H Heuristics Digital Reports

H Heuristics · Digital Report № 2026-11 · September 2026

Air Quality Improvement as a Co-Benefit of Clean Energy Transition in Megacities

How decarbonization saves millions of lives through pollution reduction every year

The same fires that heat the planet fill the lungs of the world's largest cities. Put them out for the climate, and the cities collect the health dividend first — within days, locally, and every year after.

AuthorHunter Hughes
InstitutionH Heuristics
Published15 September 2026
Report №2026-11
Reading time24 min

Abstract

Air pollution contributed to 7.9 million deaths worldwide in 2023 according to the State of Global Air 2025, and 86 per cent of them were from noncommunicable diseases. A modelling study in The BMJ attributes 5.13 million excess deaths a year (95 per cent interval 3.63 to 6.32 million) specifically to ambient air pollution from fossil-fuel use — deaths that could potentially be avoided by phasing out fossil fuels, and 82 per cent of the maximum that could be averted by controlling all anthropogenic emissions. The burden concentrates in cities: in 2019 about 86 per cent of urban inhabitants, some 2.5 billion people across 13,160 urban centres, lived above the World Health Organization's former 10 µg/m³ guideline, with 1.8 million attributable deaths. The world now has thirty-three megacities, nineteen of them in Asia, and the most polluted major cities — Delhi at 108.3 µg/m³ in 2024, Lahore at 102.1, Dhaka at 78 — sit fifteen to twenty-two times above the current 5 µg/m³ guideline.

The report's central claim is that urban air pollution and greenhouse-gas emissions are, for the most part, the same problem measured in two units. Source-apportionment studies compiled for the WHO find that traffic contributes about 25 per cent of urban PM2.5 globally, industry including power generation 15 per cent, domestic fuel burning 20 per cent, and unspecified human sources — largely secondary particles formed from combustion gases — a further 22 per cent; natural dust and sea salt account for only 18 per cent. Deaths per unit of electricity make the same point at the level of the generating plant: about 24.6 per terawatt-hour for coal and 18.4 for oil, against 0.02 to 0.04 for solar, nuclear and wind. Replacing combustion therefore removes the carbon and the co-emitted pollutants together, and the health return does not wait for the climate return: it arrives locally, within days of the change, in the city where the fuel was burned.

The evidence on the size of that return is consistent across methods. Global modelling finds greenhouse-gas mitigation avoiding 0.5, 1.3 and 2.2 million premature deaths in 2030, 2050 and 2100, with avoided mortality worth US$50 to US$380 per tonne of carbon dioxide — above marginal abatement costs in 2030 and 2050, and ten to seventy times the marginal cost in East Asia in 2030. Accelerating reductions enough to move from a 2 °C to a 1.5 °C pathway prevents 153 million premature deaths over the century, with more than a million in many individual metropolitan areas of Asia and Africa. The health damage of PM2.5 was valued at US$8.1 trillion in 2019, 6.1 per cent of global output, and the United States Clean Air Act Amendments were estimated to deliver benefits exceeding costs more than thirty to one while preventing over 230,000 early deaths in 2020.

Four megacity cases show both the reach and the limits of the dividend. Beijing cut annual PM2.5 from 89.5 to 30.5 µg/m³ between 2013 and 2024, and China's national clean-air measures avoided an estimated 0.41 million deaths in 2017 relative to 2013, mostly through industrial standards, boiler upgrades, capacity closures and residential fuel switching. London's Ultra Low Emission Zone lowered roadside nitrogen dioxide by an estimated 54 per cent in central London against a no-scheme counterfactual, yet cut carbon dioxide by only two per cent — evidence that the co-benefit runs strongly from decarbonization to clean air but weakly in reverse. Shenzhen electrified all 16,359 of its buses by 2017, and Delhi's court-ordered conversion of its public fleet to compressed natural gas improved air quality before growth elsewhere overtook it. The report concludes with recommendations for national governments, city authorities, development finance and health agencies, the most important of which is to appraise and sequence the transition by exposure reduced rather than by tonnes of carbon alone.


Executive Summary

The energy transition is usually justified by what it prevents decades from now. In the world's largest cities, its first and most measurable return is the air people breathe this year.

FINDING 01

Millions of deaths share a source with carbon

Air pollution contributed to 7.9 million deaths in 2023. An estimated 5.13 million excess deaths a year are attributable to ambient pollution from fossil-fuel use alone — deaths a transition away from combustion would remove, alongside the carbon.

FINDING 02

The dividend is local and immediate

Carbon's harm is global and slow; particulate and nitrogen dioxide harm is local and fast. A city that retires a coal plant or electrifies its buses captures the health benefit itself, within days — no international agreement or century-long wait required.

FINDING 03

The health value alone can pay for it

Avoided deaths from cleaner air are worth an estimated US$50–380 per tonne of CO2 abated — above marginal abatement costs in 2030 and 2050, and ten to seventy times the cost in East Asia. On health grounds alone, much of the transition clears the bar.

The world has thirty-three megacities, up from eight in 1975, and nineteen of them are in Asia. They are where combustion is densest — traffic, power stations, industrial boilers, diesel generators and household stoves packed into a few hundred square kilometres — and where the most people breathe the result. The five most polluted major cities in 2024, home to more than 96 million people, recorded annual fine-particulate concentrations between nine and twenty-two times the World Health Organization's guideline.

The argument of this report is simple and, on the evidence, well supported. Most of what poisons megacity air comes out of the same exhaust pipes and chimneys as the carbon dioxide that warms the planet. Replacing combustion with clean electricity — rather than filtering it — removes both at once. The climate benefit is shared by everyone, everywhere, over centuries. The health benefit is collected by the city that acts, starting immediately. That asymmetry makes decarbonization one of the few climate policies whose most visible payoff lands inside a single mayor's term.

7.9m
Deaths worldwide in 2023 to which air pollution contributed; 86% were from noncommunicable diseases
State of Global Air 2025
5.13m
Excess deaths a year attributable to ambient air pollution from fossil fuels (range 3.63–6.32m)
Lelieveld et al., The BMJ (2023)
$8.1tn
Global cost of health damage from PM2.5 exposure in 2019 — 6.1% of world GDP
World Bank (2022)
153m
Premature deaths avoided this century by moving from a 2 °C to a 1.5 °C emissions pathway
Shindell et al., Nature Climate Change (2018)

The report proceeds in seven parts. Section 1 sets out the scale and concentration of the urban burden. Section 2 shows why urban air pollution and greenhouse-gas emissions are, for the most part, the same problem. Section 3 reviews the evidence on how many lives decarbonization saves and what they are worth. Section 4 examines four megacities — Beijing, London, Shenzhen and Delhi — for what worked and what did not. Section 5 draws out design principles, Section 6 makes recommendations by actor, and Section 7 concludes.

The climate benefit of a coal plant's closure is shared by the whole planet over a century. The health benefit is collected by the city downwind, starting next week. The co-benefit asymmetry

1. The Urban Air Pollution Burden

Air pollution is the world's leading environmental risk to health, and it is concentrated where population and combustion are concentrated: in large cities.

1.1 A global burden, measured in millions

The Health Effects Institute's State of Global Air 2025 finds that air pollution contributed to 7.9 million deaths in 2023, making it the leading environmental risk factor for death worldwide. The character of that burden is often misunderstood. It is not principally a matter of acute respiratory attacks: 6.8 million of the deaths, 86 per cent, were from noncommunicable diseases — heart disease, stroke, chronic obstructive pulmonary disease, lung cancer, diabetes — and more than 625,000 were related to dementia. More than 675,000 were children under five. And 36 per cent of the world's population lives above 35 µg/m³ of PM2.5, the least stringent of the WHO's interim targets, seven times its 5 µg/m³ guideline.

A separate estimate isolates the part that energy policy can reach. Lelieveld and colleagues, writing in The BMJ, estimate all-cause excess deaths from fine particulates and ozone at 8.34 million a year, and attribute 5.13 million (95 per cent interval 3.63 to 6.32 million) specifically to ambient pollution from fossil-fuel use. Those deaths, in the authors' framing, could potentially be avoided by phasing out fossil fuels. Just over half of the burden (52 per cent) is cardiometabolic, led by ischaemic heart disease at 30 per cent; stroke and chronic obstructive pulmonary disease account for 16 per cent each.

1.2 Concentrated in cities

A study of 13,160 urban centres by Southerland and colleagues in The Lancet Planetary Health found that in 2019 approximately 86 per cent of urban inhabitants — 2.5 billion people — lived above the WHO's former 10 µg/m³ guideline, resulting in an excess of 1.8 million deaths (95 per cent interval 1.34 to 2.3 million). Two further findings in that study matter for policy. Attributable deaths rose in every region except Europe and the Americas between 2000 and 2019. And in some cities mortality rose even as concentrations fell, because ageing populations and rising rates of noncommunicable disease made each microgram more lethal. A megacity that holds its air quality steady while its population ages is losing ground.

That population is growing and concentrating. The UN's World Urbanization Prospects 2025 counts 33 megacities of more than ten million people, up from eight in 1975, with nineteen in Asia. Jakarta, with nearly 42 million residents, is now the largest, followed by Dhaka with almost 40 million and Tokyo with 33 million.

Figure 1 — Annual PM2.5 in the most polluted major cities, 2024

Annual average PM2.5 in µg/m³. The five most polluted major cities are from the IQAir 2024 World Air Quality Report; Beijing's value is the official 2024 municipal average reported by the State Council Information Office, shown for comparison and drawn from a different monitoring network. Dashed references mark the WHO's 35 µg/m³ interim target and 5 µg/m³ guideline.

1.3 Deaths even at "moderate" levels

It would be a mistake to read the burden as confined to the handful of cities at the top of Figure 1. A causal multi-city study of ten Indian cities in The Lancet Planetary Health found that between 2008 and 2019, 7.2 per cent of all deaths — about 33,000 a year — could be linked to short-term PM2.5 exposure above the WHO's 24-hour guideline of 15 µg/m³. Each 10 µg/m³ increase in short-term exposure was associated with a 1.42 per cent increase in daily deaths. Delhi had the largest attributable fraction, but Mumbai, with around a third of Delhi's annual PM2.5, still recorded over 5,000 attributable deaths a year. There is no evident threshold below which cleaner air stops paying.

Nor is PM2.5 the only urban pollutant that matters. Nitrogen dioxide, emitted overwhelmingly by road traffic and combustion, was associated with an estimated 4 million new cases of paediatric asthma each year between 2010 and 2015 across 194 countries and 125 major cities, according to Achakulwisut and colleagues. Because NO2 falls off sharply with distance from the road, its burden is almost entirely urban, and its source is almost entirely combustion.

Why estimates differ

The 7.9 million, 8.34 million and 5.13 million figures in this section come from different studies using different years, exposure–response functions and source definitions. They are not additive, and differences between them reflect method as much as change in the world. What is robust across all of them is the order of magnitude — millions of deaths a year — and the dominance of combustion as the source.


2. One Source, Two Problems

Urban air pollution and greenhouse-gas emissions are largely the same activity measured in two different units. That is what makes the co-benefit so large.

2.1 Most of the avoidable burden is fossil fuel

The most direct evidence comes from the same BMJ study. Its estimate of 5.13 million fossil-fuel-attributable deaths corresponds to 82 per cent of the maximum number of air pollution deaths that could be averted by controlling all anthropogenic emissions. Put the other way: of everything human beings could do about the air they have polluted, more than four-fifths of the mortality benefit lies in ending the combustion of coal, oil and gas. The remainder comes from sources such as agriculture, open burning and some industrial processes; natural sources such as desert dust sit outside human control altogether.

Figure 2 — How much of the air pollution death toll a fossil-fuel phase-out reaches

Excess deaths per year from PM2.5 and ozone, millions. The all-cause and fossil-fuel figures are from Lelieveld et al. (2023). The middle bar is derived by the author from the published statement that 5.13 million equals 82 per cent of the deaths avoidable by controlling all anthropogenic emissions (5.13 ÷ 0.82 ≈ 6.26).

2.2 What megacity air is made of

Source apportionment — chemically fingerprinting the particles on a filter and tracing them back to their origins — tells the same story from the ground up. A systematic review of such studies compiled for the World Health Organization by Karagulian and colleagues estimated that, globally, 25 per cent of urban PM2.5 comes from traffic, 15 per cent from industry including power generation, 20 per cent from domestic fuel burning, 22 per cent from unspecified sources of human origin, and 18 per cent from natural dust and sea salt. The "unspecified" category consists mostly of secondary particles — sulphates, nitrates and organic aerosol formed in the atmosphere from sulphur dioxide, nitrogen oxides and volatile compounds that are themselves largely products of combustion.

Figure 3 — Sources of urban PM2.5, by region

Population-weighted share of urban ambient PM2.5 by source category, per cent. From Table 3 of Karagulian et al. (2015), Atmospheric Environment 120. Rural and remote monitoring sites are excluded. "Other human" is the study's "unspecified sources of human origin", largely secondary particles from combustion gases.

The regional variation in Figure 3 is itself a guide to where the transition pays fastest. Traffic is the largest identified source in India (37 per cent), South-Eastern Asia (36 per cent) and Southern Asia (34 per cent) — regions containing many of the world's fastest-growing megacities. Domestic fuel burning dominates in Africa (34 per cent). Industry, including power generation, contributes 27 per cent in Southern Asia and the Middle East. In each case, the leading human source is a form of combustion that clean electricity can replace: vehicles with electric drives, household stoves with electric or gas cooking, boilers and generating plants with renewable power.

2.3 The deadliest and the safest electricity

The same arithmetic holds at the level of the power plant. Our World in Data's compilation of deaths per terawatt-hour of electricity, combining accidents and air pollution, puts coal at 24.6 and oil at 18.4, against 0.04 for wind, 0.03 for nuclear and 0.02 for solar. Coal is roughly 1,230 times deadlier than solar per unit of electricity. One terawatt-hour is about the annual electricity consumption of 150,000 people in the European Union — a small city.

Figure 4 — Deaths per terawatt-hour of electricity, by source

Deaths from accidents and air pollution per terawatt-hour of electricity produced. Logarithmic scale — each gridline is ten times the one before. From Our World in Data. Hydropower's rate is dominated by a single dam failure in 1975.

2.4 Where the transition cuts the pathway

Figure 5 sets out the mechanism. Combustion in the city emits two streams. Carbon dioxide rises into the global atmosphere, where it accumulates for centuries and harms everyone slowly. The co-emitted pollutants — primary particles, nitrogen oxides, sulphur dioxide and ozone precursors — stay near the ground, within the city and its region, and are breathed within hours or days. A measure that replaces the combustion cuts both streams at their common source. A measure that only filters exhaust cuts the second stream and leaves the first untouched.

Figure 5 — One fire, two streams: where clean energy intervenes

One fire, two streams Four urban combustion sources — road vehicles, power and industry, household fuels, and diesel generators and boilers — each feed a single combustion node. From that node, one stream of carbon dioxide rises to the global atmosphere, causing slow, shared climate harm over centuries. A second stream of fine particles, nitrogen oxides, sulphur dioxide and ozone precursors stays at ground level, producing local exposure within hours to days and leading to heart disease, stroke, lung disease and childhood asthma in the city. Clean energy substitution acts at the source and cuts both streams; end-of-pipe filters act only on the local stream. URBAN COMBUSTION SOURCES Road vehicles Power and industry Household fuels Generators and boilers Burning fossil fuel CO₂ → global atmosphere Accumulates for centuries Harm: shared, slow, global PM2.5 · NOₓ · SO₂ · ozone Breathed within hours to days Heart disease, stroke, COPD, childhood asthma — in the city Clean energy substitution acts at the source: cuts both streams End-of-pipe filters cut the local stream only Conceptual schematic. Stream widths are not to scale.

A conceptual schematic, not a quantitative model. Secondary particles form in the air from the local stream's gases, which is why they appear in source apportionment as "other human" rather than under a named source.

Table 1 — Transition measures and the pollution they remove

Sector Transition measure Pollutants cut Why it matters for exposure
Road transport Electric buses, two- and three-wheelers, taxis and delivery fleets; transit and cycling NO2, primary PM2.5, black carbon, ozone precursors Emitted at breathing height, metres from pedestrians, homes and schools
Power generation Retiring coal and oil plants in and near cities; solar, wind and storage SO2, NOx, PM2.5 (much of it secondary) Largest single point sources; plumes travel regionally into neighbouring cities
Buildings Electric or clean-fuel cooking; heat pumps replacing coal and oil heating PM2.5, carbon monoxide, black carbon Exposure indoors and in dense neighbourhoods, falling hardest on women and children
Industry Electrified low- and medium-temperature heat; closing obsolete boilers and kilns SO2, PM2.5, NOx Often sited in or beside the urban core in fast-industrialising economies
Backup power Reliable grids and battery storage replacing diesel generators PM2.5, NO2, black carbon Dispersed, unregulated and at street level wherever the grid is unreliable

Compiled by the author from the source categories in Karagulian et al. (2015) and the pollutant pathways in Figure 5.


3. How Many Lives Decarbonization Saves

Across different models, scenarios and decades, the evidence converges: the air-quality benefit of cutting carbon is measured in millions of lives, and its value rivals or exceeds the cost of the cuts.

3.1 Global mitigation scenarios

The foundational estimate is West and colleagues in Nature Climate Change. Simulating global greenhouse-gas mitigation against a reference scenario, they find it avoids 0.5 ± 0.2 million premature deaths in 2030, 1.3 ± 0.5 million in 2050, and 2.2 ± 0.8 million in 2100. The annual toll avoided grows as the cleaner capital stock accumulates and as populations age and urbanise.

Figure 6 — Premature deaths avoided each year by global mitigation

Millions of premature deaths avoided per year relative to a reference scenario, shown as the published central estimate (bar) with its reported ± uncertainty (whiskers). From West et al. (2013).

The same study values that benefit. Global average marginal co-benefits of avoided mortality are US$50–380 per tonne of CO2, which exceed marginal abatement costs in 2030 and 2050. In East Asia, the region containing the largest cluster of megacities, co-benefits in 2030 are ten to seventy times the marginal cost of abatement. Read plainly, that means a large share of near-term emission cuts in Asian economies would be justified on public-health grounds even if climate change did not exist.

3.2 The value of going faster

Speed matters because the health benefit arrives with the emission cut, not with the temperature outcome. Shindell and colleagues modelled the effect of cutting an additional 180 billion tonnes of carbon from 21st-century emissions — enough to shift a standard 2 °C pathway to 1.5 °C, or to reach 2 °C without relying on negative-emissions technology. The reduced air pollution yields 153 ± 43 million fewer premature deaths worldwide, with about 40 per cent occurring in the next forty years.

The study's geographic detail is what makes it a megacity finding. More than a million premature deaths would be prevented in each of many metropolitan areas in Asia and Africa, and more than 200,000 in individual urban areas on every inhabited continent except Australia. The benefits of accelerating climate policy, in other words, are not diffused thinly across the planet. They are concentrated in precisely the places with the most people and the dirtiest air.

3.3 The economic value

Two further estimates frame the scale in money. The World Bank's Global Health Cost of PM2.5 Air Pollution put the cost of health damage from fine-particulate exposure at US$8.1 trillion in 2019, equivalent to 6.1 per cent of global GDP, drawing on Global Burden of Disease estimates of 6.4 million deaths from PM2.5 that year. The International Monetary Fund's accounting of fossil-fuel subsidies reaches a related conclusion from the other side: most of the roughly US$7.4 trillion it counts is implicit — the unpriced cost of local air pollution and climate damage — borne by households' health rather than by treasuries.

The best retrospective evidence that clean-air regulation pays comes from the United States. The Environmental Protection Agency's second prospective study of the Clean Air Act Amendments estimated that their benefits exceed costs by a factor of more than thirty to one, and that in 2020 alone they would prevent over 230,000 early deaths. About 85 per cent of the monetised benefit came from reduced mortality associated with lower particulate matter.

$50–380
Health value of avoided deaths per tonne of CO2 abated, globally averaged
West et al. (2013)
10–70×
East Asian health co-benefits relative to marginal abatement cost in 2030
West et al. (2013)
>30:1
Ratio of benefits to costs for the US Clean Air Act Amendments, 1990–2020
US EPA
6.1%
Share of global GDP lost to the health damage of PM2.5 exposure in 2019
World Bank (2022)

An important qualification: cleaner air can unmask some warming

Sulphate particles from coal and oil combustion reflect sunlight, and on the IPCC's assessment human aerosols currently mask roughly half a degree of warming (Carbon Brief). Removing them brings a short-term warming penalty. This is not an argument for keeping the pollution, which kills millions every year, and it cannot be: a mask made of short-lived particles cannot hold back an accumulating stock of carbon. It is an argument for switching fuels rather than only scrubbing exhaust, because fuel switching removes the carbon along with the cooling particles, while end-of-pipe controls remove the cooling and none of the carbon. An earlier report in this series examines this asymmetry in detail.


4. Megacity Case Studies

Four cities show what cleaner air looks like in practice — how quickly it can come, which instruments deliver it, and what happens when the job is left half done.

4.1 Beijing: the fastest large-city clean-up on record

In 2013, a winter of extreme smog in northern China prompted the national Air Pollution Prevention and Control Action Plan and Beijing's own five-year clean air plan. The results are among the most dramatic ever recorded for a megacity. According to the State Council Information Office, Beijing's annual average PM2.5 fell from 89.5 µg/m³ in 2013 to 30.5 µg/m³ in 2024, a reduction of about two-thirds. Heavily polluted days fell from 58 to two, and days with good air quality rose by 114 to 290.

89.5 → 30.5
Beijing annual PM2.5, µg/m³, 2013 to 2024
State Council Information Office
58 → 2
Heavily polluted days a year in Beijing, 2013 to 2024
State Council Information Office
0.41m
PM2.5-attributable deaths avoided across China in 2017 relative to 2013
Zhang et al., PNAS (2019)

Nationally, Zhang and colleagues estimate in PNAS that the measures prevented about 0.41 million deaths in 2017 relative to 2013. Four measures did most of the work, together accounting for 0.37 million, or 92 per cent, of the avoided deaths.

Figure 7 — What cleaned China's air, 2013–2017

Contribution of each measure to the decline in national population-weighted PM2.5 in 2017, µg/m³. From Zhang et al. (2019). Together these four measures account for 92 per cent of avoided deaths.

Beijing's lesson cuts two ways, and both matter. It proves that megacity air can improve very fast when the political will is present. But most of China's early gains came from end-of-pipe controls and closing obsolete capacity rather than from decarbonization: tighter emission standards and upgraded boilers cut pollutants from plants that continued to burn coal. Residential fuel switching — replacing household coal with gas and electricity — was the measure closest to a transition, and even it contributed a substantial 2.2 µg/m³. As the cheap controls are exhausted, Beijing's remaining distance to the WHO guideline — still six times over — will have to come increasingly from replacing combustion itself.

4.2 London: a clean-air instrument, and its carbon limits

London's Ultra Low Emission Zone charges the most polluting vehicles to enter a zone that began in central London in 2019 and was extended to the whole of Greater London in 2023. The Greater London Authority's One Year Report estimates that, in 2024, roadside NO2 concentrations were 27 per cent lower across London than they would have been without the scheme and its expansions, and 54 per cent lower in central London. The benefits were progressive: for some of the most deprived communities living near London's busiest roads, the report estimates an 80 per cent reduction in people exposed to illegal levels of pollution.

Figure 8 — Roadside NO2 reduction in 2024 due to all phases of the ULEZ

Per cent reduction in roadside nitrogen dioxide concentrations compared with a modelled scenario without the ULEZ and its expansions. From the London-wide ULEZ One Year Report (March 2025).

London also demonstrates the direction in which the co-benefit flows. Over 2019–2024, the scheme is estimated to have reduced London's nitrogen oxide emissions by 24 per cent and exhaust PM2.5 by 29 per cent — but carbon dioxide by only two per cent. That is not a failing of the ULEZ, which was designed as an air-quality measure and succeeded as one. It is evidence of the asymmetry at the heart of this report. Replacing an older, non-compliant car with a newer, compliant one cleans the air but still burns fuel. Replacing combustion with electricity does both.

Figure 9 — Emission reductions due to the ULEZ, cumulative 2019–2024

Per cent reduction in London-wide emissions against a no-ULEZ scenario. The contrast between pollutants and CO2 shows that cleaner vehicles are not the same as fewer combustion engines. Same source as Figure 8.

4.3 Shenzhen: electrifying a megacity's buses

By the end of 2017, Shenzhen had put 16,359 electric buses on its streets, becoming the first city in the world to electrify its entire bus fleet (World Resources Institute). The fleet was larger than the electric bus fleets of New York, Los Angeles, New Jersey, Chicago and Toronto combined.

The logic generalises to every megacity. The World Resources Institute notes that diesel buses make up about 0.5 per cent of a city's vehicle fleet yet account for around 20 per cent of its transport emissions, because they run far longer and further than private cars — and they do so on the busiest streets, at the height of pedestrians' lungs. A publicly procured, centrally depot-charged bus fleet is the most concentrated, most controllable piece of urban combustion there is. Shenzhen's case shows it can be replaced in a few years with a single procurement decision, backed by public finance.

4.4 Delhi: a transition begun and outgrown

Delhi was a pioneer. In 1998 India's Supreme Court ordered the city's entire bus, taxi and auto-rickshaw fleet to switch to compressed natural gas, and diesel buses had almost entirely left the streets by late 2002. Analysis by Resources for the Future found that converting the buses reduced concentrations of PM10, carbon monoxide and sulphur dioxide; converting three-wheelers from petrol yielded less, possibly because of poor technology.

Yet in 2024 Delhi was the most polluted major city in the world, at 108.3 µg/m³. The CNG programme was a fuel switch within fossil fuels, confined to public transport, while the city's other sources — among them growing private traffic, industry, construction and pollution carried in from beyond its boundaries — were not tackled on the same scale. Delhi's experience is the clearest warning in the megacity record: a single-sector switch, however bold, is eroded by growth everywhere else. The gains are durable only when the transition covers every major combustion source and extends across the airshed, not merely the municipality.

Table 2 — Four megacities compared

City Main instrument Measured outcome Lesson
Beijing National action plan: industrial standards, boiler upgrades, capacity closures, residential coal replacement PM2.5 89.5 → 30.5 µg/m³ (2013–2024); 0.41m deaths avoided nationally in 2017 Rapid gains are possible; the next increment requires replacing combustion, not only cleaning it
London Ultra Low Emission Zone charging polluting vehicles Roadside NO2 54% lower in central London in 2024; CO2 2% lower over 2019–2024 Air-quality policy delivers clean air but little carbon; decarbonization delivers both
Shenzhen Full electrification of the public bus fleet 16,359 electric buses by the end of 2017 Publicly controlled fleets are the fastest combustion to eliminate
Delhi Court-ordered conversion of public transport to CNG Lower PM10, CO and SO2 from bus conversion; 108.3 µg/m³ in 2024 One sector's switch is overtaken by growth unless the transition covers the whole airshed

Outcomes as reported in the sources cited in Sections 4.1–4.4. Measures and time periods differ between cities and are not directly comparable.


5. Designing the Transition for Health

Every tonne of carbon abated is equal for the climate. It is not equal for health. A transition planned with that in mind saves far more lives for the same climate result.

5.1 Sequence by exposure, not only by tonnes

Climate planning treats a tonne of CO2 as a tonne wherever it is emitted, and for the climate that is correct. For health, what matters is how much of the co-emitted pollution reaches human lungs, and that depends on where the combustion occurs. Exhaust from a bus on a crowded street, a diesel generator in a market or a stove in a kitchen is breathed at far higher rates than emissions from a tall stack outside the city. A transition sequenced by tonnes alone may retire a remote plant first and leave the street-level sources for later. A transition sequenced by exposure starts where the combustion is closest to people — buses, taxis, two- and three-wheelers, household fuels, backup generators and in-city plants — and saves more lives per tonne abated in its early years.

5.2 Retire, do not merely retrofit

Pollution controls on a coal plant can cut its particulate and sulphur emissions substantially, and where a plant must keep running they are worth installing. But research in Nature Climate Change finds that the health co-benefits of climate mitigation depend on strategic power plant retirements and pollution controls — which plants close first, and whether controls are in place on those that remain. Retirement removes every pollutant and all the carbon; retrofits remove some pollutants and no carbon, and, as Section 3 noted, remove the cooling aerosol along with them. Where a city's air is dominated by nearby coal, the plants whose plumes reach the most people should be first in the retirement queue.

5.3 Count the health dividend in the appraisal

If avoided deaths are worth US$50–380 per tonne of CO2, a project appraisal or national climate plan that omits them understates the return of clean energy by a margin that can exceed the carbon price itself. That omission is routine. Ministries of finance appraise energy investments on energy costs, environment ministries count carbon, and health ministries — which bear the cost of pollution-related disease — are rarely at the table. Bringing the health value into appraisal would move a large share of urban clean-energy investment from "costly climate measure" to "high-return public-health investment," which is what, on the evidence, it is.

5.4 Plan at the scale of the airshed

Air does not respect municipal boundaries. A megacity's pollution includes secondary particles formed from gases emitted by power plants, industry and agricultural burning tens or hundreds of kilometres away, and its own emissions travel to its neighbours. London's scheme lowered NO2 within five kilometres beyond the Greater London boundary by an estimated 14 per cent; Delhi's clean-up was undone in part by sources it did not control. City transitions need regional counterparts, and national grids decarbonizing at the same time, or the local dividend leaks away.

5.5 Put the benefit where the burden is

Pollution exposure falls hardest on the poor — those living beside major roads, in informal settlements near industry, and in homes that still cook with solid fuels. London's ULEZ delivered its largest proportional benefits to its most deprived roadside communities. A transition that electrifies private cars for the affluent before it cleans public buses, or retires suburban plants before it replaces the stoves in low-income neighbourhoods, saves fewer lives and deepens inequity. The pollution–poverty–climate nexus discussed in an earlier report applies with particular force inside megacities.

A tonne of carbon is a tonne wherever it is burned. A lungful of exhaust is not. Sequence the transition by who breathes it. Designing for health

6. Policy Recommendations

What each of the principal actors should do to collect the health dividend of the transition in the world's largest cities.

6.1 National governments

6.2 City and metropolitan authorities

6.3 Development finance and investors

6.4 Health agencies and researchers


7. Conclusions

The transition is the largest public-health opportunity available to the world's megacities, and its dividend can be collected now.

Air pollution contributed to 7.9 million deaths in 2023, and more than five million a year are attributable to the burning of fossil fuels. That toll falls most heavily on the world's thirty-three megacities and the fast-growing cities that will join them, where combustion is concentrated and billions of people breathe the result. It is not an unavoidable cost of urban life. It is, for the most part, the local face of the same activity that is warming the planet.

That shared source is what makes the co-benefit so powerful. Replacing combustion with clean electricity removes the carbon and the co-emitted pollutants together, and the evidence on the value of doing so is remarkably consistent: hundreds of thousands to millions of deaths avoided each year, 153 million over the century from a faster pathway, and health benefits worth US$50–380 per tonne of carbon — enough, in much of Asia, to justify near-term emission cuts on public-health grounds alone.

The megacity record shows how quickly air can improve and what determines whether the gains last. Beijing cut its fine-particulate pollution by two-thirds in eleven years. London cleaned its roadside air while barely touching its carbon, proving that clean-air policy is not climate policy. Shenzhen electrified an entire bus fleet within a few years. Delhi showed that a bold switch in one sector is overtaken by growth unless the transition reaches every major source across the airshed.

The practical conclusion is to plan the transition for health as well as for carbon: to count the lives it saves in every appraisal, to sequence it by the exposure it removes, to retire the plants whose plumes reach the most people, to electrify the fleets cities control, and to put the benefit where the burden is heaviest. The climate return of decarbonization will be measured over generations. In the megacities, its health return can be measured this year, in lives.


References

Every quantitative claim above is attributed inline. The principal sources are collected here.


Metadata

Keywords
air qualityhealth co-benefitsclean energy transitiondecarbonizationmegacitiesPM2.5nitrogen dioxidefossil fuelspremature mortalityurban transport electrificationlow emission zonescoal phase-outBeijing clean air actionLondon ULEZDelhi air pollutionpublic health policy
Topics
Public Health Energy Transition Infrastructure Emerging Markets
JEL classification
Q53, I18, Q42, R41, Q58 — air pollution; government policy and regulation of health; alternative energy sources; urban transportation; environmental economics: government policy
Data and method
This report synthesises published estimates rather than producing new epidemiological modelling. Global burden figures are from the Health Effects Institute's State of Global Air 2025 (2023 data) and from Lelieveld et al. in The BMJ (2023) for the fossil-fuel-attributable share; urban exposure and mortality are from Southerland et al. in The Lancet Planetary Health (2022) and a causal multi-city study of ten Indian cities in the same journal (2024); megacity counts are from the UN World Urbanization Prospects 2025; city concentrations are from the IQAir 2024 World Air Quality Report, with Beijing's official series from China's State Council Information Office. Source shares are from Karagulian et al. in Atmospheric Environment (2015); deaths per unit of electricity from Our World in Data; co-benefit valuations from West et al. (Nature Climate Change, 2013) and Shindell et al. (Nature Climate Change, 2018); economic costs from the World Bank (2022) and the US EPA's second prospective study of the Clean Air Act. Case evidence is from Zhang et al. in PNAS (2019), the Greater London Authority's London-wide ULEZ One Year Report (March 2025), the World Resources Institute on Shenzhen and Resources for the Future on Delhi. All figures were verified against their sources in September 2026. Different studies use different years, exposure–response functions and monitoring networks, so their totals are not additive and are compared only where the report says so; the 6.26 million all-anthropogenic figure in Figure 2 is derived by the author from the published 5.13 million and 82 per cent. Figure 5 is a conceptual schematic. The report is analytical rather than predictive.
Report
H Heuristics Digital Report № 2026-11 · Published 15 September 2026
Licence
CC BY-NC-ND 4.0
Cite as
Hunter Hughes (2026). Air Quality Improvement as a Co-Benefit of Clean Energy Transition in Megacities: How decarbonization saves millions of lives through pollution reduction every year. H Heuristics Digital Report 2026-11. https://digitalreports.hheuristics.com/reports/megacity-air-quality-clean-energy/
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