientists learning from knowledge holders and communities gaining skills in documentation, analysis, and communication.

3For ocean accounting, co-production approaches may be particularly valuable for:

  • 4Identifying culturally significant marine areas and their management needs
  • 5Understanding ecosystem services that have cultural or spiritual dimensions
  • 6Documenting long-term environmental change
  • 7Developing locally appropriate indicators of ecosystem condition

8These applications connect to the indicator development processes described in TG-2.1 Aggregate Biophysical Indicators of Environmental State.

3.2.3 Documentation methods

1Documentation of traditional knowledge requires methods that are appropriate to its oral and contextual nature. Standard survey instruments developed for scientific data collection may be inappropriate for traditional knowledge, which is often embedded in narratives, ceremonies, and practices rather than expressed as discrete data points.

2Appropriate methods are summarised in Table 3.2.3 below.

MethodDescription
Participatory mappingCollaborative mapping exercises document spatial knowledge about marine areas, including locations of cultural significance, seasonal resource availability, and areas of environmental change.32
Oral history documentationStructured or semi-structured interviews document knowledge holders’ observations and experiences, preserving the narrative context that gives meaning to the knowledge.
Participant observationExtended engagement with communities enables understanding of how traditional knowledge is embedded in practice, revealing knowledge that may not be articulated in response to direct questions.
Community-led documentationCommunities document their own knowledge using methods they control, sharing results with accounting agencies according to agreed protocols.

3All documentation should include clear provenance information, noting who provided the knowledge, under what circumstances, and what conditions govern its use. This approach aligns with the quality assurance principles described in TG-0.7 Quality Assurance Principles and the guidance on non-official data sources in TG-4.4 Citizen Science and Community-Based Monitoring.

3.2.4 Data sovereignty and ownership

1Data sovereignty refers to the right of communities to control data about themselves, their lands, and their knowledge. For Indigenous Peoples, data sovereignty is an expression of self-determination, enabling communities to make decisions about what data are collected, how they are stored, and who can access them33.

2The CARE Principles for Indigenous Data Governance, developed by the Global Indigenous Data Alliance, provide a framework for operationalising data sovereignty in research and statistical contexts. The four principles are34:

  • 3Collective benefit: Data ecosystems should be designed and function in ways that enable Indigenous Peoples to derive benefit from the data. This includes supporting Indigenous governance, self-determination, and collective wellbeing.
  • 4Authority to control: Indigenous Peoples’ rights and interests in Indigenous data must be recognised, and their authority to control such data must be empowered. This includes recognising Indigenous governance structures and self-determined governance processes.
  • 5Responsibility: Those working with Indigenous data have a responsibility to share how those data are used to support Indigenous Peoples’ self-determination and collective benefit. This requires building respectful relationships and expanding the use of data for Indigenous innovation.
  • 6Ethics: Indigenous Peoples’ rights and wellbeing should be the primary concern at all stages of the data life cycle. This includes minimising harm, maximising benefit, and prioritising justice in relation to Indigenous values and collective interests.

7The CARE Principles complement the FAIR Principles (Findable, Accessible, Interoperable, Reusable) that guide open data practice more broadly. For ocean accounting, both sets of principles should be considered, as open data objectives must be balanced with Indigenous data sovereignty rights.

8Principles for data sovereignty in ocean accounting include:

9Community ownership: Data derived from traditional knowledge remain the property of the knowledge-holding community, even when documented by external parties. Agencies should not claim ownership of traditional knowledge they have recorded.

10Control over access: Communities should determine who can access data derived from their traditional knowledge and under what conditions. This may include restrictions on commercial use, requirements for attribution, or limitations on sharing with third parties.

11Capacity to benefit: Communities should have the capacity to access and use their own data for their own purposes, including through provision of data in accessible formats and support for community data management.

12Right to refuse: Communities retain the right to refuse to share knowledge, to withdraw previously shared knowledge from use, or to restrict uses they have not explicitly authorised.

13Practical implementation of data sovereignty may involve:

  • 14Research agreements that specify data ownership, access, and use conditions
  • 15Community-controlled data repositories where traditional knowledge is stored under community governance
  • 16Tiered access systems that distinguish between knowledge that can be shared publicly and knowledge that is restricted
  • 17Ongoing community review of how their knowledge is being used in accounts

18These considerations connect to the broader data infrastructure for ocean accounting described in Section 4 of the Technical Guidance.

3.3 Ethical Considerations

1Working with traditional knowledge in ocean accounting raises ethical considerations that extend beyond standard research ethics protocols. These considerations arise from the colonial history of research with Indigenous peoples, the ongoing power imbalances between scientific institutions and local communities, and the distinctive characteristics of traditional knowledge as a form of cultural property.

3.3.1 Historical context and power relations

1Scientific research has historically extracted knowledge from Indigenous peoples and local communities without consent, attribution, or benefit sharing. This extractive approach has contributed to the erosion of traditional knowledge systems and to distrust between communities and research institutions. Practitioners working with traditional knowledge must acknowledge this history and actively work to establish different relationships based on equity and respect35.

2The TNFD framework recognises that human rights considerations are integral to nature-related assessment, calling for organisations to “describe the organisation’s human rights policies and engagement activities, and oversight by the board and management, with respect to Indigenous Peoples, Local Communities, affected and other stakeholders”36. Engagement with IPLCs is a human rights issue as well as a methodological one, and this framing should inform all traditional knowledge work in ocean accounting.

3Power imbalances may manifest in:

  • 4Whose questions drive research agendas
  • 5Whose standards define data quality
  • 6Who controls how knowledge is interpreted and presented
  • 7Who benefits from the use of traditional knowledge
  • 8Whose voices are heard in decision-making

9Addressing these imbalances requires sustained attention and willingness to share power and resources with community partners. This connects to the equity considerations addressed in TG-3.5 Social Accounts, Section 3.2, which discusses distributional dimensions of ocean benefits and burdens.

3.3.2 Avoiding misappropriation

1Misappropriation of traditional knowledge occurs when knowledge is used in ways that violate community protocols, infringe intellectual property rights, or harm the interests of knowledge holders. The history of traditional knowledge misappropriation indicates the serious consequences that can result. In the marine context, the documentation and publication of traditional fishing grounds and sacred marine sites without community consent has in some cases led to increased external pressure on these areas, undermining the management systems that traditional knowledge holders sought to protect37. In other instances, traditional ecological knowledge about medicinal marine organisms has been used in commercial bioprospecting without acknowledgement or benefit sharing. Safeguards are therefore needed at every stage of engagement.

2Practices that may constitute misappropriation include:

  • 3Using traditional knowledge without consent
  • 4Failing to acknowledge the source of traditional knowledge
  • 5Using knowledge for purposes beyond those consented to
  • 6Sharing knowledge with third parties without authorisation
  • 7Claiming intellectual property rights over traditional knowledge
  • 8Commercialising knowledge without benefit sharing

9To avoid misappropriation, practitioners should:

  • 10Obtain FPIC before accessing traditional knowledge
  • 11Document the conditions under which knowledge was shared
  • 12Restrict use of knowledge to authorised purposes
  • 13Maintain attribution in all derived products
  • 14Share benefits equitably with knowledge-holding communities
  • 15Establish clear agreements regarding intellectual property

3.3.3 Protecting sacred and sensitive knowledge

1Traditional knowledge often includes information that is sacred, secret, or sensitive. Some knowledge may be restricted to particular individuals, clans, or genders. Other knowledge is associated with ceremonies that should not be discussed publicly, or relates to sites and practices that communities wish to protect from outside attention.

2Practitioners must be aware that:

  • 3Not all traditional knowledge is intended for sharing
  • 4Communities may not disclose the existence of restricted knowledge
  • 5Knowledge shared may come with conditions that are not fully articulated
  • 6Documentation and publication can harm knowledge that should remain oral

7Approaches for protecting sensitive knowledge include:

  • 8Asking explicitly what knowledge may be documented and shared
  • 9Respecting indications that some topics are not open for discussion
  • 10Establishing review processes where communities approve all uses of their knowledge before publication
  • 11Creating restricted-access categories for sensitive information in data management systems
  • 12Being willing to exclude certain knowledge from accounts when sharing would violate protocols

13Some aspects of human-ocean relationships may therefore be impossible to document in published accounts. Practitioners should accept these limitations as necessary for ethical practice, and should not treat them as obstacles to complete accounting.

3.3.4 Maintaining cultural integrity

1Integration of traditional knowledge into accounting frameworks risks decontextualisation, whereby discrete data points are extracted from the integrated worldviews that give them meaning. Such decontextualisation can distort the knowledge and obscure the cultural frameworks that are essential to understanding it.

2To maintain cultural integrity:

  • 3Present traditional knowledge in ways that preserve its context and meaning
  • 4Avoid forcing traditional knowledge into categories derived from Western scientific frameworks when these categories are inappropriate
  • 5Include narrative and qualitative elements alongside quantified data (see the qualitative approaches discussed in TG-3.5 Social Accounts, Section 3.4)
  • 6Acknowledge the limitations of accounting frameworks in representing traditional knowledge
  • 7Involve knowledge holders in reviewing how their knowledge is presented

8The SEEA EA emphasises that ecosystem accounting supports ongoing learning and analysis, and that compilation of accounts forms part of an iterative process rather than its conclusion38. This iterative framing is particularly relevant for traditional knowledge, where understanding deepens through sustained engagement over time.

3.4 Compilation Procedure for Integrating Traditional Knowledge

1This section provides step-by-step guidance on the compilation process for integrating traditional knowledge into ocean accounts. The procedure follows a phased approach that prioritises relationship-building, ethical review, and quality assurance for mixed-method data. The timelines indicated below are illustrative. Actual engagement timelines will vary substantially depending on community readiness, agency capacity, and cultural context. In some cases, relationship building alone may require years rather than months.

3.4.1 Phase 1: Pre-engagement assessment (Months 1-3)

1Step 1.1: Identify relevant communities and knowledge holders

2Review the ecosystem accounting area to identify Indigenous Peoples and Local Communities with traditional knowledge relevant to the marine areas under consideration. Sources may include:

  • 3Existing literature on Indigenous marine tenure systems
  • 4Government records of customary fishing rights
  • 5NGO documentation of community-based conservation
  • 6Previous ethnographic or anthropological research

7Step 1.2: Assess institutional readiness

8Evaluate whether the compiling agency has:

  • 9Sufficient resources for sustained engagement (minimum 12-18 months)
  • 10Personnel with cultural competence or willingness to develop it
  • 11Leadership commitment to ethical engagement principles
  • 12Budget for fair compensation of knowledge holders
  • 13Data management systems capable of implementing data sovereignty protocols

14If institutional readiness is inadequate, defer traditional knowledge engagement until capacity can be strengthened.

15Step 1.3: Identify potential knowledge contributions

16Based on preliminary review, identify the specific accounting gaps where traditional knowledge could contribute:

  • 17Ecosystem extent: Habitat boundaries, historical extent baselines
  • 18Ecosystem condition: Species abundance trends, water quality observations, phenological shifts
  • 19Ecosystem services: Cultural services, provisioning services (traditional harvest), regulating services informed by local observation
  • 20Spatial units: Customary marine tenure areas as potential ecosystem asset boundaries

21This scoping exercise should be preliminary only. Final determination of what knowledge will be shared must emerge through community engagement.

3.4.2 Phase 2: Relationship building and FPIC (Months 4-9)

1Step 2.1: Establish initial contact

2Contact community leadership through appropriate channels (government liaisons, existing relationships, or community-designated contact points). Request permission to discuss the ocean accounts program and potential collaboration.

3Step 2.2: Community briefing

4Present information about the ocean accounts program in accessible language and format, explaining:

  • 5What ocean accounts are and how they will be used
  • 6What types of information the agency hopes communities might share
  • 7How traditional knowledge would be documented and stored
  • 8What benefits might accrue to the community from participation
  • 9What risks or sensitivities might arise

10Provide materials in local languages where possible. Allow adequate time for community deliberation according to their own decision-making processes.

11Step 2.3: Negotiate terms of engagement

12If the community expresses interest in participating, negotiate terms covering:

  • 13What knowledge may be shared and what restrictions apply
  • 14How knowledge holders will be compensated for their time
  • 15How the community will be acknowledged in publications
  • 16What review processes will be established for community approval of outputs
  • 17How data sovereignty will be implemented
  • 18What benefit-sharing arrangements will apply
  • 19Under what circumstances the community may withdraw consent

20Step 2.4: Formalise agreement

21Document terms in a memorandum of understanding or research agreement signed by community representatives and agency officials. The agreement should specify:

  • 22Scope of knowledge to be documented
  • 23Data ownership and access conditions
  • 24Attribution and acknowledgement requirements
  • 25Compensation arrangements
  • 26Review and approval procedures
  • 27Dispute resolution mechanisms
  • 28Duration of agreement and conditions for renewal or termination

3.4.3 Phase 3: Knowledge documentation (Months 10-15)

1Step 3.1: Select documentation methods

2In consultation with the community, select appropriate documentation methods from those described in Section 3.2.3. Methods should align with community preferences and the nature of the knowledge being documented.

3Step 3.2: Conduct knowledge documentation

4Implement the agreed documentation methods, adhering to:

  • 5Community protocols for knowledge sharing
  • 6Compensation arrangements for knowledge holders’ time
  • 7Cultural protocols regarding who may speak on what topics
  • 8Restrictions on recording or documentation in certain contexts

9Documentation should capture not only the knowledge content but also provenance metadata including:

  • 10Identity of knowledge holders (with consent for attribution)
  • 11Date and location of documentation
  • 12Context in which knowledge was shared
  • 13Any restrictions or conditions on use
  • 14Relationships between knowledge holders and the marine areas being discussed

15Step 3.3: Community review

16Provide documented knowledge back to the community for review. Correct any errors, remove any information the community determines should not have been included, and clarify any ambiguities. This review process is distinct from the final output review, and it ensures the documentation accurately reflects what knowledge holders intended to communicate.

3.4.4 Phase 4: Quality assurance for mixed-method data (Months 16-18)

1Step 4.1: Assess fit-for-purpose for accounting

2Evaluate documented traditional knowledge against accounting requirements, considering:

  • 3Spatial coverage: Does the knowledge pertain to specific ecosystem assets or spatial units in the accounting area?
  • 4Temporal relevance: Does the knowledge provide baselines, trends, or current observations aligned with accounting periods?
  • 5Measurement units: Can the knowledge be expressed in or translated to units compatible with accounting tables (hectares, species counts, qualitative condition classes, etc.)?
  • 6Uncertainty: What is the confidence level in the knowledge? How might uncertainty be characterised and communicated?

7Step 4.2: Identify cross-validation opportunities

8Where traditional knowledge and scientific data address similar questions, plan for cross-validation:

  • 9Convergent findings strengthen confidence in both knowledge systems
  • 10Divergent findings signal areas requiring further investigation
  • 11Document both convergence and divergence transparently

12Step 4.3: Develop integration approach

13Based on the assessment, select the appropriate integration approach from Section 3.2.1:

  • 14Parallel documentation: Traditional knowledge recorded in supplementary tables alongside scientific data
  • 15Cross-validation: Traditional knowledge used to validate scientific classifications or model outputs
  • 16Gap-filling: Traditional knowledge fills spatial or temporal gaps in scientific monitoring
  • 17Contextualisation: Traditional knowledge provides interpretive context for scientific data

18Most compilations will use a combination of these approaches for different knowledge types.

19Step 4.4: Quality documentation

20Document quality dimensions following TG-0.7 Quality Assurance Principles:

  • 21Accuracy: Characterise uncertainty in traditional knowledge observations
  • 22Coherence: Assess consistency with other data sources where overlap exists
  • 23Relevance: Confirm alignment with policy and decision-maker needs
  • 24Timeliness: Note the time period to which knowledge pertains
  • 25Accessibility: Describe access conditions including data sovereignty restrictions
  • 26Metadata: Provide complete provenance documentation

3.4.5 Phase 5: Integration into accounts and community review (Months 19-21)

1Step 5.1: Integrate into accounting tables

2Incorporate traditional knowledge into the relevant account types:

  • 3Extent accounts: Use traditional knowledge for historical baseline estimates, habitat boundary validation, or identification of previously unmapped ecosystem types
  • 4Condition accounts: Incorporate traditional indicators alongside scientific metrics, noting the knowledge source for each indicator
  • 5Services accounts: Document cultural services, validate provisioning service estimates, or contextualise regulating service assessments
  • 6Monetary accounts: Where appropriate, traditional knowledge may inform valuation of cultural services or historical resource rent calculations

7Step 5.2: Draft supplementary documentation

8Prepare supplementary text explaining:

  • 9How traditional knowledge was obtained (summarising the FPIC process without disclosing sensitive details)
  • 10What knowledge was incorporated and from which communities
  • 11What restrictions or conditions apply to use of the knowledge
  • 12How quality assurance was conducted for traditional knowledge contributions
  • 13What limitations or uncertainties users should be aware of

14Step 5.3: Community review of outputs

15Provide draft accounts and supplementary documentation to the community for review. The community should assess:

  • 16Whether their knowledge is accurately represented
  • 17Whether any sensitive information has inadvertently been included
  • 18Whether attribution and acknowledgement are appropriate
  • 19Whether the integration respects the integrity of their knowledge

20Revise accounts based on community feedback. If the community determines that publication would violate protocols, respect that determination even if it means removing substantial content from accounts.

21Step 5.4: Final approval

22Obtain written community approval before publication. Archive the approval documentation as part of the accounts metadata.

3.4.6 Ongoing engagement and benefit sharing

1Traditional knowledge integration is not complete upon publication of accounts. Ongoing responsibilities include:

  • 2Provide communities with copies of published accounts in accessible formats
  • 3Share information about how accounts are being used in policy or decision-making
  • 4Fulfil any benefit-sharing commitments (capacity building, data access, etc.)
  • 5Maintain communication to support continued consent for use of knowledge
  • 6Consult the community before any new uses of their knowledge
  • 7Support community-led monitoring or data management initiatives where feasible

3.5 Cultural Services and Traditional Knowledge

1Traditional knowledge relates closely to the cultural ecosystem services recognised in the SEEA Ecosystem Accounting framework. Cultural services include “recreation-related services, visual amenity services, education, science and research services, spiritual, artistic and symbolic services at the most detailed level”39. For many Indigenous Peoples and coastal communities, marine ecosystems provide cultural services that are central to identity, spiritual practice, and intergenerational knowledge transmission.

3.5.1 Cultural services in ocean contexts

1Marine cultural services that may be informed by traditional knowledge include:

2Spiritual and ceremonial connections: Marine areas may be sites of spiritual significance, associated with ancestral beings, creation stories, or ongoing ceremonial practice. Traditional knowledge holders can identify these sites and articulate their significance, though this knowledge may be sensitive and subject to restrictions on sharing. The SEEA EA recognises that “there may be traditional harvests undertaken by indigenous groups” and that “if the harvest is retained for subsequent consumption, then the quantity of the associated biomass should be included as part of biomass provisioning services. At the same time, there would be a connection to the measurement of cultural services. In these instances, flows of cultural services should be recorded in addition to biomass provisioning services”40.

3Customary resource use: The gathering of marine resources for customary purposes contributes to cultural continuity and intergenerational knowledge transmission. Understanding these practices requires engagement with traditional knowledge holders who can explain the cultural dimensions that distinguish customary use from commercial extraction. This connects to the discussion of ocean sector employment in TG-3.5 Social Accounts, Section 3.1.2.

4Place-based knowledge and identity: For coastal communities, marine environments are often central to collective identity. Traditional place names, navigation knowledge, and environmental knowledge contribute to sense of place and cultural identity that cannot be captured in conventional ecosystem service metrics.

5Educational and intergenerational transmission: Marine environments serve as sites for education and knowledge transmission, where younger generations learn from elders through observation and practice. This educational service depends on the continued health of marine ecosystems and continuity of cultural practices.

6For guidance on the broader framework for cultural ecosystem services, see TG-2.4 Ecosystem Goods and Services. The full mapping of cultural service categories to traditional knowledge contributions is provided in Table 3.6.3 below.

3.5.2 Cultural ecosystem services framing for traditional knowledge contributions

1The cultural-service framing established in the international classifications (the Millennium Ecosystem Assessment (MEA), the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES), the Common International Classification of Ecosystem Services (CICES) v5.1, and SEEA Ecosystem Accounting Chapter 6) provides a structured entry point for incorporating traditional knowledge into ocean accounts, whilst leaving the integrity of the knowledge itself unchanged. The MEA defines cultural services as the non-material benefits people obtain from ecosystems41. IPBES recognises analogous non-material contributions, including supporting identities, learning and inspiration, and physical and psychological experiences42. CICES v5.1 organises cultural services into direct in-situ interactions and indirect interactions43. SEEA EA defines cultural services as “experiential and intangible services related to the perceived or actual qualities of ecosystems whose existence and functioning contribute to a range of cultural benefits”44 and notes (para. 6.97) the joint recording of customary harvest as both biomass provisioning and cultural service flows45.

2Traditional knowledge holders are often the principal source of information on five categories of cultural service that are otherwise difficult to observe. Each of these connects a biophysical condition signal (documented in TG-2.1 Aggregate Biophysical Indicators of Environmental State and TG-2.3 Ocean Condition Accounts) to a social or cultural dimension recorded under TG-3.5 Social Accounts, Section 3.2.5. Practitioners may consider this framing as a candidate organising structure. Specific indicator sets, units, and beneficiary classes should be co-designed with knowledge holders and need not follow the categories below rigidly.

3Recreation and customary use as a cultural service. Recreation in the CICES and SEEA EA senses includes structured market-based activities (tourism, recreational fishing) and also non-market customary practices such as gleaning of invertebrates, seasonal harvest of finfish, and gathering of marine plants. Where customary practices have strong cultural and social dimensions (intergenerational transmission, gendered roles, ceremonial timing), SEEA EA permits joint recording as a cultural service alongside biomass provisioning45. Traditional knowledge holders can articulate which specific harvest practices carry these cultural dimensions, which species or sites are involved, and which condition signals (target species abundance, habitat extent, water clarity) most directly affect the continuity of the practice. Worked numeric examples illustrating coral reef recreation, mangrove ecotourism, and invertebrate gleaning are presented in the case studies under TG-5.1 Australia through TG-5.10 Vietnam. This Circular is method-agnostic on valuation and does not endorse specific parameter values.

4Sense of place and named features. Sense of place is recognised by IPBES under “supporting identities”42 and by CICES under spiritual and symbolic interactions43. Traditional knowledge often comprises detailed place-based vocabularies (named reefs, passages, anchorages, and seasonal grounds) that may have no equivalent in scientific gazetteers. Practitioners may consider recording the existence and number of such named features (with community consent), the proportion of community members reporting strong attachment to them, and any documented changes in their physical state. The condition—wellbeing linkage is direct but often non-linear: a culturally significant feature may retain its identity value across a wide range of biophysical conditions yet become a focus of community concern when condition crosses a locally recognised threshold.

5Customary stewardship and customary tenure. Customary tenure systems (locally managed marine areas, taboo zones, seasonal closures) are recognised in CBD GBF Targets 3 and 5 and in the BBNJ Agreement. Where present, these systems are themselves cultural and institutional outcomes of long-term human-ocean relationships. Traditional knowledge holders may identify the spatial extent, governance arrangements, and current status of customary tenure, information that contributes to the cultural-service account of the present Circular and to the governance account under TG-3.7 Governance Accounts. Practitioners may consider recording the presence, extent, and observed enforcement of customary tenure as a candidate indicator, with the spatial details treated under data sovereignty protocols where required.

6Intergenerational transmission of marine knowledge. SEEA EA recognises education, science, and research as a cultural service category44. For many coastal communities, the marine environment is the principal site of intergenerational learning, and the continuity of that learning is itself an indicator of cultural-service supply. Traditional knowledge holders are the only authoritative source on whether transmission is occurring, declining, or interrupted. Practitioners may consider recording, in close consultation with communities, whether elders report that customary practices are being taught to younger generations, and whether this transmission is constrained by condition decline, access restrictions, or social change.

7Spiritual and ceremonial connections and non-use values. Some cultural services arise without direct economic interaction: the value attached to the existence of a sacred site, an ancestral being, or a species of cultural significance. The MEA and IPBES both recognise these dimensions. SEEA EA is cautious about including pure existence values in monetary ecosystem service accounts but supports their recording in supplementary or qualitative form44. For traditional knowledge contributions, the protocols in Section 3.3.3 of this Circular apply: some spiritual and ceremonial dimensions may not be appropriate for public documentation and may be recorded only under restricted-access arrangements or excluded by community decision.

8Table 3.6.3: Cultural ecosystem service categories and candidate traditional knowledge contributions

Cultural service category (per SEEA EA / CICES v5.1)Candidate TK contributionLinked condition signal (TG-2.1 / TG-2.3)Linked social-account dimension (TG-3.5 Section 3.2.5)
Physical and experiential interactions (recreation, customary harvest)Identification of culturally significant harvest practices, species, sites, and seasonal calendarsTarget species abundance; habitat extent; water clarityRecreation and nature-based tourism; customary and subsistence use
Spiritual, symbolic and other interactionsIdentification of sacred sites, ancestral narratives, ceremonial use (subject to community protocols)Condition of named features; integrity of cultural seascapesSense of place, cultural identity, spiritual values
Education and intergenerational transmissionAssessment of transmission status; identification of teaching sites and practicesContinued ecosystem functioning at teaching sitesEducation and intergenerational transmission
Heritage and identityTraditional place names; navigation knowledge; named feature inventoriesPersistence of recognisable seascape featuresSense of place; non-use values

9The cultural-service framing above is offered as a candidate scaffolding only. Practitioners may consider it where it supports community priorities and aligns with the protocols agreed under Section 3.4. Where the cultural-service vocabulary is unfamiliar or culturally inappropriate, the substantive content (named places, harvest practices, transmission status) may be recorded in narrative form following the qualitative approaches in TG-3.5 Social Accounts, Section 3.5. In all cases, the integrity of the underlying traditional knowledge takes precedence over fit with classification schemes; accounting frameworks should adapt to the knowledge, not the reverse.

3.5.3 Connections to governance accounts

1Traditional knowledge systems often include customary governance institutions that regulate access to marine resources and mediate conflicts. These customary systems may operate alongside or in tension with formal legal frameworks. Governance accounts should document customary governance arrangements where they influence marine management outcomes.

2The TNFD defines Local Communities partly in terms of their governance characteristics, noting that they may have “a set of social rules (e.g. that regulate land conflicts/sharing of benefits) and organisational-specific community/traditional/customary laws and institutions”46. For ocean accounting, documentation of these customary institutions can inform understanding of actual governance arrangements in marine areas.

3TG-3.7 Governance Accounts provides guidance on documenting customary governance alongside formal legal frameworks, including in Section 3.2.2 on customary law and Section 3.1.2 on multi-level governance structures that incorporate co-management arrangements.

4. Worked Example

1This section presents a hypothetical worked example illustrating how traditional knowledge might be incorporated into ocean accounts for a Pacific Island context. The example is entirely fictional and is designed to demonstrate the accounting structures and engagement processes described in this Circular. It is not based on any specific community or knowledge system, and should not be taken as representative of any particular Indigenous People or Local Community. In practice, every engagement with traditional knowledge holders must be tailored to the specific cultural context and conducted in accordance with the principles set out in Section 3.1.

4.1 Scenario: Mangrove cultural value assessment in a hypothetical Pacific Island community

1Setting. A national statistical office (NSO) in a Pacific Island State is compiling ecosystem accounts for a coastal lagoon system that includes 850 hectares of mangrove forest. Scientific monitoring data (satellite imagery, field surveys) provide information on mangrove extent and biophysical condition. However, the NSO recognises that the mangroves also provide cultural services to the adjacent community of approximately 2,500 people who have customary tenure over the lagoon, and that these cultural dimensions are not captured by existing scientific data.

2Objective. To incorporate traditional knowledge contributions into the cultural services component of the ecosystem accounts for the lagoon system, following the principles and processes described in this Circular.

4.2 FPIC process steps applied to the assessment

1The NSO follows the FPIC process described in Section 3.1.3. The steps below illustrate how FPIC principles translate into practice for this hypothetical case:

FPIC StepAction TakenTimeline
1. Free — Initial contact (see §3.1.3)NSO contacts community leadership through existing government liaison channels; requests a meeting to discuss the projectMonth 1
2. Prior — Community briefing (see §3.1.3)NSO staff visit the community, explain the ocean accounts programme, and describe what information they hope the community might share; materials provided in local languageMonth 2
3. Prior — Community deliberation (see §3.1.3)Community leadership consults with elders, clan heads, and knowledge holders using their own decision-making processes; NSO is not present during deliberationMonths 3-5
4. Informed — Conditions negotiated (see §3.1.3)Community agrees to participate, subject to conditions: (a) sacred site locations will not be published or georeferenced in public accounts; (b) all outputs will be reviewed by community before release; (c) community members who contribute knowledge will be compensated for their time; (d) the community will be acknowledged as knowledge holders in all publicationsMonth 6
5. Consent — Agreement documented (see §3.1.3)A memorandum of understanding is signed between the NSO and the community governance body, recording the terms of engagement and data use conditionsMonth 6
6. Ongoing consent (see §3.1.3)At each subsequent stage, the NSO confirms that the community is comfortable proceeding; the community retains the right to withdrawOngoing

4.3 Cultural services account template

1Based on the engagement process, the NSO compiles a supplementary cultural services account for the mangrove lagoon system. The account uses a parallel documentation approach (Section 3.2.1), recording scientific and traditional knowledge contributions side by side:

2Table 4.1: Cultural services account — mangrove lagoon system (hypothetical)

Cultural service category (per SEEA EA)Scientific data contributionTraditional knowledge contributionRecording in accounts
Spiritual, artistic, and symbolicNot available from scientific monitoringElders identify three areas within the mangrove system associated with ancestral narratives and ongoing ceremonial practice; one area is designated as restricted (not to be published)Supplementary note: “Three culturally significant areas identified by community knowledge holders; spatial details held under community data sovereignty protocols per MOU dated [date]“
Recreation-related (customary use)Satellite data show access trails to mangrove areasCommunity members describe traditional gleaning practices: collection of shellfish, crabs, and medicinal plants from specific mangrove zones, following seasonal calendarsSupplementary table: seasonal calendar of customary harvest activities (4 species groups, 12-month cycle), compiled from community workshops
Education, science, and researchMonitoring data cover 15 years (2010-2025)Elders provide oral history observations spanning approximately 60 years, noting changes in species composition, water clarity, and mangrove extent since the 1960sSupplementary note: “Community observations extend the baseline for condition assessment by approximately 45 years; key reported changes include [summary of reported changes, reviewed and approved by community]“
Heritage and cultural identityNot captured in biophysical monitoringCommunity identifies 12 traditional place names within the lagoon system, each associated with specific ecological features and use practices; 7 medicinal species identified by traditional healersSupplementary table: traditional place names and associated ecological features (12 entries); medicinal species inventory (7 entries, common names and uses, with community consent for publication)

4.4 Traditional knowledge inputs to condition accounts

1In addition to the cultural services account, traditional knowledge may contribute to ecosystem condition assessment. The following illustrative entries show how TK observations might appear alongside scientific indicators in a condition account:

2Table 4.2: Condition variable inputs from traditional knowledge (illustrative)

Condition variable (per SEEA EA)Scientific indicatorTK-informed indicatorIntegration notes
Species compositionSpecies richness from field survey (35 fish species, 2024)Elders report that 5 fish species commonly present 40 years ago are now rarely seen; 2 new species have appeared in last decadeCross-validation: 3 of the 5 reported absent species are confirmed absent in 2024 survey; the 2 new species are confirmed present; findings converge
Ecosystem extentSatellite-derived mangrove extent: 850 ha (2024)Community reports that mangroves extended approximately 200 m further seaward in the 1970s; a specific area of 40 ha was lost to coastal development in the 1990sGap identification: satellite record begins 2000; TK extends baseline to 1960s; reported loss of 40 ha is consistent with land use records
Water qualityTurbidity measurements from 3 monitoring stations (monthly since 2018)Fishers report that water clarity has declined noticeably since a road construction project upstream in 2015; traditionally, the bottom was visible at 3 m depth in the lagoon centreContextualisation: TK provides pre-monitoring baseline and identifies likely cause of observed turbidity increase

4.5 Benefit-sharing and capacity building outcomes

1As part of the agreed benefit-sharing arrangements, the NSO provides:

  1. 2Financial compensation: Knowledge holders who participated in documentation workshops receive hourly compensation at local professional rates (40 person-hours total)
  2. 3Capacity building: The NSO conducts a 2-day training workshop for 15 community members on basic ecosystem accounting concepts and how community knowledge contributes to national accounts
  3. 4Data access: The community receives a complete copy of the lagoon ecosystem accounts in print and digital formats, along with spatial data layers showing mangrove extent and condition
  4. 5Ongoing engagement: The NSO establishes an annual reporting schedule where accounts updates are shared with the community, and the community provides feedback on whether their knowledge continues to be appropriately represented

4.6 Key observations from the worked example

1This hypothetical example illustrates several important points about traditional knowledge integration:

  1. 2

    FPIC is a process, not an event. The engagement timeline spans at least six months before substantive knowledge exchange begins, and consent is maintained on an ongoing basis.

  2. 3

    Not all knowledge appears in published accounts. The sacred site locations are recorded under community data sovereignty protocols and do not appear in public accounts. This is consistent with the principle in Section 3.3.3 that some aspects of human-ocean relationships cannot be documented in published accounts.

  3. 4

    TK contributions appear as supplementary notes and tables, not as modifications to core SEEA accounts. The core extent and condition accounts retain their scientific basis, whilst TK contributions are recorded in supplementary tables that provide additional context, extended baselines, and culturally significant information.

  4. 5

    Cross-validation strengthens both knowledge systems. Where TK observations and scientific data converge (e.g., on species disappearances), confidence in both is increased. Where they diverge, this signals areas for further investigation.

  5. 6

    The cultural services account captures dimensions that scientific monitoring cannot. Spiritual significance, traditional place names, and customary use practices are inherently qualitative and community-specific; they can only be documented through respectful engagement with knowledge holders.

  6. 7

    Benefit-sharing is concrete and ongoing. The example includes specific financial, capacity-building, and data-access benefits that continue beyond the initial engagement period.

8Compilers should note that this example represents a favourable scenario in terms of community willingness to engage and clarity of governance structures. In practice, engagement may encounter challenges not illustrated here, including community disagreement about knowledge sharing, capacity constraints within the NSO, language barriers, and political sensitivities. The principles in Section 3.1 provide guidance for working through these challenges.

5. Compilation Considerations

5.1 Capacity and resources

1Working with traditional knowledge requires substantial investment in relationship building, culturally appropriate methods, and sustained engagement. Agencies considering incorporation of traditional knowledge into ocean accounts should secure adequate:

  • 2Time for relationship building before data collection begins (minimum 6-12 months)
  • 3Personnel with cultural competence and community engagement skills
  • 4Resources for fair compensation of knowledge holders
  • 5Capacity for ongoing community engagement, not one-time data extraction
  • 6Commitment from leadership to ethical engagement principles
  • 7Budget for translation and interpretation services where needed
  • 8Legal review capacity for research agreements and data sovereignty arrangements

9Resource planning for traditional knowledge engagement should recognise that timelines and costs differ substantially from conventional data collection. Agencies should anticipate that the relationship-building phase alone may require six to twelve months before substantive knowledge exchange can begin. Budget allocations should include provision for community liaison officers, travel to community locations, translation and interpretation services, compensation for knowledge holders’ time, and community review of outputs. Many agencies have underestimated these requirements, leading to inadequate engagement that fails to meet ethical standards or to produce reliable contributions to accounts. Where resources are insufficient for ethical engagement, it may be more appropriate to defer traditional knowledge integration until adequate support can be secured, rather than proceeding with superficial consultation that risks eroding community trust.

5.2 Limitations and uncertainties

1The incorporation of traditional knowledge into ocean accounts involves uncertainties:

  • 2Traditional knowledge may address different questions and use different concepts than those in accounting frameworks
  • 3Knowledge varies among individuals and communities, and aggregation may obscure important local variation
  • 4Not all traditional knowledge can or should be documented
  • 5Integration with scientific data involves translation between incommensurable knowledge systems (knowledge systems based on fundamentally different assumptions and methods)
  • 6Methods for validation and quality assurance are not well established

7Accounts incorporating traditional knowledge should clearly document these limitations and avoid overstating the precision or completeness of traditional knowledge contributions.

8The quality assurance framework in TG-0.7 Quality Assurance Principles provides general guidance on uncertainty characterisation. For traditional knowledge, uncertainty characterisation should address the cultural and contextual dimensions noted above, not only measurement uncertainty in the statistical sense.

5.3 Reporting and attribution

1When traditional knowledge contributes to ocean accounts, the contribution should be clearly acknowledged:

  • 2Credit knowledge-holding communities in account documentation
  • 3Distinguish traditional knowledge contributions from scientific data sources
  • 4Note any restrictions on use or sharing that apply to traditional knowledge components
  • 5Provide copies of relevant accounts to contributing communities
  • 6Recognise individual knowledge holders where they have consented to attribution

7These practices align with the metadata and provenance documentation requirements discussed in TG-4.4 Citizen Science and Community-Based Monitoring, Section 3.3.

1This Circular connects to several other components of the Technical Guidance:

Implementation Considerations

1For minimum institutional capacity, data infrastructure, and human skills requirements for compiling these accounts, see TG-0.8 Implementation Readiness Assessment. For guidance on adapting these methods to sub-national scales, see TG-3.11 Sub-National Ocean Accounts.

6. References and Further Reading

  • 1United Nations Declaration on the Rights of Indigenous Peoples (2007)
  • 2Convention on Biological Diversity, Article 8(j) and Nagoya Protocol
  • 3Kunming-Montreal Global Biodiversity Framework (2022), Targets 3, 5, 21
  • 4Agreement under the United Nations Convention on the Law of the Sea on the Conservation and Sustainable Use of Marine Biological Diversity of Areas Beyond National Jurisdiction (BBNJ Agreement, 2023)
  • 5TNFD Recommendations and Guidance on Engagement with Indigenous Peoples, Local Communities and Affected Stakeholders (2023)
  • 6SEEA Ecosystem Accounting, Chapter 6 (Ecosystem Services)
  • 7ILO Convention 169 on Indigenous and Tribal Peoples
  • 8Global Indigenous Data Alliance, CARE Principles for Indigenous Data Governance (2019)
  • 9United Nations Fundamental Principles of Official Statistics (2014)
  • 10SEEA Guidelines on Biophysical Modelling for Ecosystem Accounting, Section 5.7 (Reference Conditions)
  • 11Millennium Ecosystem Assessment (2005), Ecosystems and Human Well-being: Synthesis
  • 12IPBES (2019), Global Assessment Report on Biodiversity and Ecosystem Services
  • 13Common International Classification of Ecosystem Services (CICES) v5.1 (Haines-Young and Potschin, 2018)

14Authors: [To be confirmed] Reviewers: [To be confirmed] Last Updated: February 2026

Footnotes

  1. 1

    Huntington, H.P. et al. (2004). Matching traditional and scientific observations to detect environmental change: a discussion on Arctic terrestrial ecosystems. Ambio 33(7): 18-23.

  2. 2

    Tengoe, M. et al. (2017). Weaving knowledge systems in IPBES, CBD and beyond. Current Opinion in Environmental Sustainability 26-27: 17-25.

  3. 3

    Convention on Biological Diversity, Kunming-Montreal Global Biodiversity Framework (2022), Target 21.

  4. 4

    United Nations, Transforming our world: the 2030 Agenda for Sustainable Development, SDG Target 2.3.

  5. 5

    United Nations Fundamental Principles of Official Statistics (2014), Principle 8: Coordination among statistical agencies.

  6. 6

    See also UNSD and UNESCO Institute for Statistics discussions on integrating Indigenous knowledge into statistical frameworks, and the Pacific Community (SPC) regional guidance on cultural statistics.

  7. 7

    This characterization draws on Convention on Biological Diversity (2018), Glossary of Relevant Terms, definition of “Traditional knowledge.”

  8. 8

    Vierros, M. et al. (2010). Traditional Marine Management Areas of the Pacific in the Context of National and International Law and Policy. United Nations University — Institute of Advanced Studies.

  9. 9

    Huntington, H.P. et al. (2004). Matching traditional and scientific observations to detect environmental change: a discussion on Arctic terrestrial ecosystems. Ambio 33(7): 18-23. Whilst focused on terrestrial ecosystems, the methodological framework for integrating traditional and scientific observations applies equally to marine contexts.

  10. 10

    Johannes, R.E. (1998). The case for data-less marine resource management: examples from tropical nearshore finfisheries. Trends in Ecology and Evolution 13(6): 243-246.

  11. 11

    United Nations Declaration on the Rights of Indigenous Peoples (2007), Article 31.

  12. 12

    United Nations Declaration on the Rights of Indigenous Peoples (2007), Article 26.

  13. 13

    Convention on Biological Diversity (1992), Article 8(j).

  14. 14

    Nagoya Protocol on Access to Genetic Resources and the Fair and Equitable Sharing of Benefits Arising from their Utilization to the Convention on Biological Diversity (2010).

  15. 15

    Convention on Biological Diversity, Kunming-Montreal Global Biodiversity Framework (2022), Target 21.

  16. 16

    Convention on Biological Diversity, Kunming-Montreal Global Biodiversity Framework (2022), Target 3.

  17. 17

    Convention on Biological Diversity, Kunming-Montreal Global Biodiversity Framework (2022), Target 5.

  18. 18

    International Labour Organization, Indigenous and Tribal Peoples Convention, 1989 (No. 169), Article 6.

  19. 19

    Agreement under the United Nations Convention on the Law of the Sea on the Conservation and Sustainable Use of Marine Biological Diversity of Areas Beyond National Jurisdiction (2023), Articles 7 and 13.

  20. 20

    TNFD Recommendations (2023), Governance Disclosure C.

  21. 21

    TNFD Guidance on engagement of Indigenous Peoples, Local Communities and affected stakeholders.

  22. 22

    Johnson, N. et al. (2016). The contributions of community-based monitoring and traditional knowledge to Arctic observing networks. Arctic 69(Suppl. 1): 28-40.

  23. 23

    United Nations Declaration on the Rights of Indigenous Peoples (2007), Article 31.

  24. 24

    Nagoya Protocol (2010), Articles 5-7.

  25. 25

    TNFD Recommendations (2023), Governance Disclosure C.

  26. 26

    Jupiter, S.D. et al. (2014). Locally-managed marine areas: multiple objectives and diverse strategies. Pacific Conservation Biology 20(2): 165-179.

  27. 27

    Weiss, K. et al. (2012). Knowledge exchange and policy reform: linking marine science with management practice in Torres Strait. International Journal of Science in Society 3(2): 39-56.

  28. 28

    SEEA Ecosystem Accounting (2021), para. 6.51.

  29. 29

    Tengoe, M. et al. (2017). Weaving knowledge systems in IPBES, CBD and beyond. Current Opinion in Environmental Sustainability 26-27: 17-25.

  30. 30

    SEEA Guidelines on Biophysical Modelling for Ecosystem Accounting, paras. 183-184.

  31. 31

    Hill, R. et al. (2020). Working with Indigenous, local and scientific knowledge in assessments of nature and nature’s linkages with people. Current Opinion in Environmental Sustainability 43: 8-20.

  32. 32

    For related guidance on spatial representation in ocean accounts, see TG-0.3 Spatial and Temporal Frameworks.

  33. 33

    Global Indigenous Data Alliance, CARE Principles for Indigenous Data Governance (2019).

  34. 34

    Carroll, S.R. et al. (2020). The CARE Principles for Indigenous Data Governance. Data Science Journal 19(1): 43.

  35. 35

    Smith, L.T. (2021). Decolonizing Methodologies: Research and Indigenous Peoples (3rd ed.). Zed Books.

  36. 36

    TNFD Recommendations (2023), Governance C.

  37. 37

    Foale, S. (2006). The intersection of scientific and indigenous ecological knowledge in coastal Melanesia: implications for contemporary marine resource management. International Social Science Journal 58(187): 129-137.

  38. 38

    SEEA Ecosystem Accounting (2021), Chapter 1. See para. 1.33 on key features of ecosystem accounting that allow it to support and extend other measurement frameworks.

  39. 39

    SEEA Ecosystem Accounting (2021), Table 6.3.

  40. 40

    SEEA Ecosystem Accounting (2021), para. 6.97.

  41. 41

    Millennium Ecosystem Assessment (2005), Ecosystems and Human Well-being: Synthesis, definition of cultural services.

  42. 42

    IPBES (2019), Global Assessment Report on Biodiversity and Ecosystem Services, framing of nature’s contributions to people, including non-material contributions (NCP 15—17). 2

  43. 43

    Haines-Young, R. and Potschin, M.B. (2018), Common International Classification of Ecosystem Services (CICES) V5.1, Section 4 (Cultural services). 2

  44. 44

    SEEA Ecosystem Accounting (2021), Chapter 6, paras. 6.51 and 6.95—6.100. 2 3

  45. 45

    SEEA Ecosystem Accounting (2021), para. 6.97. 2

  46. 46

    TNFD Recommendations (2023), Annex 2 Glossary, definition of “Local Communities.”

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