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Impact of crop residue burning in Haryana on the air quality of Delhi, India

Crop residue burning (CRB) over northern India is a major air quality and human health issue. The present study assesses the impact of PM(10), PM(2.5), NO(2) and SO(2), emitted during CRB activities in Haryana on the air quality of Delhi. The transition from pre-burning to burning period, in both ra...

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Detalles Bibliográficos
Autores principales: Saxena, Pallavi, Sonwani, Saurabh, Srivastava, Ananya, Jain, Madhavi, Srivastava, Anju, Bharti, Akash, Rangra, Deepali, Mongia, Nancy, Tejan, Shweta, Bhardwaj, Shreshtha
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Elsevier 2021
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8120930/
https://www.ncbi.nlm.nih.gov/pubmed/34027176
http://dx.doi.org/10.1016/j.heliyon.2021.e06973
Descripción
Sumario:Crop residue burning (CRB) over northern India is a major air quality and human health issue. The present study assesses the impact of PM(10), PM(2.5), NO(2) and SO(2), emitted during CRB activities in Haryana on the air quality of Delhi. The transition from pre-burning to burning period, in both rabi and kharif seasons, shows considerable increase in pollutant concentrations. PM(10) and PM(2.5) concentrations exceeded NAAQS limits by 2–3 times, while NO(2) and SO(2) stayed within the limits. MODIS fire observations used to estimate CRB fire counts (confidence ≥80%) shows that rabi (burning period) fires in Haryana are ~3 times higher and more intense than in kharif. Furthermore, backward trajectories shows air mass movement from Haryana, Punjab and Pakistan. Thus, pollutants emitted reach Delhi via air masses, deteriorating its air quality. Meteorological conditions influence pollutant concentrations during both seasons. Frequent dust storms in rabi, and Dusshera and Diwali firework celebrations in kharif season exacerbate air pollution. In rabi, PM(10) and PM(2.5) have a significant negative association with (relative humidity) RH and positive association with (air temperature) AT. High AT during pre-monsoon, accompanied by low RH, loosens up soil particles and they can easily disperse. Stronger winds in rabi season promote NO(2) and SO(2) dispersion. In kharif, lower AT, higher RH and slower winds exist. Both PM(10) and PM(2.5) have a negative association with AT and (wind speed) WS. With lower temperature and slower winds during winter, pollutants are trapped within the boundary layer and are unable to disperse. As expected, NO(2) has a significant negative association with AT in Haryana. However, in case of Delhi, the association is significant but positive, and could be due to the odd-even scheme imposed by the Delhi government. More research is needed to determine the health effects of Haryana's rabi CRB activities on Delhi.