Open Access Open Access  Restricted Access Subscription Access

Effect of COVID-19 Lockdown on the Spatio-temporal Distribution of Nitrogen Dioxide Over India


Affiliations
1 Marine and Atmospheric Sciences Department, Indian Institute of Remote Sensing, Dehradun 248 001, India
 

The nationwide lockdown was implemented in India from 25 March 2020 onwards to control the spread of deadly Coronavirus disease 2019 (COVID-19). A sudden shutdown of anthropogenic activities resulted in abrupt decrease of nitrogen dioxide (NO2) across the Indian region. OMI (Ozone Monitoring Instrument) tropospheric column NO2 observations show significantly decreased values during 2020 compared to previous years during 25 March to 19 April. The spatiotemporal variation of tropospheric column NO2 difference between 2020 and average 2017–2019 shows reduction by more than 1 × 1015 molecules/cm2 over the Indo Gangetic Plain, eastern and southern India due to lockdown. However, the western Indian region shows slight enhancement which may be attributed to combined effect of transport of polluted air from Middle East and Pakistan, and relatively higher biomass burning activity during 2020. A significant reduction is also observed on the surface distribution of NOx (NO + NO2) over different Indian cities due to COVID-19 lockdown. Maximum reduction in daily average surface NOx is observed over Kolkata (65.2 ± 18.7 ppbv to 30.3 ± 4.6 ppbv) followed by New Delhi (38.8 ± 17.5 ppbv to 11.5 ± 2.9 ppbv) which may be attributed to vehicle fleet, type of fuel used, power plants and industrial emissions.

Keywords

COVID-19 Lockdown, Nitrogen Dioxide, NOx, OMI.
User
Notifications
Font Size

  • Kurokawa, J. and Ohara, T., Long-term historical trends in air pollutant emissions in Asia: Regional Emission inventory in ASia (REAS) version 3.1. Atmos. Chem. Phys. Discuss., 2019; https://doi.org/10.5194/acp-2019-1122.
  • Balakrishnan, K. et al., The impact of air pollution on deaths, disease burden, and life expectancy across the states of India: the Global Burden of Disease Study. Lancet Planetary Health, 2017, 5196(18), 30261–30244.
  • Mahajan, A. S., Smedt, I. De, Biswas, M. S., Ghude, S. D., Fadnavis, S., Roy, C. and Roozendael, M. van, Inter-annual variations in satellite observations of nitrogen dioxide and formaldehyde over India. Atmos. Environ., 2015, 116, 194–201.
  • IPCC, Climate Change, Atmospheric Chemistry and Greenhouse Gases, Contribution of Working Group I to the Third Assessment Report of the Intergovernmental Panel on Climate Change, 2001.
  • Khreis, H., Kelly, C., Tate, J., Parslow, R., Lucas, K. and Nieuwenhuijsen, M., Exposure to traffic-related air pollution and risk of development of childhood asthma: a systematic review and meta-analysis. Environ. Int., 2017, 100, 1–31.
  • Khreis, H. and Nieuwenhuijsen, M. J., Traffic-related air pollution and childhood asthma: recent advances and remaining gaps in the exposure assessment methods. Int. J. Environ. Res. Public Health, 2017, 14(3), 312; https://doi.org/10.3390/ijerph14030312
  • Abbey, D. E., Colome, S. D., Mills, P. K., Burchette, R., Beeson, W. L. and Tian, Y., Chronic disease associated with long-term concentrations of nitrogen dioxide. J. Expo. Anal. Environ. Epidemiol., 1993, 3, 181–202.
  • Blomberg, A. et al., Persistent airway inflammation but accommodated antioxidant and lung function responses after repeated daily exposure to nitrogen dioxide. Am. J. Respir. Crit. Care Med., 1999, 159, 536–543.
  • Chen, T. M., Kuschner, W. G., Gokhale, J. and Shofer, S., Outdoor air pollution: nitrogen dioxide, sulfur dioxide, and carbon monoxide health effects. Am. J. Med. Sci., 2007, 333, 249–256.
  • Beelen, R. et al., Long-term effects of traffic-related AIR pollution. Environ. Health Persp., 2008, 116(2), 196–202.
  • Hoek, G., Krishnan, R. M., Beelen, R., Peters, A., Ostro, B., Brunekreef, B. and Kaufman, J. D., Long-term air pollution exposure and cardio-respiratory mortality: a review. Environ. Health, 2013, 12, 43.
  • Bilal, Bashir, M. F. et al., Environmental pollution and COVID-19 outbreak: insights from Germany. Air Qual. Atmos. Health, 2020, 1–10; doi:10.1007/s11869-020-00893-9
  • Conticini, E., Frediani, B. and Caro, D., Can atmospheric pollution be considered a co-factor in extremely high level of SARSCoV2 lethality in Northern Italy?*. Environ. Pollut., 2020, 261, 114465.
  • Boersma, K. F. et al., An improved retrieval of tropospheric NO2 columns from the Ozone Monitoring Instrument, Atmos. Meas. Tech., 2011, 4, 1905–1928.
  • Gerboles, M., Lagler, F., Rembges, D. and Brun, C., Assessment of uncertainty of NO2 measurements by the chemiluminescence method and discussion of the quality objective of the NO2 European Directive. J. Environ. Monitoring, 2003, 5, 529–540.
  • Harrison, R. M. and Perry, R., Handbook of Air pollution Analysis, Chapman Hall, New York, 1986, 2nd edn.
  • Schroeder, W., Oliva, P., Giglio, L. and Csiszar, I. A., The New VIIRS 375 m active fire detection data product: Algorithm description and initial assessment. Rem. Sens. Environ., 2014, 143, 85–96.
  • Garg, A., Shukla, P. R., Bhattacharya, S. and Dadhwal, V. K., Sub‐region (district) and sector level SO2 and NOx emissions for India: Assessment of inventories and mitigation flexibility. Atmos. Environ., 2001, 35, 703–713.
  • Beig, G. and Ali, K., Behavior of boundary layer ozone and its precursors over a great alluvial plain of the world: Indo-Gangetic Plains. Geophys. Res. Lett., 2006, 33, L24813; doi:10.1029/ 2006GL028352.
  • Periaswamy, P. et al., Shifting cultivation in North East India: Social dimension, cross cultural reflection and strategies for improvement. Indian J. Agric. Sci., 2018, 88, 811–819.
  • Yadav, P. K., Slash-and-burn agriculture in North-East India. Exp. Op. Environ. Biol., 2013, 2; 10.4172/2325-9655.1000102.
  • Singh, R. P. and Kaskaoutis, D. G., Crop residue burning: a threat to South Asian air quality. EOS Trans. Am. Geophys. Union, 2014, 95(37), 333–340.
  • Vadrevu, K. P., Ellicott, E. and Badarinath, K., MODIS derived fire characteristics and aerosol optical depth variations during the agricultural residue burning season, North India. Environ. Pollut., 2011, 159(6), 1560–1569.
  • Mallik, C. et al., Variability of SO2, CO, and light hydrocarbons over a megacity in Eastern India: effects of emissions and transport. Environ. Sci. Pollut. Res., 2014, 21, 8692–8706.
  • Srivastava, S., Lal, S., Subrahamanyamb, D. B., Gupta, S., Venkataramani, S. and Rajesh, T. A., Seasonal variability in mixed layer height and its impact on trace gas distribution over a tropical urban site: Ahmedabad. Atmos. Res., 2010, 96, 79–87.
  • Jain, N., Bhatia, A. and Pathak, H., Emission of air pollutants from crop residue burning in India. Aerosol Air Quality Res., 2014, 14, 422–430.
  • Road Transport Year Book 2015–16, Transport Research Wing, Ministry of Road Transport and Highways, Government of India.
  • West Bengal Pollution Control Board, Annual Report 2008–2010; Government of West Bengal, Kolkata, India, 2010.
  • Ghose, M. K., Air pollution in the city of Kolkata: Health effects due to chronic exposure. In Air Pollution in Kolkata: An Analysis of Current Status and Interrelation between Different Factors; SEEU Review, Tetovo, Macedonia, 2013, vol. 8, pp. 181–214.
  • Farooqui, Z. M., John, K., Biswas, J. and Sule, N., Modeling analysis of the impact of anthropogenic emission sources on ozone concentration over selected urban areas in Texas. Atmos. Pollut. Res., 2013, 4, 33–42.
  • Mahato, S., Pal, S. and Ghosh, K. G., Effect of lockdown amid COVID-19 pandemic on air quality of the megacity Delhi, India. Sci. Total Environ., 2020, 730, 139086.

Abstract Views: 225

PDF Views: 83




  • Effect of COVID-19 Lockdown on the Spatio-temporal Distribution of Nitrogen Dioxide Over India

Abstract Views: 225  |  PDF Views: 83

Authors

Shuchita Srivastava
Marine and Atmospheric Sciences Department, Indian Institute of Remote Sensing, Dehradun 248 001, India
Asfa Siddiqui
Marine and Atmospheric Sciences Department, Indian Institute of Remote Sensing, Dehradun 248 001, India
D. Mitra
Marine and Atmospheric Sciences Department, Indian Institute of Remote Sensing, Dehradun 248 001, India
Prakash Chauhan
Marine and Atmospheric Sciences Department, Indian Institute of Remote Sensing, Dehradun 248 001, India

Abstract


The nationwide lockdown was implemented in India from 25 March 2020 onwards to control the spread of deadly Coronavirus disease 2019 (COVID-19). A sudden shutdown of anthropogenic activities resulted in abrupt decrease of nitrogen dioxide (NO2) across the Indian region. OMI (Ozone Monitoring Instrument) tropospheric column NO2 observations show significantly decreased values during 2020 compared to previous years during 25 March to 19 April. The spatiotemporal variation of tropospheric column NO2 difference between 2020 and average 2017–2019 shows reduction by more than 1 × 1015 molecules/cm2 over the Indo Gangetic Plain, eastern and southern India due to lockdown. However, the western Indian region shows slight enhancement which may be attributed to combined effect of transport of polluted air from Middle East and Pakistan, and relatively higher biomass burning activity during 2020. A significant reduction is also observed on the surface distribution of NOx (NO + NO2) over different Indian cities due to COVID-19 lockdown. Maximum reduction in daily average surface NOx is observed over Kolkata (65.2 ± 18.7 ppbv to 30.3 ± 4.6 ppbv) followed by New Delhi (38.8 ± 17.5 ppbv to 11.5 ± 2.9 ppbv) which may be attributed to vehicle fleet, type of fuel used, power plants and industrial emissions.

Keywords


COVID-19 Lockdown, Nitrogen Dioxide, NOx, OMI.

References





DOI: https://doi.org/10.18520/cs%2Fv120%2Fi2%2F368-375