Frequency distribution of pollutant concentrations over Indian megacities impacted by the COVID-19 lockdown.

Item request has been placed! ×
Item request cannot be made. ×
loading   Processing Request
  • Additional Information
    • Source:
      Publisher: Springer Country of Publication: Germany NLM ID: 9441769 Publication Model: Print-Electronic Cited Medium: Internet ISSN: 1614-7499 (Electronic) Linking ISSN: 09441344 NLM ISO Abbreviation: Environ Sci Pollut Res Int Subsets: MEDLINE
    • Publication Information:
      Publication: <2013->: Berlin : Springer
      Original Publication: Landsberg, Germany : Ecomed
    • Subject Terms:
    • Abstract:
      The megacities experience poor air quality frequently due to stronger anthropogenic emissions. India had one of the longest lockdowns in 2020 to curb the spread of COVID-19, leading to reductions in the emissions from anthropogenic activities. In this article, the frequency distributions of different pollutants have been analysed over two densely populated megacities: Delhi (28.70° N; 77.10° E) and Kolkata (22.57° N; 88.36° E). In Delhi, the percentage of days with PM 2.5 levels exceeding the National Ambient Air Quality Standards (NAAQS) between 25 March and 17 June dropped from 98% in 2019 to 61% in 2020. The lockdown phase 1 brought down the PM 10 (particulate matter having an aerodynamic diameter ≤ 10 μm) levels below the daily NAAQS limit over Delhi and Kolkata. However, PM 10 exceeded the limit of 100 μgm -3 during phases 2-5 of lockdown over Delhi due to lower temperature, weaker winds, increased relative humidity and commencement of limited traffic movement. The PM 2.5 levels exhibit a regressive trend in the highest range from the year 2019 to 2020 in Delhi. The daily mean value for PM 2.5 concentrations dropped from 85-90 μgm -3 to 40-45 μgm -3 bin, whereas the PM 10 levels witnessed a reduction from 160-180 μgm -3 to 100-120 μgm -3 bin due to the lockdown. Kolkata also experienced a shift in the peak of PM 10 distribution from 80-100 μgm -3 in 2019 to 20-40 μgm -3 during the lockdown. The PM 2.5 levels in peak frequency distribution were recorded in the 35-40 μgm -3 bin in 2019 which dropped to 15-20 μgm -3 in 2020. In line with particulate matter, other primary gaseous pollutants (NO x , CO, SO 2 , NH 3 ) also showed decline. However, changes in O 3 showed mixed trends with enhancements in some of the phases and reductions in other phases. In contrast to daily mean O 3 , 8-h maximum O 3 showed a reduction over Delhi during lockdown phases except for phase 3. Interestingly, the time of daily maximum was observed to be delayed by ~ 2 h over Delhi (from 1300 to 1500 h) and ~ 1 h over Kolkata (from 1300 to 1400 h) almost coinciding with the time of maximum temperature, highlighting the role of meteorology versus precursors. Emission reductions weakened the chemical sink of O 3 leading to enhancement (120%; 11 ppbv) in night-time O 3 over Delhi during phases 1-3.
      (© 2021. The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature.)
    • References:
      Ansari TU, Ojha N, Chandrasekar R, Balaji C, Singh N, Gunthe SS (2016) Competing impact of anthropogenic emissions and meteorology on the distribution of trace gases over Indian region. J Atmos Chem 73(4). https://doi.org/10.1007/s10874-016-9331-y.
      Bedi JS, Dhaka P, Vijay D, Aulakh RS, Gill JPS (2020) Assessment of Air quality changes in the Four metropolitan cities of India during COVID-19 pandemic lockdown. Aerosol and Air Quality Research 20(10):2062–2070. https://doi.org/10.4209/aaqr.2020.05.0209. (PMID: 10.4209/aaqr.2020.05.0209)
      Bera B, Bhattacharjee S, Shit PK, Sengupta N, Saha S (2021) Significant impacts of COVID-19 lockdown on urban air pollution in Kolkata (India) and amelioration of environmental health. Environ Dev Sustain 23(5):6913–6940. https://doi.org/10.1007/s10668-020-00898-5. (PMID: 10.1007/s10668-020-00898-5)
      Chakraborty M, Debnath S, Ghosh S (2021) A study during lockdown period based on AQI over Indian mega cities during COVID-19. J Phys: Conf Ser 1797(1):012056. https://doi.org/10.1088/1742-6596/1797/1/012056. (PMID: 10.1088/1742-6596/1797/1/012056)
      Chowdhury S, Dey S, Guttikunda S, Pillarisetti A, Smith KR, Di Girolamo L (2019) Indian annual ambient air quality standard is achievable by completely mitigating emissions from household sources. Proc Natl Acad Sci 116(22):10711–10716. https://doi.org/10.1073/pnas.1900888116. (PMID: 10.1073/pnas.1900888116)
      Chutia L, Ojha N, Girach IA, Sahu LK, Alvarado LMA, Burrows JP, Pathak B, Bhuyan PK (2019) Distribution of volatile organic compounds over Indian subcontinent during winter: WRF-chem simulation versus observations. Environ Pollut 252:256–269. https://doi.org/10.1016/j.envpol.2019.05.097. (PMID: 10.1016/j.envpol.2019.05.097)
      Dhaka SK, Chetna, Kumar V, Panwar V, Dimri AP, Singh N, Patra PK, Matsumi Y, Takigawa M, Nakayama T, Yamaji K, Kajino M, Misra P, Hayashida S (2020) PM2.5 diminution and haze events over Delhi during the COVID-19 lockdown period: an interplay between the baseline pollution and meteorology. Sci Rep 10(1):13442. https://doi.org/10.1038/s41598-020-70179-8.
      Firdaus G, Ahmad A (2011) Changing air quality in Delhi, India: determinants, trends, and policy implications. Reg Environ Change 11(4):743–752. https://doi.org/10.1007/s10113-011-0207-z. (PMID: 10.1007/s10113-011-0207-z)
      Ghude SD, Chate DM, Jena C, Beig G, Kumar R, Barth MC, Pfister GG, Fadnavis S, Pithani P (2016) Premature mortality in India due to PM2.5 and ozone exposure. Geophys Res Lett 43(9):4650–4658. https://doi.org/10.1002/2016GL068949. (PMID: 10.1002/2016GL068949)
      Girach IA, Ojha N, Babu SS (2021) Ozone chemistry and dynamics at a tropical coastal site impacted by the COVID-19 lockdown. J Earth Syst Sci 8. https://doi.org/10.1007/s12040-021-01666-3.
      Gupta AK, Karar K, Srivastava A (2007) Chemical mass balance source apportionment of PM10 and TSP in residential and industrial sites of an urban region of Kolkata India. Journal of Hazardous Materials 142(1–2):279–287. https://doi.org/10.1016/j.jhazmat.2006.08.013. (PMID: 10.1016/j.jhazmat.2006.08.013)
      Gupta AK, Karar K, Ayoob S, John K (2008) Spatio-temporal characteristics of gaseous and particulate pollutants in an urban region of Kolkata India. Atmospheric Research 87(2):103–115. https://doi.org/10.1016/j.atmosres.2007.07.008. (PMID: 10.1016/j.atmosres.2007.07.008)
      Gurjar BR, Ravindra K, Nagpure AS (2016) Air pollution trends over Indian megacities and their local-to-global implications. Atmos Environ 142:475–495. https://doi.org/10.1016/j.atmosenv.2016.06.030. (PMID: 10.1016/j.atmosenv.2016.06.030)
      Jain S, Sharma T (2020) Social and travel lockdown impact considering coronavirus disease (COVID-19) on air quality in megacities of India: present benefits, future challenges and way forward. Aerosol and Air Quality Research 20:1222–1236. https://doi.org/10.4209/aaqr.2020.04.0171. (PMID: 10.4209/aaqr.2020.04.0171)
      Kumar V, Sarkar C, Sinha V (2016) Influence of post-harvest crop residue fires on surface ozone mixing ratios in the N.W. IGP analyzed using 2 years of continuous in situ trace gas measurements. Journal of Geophysical Research: Atmospheres 121(7):3619–3633. https://doi.org/10.1002/2015JD024308. (PMID: 10.1002/2015JD024308)
      Kumar V, Chandra BP, Sinha V (2018) Large unexplained suite of chemically reactive compounds present in ambient air due to biomass fires. Sci Rep 8(1):626. https://doi.org/10.1038/s41598-017-19139-3. (PMID: 10.1038/s41598-017-19139-3)
      Kumar R, Barth MC, Pfister GG, Nair VS, Ghude SD, Ojha N (2015) What controls the seasonal cycle of black carbon aerosols in India? J Geophys Res 120(15). https://doi.org/10.1002/2015JD023298.
      Kumari S, Lakhani A, Kumari KM (2020) COVID-19 and air pollution in Indian cities: world’s most polluted cities. Aerosol and Air Quality Research 20(12):2592–2603. https://doi.org/10.4209/aaqr.2020.05.0262. (PMID: 10.4209/aaqr.2020.05.0262)
      Le T, Wang Y, Liu L, Yang J, Yung YL, Li G, Seinfeld JH (2020) Unexpected air pollution with marked emission reductions during the COVID-19 outbreak in China. Science 369(6504):702–706. https://doi.org/10.1126/science.abb7431. (PMID: 10.1126/science.abb7431)
      Lelieveld J, Evans JS, Fnais M, Giannadaki D, Pozzer A (2015) The contribution of outdoor air pollution sources to premature mortality on a global scale. Nature 525(7569):367–371. https://doi.org/10.1038/nature15371. (PMID: 10.1038/nature15371)
      Lu H, Fang G (2002) Estimating the frequency distributions of PM10 and PM2.5 by the statistics of wind speed at Sha-Lu Taiwan. Sci Total Environ 298(1–3):119–130. https://doi.org/10.1016/S0048-9697(02)00164-X. (PMID: 10.1016/S0048-9697(02)00164-X)
      Miles GH, Jakeman AJ, Bai J (1991) A method for predicting the frequency distribution of air pollution from vehicle traffic, basic meteorology, and historical concentrations to assist urban planning. Environ Int 17(6):575–580. https://doi.org/10.1016/0160-4120(91)90169-Q. (PMID: 10.1016/0160-4120(91)90169-Q)
      Molina MJ, Molina LT (2004) Megacities and atmospheric pollution. J Air Waste Manag Assoc 54(6):644–680. https://doi.org/10.1080/10473289.2004.10470936. (PMID: 10.1080/10473289.2004.10470936)
      Mondal A, Lata S, Ghosh P, Mondal S, Devalla V, Mondal AK (2021) Upliftment of societal lockdown by Indian government amid CoVID-19 crisis: boon for some and bane for others [Preprint]. https://doi.org/10.31124/advance.14806377.
      Mor S, Kumar S, Singh T, Dogra S, Pandey V, Ravindra K (2021) Impact of COVID-19 lockdown on air quality in Chandigarh, India: understanding the emission sources during controlled anthropogenic activities. Chemosphere 263:127978. https://doi.org/10.1016/j.chemosphere.2020.127978. (PMID: 10.1016/j.chemosphere.2020.127978)
      Nigam R, Pandya K, Luis AJ, Sengupta R, Kotha M (2021) Positive effects of COVID-19 lockdown on air quality of industrial cities (Ankleshwar and Vapi) of Western India. Sci Rep 11(1):4285. https://doi.org/10.1038/s41598-021-83393-9. (PMID: 10.1038/s41598-021-83393-9)
      Ojha N, Sharma A, Kumar M, Girach I, Ansari TU, Sharma SK, Singh N, Pozzer A, Gunthe SS (2020) On the widespread enhancement in fine particulate matter across the Indo-Gangetic Plain towards winter. Sci Rep 10(1):5862. https://doi.org/10.1038/s41598-020-62710-8. (PMID: 10.1038/s41598-020-62710-8)
      Ojha N, Naja M, Singh KP, Sarangi T, Kumar R, Lal S, Lawrence MG, Butler TM, Chandola HC (2012) Variabilities in ozone at a semi-urban site in the Indo-Gangetic Plain region: association with the meteorology and regional processes. Journal of Geophysical Research Atmospheres 117(20). https://doi.org/10.1029/2012JD017716.
      Pathakoti M, Muppalla A, Hazra S, Dangeti M, Shekhar R, Jella S, Mullapudi SS, Andugulapati P, Vijayasundaram U (2020) An assessment of the impact of a nation-wide lockdown on air pollution—a remote sensing perspective over India. Atmospheric Chemistry and Physics Discussions 2020:1–16. https://doi.org/10.5194/acp-2020-621. (PMID: 10.5194/acp-2020-621)
      Quinn PK, Barrett KJ, Dentener FJ, Lipschultz F, Six KD (1996) Estimation of the air/sea exchange of ammonia for the North Atlantic Basin. In R. W. Howarth (Ed.), Nitrogen cycling in the North Atlantic Ocean and its watersheds (pp. 275–304). Springer Netherlands. https://doi.org/10.1007/978-94-009-1776-7_9.
      Saltzman BE (1997) Health risk assessment of fluctuating concentrations using lognormal models. J Air Waste Manag Assoc 47(11):1152–1160. https://doi.org/10.1080/10473289.1997.10464064. (PMID: 10.1080/10473289.1997.10464064)
      Sarangi T, Naja M, Ojha N, Kumar R, Lal S, Venkataramani S, Kumar A, Sagar R, Chandola HC (2014) First simultaneous measurements of ozone, CO, and NO y at a high-altitude regional representative site in the central Himalayas: ozone, CO, and NO y over the Himalayas. Journal of Geophysical Research: Atmospheres 119(3):1592–1611. https://doi.org/10.1002/2013JD020631. (PMID: 10.1002/2013JD020631)
      Sathe Y, Gupta P, Bawase M, Lamsal L, Patadia F, Thipse S (2021) Surface and satellite observations of air pollution in India during COVID-19 lockdown: implication to air quality. Sustain Cities Soc 66:102688. https://doi.org/10.1016/j.scs.2020.102688. (PMID: 10.1016/j.scs.2020.102688)
      Saxena A, Raj S (2021) Impact of lockdown during COVID-19 pandemic on the air quality of North Indian cities. Urban Climate 35:100754. https://doi.org/10.1016/j.uclim.2020.100754. (PMID: 10.1016/j.uclim.2020.100754)
      Seinfeld JH, Pandis SN (1998) Atmospheric chemistry and physics: from air pollution to climate change. John Wiley & Sons.
      Sen A, Abdelmaksoud AS, Nazeer Ahammed Y, Alghamdi MA, Banerjee T, Bhat MA, Chatterjee A, Choudhuri AK, Das T, Dhir A, Dhyani PP, Gadi R, Ghosh S, Kumar K, Khan AH, Khoder M, Maharaj Kumari K, Kuniyal JC, Kumar M, …, Mandal TK (2017) Variations in particulate matter over Indo-Gangetic Plains and Indo-Himalayan Range during four field campaigns in winter monsoon and summer monsoon: role of pollution pathways. Atmos Environ 154:200–224. https://doi.org/10.1016/j.atmosenv.2016.12.054.
      Sharma A, Ojha N, Pozzer A, Mar KA, Beig G, Lelieveld J, Gunthe SS (2017) WRF-Chem simulated surface ozone over south Asia during the pre-monsoon: effects of emission inventories and chemical mechanisms. Atmos Chem Phys 17(23):14393–14413. https://doi.org/10.5194/acp-17-14393-2017. (PMID: 10.5194/acp-17-14393-2017)
      Sharma A, Ojha N, Pozzer A, Beig G, Gunthe SS (2019) Revisiting the crop yield loss in India attributable to ozone. Atmospheric Environment: X 1:100008. https://doi.org/10.1016/j.aeaoa.2019.100008. (PMID: 10.1016/j.aeaoa.2019.100008)
      Sharma S, Zhang M, Anshika G, J., Zhang, H., & Kota, S. H. (2020) Effect of restricted emissions during COVID-19 on air quality in India. Sci Total Environ 728:138878. https://doi.org/10.1016/j.scitotenv.2020.138878. (PMID: 10.1016/j.scitotenv.2020.138878)
      Sicard P, De Marco A, Agathokleous E, Feng Z, Xu X, Paoletti E, Rodriguez JJD, Calatayud V (2020) Amplified ozone pollution in cities during the COVID-19 lockdown. Sci Total Environ 735:139542. https://doi.org/10.1016/j.scitotenv.2020.139542. (PMID: 10.1016/j.scitotenv.2020.139542)
      Singh RP, Chauhan A (2020) Impact of lockdown on air quality in India during COVID-19 pandemic. Air Qual Atmos Health 13(8):921–928. https://doi.org/10.1007/s11869-020-00863-1. (PMID: 10.1007/s11869-020-00863-1)
      Singh V, Singh S, Biswal A, Kesarkar AP, Mor S, Ravindra K (2020) Diurnal and temporal changes in air pollution during COVID-19 strict lockdown over different regions of India. Environ Pollut 266:115368. https://doi.org/10.1016/j.envpol.2020.115368. (PMID: 10.1016/j.envpol.2020.115368)
      Singh V, Singh S, Biswal A (2021) Exceedances and trends of particulate matter (PM2.5) in five Indian megacities. Sci Total Environ 750:141461. https://doi.org/10.1016/j.scitotenv.2020.141461. (PMID: 10.1016/j.scitotenv.2020.141461)
      Soni M, Ojha N, Girach IA (2021) Impact of COVID-19 lockdown on surface ozone build-up at an urban site in western India based on photochemical box modelling. Curr Sci 120(2):376-381. https://doi.org/10.18520/cs/v120/i2/376-381.
      Srivastava S, Kumar A, Bauddh K, Gautam AS, Kumar S (2020) 21-day lockdown in India dramatically reduced air pollution indices in Lucknow and New Delhi, India. Bull Environ Contam Toxicol 105(1):9–17. https://doi.org/10.1007/s00128-020-02895-w. (PMID: 10.1007/s00128-020-02895-w)
      Srivastava AK, Bhoyar PD, Kanawade VP, Devara PCS, Thomas A, Soni VK (2021) Improved air quality during COVID-19 at an urban megacity over the Indo-Gangetic Basin: from stringent to relaxed lockdown phases. Urban Climate 36:100791. https://doi.org/10.1016/j.uclim.2021.100791. (PMID: 10.1016/j.uclim.2021.100791)
    • Contributed Indexing:
      Keywords: Anthropogenic emissions; COVID-19; Frequency distribution; Lockdown; Megacities; NAAQS
    • Accession Number:
      0 (Air Pollutants)
      0 (Environmental Pollutants)
      0 (Particulate Matter)
    • Publication Date:
      Date Created: 20211021 Date Completed: 20221121 Latest Revision: 20230117
    • Publication Date:
      20231215
    • Accession Number:
      PMC8529380
    • Accession Number:
      10.1007/s11356-021-16874-z
    • Accession Number:
      34674132