Paul Gardner Brook ← Insights

Analysis · Climate & Energy Policy

The Social Reckoning

EU Net Zero policies and the true quality-of-life cost for European families in 2026

Overview video — watch on YouTube

Executive Summary

Europe's legislative machinery for climate transition — the European Green Deal, the European Climate Law (now amended to include the legally binding 2040 target of 90% net GHG reduction), national NECPs for 2021–30, and the Paris Agreement architecture — constitutes the most ambitious regulatory realignment ever attempted by a continental polity in peacetime. In April 2026, the amended Climate Law entered into force, hardening what was already a formidable policy stack.

The fundamental question this analysis addresses is not whether these ambitions are climatically correct — the physics of greenhouse-gas forcing is not contested here. The question is one of distributional honesty: who actually bears the costs, what do those costs look like lived from inside a household budget, and are the compensatory architectures adequate? The answer, drawn from the primary data available as of mid-2026, is sobering. Progress exists, particularly on aggregate emissions (EU GHG fell 8.3% in 2023 alone, with a 37% cumulative decline versus 1990). But the social ledger records costs that have been systematically underweighted — a structural deficiency that mirrors the broader neglect of the 'S' in ESG frameworks documented in the literature.

As Vaclav Smil would frame it: the laws of physics do not negotiate timelines, but the laws of social physics — the friction of household cash flows, the inertia of building stock, the rigidity of labour markets — operate on their own clock. The distance between Brussels' institutional calendar and the kitchen table in Łódź, Seville, or Bucharest is not geographical; it is existential.

10.6%▲ 54% vs 2021of EU citizens could not adequately heat their homes in 2023
€1,112bnprojected cumulative ETS2 household cost, 2025–2040
≈ 8%of that projected cost is covered by the Social Climate Fund
I

The Policy Architecture and Its Household Interface

1.1 The Legislative Stack

The European Green Deal, launched in December 2019, set the foundational trajectory: climate neutrality by 2050, a binding 55% GHG reduction by 2030, and an ambitious 90% target for 2040 now enshrined in law. The Fit-for-55 legislative package operationalises this through more than 150 distinct policy initiatives, covering the revised EU Emissions Trading System (ETS1), a new ETS for buildings and road transport (ETS2), the Energy Performance of Buildings Directive (EPBD), the Renewable Energy Directive (RED III), the Energy Efficiency Directive (EED), the Carbon Border Adjustment Mechanism (CBAM), and the Farm to Fork food strategy.

The interface between this architecture and ordinary households is more direct and more immediate than most policy summaries acknowledge. ETS2, covering emissions from fuel combustion in buildings and road transport, begins full operations in 2027 (delayed one year, with a possible further delay to 2028 if energy prices remain extreme). The CBAM entered its definitive operational phase on 1 January 2026, requiring EU importers to pay carbon prices on steel, cement, aluminium, fertilisers, electricity, and hydrogen — a cost chain that feeds directly into construction, food production, and energy pricing. National NECPs meanwhile commit every Member State to phased trajectories of building renovation, fuel switching, and transport electrification.

1.2 The 'S' Gap in the Architecture

The EU has, to its credit, constructed compensatory mechanisms. The Social Climate Fund (SCF), established by Regulation 2023/955, covers the period 2026–2032 and is expected to mobilise €86.7 billion — financed through ETS2 auction revenues supplemented by a 25% national co-financing requirement. In absolute allocation terms, Poland (17.60%), France (11.19%), Italy (10.81%), Spain (10.52%), and Romania (9.25%) are the primary beneficiaries.

Yet the SCF's launch has been shadowed by institutional lethargy. Member States were required to submit their National Social Climate Plans by 30 June 2025; as of May 2026, progress remains 'very slow,' with local and regional governments — who must implement the programmes — still largely excluded from national planning processes. The fund that was meant to precede the pain has not yet reached the people who will feel it.

This institutional gap is not incidental. It is symptomatic of the structural asymmetry in the neglect of the 'S' in ESG: the EU has built comprehensive environmental taxonomies while social taxonomies remain 'under discussion,' regulatory compliance requirements focus on environmental metrics, and investment flows disproportionately favour environmental over social performance. The result is a transition architecture that is, in the words of the IEEP, 'at risk of being regressive without careful design.'

II

Energy — The First and Most Direct Wound

2.1 The Current State of Energy Poverty

Energy poverty is the most immediate and measurable social consequence of the transition, and its trajectory over the past five years exposes deep structural fragility. According to Eurostat data, the share of EU citizens unable to adequately heat their homes rose from 6.9% in 2021 to 9.3% in 2022, then to 10.6% in 2023 — a 54% increase in the headline indicator over just two years. The 2024 figure shows modest improvement to 9.2%, partially attributable to milder winters and targeted emergency subsidies, but the underlying structural drivers remain unresolved.

At any given moment, between 35 and 72 million EU citizens face challenges meeting the cost of their energy bills. Bulgaria, Greece, Lithuania, Portugal, and Spain lead the Member State vulnerability rankings, with over one-fifth of households in each country unable to adequately heat their homes as of 2023. The June 2026 EPAH report — a primary source commissioned by the European Commission — confirms that energy poverty is not merely an energy cost problem but a multidimensional vulnerability system encompassing climate stress, health outcomes, housing quality, and mobility access.

Energy poverty: EU citizens unable to adequately heat their homes

Eurostat headline indicator, % of population, 2021–2024

Share of EU citizens unable to adequately heat their homes 2021: 6.9 percent. 2022: 9.3 percent. 2023: 10.6 percent. 2024: 9.2 percent. 0 3 6 9 12 6.9% 9.3% 10.6% 9.2% 2021 2022 2023 2024
The indicator rose 54% between 2021 and 2023. The 2024 easing is attributed partly to milder winters and emergency subsidies; the structural drivers remain unresolved.

2.2 The ETS2 Problem

The extension of carbon pricing to buildings and road transport under ETS2 has generated the most contested social impact debate in EU climate policy. The distributional economics are unambiguous: carbon pricing on household fuels is regressive. ETS2 impacts tend to fall most heavily on lower- and middle-income households, for whom heating fuels represent a larger share of disposable income. Analysts have forecast potential fuel price increases of up to 50 cents per litre when ETS2 fully operates, imposing disproportionate burdens on households with the least financial flexibility.

A 2025 academic study using Multi-Regional Input-Output modelling specifically examined single-person and childless households — a structurally underprotected group — and found that ETS2 carbon pricing forces them to reduce spending on food in order to maintain heating. At the EU-27 aggregate level, high carbon prices under ETS2 could cost households €1,112 billion cumulatively from 2025 to 2040. The EU Parliament responded in April 2026 by voting to strengthen the Market Stability Reserve mechanism that caps carbon prices at €45 per tonne of CO₂ through 2029, with faster release of allowances to prevent price spikes — an acknowledgement that the distributional risk is real.

2.3 The Building Renovation Trap

The revised EPBD (EU 2024/1275), which entered into force in May 2024, mandates that residential building stocks reduce their average primary energy use by 16% by 2030 and 20–22% by 2035. Nearly 50% of EU housing stock was built before 1980 and requires significant renovation. The directive's general transposition deadline is 29 May 2026, and EU countries must submit final national building renovation plans by end-2026.

The cost implications for households are enormous and have not been adequately offset. The EU's renovation wave aims to renovate 35 million buildings by 2030, but the cost of renovating social housing stock alone — without even addressing the private rental market or owner-occupied stock — is formidable. In 2024, 8.2% of EU population lived in households where housing costs already exceeded 40% of disposable income. A renovation-cost burden layered onto that baseline creates a quality-of-life squeeze with no near-term exit. The EU's first-ever Affordable Housing Plan, presented in December 2025, acknowledges the problem but remains largely advisory toward Member States.

The EPAH cross-analysis of data from 17 Member States confirms a Spearman correlation: heat stress is strongly linked to poor housing conditions, and cold housing is structurally linked to general poverty. The policy to remediate this — building renovation — costs money that energy-poor households do not have. This circularity is the central structural failure of the current architecture.

III

Food Security and the Farm to Fork Paradox

3.1 Agricultural Production Effects

The Farm to Fork Strategy — positioned as the food systems centrepiece of the European Green Deal — sets targets to reduce fertiliser use by 20%, pesticide use by 50%, and increase organic farming to 25% of agricultural land by 2030. These targets interact with the CBAM's entry into force on 1 January 2026 for fertilisers, creating a compounding pressure on agricultural input costs.

The academic and analytical consensus on production effects is remarkably consistent across different methodological approaches. The USDA study projects that Farm to Fork implementation could lead to food insecurity for 22 million people, with wheat output declining by up to 48%, oilseeds by 60%, and beef by 14%. The Joint Research Centre study separately projects that between 40% and 60% of GHG emission reductions from European agriculture would be achieved by outsourcing production to third countries — carbon leakage in its most literal agricultural form. A Kiel University study projects that Europe could become a net food importer as a result. The USDA study on EU agricultural input reductions projects that the total value of EU agricultural output could shrink by 12% and domestic food prices rise by 17%.

Projected production effects of Farm to Fork

USDA Economic Research Service, projected change in output

USDA-projected effects of Farm to Fork implementation Projected declines: oilseeds output 60 percent, wheat output 48 percent, beef output 14 percent, total agricultural output value 12 percent. Oilseeds output Wheat output Beef output Ag. output value −60% −48% −14% −12%
Alongside these output declines, the same analysis projects EU domestic food prices rising ~17% and food insecurity for up to 22 million people.

3.2 Household Food Budget Pressures

The EESC's CMCC study on household costs provides a vital empirical baseline. Climate change itself — independent of policy costs — is projected to increase average household food expenditure by 0.74%–0.81% across climate scenarios, with the highest increases in Cyprus, Greece, Spain, Italy, and Portugal. The climate effect on food expenditure is regressive in Eastern EU, where the poorest households face significantly larger percentage increases.

Layer the Farm to Fork supply-side restrictions atop climate-driven demand pressures, and the food security picture deteriorates further for the bottom income quintile. The CBAM's definitive phase from 2026 applies to fertilisers, meaning that non-EU fertiliser imports now carry a carbon cost premium at EU borders, creating structural upward pressure on agricultural input costs over the medium term.

Political reality has tracked ahead of the data here. The Farm to Fork Strategy largely stalled in 2025 under pressure from farmer protests and centre-right parliamentary arithmetic, and no binding legislation was enacted on pesticide reduction targets. This is a genuinely ambiguous outcome: the targets that threatened food security were not implemented, but neither was the sustainable transformation of food systems that would ultimately reduce climate-related food costs. Europe's food system sits in a policy limbo — neither protected from climate risk nor restructured to reduce it.

IV

Transport, Mobility Poverty, and the Spatial Divide

4.1 The EV Transition and Its Affordability Problem

The Green Deal's original vision of all new cars being zero-emission by 2035 has been partially renegotiated. The December 2025 Automotive Package revised CO₂ standards to require a 90% tailpipe emissions reduction by 2035 (rather than 100%), while introducing technological neutrality provisions for e-fuels, biofuels, and plug-in hybrids. The EU Parliament in 2026 is treating the original EV-only mandate as effectively softened.

Consumer advocacy analysis from BEUC finds that battery electric vehicles will be the lowest total cost of ownership option for used-vehicle buyers and for new medium-car buyers from 2026 onwards. But 'total cost of ownership' is not the same as 'purchase affordability for a low-income family in rural Romania.' The upfront cost premium remains a structural barrier, and EV charging infrastructure remains concentrated in urban and high-income areas.

4.2 Transport Poverty as a Distinct Vulnerability

The June 2026 EPAH report introduces transport poverty as a co-dimension of energy poverty that must be assessed jointly rather than in isolation. Mobility access is critical: where households depend on private vehicles and cannot afford to transition to electric, they face both carbon cost increases under ETS2 and stranded-asset risk on existing fossil-fuel vehicles. The EPAH framework now tracks car ownership among materially deprived households, household transport expenditure shares, and the population unable to afford a personal car — each of which maps spatial vulnerability that geographically concentrated green policy may exacerbate.

Rural households, in particular, have no practical alternative to private car use and cannot benefit from urban public transport improvements. The distributional concern about carbon pricing in transport is thus not evenly distributed — it falls hardest on the geographically immobile poor, who are also least able to accelerate the transition through consumer choices.

V

Health, Safety, and Climate Stress Interactions

5.1 The Twin Burden: Policy Cost and Physical Climate Risk

The EU faces a double health exposure that makes simple cost-benefit accounting inadequate. On one side, the physical climate is already imposing health costs that are projected to intensify: climate-induced health expenditure is projected to rise by 0.3% under moderate warming and 6.2% under severe warming, with the highest increases in Cyprus, Greece, Spain, Croatia, Italy, and Portugal. Excess winter mortality remains significant across 22 Member States tracked by EUROMOMO data through Winter 2024/2025. Excess summer mortality has emerged as a parallel and growing threat, now requiring its own dedicated indicator in the EPAH framework following Summer 2025 data.

On the other side, the transition itself imposes costs that can compromise health through food budget compression, housing thermal adequacy failures, and transport access restrictions. The EPAH's cross-analysis confirms structural correlations: heat stress leading to poor housing leading to health vulnerability forms a reinforcing loop. When the policy response to heat stress (building renovation) is financially inaccessible, the health cost escalates.

5.2 Air Quality: The Clearest Positive Signal

To be precise and empirically honest: the Green Deal's push toward clean energy and transport has generated measurable health benefits. EU GHG emissions fell 37% versus 1990 and fell a further 8.3% in 2023 alone. The revised Ambient Air Quality Directive (AAQD), adopted in November 2024, sets new limits on key air pollutants by 2030. EU Commissioner Roswall confirmed in late 2025 that significant reductions in key pollutants have been achieved. The zero-pollution action plan targets a 55% reduction in air-pollution health impacts by 2030, and trajectory analysis suggests this is achievable.

−37% / −8.3% EU greenhouse-gas emissions fell 37% versus 1990, and a further 8.3% in 2023 alone — a real, measurable gain whose air-quality co-benefits fall disproportionately on lower-income urban populations.

These benefits are real and disproportionately benefit lower-income urban populations who live closest to traffic and industrial emission sources. Any intellectually honest analysis must register them alongside the costs. The net health calculus, at the EU aggregate level, likely favours transition — but the distribution of costs and benefits does not follow the same geography or income gradient. The benefits of cleaner air are diffuse and long-term; the costs of building renovation and transport fuel pricing are immediate and concentrated.

VI

Education, Human Capital, and the Jobs Transition

6.1 Skills Misalignment and the Labour Market Dislocation

The EU's green transition is projected to create 2.5 million additional jobs across renewable energy, energy efficiency, and the circular economy. The Pact for Skills initiative has committed over 1,000 companies and training providers to upskill and reskill 6 million workers, while the Just Transition Fund (€17.5 billion for 2021–2027) targets regions most dependent on fossil fuels.

However, OECD research demonstrates that displaced workers from carbon-intensive industries experience 'particularly long and significant income losses' compared to workers in other sectors, reflecting both skills specificity and geographic concentration. The 30% of corporate executives who expect some positions to become redundant during decarbonisation, while only 34% believe adverse impacts can be adequately addressed through retraining, suggests that institutional confidence in smooth transition is not uniformly shared at ground level.

The temporal and spatial misalignment is the critical problem. Green jobs are not emerging in the same places where coal mines are closing, or where oil refineries are restructuring. The skills demanded by a solar panel manufacturer in northern Germany are not the skills held by a lignite miner in Saxony or a refinery worker in Százhalombatta. Education systems have not yet recalibrated fast enough to bridge this gap at scale.

6.2 Youth and the Education System Interface

EU education systems are being asked to prepare a generation for a fundamentally different economy, while the existing labour market absorbs the disruption of the transition. Youth unemployment in carbon-intensive regions remains structurally elevated. CEDEFOP and Institut Jacques Delors analyses both identify green skills provision as underdeveloped, with the formal education system lagging behind the transition's skills requirements. The EU's Net Zero Industry Act targets at least 40% of clean technology manufactured in the EU by 2030 and has established sector-specific Net Zero Industry Academies — but 'establishing academies' and 'having a trained workforce' are separated by years of execution time.

The deepest educational challenge is not vocational but epistemic: the social legitimacy of the transition depends on citizens understanding that their personal sacrifices — higher energy bills, more expensive cars, more expensive renovation — serve a collective purpose they experience in their own lifetimes, not merely in 2050. The trust deficit between EU institutions and electorates is widening in precisely the communities bearing the highest transition costs.

VII

The Political Economy of 2025–2026 — Signals from the Real World

7.1 The Rollback Signal

The policy architecture itself is signalling the inadequacy of the social dimension. In 2025, described by FEPS as 'a hard year for the European Green Deal, with far more steps backwards and missed opportunities than forward progress,' multiple structural retreats occurred. ETS2 start date was delayed from 2027 to 2028. Car fleet CO₂ standards shifted from a hard 2030 target to a 3-year averaging window. The Omnibus simplification package proposed weakening the CSRD (raising the employee threshold from 250 to 1,000), the CSDDD, and the EU taxonomy. The Farm to Fork pesticide reduction legislation was dropped entirely. The Green Deal was described by the Delors Centre in December 2025 as being 'hollowed out.'

These retreats do not primarily reflect a change in climate science or economics. They reflect electorates — particularly in Central and Eastern Europe, and in agricultural communities throughout the West — registering that the social costs of the transition are landing unevenly and prematurely, without the compensatory structures promised. The French gilets jaunes of 2018 were not an aberration; they were a preview. Carbon pricing on transport without adequate alternatives or rebates produces political instability.

7.2 The ESG Rating Blind Spot

The 'S' has been neglected in ESG frameworks with empirical precision: academic research identifies measurement divergence as accounting for 56% of discrepancies between ESG rating agencies, with social indicators fragmented across cultural, legal, and economic contexts. The EU has implemented comprehensive environmental taxonomies; corresponding social taxonomies remain 'under discussion.' This institutional asymmetry means that the companies and policies driving Europe's green transition are being measured, rated, and rewarded primarily on their environmental performance — while their social impacts on households flow through channels that remain systematically unmeasured, underdisclosed, and underpenalised.

The practical result is that capital allocation follows the environmental signal while social damage accumulates in the background. A rating agency can award a top ESG score to a utility that has successfully decarbonised its generation portfolio while simultaneously having driven 15% of its retail customers into energy poverty through retail tariff structures. This is not a marginal calibration problem; it is a fundamental architecture failure in how sustainability is measured.

VIII

The Distributional Architecture — What Exists, What Is Insufficient

8.1 The Compensatory Toolkit

The EU has assembled a compensatory toolkit that is, in principle, substantial:

EU compensatory instruments — status as of mid-2026
InstrumentBudgetPeriodStatus as of Mid-2026
Social Climate Fund€86.7bn2026–2032Launched; National Plans delayed
Just Transition Fund€17.5bn2021–2027Operational; geographic targeting
Cohesion Funds (climate share)€275bn (NextGenEU)2021–202642% dedicated to climate action
ETS revenues for green/social€200bn+2021–2026Revenue generated; distribution uneven
Affordable Housing PlanAdvisory2026+Published Dec 2025; largely non-binding

8.2 The Adequacy Gap

The SCF at €86.7bn over 2026–2032 sounds large until placed in the context of the costs it is meant to offset. ETS2 alone could cost EU households €1,112 billion from 2025 to 2040. The fund covers roughly 8% of the projected household cost impact. Social Climate Plans were due by 30 June 2025; as of mid-2026, most Member States have not completed them, meaning that households bear costs before protection mechanisms are operational. The local governments responsible for actual programme delivery — energy bill subsidies, renovation grants, mobility support — remain 'left out' of national planning processes according to the Local Alliance policy brief of June 2025.

The adequacy gap

Social Climate Fund (€86.7bn, 2026–2032) vs projected ETS2 household cost (€1,112bn, 2025–2040)

Social Climate Fund versus projected ETS2 household cost Projected ETS2 household cost 1,112 billion euro from 2025 to 2040. Social Climate Fund 86.7 billion euro, covering roughly 8 percent. ETS2 household cost Social Climate Fund €1,112bn €86.7bn
The fund covers roughly 8% of the projected household cost impact — and most National Social Climate Plans remained incomplete as of mid-2026.

The IEEP's distributional analysis is clear: energy and carbon pricing 'places a greater financial burden on lower-income households, for whom electricity and heat represent a larger share of expenditure,' and the effect is compounded for rural, female-headed, and elder-headed households. Carbon pricing 'must be paired with compensation mechanisms that consider income levels, geography, and household socioeconomic characteristics such as rurality, gender, and age.' This requirement is stated; it is not yet achieved.

IX

Country Vulnerability — A Structured Differentiation

The EPAH's Principal Component Analysis (PCA) across 17 EU Member States grouped countries into eight Country Vulnerability Groups and four Climate Groups, providing the most statistically robust differentiation of household vulnerability currently available. The findings reveal a structural North-South and West-East gradient.

Highest structural vulnerability (Southern EU)

Characterised by higher overall vulnerability scores, heat severity, poor building thermal performance, and concurrent socioeconomic disadvantage. Greece, Bulgaria, Cyprus, and Romania face the most acute combination of climate exposure and poverty risk.

Cold-exposure vulnerability (Northern/Eastern EU)

Lower overall vulnerability but specific cold-stress exposure; policy costs of building decarbonisation land hard in countries where gas heating is universal and alternatives are nascent. Poland, Czechia, Slovakia, and Hungary remain heavily fossil-fuel dependent.

Middle-income squeeze (Western EU)

Countries like France, Germany, Belgium, and the Netherlands face the largest absolute ETS2 cost exposures in aggregate terms; middle-income households face the highest ETS2 burdens as a share of income when above subsidy thresholds but below the capital threshold for rapid adaptation.

The EESC CMCC study confirms: negative and regressive impacts on a wide set of expenditure goods and income sources will be most severe in Southern Europe — Greece in particular — with food expenditure regressivity also manifesting in Eastern EU.

X

Findings and Analytical Conclusions

The evidence assembled across these dimensions supports the following conclusions, stated without diplomatic attenuation:

  1. The social costs of EU net-zero transition are structurally regressive. Carbon pricing on heating fuels and transport, building renovation mandates, and agricultural transformation policies impose proportionally higher costs on lower-income households than on higher-income ones. This is not a disputed finding; it is confirmed by EU institutions, OECD research, and independent academic modelling.
  2. The compensatory architecture exists but is operationally premature. The Social Climate Fund is the right instrument architecturally; its inadequacy is in execution. National plans are late, local governments are excluded, and the fund covers a small fraction of the projected cost burden.
  3. Energy poverty is the most acute immediate manifestation. 10.6% of EU citizens could not adequately heat their homes in 2023 — a 54% increase from the 2021 baseline — and the structural drivers that created this situation have not been resolved. The June 2026 EPAH report confirms that energy poverty now requires assessment across 14 indicators spanning climate, health, housing, and mobility, because the problem is multidimensionally compounded.
  4. Food security risks from Farm to Fork have been politically managed but not structurally resolved. The most dangerous supply-side targets were not implemented, but neither has EU agriculture been transitioned to genuine climate resilience. The CBAM fertiliser cost channel, now operative from 2026, adds a structural input cost increment.
  5. Transport mobility poverty represents an emerging and undertracked vulnerability. Rural and lower-income households face a structural double-bind: ETS2 will raise fossil fuel costs while EV affordability and charging infrastructure remain inaccessible. The EPAH's new transport poverty indicators confirm this is a data gap being actively addressed.
  6. Air quality improvements are real but unevenly distributed. The health co-benefits of reduced fossil fuel combustion are genuine, material, and disproportionately benefit lower-income urban residents. These benefits must be transparently quantified and credited in the social ledger.
  7. The 'S' deficit in ESG is not merely analytical — it is a capital allocation failure. Because social costs of the transition are unmeasured in dominant ESG frameworks, capital flows optimise for environmental performance while social damage accumulates in household balance sheets across the EU. Until standardised, mandatory social impact measurement comparable to the environmental taxonomy is implemented, the green transition will continue to generate ESG ratings that are epistemically incomplete.
  8. Political legitimacy is the binding constraint. The 2025 rollbacks were not driven by a change in climate science. They were driven by electorates signalling that the social costs are not being managed equitably. A transition that loses political legitimacy cannot be completed — which means that a socially inadequate green transition is also, ultimately, an environmentally inadequate one.
§

Key Sources and References

  1. European Commission / EPAH. (2026, June). Expanding Energy Poverty Measurement in the EU: Integrating New Climate, Health and Mobility Indicators. Energy Poverty Advisory Hub, European Commission DG Energy, Brussels.
  2. Brook, Paul. (2026). The Neglected 'S' in ESG: Why Social Factors Demand Equal Footing with Environmental and Governance Priorities.
  3. European Economic and Social Committee / CMCC. (2023). The Cost of Climate Change on Households and Families in the EU. Publications Office of the EU.
  4. European Commission. (2026, April). European Climate Law — as amended to include the 2040 target of 90% net GHG reduction. climate.ec.europa.eu
  5. European Commission. (2024). Energy Performance of Buildings Directive (EU 2024/1275). energy.ec.europa.eu
  6. European Commission. (2023). Regulation (EU) 2023/955 Establishing a Social Climate Fund.
  7. European Commission. (2026). Carbon Border Adjustment Mechanism — Definitive Phase. taxation-customs.ec.europa.eu
  8. Solidar. (2026, May). The Social Climate Fund Launches, but Will It Support the Most Vulnerable? solidar.org
  9. Klimabündnis / Local Alliance. (2025, June). With the Deadline Near, Local Governments Still Left Out of National Social Climate Plans. Policy Brief.
  10. IEEP. (2025, May). Social Impacts in the EU Energy Transition: Distributional Effects of European Energy Policies. ieep.eu
  11. Frontiers in Environmental Science. (2025). The Economic Burden of EU ETS2 Carbon Pricing on Single and Childless Households. DOI: 10.3389/fenvs.2025.1572246
  12. ScienceDirect / Energy Policy. (2026). The Impact of the EU-ETS2 on Prices and Welfare in the European Economy. sciencedirect.com
  13. European Commission. (2025, December). European Affordable Housing Plan. housing.ec.europa.eu
  14. Transport & Environment. (2026, February). State of European Transport 2025. transportenvironment.org
  15. USDA Economic Research Service. (2020). Economic and Food Security Impacts of Agricultural Input Reduction Under the EU Green Deal's Farm to Fork and Biodiversity Strategies. Economic Brief No. EB-30.
  16. CropLife Europe. (2024, February). Farm to Fork — It Is Time to Listen to What the Data Says. croplifeeurope.eu
  17. EU Parliament / Market Stability Reserve. (2026, April). MEPs Move to Limit Carbon Price Spikes Ahead of ETS2. euperspectives.eu
  18. European Environmental Bureau (EEB). (2025). The European Green Deal Knowledge Brief.
  19. Eurostat / ECPR Loop. (2025, February). Energy Poverty in the EU. theloop.ecpr.eu
  20. European Commission DG Energy. (2024). Energy Poverty — Official Data. energy.ec.europa.eu
  21. Foundation for European Progressive Studies (FEPS). (2026, April). The European Green Deal Was Under Siege in 2025, But It Is Still Standing. feps-europe.eu
  22. Finnish Institute of International Affairs (FIIA). (2025, November). Tracking the European Green Deal: Ambitions Meet Growing Resistance. FIIA Briefing Paper 424.
  23. Delors Centre. (2025, December). Europe Is Hollowing Out Its Green Deal, Leaving a Vacuum of Political Leadership.
  24. Clean Air Fund. (2025, July). How the EU Can Meet 2030 Air Quality Goals: 10 Steps to Clean Air. cleanairfund.org
  25. Institut Jacques Delors. (2025, April). Employment and Skills for the Green Transition in the EU.
  26. European Investment Bank. (2026, January). Affordable and Sustainable Housing Knowledge — What You Need to Know.
  27. World Green Building Council Europe. (2026, January). Delivering Affordable, Sustainable and Resilient Housing in Europe.
  28. BEUC. (2025, September). Cost of Zero-Emissions Cars in Europe. beuc.eu
  29. European Commission. (2025, December). Automotive Package — CO₂ Standards Revision. transport.ec.europa.eu
  30. OECD. (2025). Employment and Skills Policies for the Green Transition. Paris: OECD Publishing.