An emission inventory of sulfur from anthropogenic sources in Antarctica
Atmos. Chem. Phys., 9, 3397–3408, 2009
www.atmos-chem-phys.net/9/3397/2009/
© Author(s) 2009. This work is distributed under
the Creative Commons Attribution 3.0 License.
Atmospheric
Chemistry
and Physics
An emission inventory of sulfur from anthropogenic sources in
Antarctica
S. V. Shirsat and H. F. Graf
Department of Geography, University of Cambridge, Cambridge, UK
Received: 8 October 2008 – Published in Atmos. Chem. Phys. Discuss.: 21 January 2009
Revised: 14 April 2009 – Accepted: 5 May 2009 – Published: 26 May 2009
Abstract. This paper presents first results of a comprehensive emission inventory of chemical species from anthropogenic activities (power generation, vehicles, ships and aircraft) in Antarctica, covering the 2004–2005 period.
The inventory is based on estimated emission rates of fuel
consumption provided by some of the Antarctic research stations. Since the emission sources have different modes of
operation and use a variety of fuel, the emission flux rate of
chemical species is calculated by multiplying the fuel consumption value with the density of fuel and appropriate emission factors. A separate inventory is prepared for each anthropogenic emission source in Antarctica.
Depending on the type of operation, emission rates of SO2 ,
and BC (Black Carbon, from shipping only) have been calculated using the above technique. However, only results of
SO2 emissions from each source are presented here. Emission inventory maps of SO2 depicting the track/path taken
by each mobile source are shown. The total annual SO2
is 158 Mg from power generation and vehicle operations,
3873 Mg from ships and 56 Mg from aircraft for 2004–2005
and these values undergo strong seasonality following the human activity in Antarctica. Though these figures are small
when compared to the emissions at most other regions of the
world, they are an indication that human presence in Antarctica leads to at least local pollution. The sources are mainly
line and point sources and thus the local pollution potentially
is relatively strong.
Correspondence to: S. V. Shirsat
()
1
Introduction
The climate system of Antarctica is very unique and extreme
compared to any other region, making it one of the most pristine (Wall, 2005) places on Earth. Chemical species play an
important role in the atmosphere, by affecting air-quality, climate, radiative forcing etc. These effects depend on the type
and chemical concentration of the species, place of emission in the atmosphere, climatic conditions of a particular
region and emission source. Globally, emissions due to anthropogenic activities account for approximately 70 Tg (S)
of the total (natural + anthropogenic) 107 Tg (S) emissions of
sulphur each year, although a greater uncertainty exists for
natural sources (Smith et al., 2000). In the Arctic, critical
concentrations of SO2 (5 µg/m3 ) have been exceeded over
a large area and pose damage to ecosystems due to anthropogenic activities (nickel smelters) occurring in the nearby
Norilsk region and Kola Peninsula (Kashulina et al., 2003;
AMAP report, 1998). In Antarctica, due to growth in tourist
and scientist visits to various continental and/or peninsular
sites, the impact has started to be recognised and is a cause
of concern.
Tourism in Antarctica started during 1950’s (Roper-Gee,
2003) with the first flight and ship visits to the Peninsular region. However, in recent years the number of tourists visiting
Antarctica has increased from approximately 6000 in 1992–
1993 to 26 000 in 2005–2006 (as available from IAATO, International Association of Antarctic Tour Operators), with
more than 98% of them being ship-borne (United States Environment Protection Agency, 2001). In recent years, due
to the growth of human activity and visits to Antarctica
(IAATO, Overview of Antarctic Tourism, 2003–2004), it is
necessary to elucidate the contribution of different emission
sources towards concentration levels of chemical species.
Earlier local investigations by Lugar (1993) revealed that
during the 1992–1993 austral summer PM10 levels measured
Published by Copernicus Publications on behalf of the European Geosciences Union.
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S. V. Shirsat and H. F. Graf: Inventory of sulfur from anthropogenic sources in Antarctica
at Central McMurdo were comparable to concentrations
found in Santa Fe, New Mexico during 1991. A study
conducted during 1992–1995 by Wolff and Cachier (1998)
shows that aetholometer readings increased dramatically due
to black particle emissions from generators present at Halley
research base. Also, Mazzera et al. (2001) in their 1995–
1996, 1996–1997 austral summer study indicate that McMurdo base (located at the Hut Point peninsula on Ross Island) was highly impacted by emissions due to human activities at the base. Studies carried out in the past take into consideration mainly single research station or sources, the only
exception being Boutron and Wolff (1989), who suggested
sulfur emissions from fuel and waste burning of 70 Mg/year
for 1987. Here, we attempt a full survey of contemporary
anthropogenic emissions in Antarctica.
Global emission inventories like GEIA (Global Emission
Inventory Activity), EDGAR (Emission Database for Global
Atmospheric Research) etc. have been developed in the past
to estimate the contributions of anthropogenic and natural
sources towards the levels of different chemical species and
greenhouse gases over national/regional/global scales. These
databases are of great importance to climate modellers and
atmospheric scientists who wish to understand the trends and
spatio-temporal distribution of chemical species in the atmosphere and deposition at the surface. Besides this, as pointed
by Buron et al. (2005), implications of these emission inventories arise for designing policies oriented towards reduction
of emissions, especially from anthropogenic sources. However, so far the “pristine” Antarctic continent has not been
included in these inventories.
This study presents a comprehensive emission inventory
of SO2 emitted due to all anthropogenic activities in Antarctica for the one-year period 2004–2005. Human activities
in Antarctica include power/heat generation at the research
base, vehicular activity, marine and air-borne traffic. Use
of diesel/gas oil in generators leads to the release of chemical species that might affect the air-quality in the vicinity
of the bases. Vehicles are used for delivering fuel, support personnel and for carrying out scientific activities across
Antarctica. Combustion of fuel in ship engines could lead
to release of different pollutants along ship tracks and along
coastal regions which might later get transported to elsewhere. Therefore, it becomes necessary to quantify the emissions from shipping operations as they tend to affect the environment especially through radiative forcing (e.g., Lawrence
and Crutzen, 1999; Endresen et al., 2003) and are likely to
be the most polluting source, particularly when compared
to vehicle e (...truncated)