Downscaling Planetary Boundaries: How Does the Framework’s Localization Hinder the Concept’s Operationalization?
Abstract
1. Introduction
1.1. Context
1.2. Research Gaps and Relevance of This Study
1.3. Theoretical Framework, Objectives, and Research Hypotheses
1.4. Article Structure
1.5. Main Theoretical Contributions and Societal Implications
2. Materials
2.1. Initial Corpus Selection Methodology
- Using a structured request with the following terms: “planetary boundaries”; “planetary boundary”; “safe and just space”; “safe operating space”; and “safe and just operating space.” In doing so, the Doughnut Economics framework (the concept of “safe and just operating space”) was included in this search because it is rooted in the Planetary Boundaries framework and has been very successful among local authorities.
- For Google Scholar, adding restrictions (“-layer-protein-chemistry”) was conducted to remove articles that were not relevant to this analysis and to limit the number of articles to be filtered. The term “layer” associated with “planetary boundaries” refers to computer modeling unrelated to the concept we are studying. The terms “protein” and “chemistry” refer to applications of the concept of “planetary boundaries” linked to a specific sector of activity. This does not correspond to the present research, which studies the territorial application of Planetary Boundaries.
2.2. Corpus Refinement
- Filter A: Alignment with the research field
- Filter B: Substantial consideration of the PBc
- Filter C: Quality and impact of journals
- Shao (2020), «Paving Ways for a Sustainable Future: A Literature Review» (Environmental Science and Pollution Research) [12];
- Hossain and Ifejika Speranza (2019), «Challenges and Opportunities for Operationalizing the Safe and Just Operating Space Concept at Regional Scale» (International Journal of Sustainable Development & World Ecology) [13].
- Filter D: Relevance for localization and local operationalization of the PBc
2.3. Final Selection
3. Characteristics of the Selected Corpus
3.1. Interdisciplinarity
3.2. Geographical Distribution
3.3. A Critical Perspective on Planetary Boundaries
- In total, 29% of the corpus deals with the following: footprints; life cycle assessment, and absolute environmental sustainability assessment (AESA).
- In total, 26%: Sustainable development goals and the concept of sustainability.
- In total, 24%: Doughnut economics.
- In total, 12%: Systems analysis (SES, socio-technical systems) and systemic modeling; putting the PBc into perspective with environmental policies, types of governance, and participatory approaches.
4. Method for Identifying Issues Related to the Downscaling of Planetary Boundaries Concept
4.1. Phase 1: Data Collection
4.2. Phase 2: Localization or Local Operationalization
4.3. Phase 3: Categorization
4.4. Phase 4: Presentation
4.5. Examples
- “This demonstrates that a scale for localized planetary boundaries needs to be chosen that makes absolute sustainability assessment meaningful and comparable.” (Wiedmann and Allen, 2021) [10]. This extract addresses a choice related to localization (“localized planetary boundaries”) and concerns the theme of scale.
- “For this reason, measuring urban environmental boundaries should take into account the threshold behaviors as well as social priorities within various forms of cities.” (Chen et al., 2021) [16]. In this extract, we identify a suggestion for improving operationalization: “take into account threshold behaviors as well as social priorities.” This fits into a theme related to better consideration of local stakeholders and the social context.
5. Results
5.1. The Questions About Localization
5.2. Gaps in the Local Operationalization of Planetary Boundaries
6. Analysis of Results and Theoretical Contributions
6.1. A Prevalent Approach to Localizing Planetary Boundaries Concept
- Sharing: Distributing numerical objects using local statistical data (quantification).
- Contextualization: Redefinition of the object in relation to the context.
- Spatialization: Cartographic representation of the object (quantification).
- No Transformation: The localized object is identical to the global object.
6.2. Categories of Constraints in the Local Operationalization of the Planetary Boundaries Concept
6.2.1. Full Consideration of the Local Context
6.2.2. Development of Social Components Specific to the PBc
6.2.3. Uptake of the Concept and Localization Method
6.3. The Operational Paradox of the Prevalent Approach to the Localization of the PBc
- Hossain and Ifejika Speranza (2019) [13], drawing on Häyhä et al. (2016) [42], highlight that “Though the initial delineation of SOS and SJOS was derived by the scientific community, designing SJOS for SES is often an ethical and political choice, as making the SJOS operational entails the engagement of relevant actors who operate at national and regional scales.” This example demonstrates that operationalizing the PB is fundamentally an ethical and political choice requiring local and regional stakeholder commitment. Top-down quantitative approaches minimize their roles in the design process, creating buy-in deficits that hinder local operationalization. In other words, this case study highlights how the technical sophistication of quantification, far from facilitating operationalization, can paradoxically hinder it by excluding those who should implement it on the ground.
- Turner and Wills (2022) [7] report from Cornwall: “Our involvement in this process of applying the doughnut framework in Cornwall has illuminated the challenges identified in the literature (…) Representing, understanding and responding to complex systems: identifying goals and monitoring progress is hampered by a lack of suitable data, targets and indicators at a county scale, as well as conflicting views among Leadership Board partners around which indicators are most appropriate. Many national datasets are unavailable locally, and for some domains, no appropriate available indicators could be identified. Available indicators predominantly assess relative progress rather than change in relation to goals or limits, for which locally appropriate values are difficult to determine.” The Cornwall experience provides a concrete example of the mismatch between the technical ambitions of the Planetary Boundaries framework and local operational realities. The lack of appropriate data, the absence of relevant indicators at the territorial scale, and disagreements among partners on the choice of metrics reveal that the focus on quantification creates practical obstacles. The pursuit of technical precision (locally appropriate boundary values) becomes counterproductive in the face of complex local systems; thus, an approach based solely on quantified indicators can hinder its own operationalization.
- Hossain and Ifejika Speranza (2019) [13] illustrate how universal indicators can have contradictory meanings across territorial contexts by demonstrating how shrimp farming simultaneously represents environmental degradation in mangrove regions and essential livelihood provision in highly saline areas. This duality reveals the impossibility of applying universal indicators without considering the territorial and social context. The example demonstrates that a purely biophysical approach, by ignoring the specific social dimensions of territories, can generate contradictions that make operationalization not only difficult but conceptually impossible in some contexts.
7. Discussion
7.1. Testing the Hypotheses
7.2. Changing Methods or Perspectives: Three Proposals
7.3. Study Limitations
8. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
Abbreviations
PBc | Planetary Boundaries concept |
PBf | Planetary Boundaries framework |
OIs | Operationalization issues |
LIs | Localization issues |
References
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Number of Review Articles | Google Scholar | Science Direct | Previous Research | Total |
---|---|---|---|---|
Initial results | 1980 | 77 | 17 | 2074 |
→ Filter A: Alignment with the territorial application of PB | 54 | 61 | 17 | 132 |
→ Filter B: Substantial commitment to PB | 42 | 18 | 16 | 76 |
→ Filter C: Peer-reviewed journals, Q1 | 36 | 18 | 13 | 67 |
→ Filter D: Relevance for localization and operationalization | 31 | 12 | 13 | 56 |
→ Final corpus, number of review articles selected: | 34 |
Ref. | Title | 1st Author | Year |
---|---|---|---|
[11] | The Boundaries of the Planetary Boundary Framework: A Critical Appraisal of Approaches to Define a “Safe Operating Space” for Humanity | Biermann F. | 2020 |
[14] | Review of life-cycle based methods for absolute environmental sustainability assessment and their applications | Bjørn A. | 2020 |
[15] | Global environmental change II: Planetary boundaries–A safe operating space for human geographers? | Brown K. | 2016 |
[16] | Revisiting the application and methodological extensions of the planetary boundaries for sustainability assessment | Chen X. | 2021 |
[17] | Dwelling in the biosphere: exploring an embodied human–environment connection in resilience thinking | Cooke B. | 2016 |
[18] | Significance of environmental footprints for evaluating sustainability and security of development | Čuček L. | 2015 |
[19] | A development of intergenerational sustainability indicators and thresholds for mobility system provisioning: A socio-ecological framework in the context of strong sustainability | Dillman K.J. | 2023 |
[20] | Matching scope, purpose and uses of planetary boundaries science | Downing A.S. | 2019 |
[21] | The double negative approach to sustainability | Feitelson E. | 2023 |
[8] | Planetary Boundaries and the Doughnut frameworks: A review of their local operability | Ferretto A. | 2022 |
[22] | Defining the “Positive Impact” of socio-technical systems for absolute sustainability: a literature review based on the identification of system design principles and management functions | Gebler M. | 2022 |
[23] | Benchmarking urban performance against absolute measures of sustainability—A review | Goodwin K. | 2021 |
[24] | Earth system justice needed to identify and live within Earth system boundaries | Gupta J. | 2023 |
[25] | Review of Quantitative Applications of the Concept of the Water Planetary Boundary at Different Spatial Scales | Han S. | 2023 |
[13] | Challenges and opportunities for operationalizing the safe and just operating space concept at regional scale | Hossain M.S. | 2019 |
[26] | The uptake of the biosphere integrity planetary boundary concept into national and international environmental policy | Hurley I. | 2020 |
[27] | For an accounting translation of the Anthropocene: fuelling the debate on planetary boundaries | Jabot R. | 2023 |
[28] | Potentials and limitations of footprints for gauging environmental sustainability | Laurent A. | 2017 |
[9] | The role of planetary boundaries in assessing absolute environmental sustainability across scales | Li M. | 2021 |
[29] | A review of collaborative planning approaches for transformative change towards a sustainable future | Linnenluecke M.K. | 2016 |
[30] | Assessing and enhancing environmental sustainability—a conceptual review | Little J.C. | 2016 |
[31] | What is a footprint? A conceptual analysis of environmental footprint indicators | Matuštík J. | 2021 |
[32] | A safe and just operating space for human identity: a systems perspective | Oliver T.H. | 2022 |
[6] | Downscaling the planetary boundaries in absolute environmental sustainability assessments—A review | Ryberg M.W. | 2020 |
[12] | Paving ways for a sustainable future: a literature review | Shao Q. | 2020 |
[33] | How to conceptualize and operationalize resilience in socio-ecological systems? | Sterk M. | 2017 |
[34] | Policy design for the Anthropocene | Sterner T. | 2019 |
[7] | Downscaling doughnut economics for sustainability governance | Turner R.A. | 2022 |
[35] | Horses for courses: analytical tools to explore planetary boundaries | Van Vuuren D.P. | 2016 |
[36] | Environmental footprint family to address local to planetary sustainability and deliver on the SDGs | Vanham D. | 2019 |
[37] | Framework to define environmental sustainability boundaries and a review of current approaches | Vea E.B. | 2020 |
[10] | City footprints and SDGs provide untapped potential for assessing city sustainability | Wiedmann T. | 2021 |
[38] | A planetary boundary-based environmental footprint family: From impacts to boundaries | Wu L. | 2021 |
[39] | The Progress and Prospects in the Scenario Simulation Research on the Sustainability of Regional Ecosystem Services Based on a “Safe Operating Space” | Zhang X. | 2023 |
IL n° | Key Issues in the Localization of the Planetary Boundaries Concept
| Review Articles | ||
---|---|---|---|---|
List | Total | % | ||
1 | What is the right scale?
| [6,7,8,10,11,13,14,15,16,17,20,21,25,26,30,33,34,35,36,38,39] | 21 | 62 |
2 | What are the characteristics of this method? | [7,8,9,10,11,14,15,16,19,20,21,22,23,25,27,31,32,33,34,37,39] | 21 | 62 |
2.a |
| [7,8,9,10,11,14,16,20,21,22,25,31,32,33,37,39] | 16 | 47 |
2.b |
| [7,8,9,10,15,19,20,21,23,27,34] | 11 | 32 |
3 | How to determine local boundary values?
| [6,7,8,9,10,11,13,14,15,16,20,21,23,27,28,31,36,38] | 18 | 53 |
4 | How can consistency be maintained between the global concept, its local representations, and the local context?
| [7,8,11,13,15,16,20,21,25,27,30,33,34,35,38] | 15 | 44 |
5 | Which indicators?
| [7,8,10,13,14,16,18,19,21,23,25,27,36,38] | 14 | 41 |
6 | What type of area should be assessed?
| [8,11,13,14,15,20,21,26,33,34,35,36,39] | 13 | 38 |
7 | Should a standardized method be developed? | [6,8,9,10,13,14,20,28,34,37] | 10 | 29 |
8 | What are the qualities of data to prioritize?
| [7,10,13,14,16,19,25] | 7 | 21 |
9 | Should new biophysical processes or environmental issues be added?
| [7,9,11,21] | 4 | 12 |
10 | How can time be integrated into the method? | [13,25,35] | 3 | 9 |
OI n° | Issues in the Local Operationalization (OI) of the Planetary Boundaries Concept | Review Articles | ||
---|---|---|---|---|
List | Total | % | ||
1 | Local stakeholders (decision-makers, method users, citizens, residents) are not sufficiently considered and mobilized. | [6,7,8,9,11,12,13,14,15,16,17,19,20,21,24,27,29,32,34,39] | 20 | 59 |
2 | Limited understanding of local socio-environmental dynamics. | [7,9,13,15,16,17,20,21,25,29,33,34,37] | 13 | 38 |
3 | Low legitimacy of the concept on a local scale: absence from legal texts; limited political support; lack of relevance on a local scale due to its global nature. | [7,10,11,13,15,19,20,24,34] | 9 | 26 |
4 | There is little consideration of the need to rethink governance within and between organizations and to implement appropriate policies. | [7,11,13,19,20,29,34] | 7 | 21 |
5 | No clearly defined aims for the context. | [7,19,20,29,34] | 5 | 15 |
6 | Underestimation of the resources required (financial, human, intellectual). | [7,10,19,34] | 4 | 12 |
7 | No consideration of how to maintain the approach over time. | [7,9,21] | 3 | 9 |
8 | Lack of transparency regarding the characteristics and uncertainties of the method. | [14,27] | 2 | 6 |
Key Issues in the Localization of Planetary Boundaries
| % | Constituents of the Localization Process | |
---|---|---|---|
Localized Object | Transformation Used to Locate the Object | ||
What is the right scale?
| 62 | The questions of scale and geographical scope seem to point towards spatialization. | |
What are the characteristics of this method? | 62 | ||
| 47 | The boundary value of indicators. | Transformation is closely linked to the direction of the method: top-down implies sharing; bottom-up favors contextualization. |
| 32 | These questions seem to focus on a numerical object (statistical data). | The standardization of a method is often based on statistical data and therefore favors transformation through quantification. |
How to determine local boundary values?
| 53 | All the questions show the importance attached to the components of the biophysical framework of the Planetary Boundaries, and, in particular, the boundary values. | Sharing. |
How can consistency be maintained between the global concept, its local representations, and the local context?
| 44 | Planetary Boundaries framework; process boundary values | This question refers to the direction of the method: top-down implies sharing; bottom-up favors contextualization. |
Which indicators?
| 41 | Indicators | Should we give priority to the original indicator, with no transformation, or redefine it to take account of specific local environmental factors (contextualize the indicator)? |
What type of area should be assessed?
| 38 | Spatialization | |
Should a standardized method be developed? | 29 | Standardization often requires numerical objects that involve local quantification. | |
What are the qualities of data to prioritize?
| 21 | The importance of issues related to the characteristics of numerical data confirms the importance of quantification. | |
Should new biophysical processes or environmental issues be added?
| 12 | Processes | Should priority be given to global biophysical processes (no transformation), or should they be redefined to take into account local environmental specificities (contextualization), or should additional processes be added (contextualization)? |
How can time be integrated into the method? | 9 |
Issues in the Local Operationalization (OI) of the Planetary Boundaries Concept (PBc) | % | Categories of Constraints | ||
---|---|---|---|---|
Consideration of the Local Context | Social Components of the PBc | Uptake by Local Stakeholders | ||
Local stakeholders (decision-makers, method users, citizens, residents) are not sufficiently considered and mobilized. | 59 | OI.1 | ||
Limited understanding of local socio-environmental dynamics. | 38 | OI.2 | ||
Low legitimacy of the concept on a local scale: absence from legal texts; limited political support; lack of relevance on a local scale due to its global nature. | 26 | OI.3 | OI.3 | OI.3 |
There is little consideration of the need to rethink governance within and between organizations and to implement appropriate policies. | 21 | OI.4 | ||
No clearly defined aims for the context. | 15 | OI.5 | ||
Underestimation of the resources required (financial, human, intellectual). | 12 | OI.6 | ||
No consideration of how to maintain the approach over time. | 9 | OI.7 | ||
Lack of transparency regarding the characteristics and uncertainties of the method. | 6 | OI.8 |
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Rieutor, D.; De Oliveira-Neves, G.; Mandil, G.; Bertozzi, C. Downscaling Planetary Boundaries: How Does the Framework’s Localization Hinder the Concept’s Operationalization? World 2025, 6, 96. https://doi.org/10.3390/world6030096
Rieutor D, De Oliveira-Neves G, Mandil G, Bertozzi C. Downscaling Planetary Boundaries: How Does the Framework’s Localization Hinder the Concept’s Operationalization? World. 2025; 6(3):96. https://doi.org/10.3390/world6030096
Chicago/Turabian StyleRieutor, Damien, Gwendoline De Oliveira-Neves, Guillaume Mandil, and Cecilia Bertozzi. 2025. "Downscaling Planetary Boundaries: How Does the Framework’s Localization Hinder the Concept’s Operationalization?" World 6, no. 3: 96. https://doi.org/10.3390/world6030096
APA StyleRieutor, D., De Oliveira-Neves, G., Mandil, G., & Bertozzi, C. (2025). Downscaling Planetary Boundaries: How Does the Framework’s Localization Hinder the Concept’s Operationalization? World, 6(3), 96. https://doi.org/10.3390/world6030096