Government policies during the COVID-19 pandemic have drastically altered patterns of energy demand around the world. Many international borders were closed and populations were confined to their homes, which reduced transport and changed consumption patterns. Here we compile government policies and activity data to estimate the decrease in CO2 emissions during forced confinements. Daily global CO2 emissions decreased by –17% (–11 to –25% for ±1σ) by early April 2020 compared with the mean 2019 levels, just under half from changes in surface transport. At their peak, emissions in individual countries decreased by –26% on average. The impact on 2020 annual emissions depends on the duration of the confinement, with a low estimate of –4% (–2 to –7%) if prepandemic conditions return by mid-June, and a high estimate of –7% (–3 to –13%) if some restrictions remain worldwide until the end of 2020. Government actions and economic incentives postcrisis will likely influence the global CO2 emissions path for decades.
Before the COVID-19 pandemic of 2020, emissions of carbon dioxide were rising by about 1% per year over the previous decade1,2,3, with no growth in 20193,4 (see Methods). Renewable energy production was expanding rapidly amid plummeting prices5, but much of the renewable energy was being deployed alongside fossil energy and did not replace it6, while emissions from surface transport continued to rise3,7.
The emergence of COVID-19 was first identified on 30 December 20198 and declared a global pandemic by the World Health Organization on 11 March 2020. Cases rapidly spread, initially mainly in China during January, but quickly expanding to South Korea, Japan, Europe (mainly Italy, France and Spain) and the United States between late January and mid-February, before reaching global proportions by the time the pandemic was declared9. Increasingly stringent measures were put in place by world governments in an effort, initially, to isolate cases and stop the transmission of the virus, and later to slow down its rate of spread. The measures imposed were ramped up from the isolation of symptomatic individuals to the ban of mass gatherings, mandatory closure of schools and even mandatory home confinement (Table 1 and Fig. 1). The population confinement is leading to drastic changes in energy use, with expected impacts on CO2 emissions.
Despite the critical importance of CO2 emissions for understanding global climate change, systems are not in place to monitor global emissions in real time. CO2 emissions are reported as annual values1, often released months or even years after the end of the calendar year. Despite this, some proxy data are available in near-real time or at monthly intervals. High-frequency electricity data are available for some regions (for example, Europe10 and the United States11), but rarely the associated CO2 emissions data. Fossil fuel use is estimated for some countries at the monthly level, with data usually released a few months later1,12. Observations of CO2 concentration in the atmosphere are available in near-real time13,14, but the influence of the natural variability of the carbon cycle and meteorology is large and masks the variability in anthropogenic signal over a short period15,16. Satellite measurements for the column CO2 inventory17 have large uncertainties and also reflect the variability of the natural CO2 fluxes18, and thus cannot yet be used in near-real time to determine anthropogenic emissions.
Given the lack of real-time CO2 emissions data, we devise an alternative approach to estimate country-level emissions based on a confinement index (CI) conceived to capture the extent to which different policies affect emissions, and available daily data of activity for six economic sectors (Table 1 and Fig. 2). The change in CO2 emissions associated with the confinement is informative in multiple ways. First, the changes in emissions are entirely due to a forced reduction in energy demand. Although in this case the demand disruption was neither intentional nor welcome, the effect provides a quantitative indication of the potential limits that extreme measures could deliver with the current energy mix (for example, a higher rate of home working or reducing consumption). Second, during previous economic crises, the decrease in emissions was short-lived with a postcrisis rebound that restored emissions to their original trajectory, except when these crises were driven by energy factors such as the oil crises of the 1970s and 1980s, which led to substantial shifts in energy efficiency and the development of alternative energy sources19. For example, the 2008–2009 Global Financial Crisis saw global CO2 emissions decline of –1.4% in 2009, immediately followed by a growth in emissions of +5.1% in 201020, well above the long-term average. Emissions soon returned to their previous path almost as if the crisis had not occurred.
The economic crisis associated with COVID-19 is markedly different from previous economic crises in that it is more deeply anchored in constrained individual behaviour. At present it is unclear how long and deep the crisis will be, and how the recovery path will look, and therefore how CO2 emissions will be affected. Keeping track of evolving CO2 emissions can help inform government responses to the COVID-19 pandemic to avoid locking future emissions trajectories in carbon-intensive pathways.
In this analysis, we used a combination of energy, activity and policy data available up to the end of April 2020 to estimate the changes in daily emissions during the confinement from the COVID-19 pandemic, and its implications for the growth in CO2 emissions in 2020. We compared this change in emissions to the mean daily emissions for the latest available year (2019 for the globe) to provide a quantitative measure of relative change compared to pre-COVID conditions.
Changes in CO2 emissions were estimated for three levels of confinement and for six sectors of the economy, as the product of the CO2 emissions by sector before confinement and the fractional decrease in those emissions due to the severity of the confinement and its impact on each sector (equation (1) in Methods). The analysis is done over 69 countries, 50 US states and 30 Chinese provinces, which represent 85% of the world population and 97% of global CO2 emissions.
The confinement index (CI) is defined on a scale of 0 to 3 and allocates the degree to which normal daily activities were constrained for part or all of the population (Table 1). Scale 0 indicates no measures were in place, scale 1 indicates policies targeted at small groups of individuals suspected of carrying infection, scale 2 indicates policies targeted at entire cities or regions or that affect about 50% of society and scale 3 indicates national policies that substantially restrict the daily routine of all but key workers (Supplementary Extended Methods). During the early confinement phase around Chinese New Year in China (starting 25 January 2020), around 30% of global emissions were in areas under some confinement (Fig. 1). This increased to 70% by the end of February, and over 85% by mid-March when confinement in Europe, India and the United States started, as China relaxed confinement (Fig. 1). At its peak in early April, 89% of global emissions were in areas under some confinement.
The six economic sectors covered in this analysis are: (1) power (44.3% of global fossil CO2 emissions), (2) industry (22.4%), (3) surface transport (20.6%), (4) public buildings and commerce (here shortened to ‘public’, 4.2%), (5) residential (5.6%) and (6) aviation (2.8% (Methods)). We collected time-series data (mainly daily) representative of activities that emit CO2 in each sector to inform the changes in each sector as a function of the confinement level (Fig. 2). The data represent changes in activity, such as electricity demand or road and air traffic, rather than direct changes in CO2 emissions. We made a number of assumptions to cover the six sectors based on the available data and the nature of the confinement (Table 2, Methods and Supplementary Tables 1–11). Changes in the surface transport and aviation sectors were best constrained by indicators of traffic from a range of countries, which included both urban and nationwide data. Changes in power-sector emissions were inferred from electricity data from Europe, the United States and India. Changes in industry were inferred mainly from industrial activity in China and steel production in the United States. Changes in the residential sector were inferred from UK smart meter data, whereas changes in the public sector were based on assumptions about the nature of the confinement. All the activity changes are relative to typical activity levels prior to the COVID-19 pandemic (Supplementary Extended Methods).
Activity data show that the changes in daily activities at the country, state or provincial level were largest in the aviation sector, with a decrease in daily activity of –75% (–60 to –90%) during confinement level 3 (Table 2). Surface transport saw its activity reduce by –50% (–40 to –65%), whereas industry and public sectors saw their activity reduce by –35% (–25 to –45%) and –33% (–15 to –50%), respectively. Also during confinement level 3, power saw its activity decrease by a modest –15% (–5 to –25%) and the residential sector saw its activity increase by +5% (0 to +10%). Activity data also show substantial decreases in activity during confinement level 2, and only small decreases during confinement level 1 (Table 2).
Daily changes in CO2 emissions
The effect of the confinement was to decrease daily global CO2 emissions by –17 (–11 to –25) MtCO2 d−1, or –17% (–11 to –25%) by 7 April 2020 (Table 2 and Supplementary Table 12), relative to the mean level of emissions in 2019. The change in emissions on 7 April was the largest estimated daily change during 1 January to 30 April 2020. Daily emissions in early April are comparable to their levels of 2006 (Fig. 3). The values in MtCO2 d−1 are close to the value in percent coincidentally, because we currently emit about 100 MtCO2 d−1. For individual countries, the maximum daily decrease averaged to –26% (±7% for ±1σ). The maximum daily decrease did not occur during the same day across countries, and hence the country decreases are more pronounced than the global maximum daily decrease. Estimated changes quantify the effect of confinement only, and are relative to underlying trends prior to the COVID-19 pandemic. The daily decrease in global CO2 emissions during the pandemic is as large as the seasonal amplitude in emissions estimated from data published elsewhere21 (–17 MtCO2 d−1; M.J.W., manuscript in preparation), which results primarily from the higher energy use in winter than in summer in the Northern Hemisphere. The range in estimate reflects the range of parameter values (Table 2) based on the spread in the underlying data (Fig. 2).
Global emissions from surface transport fell by –36% or –7.5 (–5.9 to –9.6) MtCO2 d−1 by 7 April 2020 and made the largest contribution to the total emissions change (–43%; Fig. 4, Table 2 and Supplementary Table 12). Emissions fell by –7.4% or –3.3 (–1.0 to –6.8) MtCO2 d−1 in the power sector and by –19% or –4.3 (–2.3 to –6.0) MtCO2 d−1 in the industry sector. Emissions from surface transport, power and industry were the most affected sectors in absolute values, accounting for 86% of the total reduction in global emissions. CO2 emissions declined by –60% or –1.7 (–1.3 to –2.2) MtCO2 d−1 in the aviation sector, which yielded the largest relative anomaly of any sector, and by –21% or –0.9 (–0.3 to –1.4) MtCO2 d−1 in the public sector. The large relative anomalies in the aviation sector correspond with the disproportionate effect of confinement on air travel (Table 2), although the sector contributed only 10% of the decrease in global CO2 emissions. A small growth in global emissions occurred in the residential sector, with +2.8% or +0.2 (–0.1 to +0.4) MtCO2 d−1 and only marginally offsets the decrease in emissions in other sectors.
The total change in emissions until the end of April is estimated to amount to –1,048 (–543 to –1,638) MtCO2 (Supplementary Table 13), equivalent to a –8.6% decrease over January–April 2019. Of this, the changes are largest in China, where the confinement started, with a decrease of –242 (–108 to –394) MtCO2, then in the United States, with –207 (–112 to –314) MtCO2, then Europe, with –123 (–78 to –177) MtCO2, and India, with –98 (–47 to –154) MtCO2. These changes reflect both that these regions emit high levels of CO2 on average and that their confinements were severe in the period through end of April. The integrated changes in emissions over China are comparable in magnitude with the estimate of –250 MtCO2 of Myllyvirta (2020)22 up to the end of March. The global changes in emissions is also consistent with global changes in the NO2 inventory from satellite data, although the concentration data are complex to interpret (Supplementary Figs. 1 and 2).
Implications for global fossil CO2 emissions in 2020
The change for the rest of the year will depend on the duration and extent of the confinement, the time it will take to resume normal activities and the degree to which life will resume its preconfinement course. At the time of press, most countries that were in confinement level 3 had announced dates when they anticipated some confinement would be lifted. Dates ranged between mid-April and mid-May. We used those dates where available, and for other countries we assumed an end of confinement that corresponded to those neighbouring regions or states (Supplementary Tables 14 and 15). It is possible that the end of confinement will be delayed in some countries and therefore these dates are probably the earliest possible dates. Nevertheless, the mounting social23,24 and economic pressure25, along with the improving management of healthcare, means a systematic postponement is unlikely.
We assessed the effect of the recovery time by conducting three sensitivity tests. Our sensitivity tests are not intended to provide a full range of possibilities, but rather to indicate the approximate effect of the extent of the confinement on CO2 emissions. Before COVID-19, we expected global emissions to be similar to those in 20192, so the effect of confinement on CO2 emissions provided above might be approximately equivalent to the actual change from 2019 emissions. Our sensitivity tests do not attempt to quantify the effects of multiple confinement waves, or of deeper and sustained changes in the economy that could result from either the collapse of tens of thousands of small and medium businesses or government economic stimulus packages.
In the first sensitivity test, we assumed that after the announced dates for initial deconfinement, activities will return to precrisis levels within six weeks (around mid-June), as observed for coal use in industry in China22 (Supplementary Fig. 3). In this case, the decrease in emissions from the COVID-19 crisis would be –1,524 (–795 to –2,403) MtCO2 or –4.2% (–2.2 to –6.6%). In the second sensitivity test, we assumed it takes 12 weeks to reach preconfinement levels (towards the end of July), because of the low productivity that results from social trauma and low confidence. This longer period is more aligned with the announcements of gradual deconfinements, for example, in France, the UK and Norway, where a gradual deconfinement is planned over the coming months, and with timescales for the expected progression of the illness26. In this case, the decrease in emissions from the COVID-19 crisis would be –1,923 (–965 to –3,083) MtCO2 or –5.3% (–2.6 to –8.4%).
In the third sensitivity test, we made the same assumption as in the second test, but further assumed that confinement level 1 remains in place in all the countries examined until the end of the year. This is consistent with the situation in China in general, where, although measures were lifted at the end of February in most provinces, there are still some restrictions on specific activities, such as a restricted international travel. It is also more aligned with the latest understanding of the dynamics of transmission of the disease, which suggests prolonged or intermittent social distancing may be necessary into 202227. In this case, the decrease in emissions from the COVID-19 crisis would be –2,729 (–986 to –4,717) MtCO2 or –7.5% (–2.7 to –13%).
At the regional levels, the low sensitivity test led to mid-point decreases in emissions for year 2020 of –2.6%, –6.7%, –5.1% and –5.2% respectively for China, the US, Europe (EU27 + UK) and India, while the high sensitivity test led to midpoint decreases of –5.6%, –11%, –8.5% and –8.7% for those same countries (Supplementary Table 14). For comparison, for the United States alone, the Energy Information Administration (EIA) provides a forecast of a decrease in emissions of –7.5% in 202028, which takes into account all projected economic factors, and is between our sensitivity tests 1 and 2.
In spite of the broader effects on the economy that are not included in our analysis, our 2020 estimates are similar to those that can be inferred based on the projections of the International Monetary Fund for 2020 of –3% reduction in global Gross Domestic Product29 combined with an average CO2/GDP improvement of –2.7% over the past decade2,30, which gives a –5.7% reduction in CO2 emissions in 2020. These independent global and US projections are similar to the middle sensitivity test 2 of confinement that we present in this publication (see Supplementary Table 14), while the projection of the International Energy Agency (IEA) of –8% decrease in CO2 emissions in 2020 aligns with our high-end test 331. The International Monetary Fund and EIA further forecast that emissions will rebound by +5.8 and +3.5% in 2021, respectively, for the world and US economies.
The estimated decrease in daily fossil CO2 emissions from the severe and forced confinement of world populations of –17% (–11 to –25%) at its peak are extreme and probably unseen before. Still, these only correspond to the level of emissions in 2006. The associated annual decrease will be much lower (–4.2 to –7.5% according to our sensitivity tests), which is comparable to the rates of decrease needed year-on-year over the next decades to limit climate change to a 1.5 °C warming32,33. These numbers put in perspective both the large growth in global emissions observed over the past 14 years and the size of the challenge we have to limit climate change in line with the Paris Climate Agreement.
Furthermore, most changes observed in 2020 are likely to be temporary as they do not reflect structural changes in the economic, transport or energy systems. The social trauma of confinement and associated changes could alter the future trajectory in unpredictable ways34, but social responses alone, as shown here, would not drive the deep and sustained reductions needed to reach net-zero emissions. Scenarios of low-energy and/or material demand explored for climate stabilization explicitly aim to match reduced demand with higher well-being34,35, an objective that is not met by mandatory confinements. Still, opportunities exist to set structural changes in motion by implementing economic stimuli aligned with low carbon pathways.
Our study reveals how responsive the surface transportation sector’s emissions can be to policy changes and economic shifts. Surface transport accounts for nearly half the decrease in emissions during confinement, and active travel (walking and cycling, including e-bikes) has attributes of social distancing that are likely to be desirable for some time27 and could help to cut back CO2 emissions and air pollution as confinement is eased. For example, cities like Bogota, New York, Paris and Berlin are rededicating street space for pedestrians and cyclists to enable safe individual mobility, with some changes likely to become permanent. Follow-up research could explore further the potential of near-term emissions reductions in the transport sector that could be delivered with minimal or positive impact on societal well-being.
Several drivers push towards a rebound with an even higher emission trajectory compared with the policy-induced trajectories before the COVID-19 pandemic, which include calls by some governments36 and industry to delay Green New Deal programmes and to weaken vehicle emission standards37, and the disruption of clean energy deployment and research from supply issues. The extent to which world leaders consider the net-zero emissions targets and the imperatives of climate change when planning their economic responses to COVID-19 is likely to influence the pathway of CO2 emissions for decades to come.
Changes in emissions
Changes in emissions ΔCO2c,s,d (MtCO2 d−1) for each country/state/province (c), sector (s) and day (d) are estimated using equation (1):
where CO2c (MtCO2 d−1) is the mean daily emissions for the latest available year (2017–2019) updated from the Global Carbon Project for world countries1 (Supplementary Extended Methods), EIA46 for the United States and updated national statistics47 for Chinese provinces. International aviation and shipping is allocated to each country using data from IEA48. δSc is the fraction of emissions in each sector calculated using data from the IEA48 for world countries, EIA46 for the United States and national statistics47 for Chinese provinces. ΔAs,d(CI,c) is the fractional change in activity level for each sector compared with pre-COVID levels (Fig. 2 and Table 2) as a function of the CI for each day of the year and each country, state or province (Supplementary Tables 15 and 16). The combination of CO2 emissions data from the Global Carbon Project and sector distribution from IEA enabled the use of a country’s own reported emissions to the UNFCCC (United Nations Framework Convention on Climate Change), building on our previous work1, and means that more recent emissions could be used. Our analysis is done for 69 countries, which accounts for 97% of global emissions. We do not estimate the changes in other countries.
The choice of parameters by sector is based on data that represent changes in activity rather than directly changes in CO2 emissions, and on assumptions about the nature of the confinement. Most data are available daily up to 15 April 2020. All the data (Fig. 2) are representative of changes compared to a typical day prior to confinement, taking into account seasonality and day of the week. The changes were calculated differently depending on the data availability and the causes of the seasonality and weekly variability. The uncertainty represents approximately ±1σ. Sectors and parameter choices are described in detail in Supplementary Extended Methods with the key elements summarized here.
The power sector (44.3% of global CO2 emissions) includes energy conversion for electricity and heat generation. The change in electricity and heat assumes this sector follows the change observed in electricity demand data for the United States11, selected European countries10 and India38. The analysis accounts for cooling degree-days so that the effect of the confinement alone is isolated.
The industry sector (22.4%) includes the production of materials (for example, steel) and of cement, and manufacturing. The change in industry is based on coal consumption from six coal producers in China22 and on steel production in the United States39.
The surface transport sector (20.6%) includes cars, light vehicles, buses and trucks, as well as national and international shipping. The change in transport is based on Apple mobility data41 for world countries, MS2 corporation for US state data43 and the UK government42 for traffic data, and urban congestion data from TOMTOM40. The changes in shipping are based on forecasts by the World Trade Organization.
The public sector (4.2%) includes public buildings and commerce. The change in the public sector is based on surface transport for the upper limit, assuming it is proportional to the change in the workforce. It is based on electricity changes for the lower limit, with the central value interpolated between the two.
The residential sector (5.6%) represents mostly residential buildings. The changes in residential sector is based on reports of residential use monitored with UK smart meters from Octopus Energy44.
The aviation sector (2.8%) includes both domestic and international aviation. It is based on the total number of departing flights by aircraft on ground45.
Global Carbon Project CO2 emissions data are available at https://www.icos-cp.eu/global-carbon-budget-2019. International Energy Agency IEA World Energy Balances 2019 @IEA are available at http://www.iea.org/statistics/. European Network of Transmission System Operators Electricity Transparency Platform are available at https://transparency.entsoe.eu/. Power System Operation Corporation Limited data are available at https://posoco.in/reports/daily-reports/. EIA data are available at https://www.eia.gov/realtime_grid/ and https://www.eia.gov/environment/emissions/state/. CO2 emissions data for China are available at https://doi.org/10.1038/s41597-020-0393-y/. Coal changes from China industry are available at https://www.carbonbrief.org/analysis-coronavirus-has-temporarily-reduced-chinas-co2-emissions-by-a-quarter/. American Iron and Steel Institute data are available at https://www.steel.org/industry-data/. TOMTOM Traffic Index are available at https://www.tomtom.com/en_gb/traffic-index/. MS2 Corporation traffic data are available at https://www.ms2soft.com/traffic-dashboard/. Apple Mobility Trends data are available at https://www.apple.com/covid19/mobility/. UK traffic data from the Cabinet Office Briefing are available at https://www.gov.uk/government/collections/slides-and-datasets-to-accompany-coronavirus-press-conferences. Octopus Energy Tech smart meter data are available at https://tech.octopus.energy/data-discourse/2020-social-distancing/index.html. Aircraft on Ground OAG data are available at https://www.oag.com/coronavirus-airline-schedules-data/.
Friedlingstein, P. et al. Global Carbon Budget 2019. Earth Syst. Sci. Data 11, 1783–1838 (2019).
Jackson, R. B. et al. Persistent fossil fuel growth threatens the Paris Agreement and planetary health. Env. Res. Lett. 14, 121001 (2019).
Peters, G. P. et al. Carbon dioxide emissions continue to grow amidst slowly emerging climate policies. Nat. Clim. Change 10, 3–6 (2020).
Global CO 2 Emissions in 2019 (IEA, 2019); https://www.iea.org/articles/global-co2-emissions-in-2019
Figueres, C. et al. Emissions are still rising: ramp up the cuts. Nature 564, 27–30 (2018).
Le Quéré, C. et al. Drivers of declining CO2 emissions in 18 developed economies. Nat. Clim. Change 9, 213–217 (2019).
Solaymani, S. CO2 emissions patterns in 7 top carbon emitter economies: the case of transport sector. Energy 168, 989–1001 (2019).
Report of the WHO–China Joint Mission on Coronavirus Disease 2019 (COVID-19) (WHO, 2020); https://www.who.int/publications-detail/report-of-the-who-china-joint-mission-on-coronavirus-disease-2019-(covid-19)
Sohrabi, C. et al. World Health Organization declares global emergency: a review of the 2019 novel coronavirus (COVID-19). Int. J. Surg. 76, 71–76 (2020).
ENTSO-E Transparency Platform (ENTSO, accessed 7 April 2020); https://transparency.entsoe.eu/
US Electric System Operating Data (IEA, accessed 7 April 2020); https://www.eia.gov/realtime_grid/
Andres, R. J. et al. A synthesis of carbon dioxide emissions from fossil-fuel combustion. Biogeosciences 9, 1845–1871 (2012).
Dlugokencky, E. & Tans, P. Trends in Atmospheric Carbon Dioxide (NOAA/ESRL, accessed 4 September 2018); http://www.esrl.noaa.gov/gmd/ccgg/trends/global.html
Keeling, R. F., Walker, S. J., Piper, S. C. & Bollenbacher, A. F. Atmospheric CO 2 concentrations (ppm) derived from in situ air measurements at Mauna Loa Observatory, Hawaii (Scripps Institution of Oceanography, 2016); https://scrippsco2.ucsd.edu/data/atmospheric_co2/mlo.html
Peters, G. P. et al. Towards real-time verification of CO2 emissions. Nat. Clim. Change 7, 848–850 (2017).
Ballantyne, A. P., Alden, C. B., Miller, J. B., Tans, P. P. & White, J. W. C. Increase in observed net carbon dioxide uptake by land and oceans during the last 50 years. Nature 488, 70–72 (2012).
Crisp, D. et al. The on-orbit performance of the orbiting carbon observatory-2 (OCO-2) instrument and its radiometrically calibrated products. Atmos. Meas. Tech. 10, 59–81 (2017).
Schwandner, F. M. et al. Spaceborne detection of localized carbon dioxide sources. Science 358, eaam5782 (2017).
Peters, G. P., Minx, J. C., Weber, C. L. & Edenhofer, O. Growth in emission transfers via international trade from 1990 to 2008. Proc. Natl Acad. Sci. USA 108, 8903–8908 (2011).
Peters, G. P. et al. Correspondence: rapid growth in CO2 emissions after the 2008–2009 global financial crisis. Nat. Clim. Change 2, 2–4 (2012).
Janssens-Maenhout, G. et al. EDGAR v4.3.2 Global Atlas of the three major greenhouse gas emissions for the period 1970–2012. Earth Syst. Sci. Data 11, 959–1002 (2019).
Myllyvirta, L. Coronavirus temporarily reduced China’s CO2 emissions by a quarter. Carbon Brief https://www.carbonbrief.org/analysis-coronavirus-has-temporarily-reduced-chinas-co2-emissions-by-a-quarter (2020).
Torales, J. & O’Higgins, M. & Castaldelli-Maia, J. M. & Ventriglio, A. The outbreak of COVID-19 coronavirus and its impact on global mental health. Int. J. Soc. Psychiatry https://doi.org/10.1177/0020764020915212 (2020).
van Dorn, A., Cooney, R. E. & Sabin, M. L. COVID-19 exacerbating inequalities in the US. Lancet 395, 1243–1244 (2020).
Dyer, O. Covid-19: Trump declares intention to ‘re-open economy’ within weeks against experts’ advice. Br. Med. J. 368, m1217 (2020).
Ferguson, N. M. et al. Impact of Non-Pharmaceutical Interventions (NPIs) to Reduce COVID- 19 Mortality and Healthcare Demand (Imperial College, 2020); https://www.imperial.ac.uk/media/imperial-college/medicine/sph/ide/gida-fellowships/Imperial-College-COVID19-NPI-modelling-16-03-2020.pdf
Kissler, S. M., Tedijanto, C., Goldstein, E., Grad, Y. H. & Lipsitch, M. Projecting the transmission dynamics of SARS-CoV-2 through the postpandemic period. Science https://doi.org/10.1126/science.abb5793 (2020).
Short-term Energy Outlook (EIA, accessed 19 April 2020); https://www.eia.gov/outlooks/steo/
World Economic Outlook April 2020 (IMF, 2020); https://www.imf.org/en/Publications/WEO/Issues/2020/04/14/weo-april-2020
Raupach, M. R. et al. Global and regional drivers of accelerating CO2 emissions. Proc. Natl Acad. Sci. USA 104, 10288–10293 (2007).
Global Energy Review 2020: the impacts of the Covid-19 crisis on global energy demand and CO 2 emissions (IEA, 2020).
IPCC Special Report on Global Warming of 1.5 °C (eds Masson-Delmotte, V. et al.) (WMO, 2018).
Emissions Gap Report 2019: Executive Summary (UNEP, 2019).
McCollum, D. L., Gambhir, A., Rogelj, J. & Wilson, C. Energy modellers should explore extremes more systematically in scenarios. Nat. Energy 5, 104–107 (2020).
Creutzig, F. et al. The underestimated potential of solar energy to mitigate climate change. Nat. Energy 2, 17140 (2017).
Czech PM urges EU to ditch Green Deal amid virus. Euractive https://www.euractiv.com/section/energy-environment/news/czech-pm-urges-eu-to-ditch-green-deal-amid-virus/ (2020).
Letter to U. von der Leyen, President of the European Commission (European Automobile Manufacturers Association, 2020); https://www.acea.be/uploads/news_documents/COVID19_auto_sector_letter_Von_der_Leyen.pdf
National Load Despatch Centre Daily Reports (POSOCO, accessed 19 April 2020); https://posoco.in/reports/daily-reports/
Steel Industry Data (American Iron and Steel Institute, accessed 19 April 2020); https://www.steel.org/industry-data
TOMTOM Traffic Index (TOMTOM, accessed 7 April 2020); https://www.tomtom.com/en_gb/traffic-index/
Apple Mobility Trends Reports (Apple, accessed 19 April 2020); https://www.apple.com/covid19/mobility/
Transport Use Change (Great Britain) (Cabinet Office Briefing Room, accessed 23 April 2020); https://www.gov.uk/government/collections/slides-and-datasets-to-accompany-coronavirus-press-conferences
Daily Traffic Volume Trends (MS2 Corporation, accessed 7 April 2020); https://www.ms2soft.com/traffic-dashboard/
Energy Consumption under Social Distancing Measures (Octopus Energy, accessed 7 April 2020); https://tech.octopus.energy/data-discourse/2020-social-distancing/index.html
Coronavirus Airline Schedules Data (OAG, accessed 7 April 2020); https://www.oag.com/coronavirus-airline-schedules-data
State Carbon Dioxide Emissions Data (EIA; accessed 28 March 2020); https://www.eia.gov/environment/emissions/state/
Shan, Y. L. & Huang, Q. & Guan, D. B. & Hubacek, K. China CO2 emission accounts 2016–2017. Sci. Data 7, 54 (2020).
World Energy Balances 2019 (IEA, accessed 11 November 2019); http://www.iea.org/statistics
We thank P. Hunter for insights on the evolution of the pandemic. C.L.Q. and D.R.W. were funded by the Royal Society (grant no. RP\R1\191063). P.F., A.J.D.-G., R.M.A. and G.P.P. were funded by the European Union Horizon 2020 (H2020) ‘4C’ project (no. 821003), M.W.J. and A.J.P.S. by the H2020 ‘VERIFY’ project (no. 776810), G.P.P. by the H2020 PARIS REINFORCE project (no. 820846), and M.W.J. by the H2020 ‘CHE’ project (no. 776186). R.B.J. was funded by the Gordon and Betty Moore Foundation (GBMF5439). J.G.C. was funded by the Australian National Environmental Science Program—Earth Systems and Climate Change Hub. This collaboration was made possible by prior funding from the UK Natural Environment Research Funding International Opportunities Fund (no. NE/I03002X/1), and by the Global Carbon Project. We thank the UEA HPC team for support. This analysis is based in part on data from the IEA, http://www.iea.org/statistics.
The authors declare no competing interests.
Peer review information Nature Climate Change thanks Hannah Ritchie and the other, anonymous, reviewer(s) for their contribution to the peer review of this work.
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Le Quéré, C., Jackson, R.B., Jones, M.W. et al. Temporary reduction in daily global CO2 emissions during the COVID-19 forced confinement. Nat. Clim. Chang. 10, 647–653 (2020). https://doi.org/10.1038/s41558-020-0797-x
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