PreprintPDF Available

Regional Impacts of COVID-19 on Carbon Dioxide Detected Worldwide from Space

Authors:
Preprints and early-stage research may not have been peer reviewed yet.

Abstract and Figures

Monitoring the global distribution of greenhouse gases using spaceborne observations and attributing regional anomalies of their surface fluxes to either climatic or human processes represents a new frontier in Earth system science. The reduction in economic activity in early 2020 due to the Coronavirus Disease 2019 (COVID-19) pandemic led to unprecedented decreases in monthly carbon dioxide (CO2) emissions from fossil fuel use. This paper shows, for the first time, that the regional impact of COVID-19 was observable from space. Our approach uses data assimilation to ingest satellite observations of column average CO2 (XCO2) from NASA's Orbiting Carbon Observatory 2 (OCO-2) into the Goddard Earth Observing System (GEOS), an integrated Earth system model.
Content may be subject to copyright.
1
Regional Impacts of COVID-19 on Carbon Dioxide
Detected Worldwide from Space
B Weir*1,2, D Crisp3, C W O’Dell4, S Basu2,5, A Chatterjee1,2, T Oda1,2, L E Ott2, S Pawson2, B
Poulter2, Z Zhang6, P Ciais7, S J Davis9, and Z Liu8
1Universities Space Research Association, Columbia, Maryland, USA
2NASA Goddard Space Flight Center, Greenbelt, Maryland, USA
3Jet Propulsion Laboratory, Pasadena, California, USA
4Colorado State University, Fort Collins, Colorado, USA
5Earth System Science Interdisciplinary Center, University of Maryland, College Park, Maryland, USA
6University of Maryland, College Park, Maryland, USA
7Laboratoire des Sciences du Climat et de l'Environnement, Gif sur Yvette, France
8Department of Earth System Science, University of California, Irvine, USA
9Department of Earth System Science, Tsinghua University, Beijing, China
* Correspondence to: brad.weir@nasa.gov
Abstract
Monitoring the global distribution of greenhouse gases using spaceborne observations and
attributing regional anomalies of their surface fluxes to either climatic or human processes
represents a new frontier in Earth system science. The reduction in economic activity in early 2020
due to the Coronavirus Disease 2019 (COVID-19) pandemic led to unprecedented decreases in
monthly carbon dioxide (CO2) emissions from fossil fuel use, estimated at up to 20% for a given
day and 4–7% by April. This paper shows, for the first time, that the regional impact of COVID-
19 was observable from space. Our approach uses data assimilation to ingest satellite observations
of column average CO2 (XCO2) from NASA’s Orbiting Carbon Observatory 2 (OCO-2) into the
Goddard Earth Observing System (GEOS), an integrated Earth system model. We then quantify
regional anomalies in XCO2 and attribute them to either climate-driven variability or changes in
anthropogenic emissions. Starting in February 2020 and continuing through May, XCO2 over
many of the World’s largest emitting regions was 0.24–0.48 parts per million (ppm) less than
expected in a pandemic-free scenario, consistent with reductions of 5–10% in annual, global fossil
fuel emissions. This signal is just above the detection limit of OCO-2, but still distinguishable from
climate-driven anomalies, notably related to the 2019–2020 Indian Ocean Dipole. The timings of
the monitored reductions in CO2 growth and subsequent rebound clearly coincide with changes in
country-level activity due to COVID-19. Our results also indicate considerable remaining
uncertainties about the regrowth of CO2 emissions over China following the Lunar New Year
vacation that coincided with the COVID-19 lockdown. These results demonstrate that current
spaceborne technologies designed to monitor CO2 anomalies are approaching levels of accuracy
needed to support and inform climate mitigation strategies with future missions expected to meet
those needs.
One Sentence Summary
This paper shows, for the first time, that the regional impact of COVID-19 on atmospheric carbon
dioxide was observable and quantifiable from space-based instruments.
2
Reductions in economic activity in response to the Coronavirus disease 2019 (COVID-19) at the
beginning of 2020 produced the largest short-term change in fossil fuel and cement carbon dioxide
(CO2) emissions since the Industrial Revolution (1). Preliminary emissions estimates for 2020
based on economic activity data suggest that, compared to 2019 emissions, daily global emissions
decreased by as much as 15–20% in April (2). Accumulated from the start of the year, these
reductions reached ~7.8% by June (3) and are expected to total ~4% (low estimate) to ~7% (high
estimate) for the year, with the exact annual decrease depending on the intensity of the reduction
during the lockdowns, and the timing of the return of economic activity to pre-pandemic levels
(2). Reductions in human activities were also indicated in satellite observations of changes in
nighttime light intensity (4), and observations of short lived combustion related pollutants, e.g.,
nitrogen dioxide (NO2; 5–7). While activity data based estimates are consistent with reductions in
satellite NO2 observations (2), the relationship of NO2 to CO2 emissions depends on combustion
efficiency which varies significantly across sectors and regions. Furthermore, CO2 emission
estimates based on recent activity data, rather than the annual reported inventories typically used
by “bottom-up” estimates, rely on different metrics and are thus subject to their own unique
uncertainties—the two most well-known products (2, 3), for example, produce estimates with
greater day-to-day variability by construction—and would benefit from independent verification
and analysis.
For the past two decades, space agencies from around the world have planned and launched several
satellite missions to observe vertical column average CO2 (XCO2) with a long-term goal of
quantifying anthropogenic CO2 emissions and their trends. The current constellation includes
Japan’s Greenhouse Gases Observing Satellite (GOSAT; 8), launched in 2009, NASA’s Orbiting
Carbon Observatory-2 (OCO-2; 9, 10) in 2014, Japan’s GOSAT-2 (11) in 2018 and NASA’s OCO-
3, deployed in 2019 on the International Space Station (12). These missions were all designed as
sounders that regularly sample the atmosphere at high precision, instead of mapping it in its
entirety, and had a strong focus on understanding the terrestrial biosphere. Future missions are
expected to place an increasing focus on understanding anthropogenic emissions and improve
coverage with greater swath widths and/or by sampling the atmosphere multiple times a day, e.g.,
NASA's Geostationary Carbon Observatory (GeoCarb; 13) positioned over the Americas and
many other ongoing international efforts (14).
Developing a system that uses atmospheric CO2 observations to monitor changes in anthropogenic
emissions remains a landmark achievement needed to support the implementation of international
climate accords (15, 16). Unlike NO2 observations, which display clear plumes with high
concentrations over emitting areas, CO2 has a long lifetime in the atmosphere and is well mixed.
Furthermore, in any given month, regional terrestrial biospheric fluxes have similar or greater
magnitudes than fossil fuel emissions. This means that the CO2 signals caused by even large
emissions changes are confounded by those from long range atmospheric transport and natural
fluxes. To verify emissions changes with atmospheric CO2 observations, the eventual goal is to
sample the atmosphere as densely and frequently as possible above and downwind of emitting
areas. This is not achievable with the current sparse surface network focused primarily on
background CO2, but becomes increasingly possible with satellite observations. Below, we present
our approach for monitoring changes in atmospheric CO2, analyze the observed changes in XCO2
in 2020, and demonstrate that our system can detect and quantify the impact of COVID-19 on
3
XCO2, despite the significant difficulties noted in other studies (17). We conclude with a
discussion of the scientific implications of those results.
Monitoring Atmospheric CO2 in Near Real Time
The Goddard Earth Observing System (GEOS)/OCO-2 atmospheric carbon monitoring system has
several unique characteristics that enable it to capture and quantify the signal due to COVID-19
(interactive visualizations available online at Refs. 18–20). First, it takes advantage of the unique
coverage and precision of OCO-2 measurements. Mixed throughout the atmosphere, a 7%
reduction in annual fossil fuel emissions represents just a 0.33 ppm change (21, 22) against the
global marine boundary layer background concentration of 412.22 ppm in January 2020 (23).
While previous instruments have had insufficient precision and/or coverage to detect signals of
this size, they remain within the accuracy bounds of OCO-2 (24, 25). Second, it uses coupled
meteorology-carbon cycle components within GEOS (26) and data assimilation to infer three-
dimensional, gridded fields of CO2 for the entire OCO-2 data record (see Materials and Methods
and Fig. 1). By using a transport model, our approach accounts for the year-to-year variability in
CO2 due to differences in atmospheric circulation: even with no change in surface fluxes, transport
variability can cause several ppm differences in XCO2 over the same area from one year to the
next (27; see also Fig. S5). This difference is especially relevant over North America, where
passing weather systems cause sharp gradients across frontal boundaries (28). Analyses of XCO2
retrievals that do not account for transport variability (29, 30) are therefore unlikely to capture
year-to-year differences in emissions, especially given the sparse and infrequent sampling of OCO-
2 over emitting areas. Finally, our approach produces regular updates in near real time (NRT),
taken here to mean a latency of less than a month, enabling the study of changes in the carbon
cycle as they occur (31). Other common methods for inferring surface fluxes from atmospheric
observations, e.g., flux inversion systems (27, 32, 33), typically trail the current date by a year or
more and/or can be available for just a few years.
Unprecedented Carbon Dioxide Anomalies in Early 2020
Over much of the Northern Hemisphere, home to most of the World’s largest economies and more
than 95% of global total emissions, 16-day running means of XCO2 from the GEOS/OCO-2
analysis show consistent, negative anomalies compared to a pandemic-free scenario (see Materials
and Methods) beginning in February 2020 and continuing through May (Fig. 2). At the
country/regional level, these anomalies show remarkable correlation with restrictions on activity
and their subsequent relaxation (Fig. 3). Their steep initial decrease and subsequent levelling off
corroborates activity data indicators that emissions dropped precipitously during the initial
confinement and then slowly recovered or levelled off. These anomalies are well outside the
variability over the baseline period of 2017–2019 (see Materials and Methods): peak
uncertainties for February–May 2020 ranged from 0.07–0.16 ppm while peak reductions in XCO2
growth reached 0.27–0.39 ppm (Table 1). Averaging those reductions and taking the geometric
mean of the uncertainties gives us a range of 0.24–0.48 ppm for the Northern Hemisphere.
Assuming the average reduction over the entire atmosphere is that same number at the end of the
year, these estimates would produce 0.51–1.0 Pg C less of CO2 in the atmosphere (21, 22),
corresponding to a 5–10% reduction in the 10 Pg C global fossil fuel emissions total estimated for
2019 (34). The conversion of ppm CO2 to Pg C used above (22) is only a rough indicator of
4
emissions, especially since interhemispheric mixing takes over a year to transport a signal from
the Northern to Southern Hemisphere (35).
The monitored changes in XCO2 over the Northern Hemisphere in February–May 2020 are
primarily attributable to reductions in fossil fuel emissions for two reasons. First, late 2019 through
2020 saw neutral to weak La Niña conditions (36, 37) of the El Niño/Southern Oscillation (ENSO).
Globally, the annual growth rate of CO2 correlates well with a linear combination of total
anthropogenic emissions and the Niño 3 or 3.4 ENSO index (38, 39). The latter term, which serves
as a proxy for biospheric variability, is small in 2020 (36, 37), indicating a strong anthropogenic
role in the growth rate anomaly. Regionally and monthly, ENSO remains a dominant driver of
biospheric anomalies, but not without notable exceptions (40). Second, the months of February–
May occur during a “shoulder” season in which net biospheric exchange is near its smallest (Figs.
S8 and S10), making it an ideal time to capture an anomaly driven by fossil fuel emissions.
Transport simulations of 2020 anomalies from the Lund, Potsdam, Jena - Wald, Schnee und
Landscaft (LPJ-wsl; 41) dynamic global vegetation model (see Materials and Methods) also
indicate that the biospheric anomalies in the Northern Hemisphere were relatively minor in
February–May (Fig. S9).
To further evaluate the ability of our monitoring system to provide meaningful information about
country-level fossil fuel emissions estimates, we simulate the expected anomaly for 2020 based on
the daily activity data based estimates (3), indicated by the blue boxes in Fig. 3. Overall, our results
and the bottom-up simulation agree about the magnitude of reductions at a country/regional level.
One notable disagreement is in the timing of the reduction over the United States. In the bottom-
up simulations, reductions begin before activity restrictions as air with less CO2 is transported from
China, across the North Pacific, and eventually to the United States, a process that takes several
days. These reductions are not apparent in the monitoring system. Over China (Fig. 3c) and the
North Pacific (Fig. 2), where we expect to see sustained reductions in XCO2, there is almost a
complete rebound following the Lunar New Year. This is consistent with rebounds in NO2
observations from satellites (5) and in situ sensors (7). While another study (6) found a rebound in
NO2 emissions following the Lunar New Year based on satellite observations, they did not find a
complete recovery to pre-pandemic levels. There are several factors that could play a role in these
discrepancies, each of which requires further investigation. In particular, uncertainties in Chinese
emissions are greater than perhaps any other region (42, 43), preventing us from making any strong
conclusions about the magnitude of the recovery in their emissions. Nevertheless, these differences
cannot be attributed to observational coverage or the data assimilation system—an observing
system experiment (OSE) that samples the simulated values at the time and place of OCO-2
soundings and assimilates the result is able to reproduce simulated signals (Figs. S3 and S4). While
the differences between the fossil fuel simulated and GEOS/OCO-2 analysis anomalies are on the
order of the spread over previous years (indicated in grey in Fig. 3c), there are no indications of
strong positive biospheric anomalies transported over the Pacific Ocean and North America from
a companion simulation of biospheric anomalies (Fig. S9).
Starting in 2019 and continuing through February 2020, GEOS/OCO-2 captured another striking
change in XCO2, this time originating from the influence of a record-breaking climate anomaly on
the terrestrial biosphere (Fig. 4). In 2020, well before their COVID-19 related restrictions, XCO2
growth dropped over India and sub-Saharan Africa and increased over Australia (Fig. 5). At this
5
time, the countries surrounding the Indian Ocean were experiencing the tail end of the 2019–2020
Indian Ocean Dipole (IOD) whose Dipole Mode Index was in the greatest positive phase on record
(36, 44). The impact of the IOD on the terrestrial biosphere and atmospheric circulation began in
2019, when both sub-Saharan Africa and India had wetter than usual boreal autumns—during the
positive phase, cooler-than-normal sea surface conditions persist in the eastern Indian Ocean with
warmer-than-normal conditions in the western tropical Indian Ocean (45–47). This East-West
contrast in ocean conditions alters the wind, temperature, and rainfall patterns in the region,
typically bringing mild temperatures and floods to sub-Saharan Africa and the Indian subcontinent
(48) and high temperatures and droughts to East Asia and Australia (49), among other ecological
and socio-economic impacts. That increased rainfall over sub-Saharan Africa and the Indian
subcontinent resulted in an extremely productive agricultural year and bumper crop harvests (50),
while high temperature and drought conditions resulted in a record-setting fire season throughout
Australia (51). The impact of these extremes on the carbon cycle persisted well into 2020,
eventually falling off in early March (Figs. 4 and 5; see Fig. S9 for a comparison simulation).
Conclusions
We found that satellite monitored changes in early 2020 XCO2 due to the COVID-19 pandemic
were small (0.24–0.48 ppm), negative, and consistent with country-level activity data. The United
States, Europe, and Asia each saw noticeable reductions in XCO2 growth coinciding with
restrictions placed on economic activity and a rebound in emissions as those restrictions were
lifted. Attribution of these signals to changes in anthropogenic emissions remains challenging:
interannual variability in transport and biospheric carbon-climate teleconnections both drive
concentration changes many times greater than the record-setting changes in regional
anthropogenic emissions due to COVID-19. For example, increased net vegetation growth in India
and Africa and fires and respiration in Australia driven by the record-setting 2019–2020 IOD
produced the greatest XCO2 anomaly of early 2020. The ability to detect fossil fuel CO2 emissions
changes in the midst of climate variability is a significant milestone toward the long-term goal of
monitoring future emissions reductions, especially given the planned increase in space-based
observing capability. Despite these advances, land and ocean flux variations related to ENSO and
IOD, and their related uncertainties, limit our ability to monitor and understand changes in
anthropogenic emissions. Attribution of CO2 anomalies to individual surface flux components, and
not their total, remains an active area of research with growing importance due to the societal need
to reduce and monitor emissions. This effort will benefit in the future by improvements in
terrestrial biospheric models, significant planned future increases in the space-based coverage of
CO2 observations from NASA’s Geostationary Carbon Observatory, Japan’s Greenhouse gases
Observing SATellites (GOSATs), and the European CO2 Monitoring mission with a greater
emphasis on monitoring fossil fuel emissions, colocation with other remote-sensing observations,
e.g., NO2, and in situ measurements, e.g., 14C in CO2 data (52).
References
1. N. S. Diffenbaugh et al., The COVID-19 lockdowns: a window into the Earth System. Nat.
Rev. Earth Environ. 1, 470-481 (2020).
2. C. Le Quéré et al., Temporary reduction in daily global CO2 emissions during the COVID-
19 forced confinement. Nat. Clim. Change 10, 647-653 (2020).
6
3. Z. Liu et al., Near-real-time monitoring of global CO2 emissions reveals the effects of the
COVID-19 pandemic. Nat. Commun. 11, 5172 (2020).
4. Q. Liu et al., Spatiotemporal Patterns of COVID-19 Impact on Human Activities and
Environment in Mainland China Using Nighttime Light and Air Quality Data. Remote Sens.
12, 1576 (2020).
5. F. Liu et al., Abrupt decline in tropospheric nitrogen dioxide over China after the outbreak
of COVID-19. Sci. Adv. 6, eabc2992 (2020).
6. K. Miyazaki et al., Air Quality Response in China Linked to the 2019 Novel Coronavirus
(COVID‐19) Lockdown. Geophys. Res. Lett. 47, e2020GL089252 (2020).
7. C. A. Keller et al., Global Impact of COVID-19 Restrictions on the Surface Concentrations
of Nitrogen Dioxide and Ozone. Preprint at https://acp.copernicus.org/preprints/acp-2020-
685 (2020).
8. A. Kuze, H. Suto, M. Nakajima, T. Hamazaki, Thermal and near infrared sensor for carbon
observation Fourier-transform spectrometer on the Greenhouse Gases Observing Satellite
for greenhouse gases monitoring. Appl. Opt. 48, 6716-6733 (2009).
9. A. Eldering et al., The Orbiting Carbon Observatory-2: First 18 months of science data
products. Atmos. Meas. Tech. 10, 549-563 (2017).
10. A. Eldering et al., The Orbiting Carbon Observatory-2 early science investigations of
regional carbon dioxide fluxes. Science 358, eaam5745 (2017).
11. H. Suto et al., Thermal and near-infrared sensor for carbon observation Fourier-transform
spectrometer-2 (TANSO-FTS-2) on the Greenhouse Gases Observing Satellite-2 (GOSAT-
2) during its first year on orbit. Preprint at https://amt.copernicus.org/preprints/amt-2020-
360 (2020).
12. T. E. Taylor et al., OCO-3 early mission operations and initial (vEarly) XCO2 and SIF
retrievals. Remote Sens. Environ. 251, 112032 (2020).
13. B. Moore III et al., The potential of the geostationary Carbon Cycle Observatory (GeoCarb)
to provide multi-scale constraints on the carbon cycle in the Americas. Front. Environ. Sci.
6, 109 (2018).
14. D. Crisp et al., A constellation architecture for monitoring carbon dioxide and methane from
space. Prepared by the CEOS Atmospheric Constellation Greenhouse Gas Team. Available
at http://ceos.org/document_management/Meetings/Plenary/32/documents/CEOS_AC-
VC_White_Paper_Version_1_20181009.pdf (2020).
15. P. Ciais et al., Current systematic carbon-cycle observations and the need for implementing
a policy-relevant carbon observing system. Biogeosci. 11, 3547-3602 (2014).
16. G. P. Peters et al., Towards real-time verification of CO2 emissions. Nat. Clim. Change 7,
848-850 (2017).
17. F. Chevallier et al., Local anomalies in the column‐averaged dry air mole fractions of carbon
dioxide across the globe during the first months of the coronavirus recession. Geophys. Res.
Lett. e2020GL090244. In print at https://doi.org/10.1029/2020GL090244 (2020).
18. NASA/ESA/JAXA, Earth Observing Dashboard, https://eodashboard.org (2020).
19. NASA, COVID-19 Dashboard: Carbon Dioxide,
https://earthdata.nasa.gov/covid19/indicators/co2 (2020).
20. NASA Global Modeling and Assimilation Office (GMAO) and NASA Center for Climate
Simulation (NCCS), Framework for Live User-Invoked Data (FLUID): Carbon
Constituents, https://fluid.nccs.nasa.gov/carbon (2020).
7
21. K. E. Trenberth, L. Smith, The mass of the atmosphere: A constraint on global analyses. J.
Clim. 18, 864-875 (2005).
22. A. P. Ballantyne, C. B. Alden, J. B. Miller, P. P. Tans, J. W. C. White, Increase in observed
net carbon dioxide uptake by land and oceans during the past 50 years. Nature 488, 70-72
(2012).
23. E. Dlugokencky, P. Tans, The marine boundary layer reference. Downloaded in May 2020
from https://www.esrl.noaa.gov/gmd/ccgg/mbl/mbl.html (2020).
24. D. Wunch et al., Comparisons of the Orbiting Carbon Observatory-2 (OCO-2) XCO2
measurements with TCCON, Atmos. Meas. Tech. 10, 2209–2238 (2017).
25. C. O'Dell et al., Improved retrievals of carbon dioxide from Orbiting Carbon Observatory-2
with the version 8 ACOS algorithm, Atmos. Meas. Tech. 11, 6539–6576, (2018).
26. L. E. Ott et al., Assessing the magnitude of CO2 flux uncertainty in atmospheric CO2
records using products from NASA's Carbon Monitoring Flux Pilot Project. J. Geophys.
Res.: Atmos. 120, 734-765 (2015).
27. S. Guerlet et al., Reduced carbon uptake during the 2010 Northern Hemisphere summer
from GOSAT. Geophys. Res. Lett. 40, 2378-2383 (2013).
28. S. Pal et al., Observations of Greenhouse Gas Changes Across Summer Frontal Boundaries
in the Eastern United States. J. Geophys. Res.: Atmos. 125, e2019JD030526 (2020).
29. J. Hakkarainen, I. Ialongo, J. Tamminen, Direct space-based observations of anthropogenic
CO2 emission areas from OCO‐2. Geophys. Res. Lett. 43, 11-400 (2016).
30. M. Buchwitz et al., Can a regional-scale reduction of atmospheric CO2 during the COVID-
19 pandemic be detected from space? A case study for East China using satellite XCO2
retrievals. Preprint at https://amt.copernicus.org/preprints/amt-2020-386 (2020).
31. B. Weir et al., Calibrating satellite-derived carbon fluxes for retrospective and near real-time
assimilation systems. Preprint at https://acp.copernicus.org/preprints/acp-2020-496 (2020).
32. J. Liu et al., Contrasting carbon cycle responses of the tropical continents to the 2015–2016
El Niño. Science 358, eaam5690 (2017).
33. S. Crowell et al., The 2015–2016 carbon cycle as seen from OCO-2 and the global in situ
network. Atmos. Chem. Phys. 19, 9797-9831 (2019).
34. P. Friedlingstein et al., Global carbon budget 2019. Earth Syst. Sci. Data 11, 1783-1838
(2019).
35. R. J. Francey et al., Atmospheric verification of anthropogenic CO2 emission trends. Nat.
Clim. Change 3, 520-524 (2013).
36. N. A. Rayner et al., Global analyses of sea surface temperature, sea ice, and night marine air
temperature since the late nineteenth century, J. Geophys. Res.: Atoms. 108, 4407 (2003).
37. NOAA Physical Sciences Laboratory, Niño 3.4 SST Index. Downloaded in May 2020 from
https://psl.noaa.gov/gcos_wgsp/Timeseries/Data/nino34.long.anom.data (2020).
38. C. D. Jones, P. M. Cox, On the significance of atmospheric CO2 growth rate anomalies in
2002–2003. Geophys. Res. Lett. 32, L14816 (2005).
39. R. A. Betts, C. D. Jones, J. R. Knight, R. F. Keeling, J. J. Kennedy, El Niño and a record
CO2 rise. Nat. Clim. Change 6, 806-810 (2016).
40. B. Poulter et al., Contribution of semi-arid ecosystems to interannual variability of the
global carbon cycle. Nature 509, 600-603 (2014).
41. S. Sitch et al., Evaluation of ecosystem dynamics, plant geography and terrestrial carbon
cycling in the LPJ dynamic global vegetation model. Global Change Biol. 9, 161-185
(2003).
8
42. Z. Liu et al., Reduced carbon emission estimates from fossil fuel combustion and cement
production in China. Nature, 524, 335-338 (2015).
43. P. Han et al., Evaluating China's fossil-fuel CO2 emissions from a comprehensive dataset of
nine inventories. Preprint at https://doi.org/10.5194/acp-2019-643 (2020).
44. NOAA Physical Sciences Laboratory, Dipole Mode Index. Downloaded in May 2020 from
https://psl.noaa.gov/gcos_wgsp/Timeseries/Data/dmi.had.long.data (2020).
45. N. H. Saji et al., A dipole mode in the tropical Indian Ocean. Nature 401, 360-363 (1999).
46. P. J. Webster, A. M. Moore, J. P. Loschnigg, R. R. Leben, Coupled ocean–atmosphere
dynamics in the Indian Ocean during 1997–98. Nature 401, 356-360 (1999).
47. B. Lu, H. L. Ren, What caused the extreme Indian Ocean Dipole event in 2019?. Geophys.
Res. Lett. 47, e2020GL087768 (2020).
48. K. Ashok, Z. Guan, N. H. Saji, T. Yamagata, Individual and combined influences of ENSO
and the Indian Ocean dipole on the Indian summer monsoon. J. Clim. 17, 3141-3155 (2004).
49. W. Cai, T. Cowan, A. Sullivan, Recent unprecedented skewness towards positive Indian
Ocean Dipole occurrences and its impact on Australian rainfall. Geophys. Res. Lett. 36,
L11705 (2009).
50. Food and Agriculture Organization of the United Nations, Crop Prospects and Food
Situation - Quarterly Global Report No. 2, July 2020. Available at
https://doi.org/10.4060/ca9803en (2020).
51. M. M. Boer, V. R. de Dios, R. A. Bradstock, Unprecedented burn area of Australian mega
forest fires. Nat Clim. Change 10, 171-172 (2020).
52. S. Basu et al., Estimating US fossil fuel CO2 emissions from measurements of 14C in
atmospheric CO2. Proc. Natl. Acad. Sci. 117, 13300-13307 (2020).
53. OCO-2 Science Team / M. Gunson et al., OCO-2 Level 2 bias-corrected XCO2 and other
select fields from the full-physics retrieval aggregated as daily files, Retrospective
processing V10r, Greenbelt, MD, USA, Goddard Earth Sciences Data and Information
Services Center (GES DISC). Accessed: 30 August 2020.
https://doi.org/10.5067/E4E140XDMPO2 (2020).
54. OCO-2 Science Team / G. Osterman et al., OCO-2 & OCO-3 data product user’s guide,
Operational level 2 data versions 10 and lite file version 10 and vEarly.
https://docserver.gesdisc.eosdis.nasa.gov/public/project/OCO/OCO2_OCO3_B10_DUG.pdf
(2020).
55. R. N. Bannister, A review of operational methods of variational and ensemble‐variational
data assimilation. Q. J. R. Meteorol. Soc. 143, 607-633 (2017).
56. P. J. Rayner, A. M. Michalak, F. Chevallier, Fundamentals of data assimilation applied to
biogeochemistry. Atmos. Chem. Phys. 19, 13911–13932 (2019).
57. P. Bergthórsson, B. R. Döös, Numerical weather map analysis. Tellus 7, 329-340 (1955).
58. E. N. Lorenz, Deterministic nonperiodic flow. J. Atmos. Sci. 20, 130-141 (1963).
59. W. S. Wu, R. J. Purser, D. F. Parrish, Three-dimensional variational analysis with spatially
inhomogeneous covariances. Mon. Weather Rev. 130, 2905-2916 (2002).
60. R. Todling, A. El Akkraoui, The GMAO Hybrid Ensemble-Variational Atmospheric Data
Assimilation System: Version 2.0. Available at
https://gmao.gsfc.nasa.gov/pubs/docs/Todling1019.pdf (2018).
61. R. Gelaro et al., The modern-era retrospective analysis for research and applications, version
2 (MERRA-2). J. Clim. 30, 5419-5454 (2017).
9
62. K. Wargan, N. Kramarova, B. Weir, S. Pawson, S. M. Davis, Toward a Reanalysis of
Stratospheric Ozone for Trend Studies: Assimilation of the Aura Microwave Limb Sounder
and Ozone Mapping and Profiler Suite Limb Profiler Data. J. Geophys. Res.: Atmos. 125,
e2019JD031892 (2020).
63. K. Wargan, B. Weir, G. L. Manney, S. E. Cohn, N. J. Livesey, The anomalous 2019
Antarctic ozone hole in the GEOS Constituent Data Assimilation System with MLS
observations. J. Geophys. Res.: Atmos. 125, e2020JD033335 (2020).
64. E. Bell et al., Evaluation of OCO‐2 XCO2 Variability at Local and Synoptic Scales using
Lidar and In Situ Observations from the ACT‐America Campaigns. J. Geophys. Res.:
Atmos. 125, e2019JD031400 (2020).
65. N. Zeng et al., Global to local impacts on atmospheric CO2 caused by COVID-19 lockdown.
Preprint at https://arxiv.org/abs/2010.13025 (2020).
66. T. Oda, S. Maksyutov, R. J. Andres, The Open-source Data Inventory for Anthropogenic
Carbon dioxide (CO2), version 2016 (ODIAC2016): A global, monthly fossil-fuel CO2
gridded emission data product for tracer transport simulations and surface flux inversions.
Earth Syst. Sci. Data 10, 87 (2018).
67. D. L. Goldberg, S. C. Anenberg, D. Griffin, C. A. McLinden, Z. Lu, D. G. Streets,
Disentangling the impact of the COVID‐19 lockdowns on urban NO2 from natural
variability. Geophys. Res. Lett. 47, e2020GL089269 (2020).
68. A. Chatterjee et al., Influence of El Niño on atmospheric CO2 over the tropical Pacific
Ocean: Findings from NASA’s OCO-2 mission. Science 358, eaam5776 (2017).
69. M. L. L’Heureux, M. K. Tippett, A. G. Barnston, Characterizing ENSO coupled variability
and its impact on North American seasonal precipitation and temperature. J. Clim. 28, 4231-
4245 (2015).
70. J. R. Worden et al., Evaluation and attribution of OCO-2 XCO2 uncertainties. Atmos. Meas.
Tech. 10, 2759-2771 (2017).
71. S. S. Kulawik, C. O'Dell, R. R. Nelson, T. E. Taylor, Validation of OCO-2 error analysis
using simulated retrievals. Atmos. Meas. Tech. 12, 5317-5334 (2019).
72. M. Kiel et al., How bias correction goes wrong: measurement of XCO2 affected by
erroneous surface pressure estimates. Atmos. Meas. Tech. 12, 2241–2259 (2019).
73. G. Desroziers, L. Berre, B. Chapnik, P. Poli, Diagnosis of observation, background and
analysis‐error statistics in observation space. Q. J. R. Meteorol. Soc. 131, 3385-3396 (2005).
74. M. Crippa et al., High resolution temporal profiles in the Emissions Database for Global
Atmospheric Research. Nature Sci. Data 7, 121 (2020).
75. Z. Zhang, N. E. Zimmermann, L. Calle, G. Hurtt, A. Chatterjee, B. Poulter, Enhanced
response of global wetland methane emissions to the 2015–2016 El Niño-Southern
oscillation event. Environ. Res. Lett. 13, 074009 (2018).
Acknowledgements
The authors dedicate this article to the memory of Michael Freilich, the former director of the
Earth Science Division of NASA. His skill, dedication, bravado, and commitment were critical to
ensuring that the Orbiting Carbon Observatory-2 even existed. The authors would also like to thank
Kenneth W. Jucks for his invaluable scientific insights and guidance as program manager, Peter
H. Jacobs for comments and suggestions, the NASA Center for Climate Simulation (NCCS),
where all of the computing for this project was conducted, and the Total Carbon Column Observing
10
Network (TCCON) and NOAA for providing data. This work was supported by NASA’s Carbon
Monitoring System (NNH16DA001N-CMS 16-CMS16-0054), Science Team for the OCO
Missions (NNH17ZDA001N-OCO2 17-OCO2-17-0010), and Modeling, Analysis, and Prediction
(NNH16ZDA001N-MAP 16-MAP16-0165) projects. Some of the work described here was
performed at the Jet Propulsion Laboratory, California Institute of Technology, under contract to
the National Aeronautics and Space Administration. Government sponsorship acknowledged. All
authors contributed to the development of the ideas described within this manuscript, the data
collection, and the manuscript’s composition. B. Weir led the writing and development of the data
assimilation system. D. Crisp and C. O’Dell led the development and processing of OCO-2
retrievals. T. Oda led the development of the ODIAC fossil fuel emissions, B. Poulter and Z. Zhang
the LPJ-wsl biospheric model, and P. Ciais, Z. Liu, and S. Davis the NRT activity data based fossil
fuel emissions. The authors declare no competing interests. OCO-2 data were produced by the
OCO-2 project at JPL and were obtained from the free data archive maintained at the Goddard
Earth Sciences Data and Information Services Center (GES DISC;
https://disc.gsfc.nasa.gov/OCO-2). The GEOS/OCO-2 analyzed fields used in this study will be
made available at GES DISC as well.
11
Fig. 1. Snapshots OCO-2 data and assimilated GEOS/OCO-2 fields. (A) 16 days of OCO-2
XCO2 soundings over April 1–16, 2020, (B) transects of 3-hourly, 3-dimensional GEOS/OCO-2
CO2 on April 9, 2020 at 00:00 UTC at the surface (bottom), 15 km above sea level (top,
transparent), and along the International Dateline (right), and (C) the 16-day average of
GEOS/OCO-2 assimilated XCO2 over the same period. In the data assimilation system, satellite
observations (A) are used to update the instantaneous, gridded GEOS fields (B), from which
vertical and temporal averages follow (C). OCO-2 sounding coverage for each month is shown in
Fig. S1 and the impact of assimilation on the fits to observations in Fig. S2.
12
Fig. 2. Anomalies of GEOS/OCO-2 16-day average XCO2 in ppm over the Northern
Hemisphere starting on March 1, 2020 and continuing through June 5, 2020. Blue colors
indicate decreases in XCO2 growth compared to a pandemic-free scenario (see Materials and
Methods), while red colors indicate increases. Reductions surpassing 1 ppm, depicted in deep blue,
developed over North America and Europe in March through May as COVID-19 related
restrictions on activity were put in place. Afterwards, in late May to early June, mixing by
atmospheric transport, rebounds in emissions, and variability in the terrestrial biosphere diminish
the magnitude and coherence of the COVID-19 signal.
13
Fig. 3. Time series of regional average anomalies in GEOS/OCO-2 running 16-day XCO2
anomalies. (A) the United States, (B) Western Europe, (C) Russia, and (D) China. The grey shaded
area indicates the spread of anomalies across the nominal years (2017–2019) and the stem plot
indicates the 2020 anomaly. Simulations for 2020 using activity based emissions estimates (3) are
depicted in blue with asterisks. Dot-dashed lines indicate a rough beginning and end (when
appropriate) to confinements for each area and are provided in Table 1. For the corresponding
histograms of daily sounding counts, see Fig. S3.
Peak reduction
Peak 1
𝜎
uncertainty
Start
End
United States
0.39 ppm
0.07 ppm
March 21
May 16
Western Europe
0.27 ppm
0.16 ppm
March 13
May 20
Russia
0.38 ppm
0.11 ppm
March 31
May 15
China
0.38 ppm
0.13 ppm
January 25
March 25
Table 1. GEOS/OCO-2 February–May regional reductions in XCO2 growth and associated
uncertainties. Reductions and uncertainties are calculated from the data depicted in Fig. 3 (stem
plot and grey shading) as the peak 2020 reduction and peak 1
𝜎
uncertainty in the 2017–2019
spreads for February–May (see Materials and Methods). Start dates and end dates are taken from
activity data (3). The average reduction over all four regions is 0.36 ppm and the geometric mean
of the uncertainties is 0.12 ppm, giving a 1
𝜎
range of 0.24–0.48 ppm for the reduction over the
Northern Hemisphere.
14
Fig. 4. Identical to Fig. 2, but over the Indian ocean before the start of COVID-19 related
confinements. The dominant signal is from the carbon-climate teleconnection between the 2019–
2020 Indian Ocean Dipole (IOD), the strongest on record, and terrestrial biospheric exchange. In
January and February 2020, greater than average precipitation over India and Africa drove
increased biospheric uptake, while higher than average temperatures over Australia and Southeast
Asia drove increased respiration and biomass burning.
Fig. 5. Identical to Fig. 3, but for different regions. (A) India, (B) Australia, and (C) Southern
Africa. The dominant signal is that of the IOD impact over India, but most of the anomalies are
within the range of typical changes. As opposed to the Northern Hemisphere (Fig. 3), early in the
calendar year is a time of significant biospheric activity in the Tropics and Southern Hemisphere
15
(Figs. S8–S10), complicating the interpretation of any anthropogenic variability. For the
corresponding histograms of daily sounding counts, see Fig. S4.
16
Supplementary Materials
Materials and Methods
Data assimilation
The GEOS/OCO-2 atmospheric carbon monitoring system tracks changes in CO2 throughout the
atmosphere every three hours by ingesting OCO-2 Build 10 XCO2 full-physics retrievals (53, 54)
into GEOS using a statistical technique commonly referred to as data assimilation (used here)
and/or state estimation (55, 56). Data assimilation synthesizes simulations and observations,
adjusting the atmospheric state of atmospheric constituents like CO2 to reflect observed values,
thus gap-filling observations when and where they are unavailable. These features are particularly
appealing given the narrow, 10 km wide swath and 16-day repeat time of OCO-2 (Fig. 1).
Compared to interpolation, Kriging, and machine learning methods, data assimilation has the
advantage that it makes estimates based on our collective scientific understanding of Earth’s
carbon cycle, as encapsulated within GEOS, rather than relying on functional relationships that
rarely hold in nature. The value of relying on forecasted fields instead of functional relationships
in data analysis has been understood in the numerical weather prediction community since at least
1954 (57), almost a decade before E. Lorenz’s seminal work (58), yet receives less attention in
other disciplines.
GEOS/OCO-2 applies an implementation of the GEOS Constituent Data Assimilation System
(CoDAS), a high-performance computing implementation of the Gridpoint Statistical Interpolation
(GSI; 59) technique for finding the analyzed state that minimizes the three-dimensional variational
(3D-Var) cost function formulation of its differences with observed and simulated values. In
particular, it ingests column retrievals of trace gas abundances taking into account both their
vertical sensitivity/averaging kernel and a priori assumptions. While current versions of GSI
include the ability to use four-dimensional variational (4D-Var) and hybrid ensemble-variational
formulations (60), this application relies on the simpler 3D-Var technique. In GEOS CoDAS, the
atmospheric circulation is constrained by the millions of remote sensing and in situ observations
every hour included in the Modern Era Retrospective analysis for Research and Application,
version 2 (MERRA-2; 61). This accurate representation of transport patterns is critical for
interpreting measured variations that reflect a combination of nearby and distant surface fluxes
due to the long lifetime of CO2. In other applications, GEOS CoDAS has been used to analyze
multi-decadal trends of stratospheric ozone (62) and the anomalously small ozone hole of 2019
(63).
GEOS/OCO-2 runs on a horizontal grid with a nominal horizontal resolution of 50 km and 72
terrain-following vertical levels from the surface up to 0.01 hPa. Fig. 1 demonstrates the impact
of data assimilation on OCO-2 coverage for April 2020. Before assimilation (top panel), there are
notable patches of missing data where either clouds (e.g., the Amazon), aerosols (China), and high
solar zenith angles (the poles) prevent reliable measurements. Assimilation produces three-
dimensional CO2 fields with global coverage that are updated every three hours (middle panel).
Values in missing areas are inferred from nearby observational data and model relationships. The
16-day running means (bottom panel) and monthly means analyzed in this paper follow from
17
simple averaging of the assimilated CO2 fields. Data processing is divided into six separate streams
covering 2015–2020. Each stream begins on October 31 of the previous year to allow some
equilibration of the analysis prior to the period of interest beginning on January 1. Differences
between overlapping streams are less than 10% of the magnitude of the anomalies analyzed in this
paper, and thus can be safely ignored.
GEOS/OCO-2 has been previously documented for an earlier version of OCO-2 data (10), and has
been available to the public through May 2020 on the NASA/ESA/JAXA trilateral Earth
Observing Dashboard (18) since late July. Its fine spatial resolution enables it to reproduce
atmospheric observations with high fidelity (31, 64), especially over North America, where there
is a wealth of data, e.g., airborne in situ measurements from NASA’s Atmospheric Carbon and
Transport - America (ACT-America) campaign (64). Its extensive evaluation makes us confident
in its ability to reproduce regional signals with small magnitudes. A recent study (65) claims to
have found a COVID-19 signal on the global scale (50°N to 50°S), but most likely mistook it for
the record-setting IOD signal, since they find reductions starting in January (before lockdowns)
concentrated mostly in the Tropics and Southern Hemisphere, emphasizing the need for regional
and monthly resolution and careful consideration in the analysis of anthropogenic CO2 signals.
A unique feature of GEOS CoDAS is its ability to process data in NRT, as retrievals become
available to assimilate. This is accomplished primarily through the use of a surface flux collection,
the Low-order Flux Inversion (LoFI; 31) with distinct modes for retrospective and NRT
simulations. In retrospective simulations, the system uses surface fluxes informed by several
remote sensing datasets that include fire radiative power, nighttime lights, and vegetation
properties like leaf area index (26) and atmospheric growth rate estimates derived from surface
observations. In near real time, before many of these datasets become available, LoFI uses fluxes
and a projected atmospheric growth rate based on data from previous years and the current ENSO
phase (38, 39). This dual capability ensures a strong, multi-platform data constraint on XCO2 on
previous years for computing anomalies while the products for the current year highlight areas
where land, ocean, and fossil fuel fluxes deviate from expectations. For fossil fuel emissions, we
use the 2018 version of the Open-source Data Inventory for Anthropogenic CO2 (ODIAC; 66),
which estimates emissions by tracking fossil fuel consumption (i.e., barrels of oil, tons of coal,
etc.) and cement production. The ODIAC 2018 product ends in 2018. In 2019, we rescale the 2018
monthly gridded maps to match the Global Carbon Project (GCP) 2019 global emissions estimate
(34), and for 2020 we simply repeat 2019 emissions.
Anomalies and pandemic-free baseline atmospheric CO2 fields
Even after obtaining realistic, gap-filled XCO2 maps, defining 2020 anomalies for CO2 is more
challenging than for most other species. For NO2, which is short-lived, simply subtracting a multi-
year mean from the 2020 values is often sufficient for highlighting recent emissions changes (5),
although recent research suggests that such methods can ignore important meteorological
variations (7, 67). For CO2 and other long-lived species, this simple anomaly calculation reveals a
strong imprint of circulation anomalies, which can have a greater impact than and obscure the
spatial signature of emissions changes (Fig. S5). To minimize the circulation influence, at the
beginning of each year we start a companion GEOS simulation that is identical to the analyzed
product, except that OCO-2 data are not assimilated. By subtracting the simulated anomaly from
18
the analysis anomaly, we isolate the flux-driven signal observed by OCO-2 from the transport-
variability-driven signal. We refer to this difference as the “analysis correction.” The pandemic-
free, baseline scenario is then the average of all analysis corrections for 2017–2019 plus the GEOS
simulation for 2020. This represents 2020 transport while applying the mean analysis corrections
due to assimilating OCO-2. Subtracting the 2020 analysis from the pandemic-free field then gives
the flux driven GEOS/OCO-2 anomaly depicted in Figs. 2–5 and in the supplemental figures.
We omit 2015 and 2016 from our baseline years because they contain one of the strongest ENSOs
on record and are not representative of 2020, which was neutral in the first three months of 2020,
and transitioned to a moderate La Nina in April 2020 (36, 37). Strong ENSO signals produce
significant inter-annual variability in carbon fluxes over ocean and land (32, 68) as well as
atmospheric circulation patterns (69). Figs. S6 and S7 add the 2015 and 2016 anomalies onto the
plots from Figs. 3 and 5. The ENSO years (red) are clear outliers, supporting their exclusion from
the analysis.
Uncertainty quantification
As an indicator of uncertainty, we use the range of analysis corrections for individual years in
2017–2019 depicted as the grey shading in Figs. 3 and 5. From the ranges, we calculate the 2
𝜎
uncertainty as half the min-to-max range of the grey shaded area, corresponding to an assumption
that the 2017–2019 range represents about 95% of year-to-year variability in neutral ENSO
conditions. The uncertainty ranges reported in Table 1 are consistent with evaluations of
GEOS/OCO-2 against independent surface in situ and remote sensing observations and a posteriori
tests of the statistical consistency of the data assimilation system (see Supplement). They are
smaller than, but the same order as the errors reported by the analyses in several previous studies
(17, 70–72). This is to be expected as our uncertainty estimate does not include persistent biases,
while those estimates do. They also coincide with a 0.15 ppm standard deviation of the analysis
error uncertainty for the GEOS/OCO-2 fields calculated from an a posteriori diagnostic (73).
Separating the COVID-19 atmospheric CO2 signal from natural variability
In order to help separate anthropogenic from natural variability, we perform two supplementary
GEOS CO2 simulations. The first transports the difference in 2020 and 2019 emissions from the
daily activity data based fossil fuel estimates (3) through the atmosphere using the same settings
as the GEOS/OCO-2 assimilation run (see the monthly global maps in Fig. S9). For these
simulations, daily country-level emissions totals for 2019 and 2020 are spatially downscaled using
2015 monthly EDGAR v5.0 sector totals (74) for power generation, ground transportation,
industry, aviation, residential energy usage, and international shipping. The second simulation
aims to represent the difference in 2020 biospheric flux by transporting the difference between
2020 and the 2017–2019 average calculated using the LPJ-wsl dynamic global vegetation model
(Figs. S8–S10). While LPJ-wsl is a different model of the terrestrial biosphere than we use for our
prior fluxes, it is useful as a prognostic, independent method of identifying regional biospheric
anomalies and has been demonstrated to realistically reproduce interannual variations in global net
flux (34). For consistency, we apply the same MERRA-2 meteorological data used to force our
transport simulations and as inputs to LPJ-wsl (75).
19
Fig. S1. Monthly maps of OCO-2 B10 XCO2 retrieval coverage. The OCO-2 satellite flies in a
sun-synchronous, low-Earth orbit with a local overpass time of 1:30 PM in NASA’s Afternoon
Train (A-Train) formation.
20
Fig. S2 (continued below ...). Monthly maps of OCO-2 minus GEOS/OCO-2 background
(before assimilation; top rows) and analysis (after assimilation; bottom rows) XCO2.
Assimilation clearly improves the fits to the assimilated data, as intended. Differences after
assimilation have O(0.1 ppm) magnitudes, further supporting the uncertainty quantification in the
paper.
21
Fig. S2 (... continued from above).
22
Fig. S3. Identical to Fig. 3 with OSE results (red open squares) and daily soundings (lower
panel) for 2020 (black lines) and the 2017–2019 average (grey shading). The proximity of the
OSE results to the simulated values (blue dots) demonstrates that the data coverage and
assimilation system can reliably capture the signal of activity-data emissions reduction estimates,
i.e., differences between the analyzed 2020 values (stem plot) and simulated values (blue dots)
cannot be attributed to the data constraint alone.
23
Fig. S4. Identical to Fig. 5 with OSE results (red open squares) and daily soundings (lower
panel) for 2020 (black lines) and the 2017–2019 average (grey shading). While the OSE results
reproduce the general features of the simulated values (blue dots), there is a noticeable offset in all
three regions. This is to be expected given the greater biospheric influence than in the Northern
Hemisphere (Fig. S9) represented by the greater width of the grey shaded area and the low
sounding coverage over India during their monsoon.
24
Fig. S5. Anomalies of GEOS/OCO-2 monthly average XCO2 in ppm during early 2020
computed with two different pandemic-free baseline scenarios. The top row, used in the text,
makes an adjustment for year-to-year variability in atmospheric transport by subtracting out
simulated values. The bottom row does not make this adjustment, and much of its variability is
thus dominated by that due to transport. In particular, the large positive/negative anomaly over
Western/Eastern Europe in May 2020 in the calculation without the adjustment (bottom right) is
almost entirely due to an anomaly in atmospheric circulation patterns (Fig. S11).
25
Fig. S6. Identical to Fig. 3, but with the range of the 2015–2016 ENSO years included. ENSO
anomalies are negative because our surface fluxes underpredict the Northern Hemisphere land sink
in these years.
Fig. S7. Identical to Fig. 5, but with the range of the 2015–2016 ENSO years included.
26
Fig. S8. Cumulative NBE anomalies from LPJ-wsl terrestrial biospheric model over different
countries/regions. Each line represents a different year with years before the OCO-2 launch
(2014) drawn in grey, years after the OCO-2 launch drawn in black, 1982 drawn in green (most
recent IOD of comparable magnitude), and 2020 drawn in red. The year 2020 is a clear outlier in
South Asia and Oceania/Australia, indicating strong biospheric anomalies. Over North America,
Europe, and East Asia (viz., China), 2020 is a typical year for the biosphere, if not more of a source
(positive values) of carbon to the atmosphere.
27
Fig. S9 (continued below ...). Monthly maps of XCO2 in ppm from the GEOS/OCO-2
anomaly analysis (top), simulation of LPJ-wsl biospheric flux anomalies (middle), and
simulation of fossil fuel emissions (3) anomalies (bottom). In January through February, the
GEOS/OCO-2 anomaly captures the IOD signal over India, Australia, and Africa, showing
remarkable agreement with the spatial patterns from the LPJ-wsl simulation. The difference in
amplitudes is because LPJ-wsl tends to produce a far greater seasonal cycle amplitude over these
regions than we would expect from LoFI (Fig. S10).
28
Fig. S9 (... continued from above and below ...). In February–May, the biospheric variability
over the United States, Europe, Russia, and China simulated from LPJ-wsl remains relatively small
and, if anything, net positive, supporting the attribution of the analysis anomalies changes in fossil
fuel emissions. In June, biospheric variability begins to dominate in the Northern Hemisphere,
complicating the interpretation of any anthropogenic signals (cf. the growth into June and July of
the grey shaded regions in Fig. 3), e.g., the large negative analysis anomaly over Siberia in June
(top right) is most likely due to the biosphere (middle right).
29
Fig. S9 (... continued from above).
30
Fig. S10. NBE from our a priori surface fluxes (LoFI, black) and the LPJ-wsl model (red)
used for simulating biospheric anomalies. There is striking similarity between the two globally
and over much of the world, e.g., Boreal Eurasia and Europe. Over North and South Africa, LPJ-
wsl produces a seasonal cycle that is about twice as great as LoFI, while over Boreal North
America the difference in amplitude is roughly a factor of three. The difference in Temperate North
America is likely due to significant differences in the representation of corn and soybean harvest
between the two products.
31
Fig. S11 (continued below …). Meteorological anomalies for 2020 in percent for sea-level
pressure (top) and the geopotential height at 500 hPa (bottom). The strong correlation between
the two is due to hydrostatic balance.
32
Fig S11 (... continued from above).
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
The COVID-19 pandemic resulted in reduced anthropogenic carbon dioxide (CO2) emissions during 2020 in large parts of the world. To investigate whether a regional-scale reduction of anthropogenic CO2 emissions during the COVID-19 pandemic can be detected using space-based observations of atmospheric CO2, we have analysed a small ensemble of OCO-2 and GOSAT satellite retrievals of column-averaged dry-air mole fractions of CO2, i.e. XCO2. We focus on East China and use a simple data-driven analysis method. We present estimates of the relative change of East China monthly emissions in 2020 relative to previous periods, limiting the analysis to October-to-May periods to minimize the impact of biogenic CO2 fluxes. The ensemble mean indicates an emission reduction by approximately 10 % ± 10 % in March and April 2020. However, our results show considerable month-to-month variability and significant differences across the ensemble of satellite data products analysed. For example, OCO-2 suggests a much smaller reduction (∼ 1 %–2 % ± 2 %). This indicates that it is challenging to reliably detect and to accurately quantify the emission reduction with current satellite data sets. There are several reasons for this, including the sparseness of the satellite data but also the weak signal; the expected regional XCO2 reduction is only on the order of 0.1–0.2 ppm. Inferring COVID-19-related information on regional-scale CO2 emissions using current satellite XCO2 retrievals likely requires, if at all possible, a more sophisticated analysis method including detailed transport modelling and considering a priori information on anthropogenic and natural CO2 surface fluxes.
Article
Full-text available
Social distancing to combat the COVID-19 pandemic has led to widespread reductions in air pollutant emissions. Quantifying these changes requires a business-as-usual counterfactual that accounts for the synoptic and seasonal variability of air pollutants. We use a machine learning algorithm driven by information from the NASA GEOS-CF model to assess changes in nitrogen dioxide (NO2) and ozone (O3) at 5756 observation sites in 46 countries from January through June 2020. Reductions in NO2 coincide with the timing and intensity of COVID-19 restrictions, ranging from 60 % in severely affected cities (e.g., Wuhan, Milan) to little change (e.g., Rio de Janeiro, Taipei). On average, NO2 concentrations were 18 (13–23) % lower than business as usual from February 2020 onward. China experienced the earliest and steepest decline, but concentrations since April have mostly recovered and remained within 5 % of the business-as-usual estimate. NO2 reductions in Europe and the US have been more gradual, with a halting recovery starting in late March. We estimate that the global NOx (NO + NO2) emission reduction during the first 6 months of 2020 amounted to 3.1 (2.6–3.6) TgN, equivalent to 5.5 (4.7–6.4) % of the annual anthropogenic total. The response of surface O3 is complicated by competing influences of nonlinear atmospheric chemistry. While surface O3 increased by up to 50 % in some locations, we find the overall net impact on daily average O3 between February–June 2020 to be small. However, our analysis indicates a flattening of the O3 diurnal cycle with an increase in nighttime ozone due to reduced titration and a decrease in daytime ozone, reflecting a reduction in photochemical production. The O3 response is dependent on season, timescale, and environment, with declines in surface O3 forecasted if NOx emission reductions continue.
Article
Full-text available
We use a global transport model and satellite retrievals of the carbon dioxide (CO2) column average to explore the impact of CO2 emissions reductions that occurred during the economic downturn at the start of the Covid‐19 pandemic. The changes in the column averages are substantial in a few places of the model global grid, but the induced gradients are most often less than the random errors of the retrievals. The current necessity to restrict the quality‐assured column retrievals to almost cloud‐free areas appears to be a major obstacle in identifying changes in CO2 emissions. Indeed, large changes have occurred in the presence of clouds and, in places that were cloud‐free in 2020, the comparison with previous years is hampered by different cloud conditions during these years. We therefore recommend to favor all‐weather CO2 monitoring systems, at least in situ, to support international efforts to reduce emissions.
Article
Full-text available
The COVID-19 pandemic is impacting human activities, and in turn energy use and carbon dioxide (CO₂) emissions. Here we present daily estimates of country-level CO2 emissions for different sectors based on near-real-time activity data. The key result is an abrupt 8.8% decrease in global CO₂ emissions (−1551 Mt CO₂) in the first half of 2020 compared to the same period in 2019. The magnitude of this decrease is larger than during previous economic downturns or World War II. The timing of emissions decreases corresponds to lockdown measures in each country. By July 1st, the pandemic’s effects on global emissions diminished as lockdown restrictions relaxed and some economic activities restarted, especially in China and several European countries, but substantial differences persist between countries, with continuing emission declines in the U.S. where coronavirus cases are still increasing substantially.
Article
Full-text available
Plain Language Summary Satellite measurements such as TROPOMI have already captured the public's attention through remarkable images of pollutant reductions. However, the inference of emissions must account for variations in atmospheric transport, chemical environment, and meteorology. To that end, we used an advanced chemical data assimilation system that incorporate these factors through ingestion of multiple chemical satellite and in situ observations into a chemical transport model. We then quantified the reductions in emissions attributable to COVID‐19 lockdown and determine the impact of those reduction on human health through pollutant exposure. We find that our Chinese NOx emission reductions had opposing air quality responses depending on timing, location, and pollutant. Our investigation showed increases in ozone‐related morbidity incidences in Northern China but larger nationwide reductions from PM2.5 that led to overall reductions in hospital admissions and alleviating negative impacts of delayed treatment.
Article
Full-text available
NASA's Orbiting Carbon Observatory-3 (OCO-3) was installed on the International Space Station (ISS) on 10 May 2019. OCO-3 combines the flight spare spectrometer from the Orbiting Carbon Observatory-2 (OCO-2) mission, which has been in operation since 2014, with a new Pointing Mirror Assembly (PMA) that facilitates observations of non-nadir targets from the nadir-oriented ISS platform. The PMA is a new feature of OCO-3, which is being used to collect data in all science modes, including nadir (ND), sun-glint (GL), target (TG), and the new snapshot area mapping (SAM) mode. This work provides an initial assessment of the OCO-3 instrument and algorithm performance, highlighting results from the first 8 months of operations spanning August 2019 through March 2020. During the In-Orbit Checkout (IOC) phase, critical systems such as power and cooling were verified, after which the OCO-3 spectrometer and PMA were subjected to a series of rigorous tests. First light of the OCO-3 spectrometer was on 26 June 2019, with full science operations beginning on 6 August 2019. The OCO-3 spectrometer on-orbit performance is consistent with that seen during preflight testing. Signal to noise ratios are in the expected range needed for high quality retrievals of the column-averaged carbon dioxide (CO2) dry-air mole fraction (XCO2) and solar-induced chlorophyll fluorescence (SIF), which will be used to help quantify and constrain the global carbon cycle. The first public release of OCO-3 Level 2 (L2) data products, called “vEarly”, is being distributed by NASA's Goddard Earth Sciences Data and Information Services Center (GES DISC). The intent of the vEarly product is to evaluate early mission performance, facilitate comparisons with OCO-2 products, and identify key areas to improve for the next data release. The vEarly XCO2 exhibits a root-mean-squared-error (RMSE) of ≃ 1, 1, 2 ppm versus a truth proxy for nadir-land, TG&SAM, and glint-water observations, respectively. The vEarly SIF shows a correlation with OCO-2 measurements of >0.9 for highly coincident soundings. Overall, the Level 2 SIF and XCO2 products look very promising, with performance comparable to OCO-2. A follow-on version of the OCO-3 L2 product containing a number of refinements, e.g., instrument calibration, pointing accuracy, and retrieval algorithm tuning, is anticipated by early in 2021.
Article
Full-text available
A rare disturbance of the stratospheric Antarctic polar vortex in September 2019 led to a significantly higher than usual polar total ozone column. We use assimilation of ozone, HCl, and N2O data from the Microwave Limb Sounder with the Global Earth Observing System (GEOS) Constituent Data Assimilation System driven by reanalysis meteorology to study the evolution of the 2019 Antarctic polar ozone. We find that the maximum 2019 ozone hole area was near 10 × 10⁶ km², and as little as 20% of that in 2018 in mid‐September. However, the magnitude of vortex‐averaged chemical ozone depletion was not significantly different between the 2 years despite earlier chlorine deactivation in 2019. The assimilation results show that most of the differences between 2018 and 2019 Antarctic ozone resulted from two factors: (1) the geometry of the 2019 vortex, with ozone‐rich middle‐stratospheric air masses overlying the lower portion of the vortex and leading to a significant reduction of the total column, and (2) significantly reduced vortex volume. The anomalously small ozone hole of 2019 was comparable in size to the record breaking 2002 case and the mechanisms responsible were similar in the two cases. While the 2019 sudden stratospheric warming is classified as minor, its impact on ozone was very significant.
Article
Full-text available
TROPOMI satellite data show substantial drops in nitrogen dioxide (NO2) during COVID-19 physical distancing. To attribute NO2 changes to NOX emissions changes over short timescales, one must account for meteorology. We find that meteorological patterns were especially favorable for low NO2 in much of the U.S. in spring 2020, complicating comparisons with spring 2019. Meteorological variations between years can cause column NO2 differences of ~15% over monthly timescales. After accounting for sun angle and meteorological considerations, we calculate that NO2 drops ranged between 9.2 - 43.4% among twenty cities in North America, with a median of 21.6%. Of the studied cities, largest NO2 drops (>30%) were in San Jose, Los Angeles, and Toronto, and smallest drops (<12%) were in Miami, Minneapolis, and Dallas. These normalized NO2 changes can be used to highlight locations with greater activity changes and better understand the sources contributing to adverse air quality in each city.
Article
Full-text available
Restrictions to reduce human interaction have helped to avoid greater suffering and death from the COVID-19 pandemic, but have also created socioeconomic hardship. This disruption is unprecedented in the modern era of global observing networks, pervasive sensing and large-scale tracking of human mobility and behaviour, creating a unique test bed for understanding the Earth System. In this Perspective, we hypothesize the immediate and long-term Earth System responses to COVID-19 along two multidisciplinary cascades: energy, emissions, climate and air quality; and poverty, globalization, food and biodiversity. While short-term impacts are dominated by direct effects arising from reduced human activity, longer-lasting impacts are likely to result from cascading effects of the economic recession on global poverty, green investment and human behaviour. These impacts offer the opportunity for novel insight, particularly with the careful deployment of targeted data collection, coordinated model experiments and solution-oriented randomized controlled trials, during and after the pandemic.
Article
Full-text available
China’s policy interventions to reduce the spread of the coronavirus disease 2019 have environmental and economic impacts. Tropospheric nitrogen dioxide indicates economic activities, as nitrogen dioxide is primarily emitted from fossil fuel consumption. Satellite measurements show a 48% drop in tropospheric nitrogen dioxide vertical column densities from the 20 days averaged before the 2020 Lunar New Year to the 20 days averaged after. This is 21% ± 5% larger than that from 2015–2019. We relate this reduction to two of the government’s actions: the announcement of the first report in each province and the date of a province’s lockdown. Both actions are associated with nearly the same magnitude of reductions. Our analysis offers insights into the unintended environmental and economic consequences through reduced economic activities.