Factors influencing atmospheric wet deposition of trace elements in
rural Korea
Jung-Eun Kim
a
, Young-Ji Han
a,
⁎, Pyung-Rae Kim
a
, Thomas M. Holsen
b
a
Department of Environmental Science, College of Natural Science, Kangwon National University, 192‐1 Hyoja-2-dong, Chuncheon, Kangwon-do, 200‐701,
Republic of Korea
b
Department of Civil and Environmental Engineering, Clarkson University, 8 Clarkson Ave., Potsdam, NY, 13699‐5710, USA
article info abstract
Article history:
Received 6 December 2011
Received in revised form 7 March 2012
Accepted 23 April 2012
In this study, precipitation samples were collected in a rural area of Korea between August
2006 and July 2009. The volume weighted mean (VWM) concentrations showed distinct
seasonal variations, having high values in winter and low values in summer. Westerly winds
that prevailed during the cold season were associated with enhanced concentrations of trace
elements in precipitation. Based on back-trajectory analysis these samples were often
associated with industrialized areas of China and metropolitan areas of Korea. Wet deposition
fluxes of trace elements were inversely related to the VWM concentration, having high values
in the summer due to the large precipitation depths. However, the largest wet deposition
fluxes were observed for snow events despite their low precipitation depth, indicating that
snow was a more efficient scavenger of trace elements than rain.
© 2012 Elsevier B.V. All rights reserved.
Keywords:
Precipitation
Wet deposition
Trace element
Snow
Rural area
1. Introduction
In Korea the concentration of atmospheric fine particles
has increased or been relatively consistent despite many
efforts (such as industrial transfer and fuel conversion) to
improve air quality, while the concentrations of other
pollutants such as sulfur dioxide and carbon monoxide have
steadily decreased over the past few decades. Atmospheric
particles consist of various chemical constituents including
ionic and carbonaceous compounds, and other trace ele-
ments (Yubero et al., 2010). Trace elements including toxic
heavy metals are emitted from both natural and anthropo-
genic sources. While crustal elements including Al, Mn, Si,
and Fe are emitted from windborne dust and volcanoes,
elements such as Cr, Cu, Zn, and Pb are mainly emitted from
anthropogenic sources including transportation, industrial
processes, and fuel combustion (Danielyan, 2010). Source
types often determine the size distribution of aerosol;
accumulation mode (0.1–1 μm) is often the result of combus-
tion of fossil fuels and high temperature processes while
elements in the coarse mode (>1 μm) are usually produced by
mechanical processes such as wind or erosion (Seinfeld and
Pandis, 2006). Therefore, the elements in the accumulation
mode (such as Cr, Cu, and Zn) can remain in the atmosphere for
days or weeks and thus be subject to long-range transboundary
transport.
As trace elements are deposited into surface water and the
terrestrial environment through dry and wet depositions,
they are associated with adverse human and wildlife health
effects. Wet deposition of gaseous pollutants occurs through
both rainout (referring to in-cloud scavenging) and washout
(referring to below-cloud scavenging); however, particles are
mainly deposited via washout as a raindrop collides with
them. Heavy metals emitted by combustion processes usually
have relatively high solubility and reactivity, dissolving
readily in rain (Nriagu, 1984; Migon et al., 1997; Hou et al.,
2005). Wet deposition of As, Cd, Cr and Pb has been a major
concern due to their potential carcinogenic effects on humans
and adverse effect on ecosystem health (Mijic et al., 2010).
Atmospheric Research 116 (2012) 185–194
⁎ Corresponding author at: Department of Environmental Science, 192‐1,
Hyoja-2-dong, Kangwon National University, Chuncheon, Kangwon-do, 200‐
701, Republic of Korea. Tel.: +82 33 250 8579; fax: +82 33 251 3991.
E-mail address: youngji@kangwon.ac.kr (Y.-J. Han).
0169-8095/$ – see front matter © 2012 Elsevier B.V. All rights reserved.
doi:10.1016/j.atmosres.2012.04.013
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