The indicators that best reflect major trends related to the transition towards a CE are to be carefully selected. The number of potentially useful indicators can be large. It is therefore necessary to agree upon criteria that guide and validate their choice and keep the selection at a manageable level. Building on earlier OECD work on environmental and green growth indicators the key principles in selecting indicators include: policy relevance and utility for users, analytical soundness, measurability (Box 4.1). These criteria are in line with the indicator selection criteria recommended under the Bellagio principles (EEA, 2021[13]): Relevant, Accepted, Credible, Easy to monitor, and Robust (RACER).
Monitoring Progress towards a Resource-Efficient and Circular Economy
4. The indicator set
Copy link to 4. The indicator set4.1. Identifying relevant indicators
Copy link to 4.1. Identifying relevant indicatorsBox 4.1. Key principles in selecting indicators to monitor progress towards a circular economy
Copy link to Box 4.1. Key principles in selecting indicators to monitor progress towards a circular economy
Policy relevance and utility for users |
The indicator set should have a clear policy relevance, and in particular:
|
Analytical soundness |
The indicators should be analytically sound and benefit from a consensus about their validity. They should further lend themselves to being linked to economic and environmental modelling and forecasting. |
Measurability |
The indicators should be based on data that are available or that can be made available at a reasonable cost, and that are of known quality and regularly updated. |
Note: These principles and criteria describe the “ideal” indicator; not all of them will be met in practice. They are in line with the criteria recommended under the Bellagio principles (EEA, 2021[13]).
Source: Adapted from (OECD, 2011[14]) and from (OECD, 1993[15]).
As the CE is a cross-cutting multi-dimensional concept based on systemic approaches, it is important that the indicators selected under the different building blocks and themes:
are aligned and can be interconnected to inform the assessment of policy outcomes and progress made. Indicators listed under “material life-cycle” could have a counterpart under “responses and actions”, as well as under “socio-economic opportunities”. This would help linking responses to results obtained as a first step in monitoring the effectiveness of policies.
fit into an overall narrative framework while supporting more granular analysis.
As information on a CE is not yet available for all dimensions and aspects to be considered, the proposed indicator set encompasses both operational and aspirational indicators.
Operational indicators are indicators that are available or could be made available at a reasonable cost in the short to medium term, and that build on recognised definitions and methodologies.
Aspirational indicators are new or improved indicators that while relevant and desirable to fill gaps require important statistical and methodological efforts to become operational. Such indicators could become part of an internationally coordinated research agenda (see Chapter 5 and 6).
4.2. A 3-tier structure of indicator types
Copy link to 4.2. A 3-tier structure of indicator typesAs for other OECD environmental indicators, a 3-tier structure of core, complementary and contextual indicators is used, based on their relevance, measurability, and usefulness to track key features of a CE transition.
Core indicators (or their proxy when the core indicator is currently not measurable) are indicators that capture key elements of a CE, respond to main CE policy questions and point at developments or changes that require further analysis and possible action. Core indicators are designed to provide the big picture of the transition to a CE. They represent a common minimum set of indicators for use in OECD and other international work and that countries would be encouraged to produce or adapt to their own circumstances. The number of core indicators (or their proxy) should be limited so as to facilitate the monitoring and communication of major trends; it should not exceed 20-25.
Both operational and aspirational core indicators are proposed. Operational core indicators are indicators that are highly relevant from a CE point of view, already measurable in a representative number of OECD countries or that OECD countries would be willing and able to report to in the short term or the medium term (e.g., within the next few years). Operational indicators mainly cover basic waste management, material flow and resource efficiency aspects. Aspirational core indicators are indicators that are highly relevant from a CE point of view, but not yet measurable, and that require further methodological and statistical developments. Most indicators needed to reflect the circularity of materials flows are aspirational, as are many response and opportunity indicators. They are included as an incentive for countries to develop underlying methodologies and/or to produce the required data. They are also proposed to become part of a research roadmap to be internationally coordinated.
In the future, a shortlist of core indicators could be identified as headline indicators to inform high-level decision-makers and civil society and enable wider communication with the public.
Complementary indicators: Indicators that accompany or complement the message conveyed by “core” indicators, by providing additional detail (sub-national detail, sectoral detail) or focus (particular materials or activities), or by covering additional aspects. For country application of the framework, other country-specific indicators can be added. For application in international work, complementary indicators that describe country-specific features are useful for country projects and peer reviews. Complementary indicators also include new and innovative indicators that are yet to be defined and developed, and that could become core indicators in future.
Contextual indicators: indicators that provide background information on socio-economic and environmental variables to facilitate interpretation in the appropriate country context and to inform about drivers of material use. They include general indicators on the characteristics of economic growth (GDP, income), changes in countries’ industrial structure, demographic structure and final consumption expenditure, as well as general inequality indicators. They also include general indicators on the factors that influence the environmental implications of material use such as energy and water use or the extent of protected areas.
The indicators are accompanied with references to additional information needed to guide interpretation, and with cross-references to other indicators and indicator sets.
4.3. Proposed indicator set
Copy link to 4.3. Proposed indicator setThe list of proposed indicators draws on indicators available from the OECD’s own work and work by other international organisations, including:
The OECD Core Set of Environmental Indicators, OECD sectoral sets of environmental indicators, the set of Green Growth indicators, and OECD indicators to monitor material flows and resource productivity [ENV/EPOC/WPEI(2011)4/REV].
The revised EU monitoring framework for the circular economy (European Commission, 2023[16]).
The list of indicators shortlisted by the UNECE Task Force on Measuring Circular Economy.
The list also considers indicators listed in national work, the OECD Inventory of Circular Economy Indicators (OECD, 2020[17]), the work by PACE on Circular Indicators for Governments (PACE, 2021[18]), and work by ISO 59004 WD2 on Circularity Measurement Taxonomy (ISO, 2024[19]). Coherence with the global list of SDG indicators and with the Bellagio principles (EEA, 2021[13]) is ensured. See Annex B for examples of national indicator sets considered.
It should be noted that the indicator set mainly focuses on the national and macro level but can easily be applied or adapted to other levels (sub-national, sectors, industries or firms, products). Furthermore, not all elements of a CE lend themselves to being measured by quantitative indicators and for several aspects current data availability is low. Also, there is no one-to-one correspondence between the CE dimensions and the indicators identified: a specific indicator can be relevant for more than one CE dimension; and an indicator listed under one theme can reflect a driver or a pressure for another theme.
Table 4.1 gives an overview of the proposed core indicators, structured in line with the conceptual framework. The list should not be considered as final. It may be reviewed and refined as data availability and quality progress and feedback from the use of the indicators is received.
Table 4.2 presents the complete list of the proposed indicator set together with an initial assessment of their relevance and measurability. Annex A provides further details to this list, including references to other sets in which the proposed indicators feature, and comments on their definitions, interpretation and measurability. This list and its initial assessment will be refined as work on the calculation methods and underlying data sources progresses. New data sources need to be identified for highly relevant indicators that are not yet measurable. Indicators that should be given priority for further research and development need to be identified (see Chapters 5 and 6).
Countries interested in applying the proposed indicator set may adapt it to their own circumstances and policy needs with a phased implementation that takes into account their capacity to engage in the production of CE data and indicators and to ensure proper interpretation (Section 5.2).
4.4. Communicating the indicators
Copy link to 4.4. Communicating the indicatorsThe indicators can be presented and communicated in various ways. The most appropriate way depends on the target audience and on the context in which the indicators are to be used. The joint presentation of a suite of indicators reflecting various dimensions of a CE is most useful. Individual indicators can provide information about specific aspects relevant to the CE transition, but it is the indicator set that ensures a comprehensive and coherent monitoring.
As for other indicators, it is important to note that while CE indicators simplify the communication process, their relevance can vary by country, by audience, and by context. Supplementary information and analyses, and policy-oriented interpretation are required for them to acquire their full meaning. The dissemination and communication of the indicators can thus be greatly enhanced by preparing regular synthesis reports or factsheets that would leverage the analyses carried out and by providing links to more detailed statistics and additional information to ensure appropriate context on what is behind the values of the more aggregated indicators. Other tools that could usefully complement the indicators include scenario modelling that could help guide decision-makers towards optimal outcomes, life-cycle assessments (LCA) and environmentally extended input-output analysis that could enrich the messages conveyed by macro-level indicators.
An interesting avenue is to link and combine different indicators to balance the message conveyed, reflect the multi-dimensional features of a CE and facilitate interpretation. As a rule, indicators on responses and actions should lend themselves to being related to indicators on the material life cycle and to indicators on opportunities to help linking responses to results obtained as a first step in monitoring the effectiveness of policies. Indicators on the material life cycle should lend themselves to being linked to reference values (benchmarks, thresholds, baselines, objectives, targets) and to environmental issues such as climate change, toxic contamination, biodiversity, natural resource management.
Where data are available, indicators on the material life cycle broken down by industry can be presented as part of sector profiles together with data from the SNA and the sequence of SEEA accounts, such as economic activity data (e.g. industry output, value added, operating surplus, employment), information on economic instruments (e.g. taxes, subsidies) and data on environmental pressures (e.g. GHG emissions, use of water resources).
Table 4.1. Overview of framework themes and proposed core indicators
Copy link to Table 4.1. Overview of framework themes and proposed core indicators
Framework |
Themes |
Proposed core indicators (a) |
|
---|---|---|---|
Material life-cycle and value chain |
The material basis of the economy |
1 |
Material consumption & productivity (DMC, RMC): trends and mix |
The circularity of material flows and the management efficiency of materials & waste |
2 |
Total waste generation: trends, intensity per GDP and per capita |
|
3 |
Circular material use rate |
||
4 |
National recycling rate |
||
5 |
Waste going to final disposal |
||
Interactions with trade |
none |
||
Interactions with the environment (b) |
Natural resource implications |
6 |
Natural resource index: energy & mineral resources |
7 |
Intensity of use of renewable freshwater resources |
||
Environmental quality implications |
8 |
GHG emissions from production activities |
|
9 |
Pollutant discharges from production activities to water bodies and proportion safely treated |
||
10 |
Placeholder: Impacts on human health |
||
Responses and actions |
Support circular use of materials, promote recycling markets and optimise design |
11 |
Taxes and government support for circular business models |
Improve the efficiency of waste management and close leakage pathways |
12 |
Investment in waste management infrastructure, waste collection and sorting (government, businesses) |
|
Boost innovation and orient technological change for more circular material lifecycles |
13 |
R&D expenditure on CE technologies (government, businesses) |
|
Target setting and planning |
none |
||
Strengthen financial flows for a circular economy and reduced leakage |
14 |
Business investment in CE activities |
|
Inform, educate, train |
15 |
Placeholder: Education and training |
|
Socio-economic opportunities for a just transition |
Market developments and new business models |
16 |
Gross value added of CE sectors |
17 |
Jobs in CE sectors |
||
Trade developments |
none |
||
Skills, awareness, behaviour |
18 |
Placeholder: Behaviour |
|
Inclusiveness of the transition |
19 |
Placeholder: Distributional aspects & socio-economic inequality of CE policies |
Notes:
(a) The proposed core indicators include both operational core indicators that are measurable for most OECD countries, and aspirational core indicators that require further work and that countries are encouraged to produce. Placeholders refer to indicators that are yet to be identified and defined. Other indicators that could become core indicators in future can be found in Table 4.2.
(b) Can easily be complemented with other core environmental indicators to give a balanced picture of interactions with the environment. See the OECD Core Set of Environmental Indicators and environmental indicators used to monitor the SDGs.
Table 4.2. Framework themes and proposed indicators
Copy link to Table 4.2. Framework themes and proposed indicatorsAnnex A provides further details to this list, including references to other sets in which the proposed indicators feature, and comments on their definitions, interpretation and measurability.
Framework themes and indicator topics |
Proposed indicators (a) |
Type (b) |
Rel. (c) |
Meas. (d) |
|||
---|---|---|---|---|---|---|---|
Material life-cycle and value chain |
|||||||
1. The material basis of the economy - Production, consumption, accumulation |
|||||||
1.1 Material inputs |
|
Comp |
H |
H/M |
|||
|
Comp |
H |
H |
||||
1.2 Material consumption |
Material consumption and productivity (DMC, RMC): trends and mix |
Core |
H |
H/M |
|||
|
Comp |
H |
H |
||||
|
Comp |
M |
L |
||||
1.3 Material accumulation |
|
Comp |
H |
M |
|||
|
Comp |
M |
L |
||||
2. The circularity of material flows and the management efficiency of materials and waste |
|||||||
2.1 Waste generation (materials ending up as waste) |
Total waste generation: trends and intensity per GDP, per capita ‒ Municipal waste generation |
Core |
H M |
M H/M |
|||
|
Comp |
H |
M |
||||
|
Comp |
H |
M/L |
||||
|
Comp |
M |
M |
||||
|
Comp |
H |
L |
||||
|
Comp |
M |
M |
||||
2.2 Circularity of material flows |
Circular material use rate |
Core |
H |
H/M |
|||
|
Comp |
H |
L |
||||
|
Comp |
H |
L |
||||
2.3 Products diverted from the waste stream |
|
Comp |
H |
M/L |
|||
|
Comp |
H |
|||||
2.4 Materials diverted from final disposal through recycling or recovery |
National recycling rate ‒ Municipal waste recycling rate |
Core |
H |
M |
|||
|
Comp |
H |
M |
||||
|
Comp |
M |
H |
||||
|
Comp |
M |
M |
||||
2.5 Materials leaving the economic cycle |
Waste going to final disposal |
Core |
H |
H/L |
|||
3. Interactions with trade (see also “opportunities” below) |
|||||||
3.1 Trade in materials |
|
Comp |
M |
H |
|||
|
Comp |
M |
H |
||||
3.2 Trade in CE related materials and products |
|
Comp |
M |
M |
|||
Interactions with the environment (to be supplemented with other environmental indicators as appropriate) |
|||||||
1. Natural resource implications |
|||||||
1.1 Changes in natural resource stocks |
Natural resource index: energy & mineral resources / Depletion ratios |
Core |
M |
M/L |
|||
|
Comp |
M |
H |
||||
|
Ctx |
M |
M |
||||
Intensity of use of renewable freshwater resources (water stress) |
Core |
H |
M |
||||
|
Comp |
H |
M |
||||
1.2 Other natural resource impacts |
|
Comp |
M |
M |
|||
|
Comp |
M |
M |
||||
|
Comp |
M |
L |
||||
2. Environmental quality implications |
|||||||
2.1 Impacts on climate |
GHG emissions from production activities ‒ Total GHG emissions |
Core |
H |
M H |
|||
|
Comp |
M |
M |
||||
|
Comp |
H |
M |
||||
|
Comp |
M |
L |
||||
2.2 Impacts on air quality |
|
Comp |
M |
M |
|||
2.3 Impacts on water and soil quality |
Pollutant discharges from production activities to water bodies & proportion safely treated ‒ Total discharges to water bodies & proportion safely treated |
Core |
H |
M |
|||
|
Comp |
M |
M |
||||
Placeholder: Soil contamination |
Comp |
M |
|||||
2.4 Impacts on biodiversity |
Placeholders: Impacts on land, habitats and species |
Comp |
H |
||||
2.5 Impacts on human health |
Placeholder |
Core |
H |
||||
Population exposure to air pollution; related premature deaths and welfare costs |
Comp |
M |
M |
||||
Placeholder: Water-related health impacts |
Comp |
M |
|||||
Placeholder: Population living in the vicinity of waste management sites and production sites |
Comp |
M |
|||||
Responses and actions |
|||||||
1. Support circular use of materials, promote recycling markets and optimise design |
|||||||
1.1 Measures supporting circular business models and encouraging reuse, repair, remanufacturing |
Taxes and government support for circular business models ‒ VAT relief and tax credits for refurbished/repaired items; Tax benefits for businesses for the purchase/use of repaired, refurbished, remanufactured items ‒ Trade tariffs: Import/export taxes for re-used & refurbished equipment compared to taxes on new equipment ‒ Subsidies and other transfers supporting a CE |
Core |
H |
M |
|||
|
Comp |
H |
L |
||||
|
Comp |
H |
L |
||||
|
Ctx |
H |
L |
||||
1.2 Measures encouraging eco-design |
|
Comp |
H |
M |
|||
|
Comp |
H |
M |
||||
1.3 Measures encouraging efficient use of materials and economically efficient waste recovery |
|
Comp |
H |
M |
|||
|
Comp |
M |
M |
||||
|
Comp |
M |
H/M |
||||
2. Improve the efficiency of waste management and close leakage pathways |
|||||||
2.1 Measures to improve waste management |
Investments in waste management infrastructure, waste collection and sorting |
Core |
H |
M |
|||
|
Ctx |
M |
H |
||||
2.2. Measures to encourage waste reduction |
|
Comp |
H |
H |
|||
|
Comp |
H |
H |
||||
|
Comp |
H |
H |
||||
3. Boost innovation and orient technological change |
|||||||
3.1 Measures supporting R&D |
R&D expenditure on CE technologies |
Core |
H |
M/L |
|||
3.2 Technology development and international diffusion |
|
Comp |
M |
M/L |
|||
4. Target setting and planning |
|||||||
4.1 Targets & distance to targets |
Placeholder: Distance to targets (resource productivity; recycling; waste reduction & prevention; recycled content; reuse; landfill) |
Comp |
H/M |
||||
4.2 CE strategies & plans |
Placeholder |
Comp |
M |
||||
5. Strengthen financial flows |
|||||||
5.1 Domestic financial flows |
Business investment in CE activities |
Core |
H |
M |
|||
|
Comp |
H |
H/M |
||||
|
Comp |
H |
M |
||||
5.2 International financial flows |
|
Comp |
M |
L |
|||
|
Comp |
M |
L |
||||
6. Inform, educate and train |
|||||||
6.1 Information instruments |
Placeholders: Eco-labelling; product labelling & certificates; requirement to provide repair guidelines: (i) information on expected lifespan, (ii) dismantling guidelines & material content lists |
Comp |
M |
||||
6.2 Education and training |
Placeholder: Integration of CE issues in school curricula and professional training |
Core |
H |
||||
Socio-economic opportunities for a just transition |
|||||||
1. Market developments and new business models |
|||||||
1.1 CE entrepreneurship, goods & services |
Gross value added of CE sectors |
Core |
H |
H/L |
|||
CE start-ups and trademarks; CE certification of companies |
Comp |
M |
L |
||||
1.2 Employment markets & jobs |
Jobs in CE sectors |
Core |
H |
H/L |
|||
Jobs in sharing economy, reuse and repair activities |
Comp |
H |
L |
||||
1.3 Recycling markets |
Markets for recycled materials |
Comp |
H |
L |
|||
2. Trade developments |
|||||||
2.1 Trade in CE related goods and services |
|
Comp |
M |
M/L |
|||
|
Comp |
M |
L |
||||
2.2 Supply security |
|
Comp |
H |
H |
|||
|
Comp |
H |
M |
||||
|
Comp |
H |
M |
||||
3. Skills, awareness and behaviour |
|||||||
3.1 Skills |
Placeholders: CE literacy ; CE skills |
Comp |
H |
||||
3.2 Awareness |
|
Comp |
M |
L |
|||
3.3 Behaviour |
Placeholder: Change in household, consumer, firm behaviour |
Core |
H |
||||
4. Inclusiveness of the transition |
|||||||
Placeholder: Distributional aspects & socio-economic inequality of CE policies |
Core |
M |
|||||
Socio-economic and environmental context |
|||||||
1. Factors that drive demand for materials |
|||||||
1.1 Socio-demographic factors |
|
Ctx |
M |
H |
|||
1.2 Economic factors |
|
Ctx |
M |
H |
|||
|
Ctx |
M |
H |
||||
|
Ctx |
M |
H/M |
||||
|
Ctx |
M |
H |
||||
|
Ctx |
M |
H |
||||
1.3 Sectoral drivers |
|
Ctx |
H |
M/L |
|||
|
|||||||
2. Factors that influence the environmental implications of material use |
|||||||
2.1 Environmental drivers |
|
Ctx |
H |
H |
|||
|
Ctx |
H |
M |
||||
|
Ctx |
M |
H/M |
||||
|
Notes: (a) All indicators are expected to reflect change over time. For a more detailed list of indicators with references to international indicators’ sets and comments on the indicators’ measurability and interpretation, see Annex A.
(b) Indicator types: A 3-tier structure, based on the indicators’ relevance, measurability and usefulness to track aspects of a circular economy transition: Core indicator (Core) (red colour) or their proxies (-); Complementary indicator (Comp); Contextual indicator (Ctx). Placeholders refer to indicators that are yet to be identified and defined.
(c) Relevance indicates the level of relevance/usefulness of the proposed indicator for the given topic: High (H); Medium (M); Low, to be reviewed (L).
(d) Measurability indicates the current availability of data and agreed methodologies.
High (H) = measurable in the short term; Medium (M) = measurable in the medium term; Low (L) = measurable in the longer term.