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collection of scientific article
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demand variability
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electricity demand value
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emission reduction factor
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energy industry
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impact of covid 19
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pandemic lockdown
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reg AP emission inventory
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threshold temperature value
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Bibliography on air quality before, during and after lockdown.
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http://w3id.org/ro/earth-science#Sentence
Collection of scientific articles and other communications related to the impact of COVID-19 pandemic lockdown on air quality pollution.
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http://w3id.org/ro/earth-science#Sentence
Figure summarizes the main statistics (normalized meanbias, NMB; normalized root mean square error, NRMSE;and correlation, r) obtained from the comparison betweenmeasured and ML based electricity demand during the first months of for selected countries.
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
http://w3id.org/ro/earth-science#Sentence
In this study, ML models are used for predictingthe fluctuations of electricity demand based on the temper ature (and additional time features) assuming that temper ature is a strong driver of electricity demand (for heatingand air conditioning) However, temperature is obviously notthe only driver of electricity demand variability that can beinfluenced by various other factors (e.g. change of technol ogy, behaviour, regulation) In addition, the GBM modelsused in this study are non parametric, meaning that they can not extrapolate, i.e. predict electricity demand values out side the range of values used during the training phase.
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
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The ECHAM HAM and CESM NoT ensembles allow more freedom for temperature adjustment.
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The ECHAM HAM simulation set up is most similar to the CESM NoT ensemble described below.
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The average temperature was not availablefor Los Angeles (LA) New York City (NYC) and Sydney, so the maximum temperature was used,as the maximum temperature is important for ozone formation.
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
http://w3id.org/ro/earth-science#Sentence
The daily median AQI was used in this study for each of major cities.
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
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The datasetprovides a statistical summary for each of the air pollutant species, all air pollutants are converted toan Air Quality Index (AQI) with the U.S. Environmental Protection Agency (EPA) standard calculation.
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
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The same emissions scenario (from Forster et al.) is run as for CESM using monthly emissions.
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Thepoorest performance was obtained in Finland (r.) dueto a strong negative anomaly (on average) of elec tricity demand in January February compared to pre vious years used for training.
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in spring
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winter
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European Union
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Google
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International Agency for Research on Cancer
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International Energy Agency
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National Aeronautics and Space Administration
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Oxford University
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World Health Organization
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World Meteorological Organization
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Barcelona
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Belgium
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Berlin
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Brazil
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British Columbia
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Bulgaria
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China
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Claremont
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Cyprus
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Delaware
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Delhi
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Denmark
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Estonia
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Europe
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Finland
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France
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Georgia
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Germany
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Hungary
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India
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Iran
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Ireland
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Istanbul
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Italy
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Japan
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Leeds
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Lima
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Mexico City
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Mexico
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New Hampshire
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New York
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Norway
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Occident
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Oxford
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Paris
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Reading
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Rome
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Russia
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Seoul
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Slovakia
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South America
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South Korea
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Spain
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Sweden
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The COVID-19 pandemic led to dramatic changes in economic activity in 2020. In this paper the authors use estimates of emission changes for 2020 in two Earth System Models (ESMs) to simulate the impacts of the COVID-19 economic changes.
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Climate Impacts of COVID-19 Induced Emission Changes
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The COVID-19 pandemic has affected severely the economic structure and health care system, among others, of India and the rest of the world. The magnitude of its aftermath is exceptionally devastating in India, with the first case reported in January 2020, and the number has risen to ~31.3 million as of July 23, 2021. India imposed a complete lockdown on March 25, which severely impacted migrant population, industrial sector, tourism industry, and overall economic growth. Herein, the impacts of lockdown and unlock phases on ambient atmospheric air quality variables have been assessed across 16 major cities of India covering the north-to-south stretch of the country. In general, all assessed air pollutants showed a substantial decrease in AQI values during the lockdown compared with the reference period (2017–2019) for almost all the reported cities across India. On an average, about 30–50% reduction in AQI has been observed for PM2.5, PM10, and CO, and maximum reduction of 40–60% of NO2 has been observed herein, while the data was average for northern, western, and southern India. SO2 and O3 showed an increase over a few cities as well as a decrease over the other cities. Maximum reduction (49%) in PM2.5 was observed over north India during the lockdown period. Furthermore, the changes in pollution levels showed a significant reduction in the first three phases of lockdown and a steady increase during subsequent phase of lockdown and unlock period. Our results show the substantial effect of lockdown on reduction in atmospheric loading of key anthropogenic pollutants due to less-to-no impact from industrial activities and vehicular emissions, and relatively clean transport of air masses from the upwind region. These results indicate that by adopting cleaner fuel technology and avoiding poor combustion activities across the urban agglomerations in India could bring down ambient levels of air pollution at least by 30%.
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Effect of Lockdown Amid COVID-19 on Ambient Air Quality in 16 Indian Cities
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There is a strong body of evidence to show how air pollution affects different aspects of health at even lower concentrations than previously understood. But here’s what hasn’t changed: every year, exposure to air pollution is still estimated to cause millions of deaths and the loss of healthy years of life.
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WHO global air quality guidelines. Particulate matter (PM2.5 and PM10), ozone, nitrogen dioxide, sulfur dioxide and carbon monoxide
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In this paper the authors quantify the reductions in primary emissions due to the COVID-19 lockdowns in Europe. Their estimates are provided in the form of a dataset of reduction factors varying per country and day that will allow the modelling and identification of the associated impacts upon air quality.
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Time-resolved emission reductions for atmospheric chemistry
modelling in Europe during the COVID-19 lockdowns
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Waste natural gas from industrial oil and gas fields could be a source of nitrogen dioxide and black carbon pollution, according to new research.
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Scientists Show Connection Between Gas Flaring and Arctic Pollution
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This study has used, in a first stage, Sentinel-5P and CAMS service to analyze the air quality in the territory of Iberian Peninsula, as well as assess in detail major cities within the region (Lisbon, Porto and Madrid), for a period from January 2018 to April 2020. On a later stage, the data from Sentinel-3A and 3B allowed the analysis of water quality during the months March, April and May 2020, in the Portuguese coast. Regarding the air quality, NO2 and PM10 levels in the Iberian Peninsula were consistently lower compared to the same periods in the two past years.
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Air and Water Quality Improvement during COVID-19 lockdown
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In this work the authors investigate the short-term variations in air quality emissions, attributed to the prevention measures, applied in different cities, to mitigate the COVID-19 spread. Part of the analysis employs a variety of machine learning tools.
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Assessing the Lockdown Effects on Air Quality during COVID-19 Era
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Paris coronavirus. Man wearing a mask walking in front of the Eiffel Tower on the first day of Paris lock-down. Photo by The Paris Photographer on Unsplash
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Paris during the lockdown
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Concawe has undertaken a city-level analysis to quantify the
ways in which the Covid-19 lockdown measures have had an
impact on air quality in Europe. This article presents the results of the analysis for particulate matter (PM 2.5 ), nitrogen dioxide (NO2 ) and ozone (O3 ).
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How Covid-19 lockdown affected air pollution in Europe — a multi-city analysis
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To assess the impact of the COVID-19 pandemic lockdown on air quality worldwide, Air Quality Index (AQI) data was used to estimate the change in air quality in 20 major cities on six continents. Our results show significant declines of AQI in NO2 , SO2 , CO, PM 2.5 and PM 10 in most cities, mainly due to the reduction of transportation, industry and commercial activities during lockdown.
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Impact of the COVID-19 Pandemic Lockdown on Air Pollution in 20 Major Cities around the World
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https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/resources/bc6922f1-debf-46ae-ba79-d574f6f5c064
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://purl.org/wf4ever/wf4ever#Resource
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/resources/bc6922f1-debf-46ae-ba79-d574f6f5c064
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://schema.org/MediaObject
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/ro-crate-metadata.json
http://purl.org/dc/terms/conformsTo
https://w3id.org/ro/crate/1.1
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/ro-crate-metadata.json
http://schema.org/about
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/ro-crate-metadata.json
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://schema.org/CreativeWork
mailto:annefou@geo.uio.no
http://schema.org/affiliation
Nordic e-Infrastructure Collaboration (NeIC)
mailto:annefou@geo.uio.no
http://schema.org/email
annefou@geo.uio.no
mailto:annefou@geo.uio.no
http://schema.org/name
Anne Fouilloux
mailto:annefou@geo.uio.no
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://xmlns.com/foaf/0.1/Agent
mailto:annefou@geo.uio.no
https://w3id.org/dingo#orcid
0000-0002-1784-2920
mailto:jean.iaquinta@geo.uio.no
http://schema.org/affiliation
UiO
mailto:jean.iaquinta@geo.uio.no
http://schema.org/email
jean.iaquinta@geo.uio.no
mailto:jean.iaquinta@geo.uio.no
http://schema.org/name
Jean Iaquinta
mailto:jean.iaquinta@geo.uio.no
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://xmlns.com/foaf/0.1/Agent
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/provenance
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/assertion
http://www.w3.org/ns/prov#wasDerivedFrom
https://api.rohub.org/api/ros/374d0d3a-4807-4925-be83-b9eea52356e3/crate/download/ro-crate-metadata.json
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/pubinfo
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
http://purl.org/dc/terms/created
2026-03-03T16:43:09.546+01:00
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
http://purl.org/dc/terms/creator
https://w3id.org/kpxl/gen/terms/RoCrateBot
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
http://purl.org/nanopub/x/introduces
https://w3id.org/ro-id/374d0d3a-4807-4925-be83-b9eea52356e3/
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
http://www.w3.org/1999/02/22-rdf-syntax-ns#type
http://purl.org/nanopub/x/RoCrateNanopub
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
http://www.w3.org/2000/01/rdf-schema#label
Bibliography on air quality before, during and after lockdown.
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/sig
http://purl.org/nanopub/x/hasAlgorithm
RSA
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/sig
http://purl.org/nanopub/x/hasPublicKey
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https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/sig
http://purl.org/nanopub/x/hasSignature
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https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/sig
http://purl.org/nanopub/x/hasSignatureTarget
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4
https://w3id.org/np/RAEe7AGjhCphfW3jm6KOb-HHTMFLktTf8V5vKT5mPDcD4/sig
http://purl.org/nanopub/x/signedBy
https://w3id.org/kpxl/gen/terms/RoCrateBot