Abstract

The historical (1835–2020) dry deposition of major air pollutants (SO2, NOx, O3 and PM2.5) in the urban background in Oslo, Norway, in a situation that could represent the building facades, was approximated from reported fuel combustion, emission factors, air concentrations since 1960, and dry deposition velocities. The annual accumulated dry deposition (and thus not considering the removal processes) of the pollutants, together, was found to have varied from about 2.3 to 27 g m−2, with the maximum in the 1960s caused by high SO2 emissions from the combustion of fuel oils, and with 1.6 kg m−2 having deposited over all the years. The deposition of PM2.5 was found to have dominated from 1835, have increased to a maximum in 1875 and then slowly decreased. The SO2 deposition decreased to a low value around 1990. The NOx deposition was also at its highest in the 1960s to about 1970, it became the largest from the 1980s, and then showed a clear decrease from about 2010. The O3 deposition was lower in the years of the maximum total and NOx deposition. The dry deposition of O3 and NOx were found to be about similar in 2020, more than two times that of PM2.5 and more than four times that of SO2. The trends of the NOx emissions were found to reflect the relative (1975) and absolute (∼2000) turning points of the environmental Kuznets curves (EKC) that has been suggested for Norway, whereas the trend of the SO2 emissions seems to have “shortcut” this development by the strong regulations in the emissions from 1970 that lead to near simultaneous relative and absolute reductions. The gradual decrease of the PM2.5 emissions from about 1945 seems to correspond with the decrease in combustion energy intensity in the economy as wood was substituted with more energy efficient fuels and then with the continued reduction in the wood burning.

Highlights

  • Anthropogenic air pollution damages health (WHO, 2013; WHO, 2005), natural ecosystems (Maas and Grennfelt, 2016), and built structures (Watt et al, 2009; Brimblecombe, 2003) which are the topic of this work

  • The historical (1835–2020) dry deposition of major air pollutants (SO2, NOx, O3 and PM2.5) in the urban background in Oslo, Norway, were approximated from reported fuel combustion, emission factors, air concentrations since 1960, and dry deposition velocities. Over these years the total accumulated dry deposition of the pollutants was found to have varied from 2.3 to 27 ± 1 g m− 2 a− 1, with 1.6 ± 0.1 kg m− 2 having deposited over all the years

  • The total maximum in the 1960s was caused by high SO2 emissions from the combustion of fuel oils

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Summary

Introduction

Anthropogenic air pollution damages health (WHO, 2013; WHO, 2005), natural ecosystems (Maas and Grennfelt, 2016), and built structures (Watt et al, 2009; Brimblecombe, 2003) which are the topic of this work. As the precipitation will affect the accumulation of the pollutants in different ways and often lead to rain washing, the deterioration effects of the wet deposition are less predictable (Grossi and Brimblecombe., 2004). The particle soiling and combined effect with SO2 and sulfate (SO42− ) in the formation of black crusts on limestone (Brim­ blecombe, 2003; Inkpen, 2004) and corrosion of steel and other metals (Graedel and Leygraf, 2000) are among the most observed damages. O3 can react indoors with NO2 to form nitrate radicals, and heterogeneously on surfaces to nitrous (HNO2) and nitric acid (HNO3), that can damage sensitive ma­ terials (Graedel and Leygraf, 2000; Nazaroff and Weschler, 2021; Weschler and Shields, 1997; Hackney, 2016)

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