Trajectories, Fairness, and Convergence: Global Development in a Multidimensional Econo-Environmental Capability Space
Abstract
1. Introduction
- RQ1: How can countries be characterized by a set of stable archetypes in the five-lens environmental capability framework over 1995–2024, and how do these archetypes behave and exhibit persistence over time?
- RQ2: Is cross-sectional inequality in capability small and declining, and how is fairness related to a deceleration near the frontier as the distance to the ideal state becomes smaller?
- RQ3: How do starting distance, archetype membership, and regional context shape transition probabilities, permanence, and reversals, and do these mechanisms produce tempered club convergence?
2. Literature Review
3. General Research Framework
3.1. Analytical Flow
3.2. The 5-Dimensional Environmental Lenses
- Productive capacity (PC)
- Developmental momentum (DM)
- Resource efficiency (RE)
- Resource depletion and degradation ratio (DDR)
- Remaining Development potential (RDP)
4. Methodology
4.1. Data and Preprocessing
4.2. Mathematical Specification of the Five Lenses
4.2.1. Productive Capacity
4.2.2. Development Momentum
4.2.3. Resource Efficiency
4.2.4. Degradation and Depletion Ratio
4.2.5. Remaining Development Potential
4.3. Archetype Construction and Clustering Procedure
4.4. Fairness Analysis
4.5. Temporal Analysis
4.6. Dynamic Distance Improvement (DDI) Analysis
4.7. Sensitivity Analysis
4.8. Generative AI Usage
5. Results and Discussion
5.1. Cluster Formation and Archetypes
- Cluster 1—Carbon pressured, efficiency lagging
- Cluster 2—Headroom rich, low intensity
- Cluster 3—Transition middle, gradual upgrading
- Cluster 4—Capability strong, headroom tight
5.2. Five-Dimensional Gini and Palma Ratio
5.3. Cluster Dynamics and Temporal Analysis
5.4. Dynamics Evolution of Countries and Region
5.5. Frontier Slowdown in the Environmental Capability Space
5.6. Robustness and Sensitivity Checks
6. Conclusions and Policy Implication
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Abbreviations
| ARI | Adjusted Rand index |
| ASEAN | Association of Southeast Asian Nations |
| DDI | Distance to ideal improvement |
| DDR | Degradation and depletion ratio lens |
| DM | Developmental momentum lens |
| EF | Ecological Footprint |
| EPI | Environmental Performance Index |
| ESI | Environmental Sustainability Index |
| GHG | Greenhouse gases |
| HDI | Human Development Index |
| KDE | Kernel density estimate |
| LAC | Latin America and the Caribbean |
| MENA | Middle East and North Africa |
| PC | Productive capacity lens |
| PCA | Principal component analysis |
| RDP | Remaining development potential |
| RE | Resource efficiency lens |
| SDG | Sustainable Development Goals |
| SSA | Sub-Saharan Africa |
| WGI | Worldwide Governance Indicators |
| WCD | Within cluster distance |
| PWT | Penn World Table |
| WDI | World Development Indicators |
| EU | European Union |
Appendix A



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| Reference | Method | Scope | Timeframe | Focus | Relevance |
|---|---|---|---|---|---|
| Agusdinata et al. (2020) | CART classification (country archetypes) | Global | 1980 to 2014 | CO2 per capita trajectory (slope); GDP growth trend | Supports multi-path emissions archetypes beyond EKC; intensity focus (RQ1, RQ3) |
| Alotaiq (2024) | k-means clustering | Global | 2015 to 2020 | Renewables share; electrification; GDP growth; HDI; governance (WGI); | Motivates archetype-specific transition routes; not region-generic (RQ3) |
| Moallemi et al. (2022) | Systems archetype analysis (causal-loop) | Global | — | SDG interaction patterns; feedbacks; policy levers | Alerts to trade-offs and rebound; monitor reversals (RQ3) |
| Eisenack et al. (2019) | Archetype analysis framework (conceptual) | Global | — | Conceptual framework | Advocates transferable, scale-aware archetypes with validity domains (RQ1) |
| Küppers et al. (2019) | k-means clustering | Global (140 countries) | 2015 to 2015 | 49 socioeconomic, climatic, and energy indicators | Suggests tentative clubs; requires dynamic tracking for persistence (RQ3) |
| Partelow et al. (2025) | Hierarchical clustering | Global (150 countries) | 2015 to 2019 | 42 indicators across social, economic, governance, environmental, and production | Notes risk constraints on mobility and reversal risk (RQ3) |
| Pedde et al. (2019) | Scenario archetypes (SSP/worldviews) | Global and subnational | — | SSP narratives; STEEP indicators; worldview coding | Emphasizes context dependence; global families fragment locally (RQ3) |
| Sietz et al. (2019) | Methodological synthesis of archetype analysis | Global | — | Sustainability systems | Prioritizes temporal stability validation over static snapshots (RQ1) |
| Hansen et al. (2018) | Special issue introduction | Global (developing-country focus) | — | Country sustainability transitions | Highlights durability factors; nurture niches and value-chain links (RQ3) |
| Eleftheriou et al. (2024) | Phillips–Sul club convergence | Global (137 countries) | 1990 to 2019 | SDI inputs: CO2 per capita; material footprint; HDI components | Shows club-specific convergence; paths differ by development stage (RQ3) |
| Erdogan and Okumus (2021) | Phillips–Sul club convergence | Global (89 countries) | 1961 to 2016 | Ecological footprint per capita | Documents multiple steady states; aggregate convergence misleads (RQ3) |
| Arogundade et al. (2023) | Phillips–Sul club convergence | Global (189 countries) | 1990 to 2017 | Ecological footprint per capita | Regional clubs shaped by starting pressure and resources (RQ3) |
| Haider and Akram (2019) | Phillips–Sul club convergence | Global (77 countries) | 1961 to 2014 | Ecological footprint per capita; carbon footprint per capita | Two steady states; design policy by club (RQ3) |
| Emir et al. (2019) | Phillips–Sul club convergence | EU (country level) | 1990 to 2016 | CO2 intensity (kg CO2 per kg oil-equivalent energy) | EU shows multiple clubs; differentiate targets (RQ3) |
| Panopoulou and Pantelidis (2009) | Phillips–Sul club convergence with club identification | Global 128 countries) | 1960 to 2003 | CO2 emissions per capita | Early convergence splits into two clubs; track permanence and reversals (RQ3) |
| Gómez and Rodríguez (2024) | Phillips–Sul club convergence | Americas (7 countries) | 1990 to 2022 | Energy consumption per capita; CO2 per capita; Ecological footprint per capita; energy intensity; load capacity factor | Indicator-specific clubs; region- and indicator-tailored pathways (RQ3) |
| Ulucak and Apergis (2018) | Phillips–Sul club convergence | EU (country level; 20) | 1961 to 2013 | Ecological footprint per capita | EU convergence rejected; persistent multiple clubs require differentiation (RQ3) |
| Ma et al. (2025) | Product-space network analysis (“SDG space”) | Global (country level; 166) | 2000 to 2022 | 96 SDG indicators | Polarized specialization; use distance-aware targeting and monitor reversals (RQ3) |
| Amann et al. (2013) | Global emission inventories and scenario review | Global | 1990 to 2010 | SO2; NOx; BC; OC; NH3 (inventories) | Decoupling uneven; structure and controls govern permanence or reversals (RQ3) |
| Gilli et al. (2013) | Shift-share decomposition (sectoral) | EU (DE, FR, IT, NL, SE; sector level) | 2000 to 2008 | Eco-innovation adoption; productivity; CO2/VA; SOx/VA; energy intensity | Sectoral mix and eco-innovation drive decoupling durability (RQ3) |
| Renou-Maissant et al. (2022) | PCA + hierarchical clustering | EU-28 | 2000 to 2019 | GHG per capita; primary energy intensity; renewables share | Multi-speed transitions; policy mix and innovation systems shape movement (RQ3) |
| Stefani et al. (2022) | Structural Topic Modeling (STM) | Global literature corpus | 2010 to 2020 | Topic tokens; year/journal covariates | Field branches across domains; transitions mediated by governance contexts (RQ3) |
| Bluszcz (2016) | Comparative analysis of synthetic indicators | Poland vs. Czech Republic | 2006 to 2014 | SSI (21 indicators); EPI components; EF components | Indices disagree; favor capability panels and dynamic tracking (RQ1, RQ2) |
| Ekins (1993) | Conceptual synthesis (limits-to-growth vs. sustainable development) | Global | — | Conceptual synthesis contrasting limits to growth and sustainable development | Limits and externalities justify frontier-aware assessment (RQ2) |
| Halvorsen and Smith (1984) | Duality-based estimation of scarcity rents | Canada | 1956 to 1974 | Shadow price of ore in situ; processed ore price; factor prices | Track stock scarcity and efficiency, not output alone (RQ2) |
| Krautkraemer (1998) | Theoretical and empirical review of resource scarcity | Global | — | Resource price; in-situ value (user cost); extraction cost; exploration and capital dynamics | Expect frontier slowdowns; measure rents and capacity (RQ2) |
| Siche et al. (2008) | Comparative analysis of national sustainability indices | Global | — | EF components; ESI variables; emergy indices | Indices disagree; triangulate measures (RQ1, RQ2) |
| Stern et al. (1996) | EKC critical review with simulations | Global (country level) | 1960 to 1990 | Income per capita; SO2 per capita; suspended particulates; deforestation | Rely on distance-to-target and policy or technology shifts (RQ2, RQ3) |
| Dimensional Lens | Indicator Data |
|---|---|
| Productive Capacity (PC) | Main Data (PWT, 1995–2019):
|
| Developmental Momentum (DM) | Main Data:
|
| Resource Efficiency (RE) | GDP per unit of energy use— (PPP $/kgoe, energy productivity) GDP per unit of GHG emissions— (PPP $ per tCO2e, carbon productivity) |
| Depletion and Degradation Ratio (DDR) | Mineral depletion— (% of GNI, income-equivalent loss from mineral extraction) Energy depletion— (% of GNI, loss from fossil fuel extraction) Forest depletion— (% of GNI, net forest rent losses) |
| Remaining Development Potential (RDP) | CO2 emissions per capita— (tCO2e/person, carbon pressure) |
| Notes: Unless otherwise stated, indicators were sourced from WDI (2024 release). | |
| Region | Dominant Archetype | Typical Mobility Pathways | Oscillation or Reversal Tendency | Permanence Tendency |
|---|---|---|---|---|
| ASEAN | C2–C3 mix with C3 rising (plus persistent C1 and a C4 anchor) | C2 → C3 and C1 → C3 | Low | Medium |
| East and Central Asia | Bifurcated profile (C4 anchors + C1 persistence + C3 middle) | C2 → C3 (Armenia) and C3 → C4 (Korea); localized C3 → C1 dips (China) | Low | High |
| South Asia | C2 dominant with selective C3 upgrading | C2 → C3 (India, Sri Lanka) | Very low | High |
| Oceania | C4 Dominant | Stable C3 and C4 | Very low | Very High |
| Europe West | C4 dominant | Mostly stable C4; | Very low | Very high |
| Europe East | C3 with sustained upgrading into C4 plus a persistent C1 cases | Limited: C3 → C4 | Low | High |
| North America | C4 anchored with a stable C3 member | No mobility observed | Very low | Very high |
| Latin America and Caribbean | C2 and C3 dominant | C2 → C3 and C3 → C4 | Medium | Medium |
| Middle East and North Africa | C1 and C3 dominant | C1 → C3 and C3 → C4 (limited) | Low | Medium |
| Sub-Saharan Africa | C2 dominant with sparse C3 and localized C1 outliers | Mostly stable C2; rare C2 → C3 upgrades | low | High |
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Share and Cite
Imaduddin, M.H.; Basu, S.; Okumura, H. Trajectories, Fairness, and Convergence: Global Development in a Multidimensional Econo-Environmental Capability Space. Economies 2026, 14, 16. https://doi.org/10.3390/economies14010016
Imaduddin MH, Basu S, Okumura H. Trajectories, Fairness, and Convergence: Global Development in a Multidimensional Econo-Environmental Capability Space. Economies. 2026; 14(1):16. https://doi.org/10.3390/economies14010016
Chicago/Turabian StyleImaduddin, Muhammad Hasan, Soumya Basu, and Hideyuki Okumura. 2026. "Trajectories, Fairness, and Convergence: Global Development in a Multidimensional Econo-Environmental Capability Space" Economies 14, no. 1: 16. https://doi.org/10.3390/economies14010016
APA StyleImaduddin, M. H., Basu, S., & Okumura, H. (2026). Trajectories, Fairness, and Convergence: Global Development in a Multidimensional Econo-Environmental Capability Space. Economies, 14(1), 16. https://doi.org/10.3390/economies14010016

