Distributional Consequences of Becoming Climate-Neutral
What this paper finds — and why it matters
Layer 1: Overview
This paper investigates how the EU’s Fit-for-55 climate package will affect aggregate output and distribute its costs across the income distribution. The question matters because energy is a necessity good — poorer households devote a larger share of spending to energy — so policies that raise energy prices are regressive in their first-order incidence. Despite a large literature on the aggregate macroeconomics of the green transition, distributional consequences have received limited attention.
The authors build a parsimonious dynamic general-equilibrium model with two infinitely-lived households (rich and poor), a standard output-producing firm that treats energy as a complementary CES input alongside the capital-labor aggregate, and an energy-producing sector that combines a carbon-intensive brown technology with a carbon-free green technology as imperfect substitutes (CES with elasticity of substitution calibrated to 3 following Papageorgiou et al. 2017). The novel feature is Price Independent Generalized Linearity (PIGL) non-homothetic preferences following Boppart (2014), which generate nonlinear Engel curves: the poor agent’s energy expenditure share exceeds the rich agent’s, matching Eurostat Household Finance and Consumption Survey data (2015) showing the bottom income quintile has more than twice the energy expenditure share of the top quintile. The model targets an 18% energy expenditure share for the poor agent and 7.5% for the rich agent. The rich agent holds all financial wealth; the poor agent lives on labor income alone. The government taxes the brown technology and recycles revenue as a green-technology subsidy under a balanced budget, representing the ETS. Agents have perfect foresight. The paper simulates perfect-foresight transitions from an initial steady state to a new climate-neutral steady state, with the transition path endogenously determining the new steady state — a nonstandard feature arising from non-homothetic preferences.
In the baseline scenario (linear tax ramp over 25 years), achieving an 85% reduction in brown energy use requires a 168% tax on the brown technology. This drives the price of energy services up by 49%, GDP down by 9.3% in the new steady state, energy as a production input down by 10.9%, and capital input down by 9.3%, while the real wage falls by roughly 7% and the real interest rate is nearly unchanged (dropping by only 0.02 percentage points transiently). The welfare cost measured in expenditure-equivalent terms is a 10.8% loss for the rich agent and a 16.2% loss for the poor agent — the poor agent suffers approximately 50% more. To finance consumption during the transition the poor agent accumulates debt equal to 38.8% of annual income.
Results are highly sensitive to the brown-green substitution elasticity: raising it from 3 to 5 roughly halves the required tax (to 78.6%) and halves GDP losses (to 4.7%); lowering it to 2 roughly doubles the tax (to 354%) and GDP losses (to 17.7%). Non-homothetic preferences matter quantitatively: switching to homothetic preferences (while preserving different expenditure shares) shrinks aggregate GDP losses by 26% and eliminates nearly all distributional disparity, confirming that the non-homotheticity — not merely different expenditure levels — is the operative distributional mechanism. If the Fit-for-55 energy efficiency improvement target of 1.49% per year is simultaneously achieved, the required tax falls to 136%, the price of energy actually declines by 5.5%, and GDP rises by 1.1% in the new steady state, with the poor agent benefiting slightly more and accumulating assets (4% of annual income) rather than debt.
Layer 2: Deep Dive
What is the core modeling and calibration strategy, and what are the main threats?
The paper is a quantitative theory exercise with no econometric identification. Calibration targets HFCS Eurostat data (2015) for energy expenditure shares by income quintile, the Papageorgiou et al. (2017) estimate of the brown-green substitution elasticity (ρE = 3), and stylized facts on wealth and income distribution from Krueger, Mitman, and Perri (2016). The main threat is parameter uncertainty around ρE, which the paper acknowledges is poorly identified empirically and which drives the results almost one-for-one. The sensitivity analysis explores ρE ∈ {2, 3, 5}, a range the paper concedes is narrow relative to the literature’s full dispersion.
What are the main mechanisms generating the distributional gap between rich and poor?
Three reinforcing channels: (1) Non-homothetic preferences give the poor agent a higher energy expenditure share (18% vs. 7.5%), so the 49% energy price increase hits the poor’s budget much harder as a share of income. (2) The poor agent cannot buffer the shock through wealth drawdowns (holding zero net assets initially), forcing it to accumulate debt of 38.8% of annual income. (3) Non-homothetic preferences alter the labor supply response: as expenditures fall, the poor agent’s labor supply declines less than the rich agent’s (the rich agent decreases labor supply by 0.2 percentage points more), reflecting that leisure is a luxury good in this preference system. In the new steady state the rich agent’s consumption of the consumption good drops sharply while the rich agent front-loads consumption at the announcement, immediately jumping 2% higher.
How are non-homothetic preferences distinguished empirically and in the model from simply having different expenditure shares?
Section 4.4 runs a counterfactual with homothetic preferences (ε = 0) but preserves identical initial expenditure shares for each agent (7.5% and 18%) by making ν agent-specific. Under homotheticity the expenditure shares do not vary with income as the transition unfolds. The comparison shows that GDP losses shrink by 26% (from 9.3% to 6.9%) and the distributional gap nearly vanishes — both agents experience almost identical welfare losses. This decomposition isolates the effect of non-homotheticity itself: it is the income-dependent adjustment of expenditure shares during the transition, not merely the different initial levels, that drives both larger aggregate losses and the distributional disparity.
What heterogeneity is documented and along what dimensions?
Heterogeneity is modeled along two dimensions: initial wealth (rich holds all assets; poor holds zero) and energy expenditure shares (18% for poor, 7.5% for rich) arising from non-homothetic preferences. The model produces no within-group heterogeneity by construction (two-agent framework). The paper documents the time paths of consumption, expenditures, expenditure equivalents, energy expenditure shares, and wealth shares for each agent separately along the transition, showing that both agents cut energy consumption by roughly 15% while the poor agent cuts consumption-good spending by substantially more than the rich agent.
What alternative transition timing paths are explored and what do they imply?
Three alternatives supplement the linear baseline: tax introduction after 1 year, after 12.5 years, and after 25 years of the announcement. Key findings: (a) the required final tax rate is nearly insensitive to timing — the 25-year-delayed scenario requires 172% vs. 168% in the baseline; (b) conditional on excluding climate damages, it is always welfare-superior to delay implementation, with the poor agent gaining close to 3.5 percentage points in expenditure equivalent welfare by delaying to 25 years vs. implementing after 1 year; (c) gradual vs. immediate introduction yields similar welfare outcomes in the benchmark without adjustment costs, but with investment adjustment costs (χ = 10) a sudden implementation causes a brief sharp drop in the real interest rate without large quantity effects.
How does the GDP measure differ from aggregate output in the model?
GDP is defined to exclude the share of final output used as input into energy production. Aggregate output Y falls 7.3% in the new steady state, but GDP falls 9.3%. The gap (approximately 2 percentage points) reflects the increased resource cost of energy production under the green transition: because the brown and green technologies are imperfect substitutes, satisfying the emission reduction target requires devoting a larger share of final output to producing energy services, a real resource drain captured in the GDP definition but excluded from raw output Y.
What does the energy efficiency scenario imply, and what is its key caveat?
If energy efficiency improves at 1.49% per year over 25 years (a 45% cumulative gain in energy-producing-firm total factor productivity), the required tax falls to 136.3%, the price of energy declines by 5.5% (rather than rising 49%), and GDP rises 1.1% rather than falling 9.3%. The poor agent benefits more from the efficiency gains and accumulates assets worth 4% of annual income rather than debt. The critical caveat is that the efficiency improvement is modeled as purely exogenous and costless. The paper explicitly acknowledges that achieving these efficiency gains may require investment that is not modeled, so the results should be interpreted as an upper bound on the offsetting potential.
How does the paper relate to and differ from the most closely related prior work?
Ascari et al. (2025) is the closest related paper (developed independently). Differences: (i) Ascari et al. use a Bewley-type incomplete-markets model generating heterogeneity through random discount factors, whereas this paper uses a two-agent complete-markets construct with exogenously fixed initial wealth; (ii) this paper allows endogenous labor supply, which increases short-run flexibility; (iii) this paper does not consider transfer schemes to redistribute away from distributional consequences. Results are described as broadly consistent. Fried, Novan, and Peterman (2018) and Boehl and Budianto (2024) use OLG models and find inequality implications but focus on inter-generational rather than intra-generational distributional effects.
What are the policy implications and their scope conditions?
The core implications are: (1) the Fit-for-55 emission tax alone is regressive — the poor bear a welfare loss 50% larger than the rich and end up with 38.8% of annual income in additional debt; (2) delaying tax implementation (with early announcement) is welfare-improving in the absence of climate damage modeling — the welfare difference is nearly 3.5 percentage points for the poor between fastest and latest implementation; (3) if energy efficiency targets are met exogenously, the transition is nearly costless and distributional concerns vanish; (4) the regressive result is conditional on the government recycling tax revenues to green-technology subsidies rather than to household transfers. All these implications are conditional on European economies where climate damages are plausibly small and the model abstracts from open-economy dynamics, endogenous technology, and within-income-group heterogeneity.
What robustness checks are reported?
Five robustness exercises are reported: (1) investment adjustment costs raised from χ = 0 to χ = 10 — minimal effect on welfare or quantities in the smooth baseline, though sudden tax introduction produces a brief interest-rate plunge; (2) homothetic preferences counterfactual while maintaining initial expenditure shares (Section 4.4); (3) elasticity of substitution between brown and green technology at ρE = 2 and ρE = 5 (Section 4.3, Table 2); (4) alternative transition timing (1 year, 12.5 years, 25 years post-announcement; Section 4.2); (5) simultaneous energy efficiency improvement of 1.49% per year (Section 4.5). A New Keynesian extension with Rotemberg price adjustment costs and a Taylor rule (Appendix B) is also provided for robustness on inflation dynamics.
What are the main caveats or limitations acknowledged by the authors?
Climate damages are excluded, so the paper understates the case for early action and cannot provide a full welfare comparison between acting early and acting late. Energy efficiency improvement is modeled as exogenous and costless, overstating the net gain from that channel. The two-agent framework abstracts from within-group heterogeneity and overlapping generations. Open-economy dynamics are not modeled; the brown-technology structure serves as a reduced-form for energy imports but does not capture international price feedback. The elasticity of substitution between brown and green technology is uncertain, and results are nearly proportional to this parameter. The model has no endogenous innovation or directed technical change, limiting applicability to long-run transition analysis.
Key Concepts
Non-homothetic PIGL preferences: Preferences of the Price Independent Generalized Linearity class (Boppart 2014) where energy expenditure shares depend on income level, making energy a necessity good (share declining in income) and consumption goods a luxury. Parameter ε ∈ (0,1) controls non-homotheticity; ε = 0 recovers homothetic preferences. The paper calibrates γ = 0.639 from CEX data, implying an elasticity of substitution between consumption and energy goods of approximately 0.4.
Brown vs. green technology: Two imperfectly substitutable technologies for producing energy services within the model’s energy sector. The brown technology converts units of final output into energy services using a carbon-intensive (emission-producing) process; the green technology is emission-free. They enter a CES aggregator for energy production with elasticity ρE calibrated to 3. Imperfect substitutability means the green transition raises the cost of energy services even with subsidies to green technology.
Expenditure equivalent loss: The welfare metric used in the paper: the percentage change in expenditures in the initial steady state (without any tax) that would make an agent indifferent between remaining in the initial steady state and living through the actual transition path. Defined implicitly by equating flow utility at scaled initial expenditures to flow utility along the transition. Baseline results: -10.8% for the rich agent and -16.2% for the poor agent.
Tax on the brown technology: The policy instrument modeled as capturing the essence of EU ETS and national carbon schemes. It raises the unit cost of the emission-intensive energy input; revenue is recycled as a subsidy to the green technology within a balanced government budget rather than distributed to households. A 168% tax achieves the 85% emission reduction target in the baseline, implying fossil fuel prices nearly triple.
Endogenous final steady state: The model’s new steady state after the green transition is not predetermined; it depends on the wealth distribution that emerges endogenously during the transition. Because markets are complete and preferences are non-homothetic, different transition paths generate different terminal wealth distributions and therefore different aggregate outcomes in the new steady state. This prevents backward solution and requires a fully nonlinear transition path solver.
Energy expenditure share by income quintile: The empirical regularity, documented from Eurostat HFCS data (2015), that the bottom income quintile devotes more than twice the fraction of disposable income to energy (electricity, gas, fuels for personal transport) as the top quintile. This fact calibrates the non-homotheticity of preferences (targeting 18% for the poor agent and 7.5% for the rich agent) and motivates the paper’s focus on distributional consequences.
Elasticity of substitution between brown and green technology (ρE): The key production-side parameter governing how easily the energy sector can switch from fossil-fuel to clean inputs. Calibrated to ρE = 3 from Papageorgiou et al. (2017). Results are nearly proportional to this parameter: ρE = 5 halves and ρE = 2 roughly doubles the required tax, GDP losses, and welfare costs. The paper identifies this as the dominant source of quantitative uncertainty.