Background
From dollars per tonne to dollars per degree
Four short notes for readers new to abatement cost curves. If you already know what a MACC is and why GWP₁₀₀ is contested, skip to the figures.
Abatement cost curves rank climate action by price
A marginal abatement cost curve (MACC) lines up mitigation measures from cheapest to most expensive, so policymakers can see how much can be done, and at what price. The traditional version measures everything in dollars per tonne of CO₂-equivalent avoided.
CO₂-equivalent hides when the warming happens
Converting every gas to CO₂-equivalent with a 100-year Global Warming Potential flattens time. Methane and black carbon warm intensely but fade within years to a decade; CO₂ lingers for centuries. One equivalence number cannot capture both the size and the timing of their effects.
The target is temperature, not tonnes
With warming likely to overshoot 1.5 °C before declining, what matters for policy is the temperature path itself: how high the peak goes and how fast it comes back down. Short-lived pollutants are the fastest lever on that path, yet a tonnes-based curve makes them look marginal.
T-MACC prices measures in degrees avoided
The Temperature-MACC re-expresses each measure in dollars per degree of warming avoided, using pollutant-specific atmospheric lifetimes and warming potentials. The same measures reorder, and short-lived-pollutant and integrated measures rise to the top where near-term temperature is concerned.
The timing
Different pollutants warm on different clocks
The whole framework turns on one physical fact: a tonne cut today buys a different amount of near-term cooling depending on the gas. This is what a tonnes-based curve cannot see, and what pricing in degrees restores.
Why timing changes the ranking: three pollutants, three clocks
Each curve is the share of a pollutant’s near-term(20-year) temperature benefit that has actually arrived by year t, for a sustained cut starting now. Black carbon (~7-day lifetime) delivers essentially all of it within weeks; methane (12.4 years) most of it within a decade; CO₂’s benefit keeps accumulating for centuries, so at 20 years only a fraction of its eventual effect is in. For minimizing an overshoot peak, the fast forcers do the work.
Computed from each pollutant’s atmospheric burden build-up (§2.4): black carbon reaches 100% within a year, methane 79% by its 12.4-year lifetime, while CO₂ passes 221%of its 20-year value only by year 50 and keeps climbing. Curves are normalized to each gas’s own 20-year value to isolate timing from magnitude; the T-MACC then weights each by its warming potential.
View as table
| Year | Black carbon | Methane | CO₂ |
|---|---|---|---|
| 1.0 | 100% | 10% | 6% |
| 5.0 | 100% | 41% | 29% |
| 10.0 | 100% | 69% | 54% |
| 12.4 | 100% | 79% | 66% |
| 20.0 | 100% | 100% | 100% |
| 30.0 | 100% | 114% | 143% |
| 40.0 | 100% | 120% | 183% |
The curve
Every measure, ordered by cost per degree
The signature T-MACC figure, built live and filterable. Order measures cheapest first, give each a width equal to the temperature it avoids, and the cost-negative territory below the line becomes impossible to miss.
1.232 °C of mitigation, ordered by cost-effectiveness
The selected measures, laid out cheapest first. Width is temperature avoided, height is marginal cost. Bars below the line are cost-negative. Hover or tap a bar for detail; muted bars are avoided-upstream methane co-benefits.
Built live from the paper’s Table 1 (31itemized measures). The paper’s aggregate tables report 1.296 °C across a fuller 38-measure set; the small gap to the itemized total is Table 1-vs-Table 2 rounding in the source, kept rather than papered over.
The same measures as a league table
The breakdown
Where the degree comes from, and what it costs
The paper’s aggregate results: temperature reduction split by pollutant and by cost band. Together they make the central claim, that the majority of near-term cooling is both short-lived-pollutant driven and cheaper than inaction.
Where the degree comes from
The paper’s Table 2. Short-lived forcers, methane and black carbon, supply the majority of near-term temperature reduction, far out of proportion to their share of emissions.
CH₄ (avoided) is the upstream methane leakage eliminated when clean energy displaces gas and oil, a co-benefit invisible to combustion-only accounting.
View as table
| Pollutant | Direct (°C) | Avoided (°C) | Total (°C) | Share |
|---|---|---|---|---|
| CO₂ | 0.485 | – | 0.485 | 37% |
| CH₄ (direct) | 0.460 | – | 0.460 | 35% |
| CH₄ (avoided) | 0.000 | 0.102 | 0.102 | 8% |
| Black carbon | 0.184 | – | 0.184 | 14% |
| HFCs | 0.065 | – | 0.065 | 5% |
How much is already cheaper than doing nothing
The paper’s Table 3. Bars: temperature reduction available in each cost band. Line: the cumulative curve. The first band alone, measures that save money, delivers 0.946 °C.
22 of 38 measures are cost-negative, together worth 0.946 °C, most of the way to the 1.30 °C total before any net-cost measure is reached.
View as table
| Cost range | Measures | Reduction (°C) | Cumulative (°C) |
|---|---|---|---|
| < $0 | 22 | 0.946 | 0.946 |
| $0–25 | 8 | 0.249 | 1.195 |
| $25–50 | 3 | 0.055 | 1.250 |
| > $50 | 5 | 0.046 | 1.296 |
Applied case
A state methane portfolio, scored in temperature
The same temperature lens applied to real policy: state-level methane mitigation in Haryana, India, across six sectors and their alternative scenarios, using the AGTP method. Results are in micro-degrees Celsius, the global warming one state’s methane cuts avoid.
µ°C(micro-degrees Celsius) = 10⁻⁶ °C = 0.000001 °C. Values look small because they are the global temperature effect of one Indian state’s methane; they aggregate with every other source worldwide. Methane is potent but short-lived (~12-year lifetime), so cuts act fast.Temperature reduction by sector (2047, MAS)
Contribution of each sector’s Maximum-Ambition scenario in 2047. Livestock dominates Haryana’s methane temperature impact.
View as table
| Sector | ΔT 2047 (µ°C) |
|---|---|
| Livestock | 36.15 |
| Waste | 5.63 |
| Agriculture | 4.43 |
| Transport | 0.77 |
| Residential | 0.22 |
| Industry | 0.06 |
MAS impact timeline (2030–2047)
Avoided warming accumulates as reductions compound and the AGTP kernel integrates past cuts. Every point is a full AGTP convolution of the report’s emission series up to that year.
Alternative scenarios within a sector (2047)
Each sector has several ALT mitigation strategies; the Maximum Ambition Scenario picks the most effective one (highlighted). Choose a sector to compare its options.
Livestock MAS uses ALT 3: Purna Gau Charan Bhumi (open grazing of all dairy cattle).
How the temperature impact is calculated
The dashboard uses the AGTP (Absolute Global Temperature change Potential) approach: for each target year, it sums the temperature response of every past annual emission reduction, weighted by the pollutant’s decay, indirect feedbacks, and climate inertia.
- lag = target_year − emission_year
- AGTP kernel: temperature response per unit emission, set by methane’s ~12-year lifetime and radiative forcing
- find (indirect effects): ozone formation, stratospheric water vapor, CO₂ from oxidation. Combined ≈ 1.75×; slider above.
- Scenarios: BAU (business as usual), ALT 1–4 (alternatives), MAS (best ALT per sector)
- Emissions data: HSPCB / IGSD / TERI report (2025), sectoral CH₄ BAU + ALT reductions, 2019–2047
- Calibration: kernel scale set to the published 2047 total; 2040 reproduced within ~2% as an independent check
Mitigation scenario descriptions for Haryana
Each sector’s alternative (ALT) strategies. The scenario selected into the Maximum Ambition Scenario is highlighted.
LivestockMAS: ALT 3
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | Gausamvardhan (selective breed development) |
| ALT 2 | Limited Gau Charan Bhumi (indigenous cattle pasture grazing) |
| ALT 3 | Purna Gau Charan Bhumi (open grazing of all dairy cattle) |
WasteMAS: ALT 4
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | 32% diversion (waste-to-energy + MRFs) |
| ALT 2 | 40% diversion (compost, AD, RDF, recycling) |
| ALT 3 | 50% diversion (compost, AD, RDF, recycling) |
| ALT 4 | 60% diversion (compost, AD, RDF, recycling) |
AgricultureMAS: ALT 3
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | System of Rice Intensification (SRI), 5% annual adoption |
| ALT 2 | Natural Farming on SRI-converted land, 5% annual adoption |
| ALT 3 | ALT 1 + 2 + crop diversification (rice to non-rice), 5% annual |
TransportMAS: ALT 4
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | Electrification of bus fleet |
| ALT 2 | Vehicle scrappage policy (30/60/80%) |
| ALT 3 | Hydrogen blending in CNG (18% by 2047) |
| ALT 4 | EV policy for all new vehicles (50/70/100%) |
ResidentialMAS: ALT 3
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | Improved biomass cookstoves for non-LPG households |
| ALT 2 | Improved cookstoves 30% + biogas 30% + solar cooking 40% |
| ALT 3 | Phased transition to solar cooking (100% by 2047) |
IndustryMAS: ALT 2
| Scenario | Mitigation strategy |
|---|---|
| ALT 1 | Coal to natural gas in industrial boilers (raises CH₄) |
| ALT 2 | Community boilers, 30% fuel-consumption reduction |
| ALT 3 | Green hydrogen expansion (5% by 2040, 8% by 2047) |
Your portfolio
Build a temperature budget of your own
Pick a set of measures and watch the curve, the degree, and the bill recompute. Then see why a static price misleads: costs move down learning curves as deployment scales.
Assemble a temperature budget from the menu of measures
Tick measures on or off. The curve and the totals recompute live from the paper’s Table 1 values. Start from the cost-negative set (the default) and see how far a money-saving portfolio gets before you have to spend anything.
Why today’s costs mislead: the learning curve
A T-MACC is not static, because technology costs are not. Under Wright’s Law each doubling of cumulative production cuts unit cost by a fixed learning rate. Battery packs have tracked a ~19% rate for decades. Drag the rate and the production-growth assumption to project the $/kWh path the paper uses to move electric vehicles into cost-negative territory.
At a 19% learning rate and 24%/yr production growth, packs reach $25/kWhby 2045. The paper’s reference trajectory ($100 → $50 → $25/kWh, 2025–2045) assumes ≈19% and lands near $25. Leading manufacturers were already at $75–85/kWh in 2024, achieving cost parity 2–3 years ahead of projection. Reference rates: Solar PV 20% · Batteries 19% · Wind 15% · LED lighting 25%.
The method
The four steps behind this page
T-MACC rests on established climate physics: absolute global temperature potentials, pollutant-specific decay, and technology learning curves. What changes is the output unit, temperature, which makes the metric answer the question policymakers actually ask.
Emissions → temperature (AGTP)
Rather than integrate radiative forcing like GWP, the framework uses the Absolute Global Temperature Potential: the temperature change at a chosen time from a pulse emission (Aamaas et al. 2013; Fuglestvedt et al. 2010), summed over pollutants and years.
AGTPicarries each pollutant’s own atmospheric lifetime, so a tonne of black carbon and a tonne of CO₂ map to temperature on entirely different clocks.
Pollutant-specific decay
CO₂ persists across four sink timescales; short-lived forcers decay exponentially with a single lifetime (§2.4.2).
- GWP₂₀: CH₄ = 82, BC = 900, HFCs = 1000–4000 (AR6 Table 7.15)
- Climate sensitivity: 0.45 °C per 1000 GtCO₂e
Dynamic cost (Wright’s Law)
Costs fall predictably with cumulative production, so a static $/tonne understates fast- learning technologies. Each doubling cuts cost by the learning rate LR (§2.5.1).
- Solar PV 20% · Batteries 19% · Wind 15% · LED 25%
- Battery packs: $100/kWh (2024) → $25/kWh (2045) on the reference path
The temperature cost metric
Total implementation cost (net of co-benefits) is divided by total temperature reduction, converting the whole curve from $/tonne into $/°C avoided (§2.8.1).
- The reordering: a measure with high $/tCO₂e can have low $/°C if it targets a short-lived pollutant with high near-term warming.
- Co-benefits: health, agricultural and ecosystem values can exceed direct costs, turning positive-cost measures cost-negative.
Companion to the working paper “Temperature-Based Marginal Abatement Cost Curves: A New Framework for Climate Mitigation Prioritization” (v4). Values reproduce the paper’s Tables 1 to 3. Built with React and Recharts.