Abstract

Abstract. Air pollution resulting from rapid urbanization and associated human activities in the Kathmandu Valley of Nepal has been leading to serious public health concerns over the past 2 decades. These concerns led to a multinational field campaign SusKat-ABC (Sustainable atmosphere for the Kathmandu Valley – Atmospheric Brown Clouds) that measured different trace gases, aerosols and meteorological parameters in the Kathmandu Valley and surrounding regions during December 2012 to June 2013 to understand local- to regional-scale processes influencing air quality of the Kathmandu Valley. This study provides information about the regional distribution of ozone and some precursor gases using simultaneous in situ measurements from a SusKat-ABC supersite at Bode, Nepal, and two Indian sites: a high-altitude site, Nainital, located in the central Himalayan region and a low-altitude site, Pantnagar, located in the Indo-Gangetic Plain (IGP). The diurnal variations at Bode showed a daytime buildup in O3 while CO shows morning and evening peaks. Similar variations (with lower levels) were also observed at Pantnagar but not at Nainital. Several events of hourly ozone levels exceeding 80 ppbv were also observed at Bode. The CO levels showed a decrease from their peak level of about 2000 ppbv in January to about 680 ppbv in June at Bode. The hourly mean ozone and CO levels showed a strong negative correlation during winter (r2 = 0.82 in January and r2 = 0.71 in February), but this negative correlation gradually becomes weaker, with the lowest value in May (r2 = 0.12). The background O3 and CO mixing ratios at Bode were estimated to be about 14 and 325 ppbv, respectively. The rate of change of ozone at Bode showed a more rapid increase ( ∼ 17 ppbv h−1) during morning than the decrease in the evening (5–6 ppbv h−1), suggesting the prevalence of a semi-urban environ. The lower CO levels during spring suggest that regional transport also contributes appreciably to springtime ozone enhancement in the Kathmandu Valley on top of the local in situ ozone production. We show that regional pollution resulting from agricultural crop residue burning in northwestern IGP led to simultaneous increases in O3 and CO levels at Bode and Nainital during the first week of May 2013. A biomass-burning-induced increase in ozone and related gases was also confirmed by a global model and balloon-borne observations over Nainital. A comparison of surface ozone variations and composition of light non-methane hydrocarbons among different sites indicated the differences in emission sources of the Kathmandu Valley and the IGP. These results highlight that it is important to consider regional sources in air quality management of the Kathmandu Valley.

Highlights

  • The Himalayan region is among the least studied regions in the world despite its known importance in influencing the livelihood of about a billion people and agricultural systems

  • In light of the above conditions, this study aims to provide the first information about the regional distribution of ozone and related gases during SusKat-ABC by synergistically analyzing simultaneous in situ measurements of surface ozone and CO at Bode from January to June 2013 with those from two Indian sites, namely Nainital and Pantnagar

  • The Kathmandu Valley is located in the central Himalayan region due north of the Indo-Gangetic Plain (IGP) and south of the Tibetan Plateau

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Summary

Introduction

The Himalayan region is among the least studied regions in the world despite its known importance in influencing the livelihood of about a billion people and agricultural systems. The urban centers in the mountain regions often face severe air pollution problems since the mountains act as a barrier to horizontal ventilation of the pollutants and local mountain valley winds govern the diurnal variations in air pollutants. These processes have been well studied over other parts of the world, such as Mexico City (de Foy et al, 2006; Molina et al, 2007 etc.), Po Valley (Martilli et al, 2002) and Santiago de Chile (Schmitz, 2005; Rappenglück et al, 2005). Only a few surface measurements of ozone and related trace species have been reported so far from this region (Pudasainee et al, 2006; Panday and Prinn, 2009; Cristofanelli et al, 2010; Putero et al, 2015; Mahata et al, 2017)

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