HEAVY
METALS EMISSIONS INVENTORY AND CONCENTRATIONS IN THE ENVIRONMENT IN RUSSIA:
SPATIAL AND TEMPORAL TREND ANALYSIS.
Veronika A. Ginzburg, Sergey A. Gromov
Laboratory of Integrated
Monitoring, Institute of Geography RAS, Glebovskaya 20-B, 107258, Moscow,
Russia
E-mail: vergiliy@mtu-net.ru, fax: 7 (095)
1600831, tel.: 7 (095) 1600840
Abstract
The general idea of this study is to summarize various
available information on atmospheric heavy metal emissions over the territory
of Russia as well as make the analytical comparison of different information
sources. Spatial distribution and temporal trends of heavy metals antropogenic
emissions are presented in the article. The assessment is made for the period
from 1990 till now (the latest available data are for the year 1997) and covers
the whole territory of Russia based on the administrative division. Lead (Pb)
is used in the study as a basic element for which the most complete data are
presented. However, some partial space and time distribution analysis of other
heavy metals (Cd and Hg) is also included in the article. The main principles
of the spatial distribution of heavy metal concentrations in the environment of
background territories is evaluated from the point of view of their correlation
with emission fields.
Introduction
Heavy metal emissions into the atmosphere cause global
environmental problems due to the long life of these elements, their capacity
to be transported over long distances, and also their increasing rate of
accumulation in the environment even in the most remote territories. Most trace
elements enter the atmosphere by natural and man-made aerosols. The main
sources of natural aerosols in the atmosphere are soil erosion and weathering
of mountain rocks, volcanic and space dust, forest fire smoke and others. Major
antropogenic sources of toxic elements are fossil fuel combustion, mining,
industrial processes and waste incineration. The antropogenic flow of heavy
metals into the atmosphere is about 94-97% of the total flow.
An inventory of emission sources is a necessary step
in developing both a control strategy and also a model of global and regional
cycles of trace elements. However, for the territory of Russia there is still
no proper information about the level of emissions. Data presented in different
sources are very much different. The general idea of this study is to summarize
various available information on atmospheric heavy metal emissions over the
territory of Russia compare data presented by different information sources.
The results of emissions inventory are compared with
measurement data of heavy metals contents in the atmosphere gathering from
Integrated Background Monitoring Network (IBMoN) stations. The IBMoN was
established in the former Soviet Union as a specific observation system, which
main goal is to detect an anthropogenic impact on regional and global
environment as well as to reflect global and regional trends of environmental
pollution level.
Method
There are three main types of information sources on
emissions pattern in Russia: official statistical data, expert evaluations and
data of emissions inventory made in the framework of international projects.
All these sources has its own advantages and disadvantages. In this paper
official statistical data are gathered from statistical reports of Russian
industrial enterprises, prepared according to officially ratified form (General
report … 1994, Year book… 1997, Year book… 1998). Activity concerning the EMEP
program and the realization of the Convention on Long-Range Transboundary Air
Pollution not only engaged countries to submit annual emissions data but also
initiated many experts investigations. Therefore, in this paper emissions data
presented for the joint report of EMEP Centers (1999) are used as an example of
emissions inventory made in the framework of international projects. Emissions
evaluation made by Yasenskiy et al. (1998) is used as an example of expert's
estimations. Industrial emissions of Pb, Cd and Hg are calculated by Yasenskiy
et al. (1998) using official statistics on fossil fuel consumption and emission
coefficients adopted to Russian conditions from the atmospheric emission
inventory guidebook (1996).
Official statistics, which represents the most completed
set of sources and allows analyzing spatial distribution fields of emissions,
is usually presented in the form of total emissions per administrative unit.
Expert’s evaluations, which are usually more precise but represent only a
certain sample of sources, are made for all main industrial sources and
transport based on initial data on fuel balance. All data on transport
emissions are taken from expert evaluations. Transport emissions are estimated
according to road density and fuel consumption. The fuel balance data for the
territory of Russia (per administrative units) are used as a basic material for
motor petrol consumption
Results and discussion
Total emissions of lead, cadmium and mercury published
by official authorities are significantly lower than experts evaluations and
even lower than data prepared by Russia in the framework of the Convention.
Data of official inventory for lead in 1993 were 9 times less than experts
evaluations, for cadmium - up to 30 times less (Table 1).
Table 1.
Emissions
of Pb, Cd and Hg in Russia in 1993 according to different sources, t/year.
|
|
Official
statistics |
Official
data prepared for the Convention |
Experts
evaluations |
|
Lead |
1070 |
2376 |
9168 |
|
Cadmium |
6 |
59 |
188 |
|
Mercury |
7,8 |
11,8 |
30 |
Temporal trends of heavy metal emissions are presented
on Fig. 1. The curves named "lead", "cadmium" and
"mercury" reflect data obtained from official statistics, while
curves named "lead1", "cadmium1" and "mercury1"
reflect data prepared in the framework of the Convention. According to all
these data (except "cadmium"), emissions of the elements decreased
during the last decade. The growth of cadmium emissions according to official
data can be explained by the including of greater number of sources into
inventory than it was in previous years.
Despite the fact, proved by different investigator,
that official statistical information is usually quite far from reality, it
represents probably the most completed set of sources and provides spatial
distribution fields of emissions. Therefore, the share of different economic
regions on total emissions of Pb, Cd and Hg in Russia was analyzed according to
official statistical data (Fig. 2).
The most valuable contribution to the total emissions
of lead and cadmium provides by Ural region (up to 74-77%). That is the most
industrialized region of Russia. Even taking into account the area of different
regions, emissions per square kilometer are the highest in Ural region (about
900 t Pb per sq.km/year). About 70% of mercury is emitted from the industries
situated in Ural and East Siberian regions (40 and 30% respectively). Emission
from vehicles is shared more equally among regions. It is mainly depends of
traffic activity and the area of the region.
The contribution of various
industries in total lead and mercury emissions in Russia is presented on Fig. 3
The most important industrial emission sources of lead in Russia is metallurgy
enterprises, especially non-ferrous metal industry. The most important role in
mercury emission played by chemical industry, which contribute about 55% of
total industrial emissions. About 40% of mercury is emitted from non-ferrous
metal industry.
From this point of view it
is interesting to compare geographical distribution of emission sources and
concentration fields of heavy metals in the atmosphere. According to the data
of the review of the state of background environment over the territory of CIS
countries and its dynamic during the last ten years (1999) there are three
types of territories characterized by comparatively low, medium and high levels
of Pb and Cd concentrations in the atmosphere. The highest concentrations are
observed at the European part of Russia and over territories situated less than
1000 km from main emissions sources.
Average annual
concentrations of lead over the European part of Russia are varied in the
limits of 4.8-11 ng/m3. The highest concentration over the territory
of Russia is observed in Astrahanskiy and Voronezhskiy reserves - 9.8 ng/m3
and 11 ng/m3 respectively. Variation of concentrations from year to
year is quite significant. Average annual concentrations of lead over the
European part of Russia are varied from 0.18 to 0.25 ng/m3. Annual
average concentrations of mercury in the atmosphere of Russia are varied in the
limits of 3-11 ng/m3.
Penetration of air masses
from industrial and urban regions significantly influences the concentration of
heavy metals in the atmosphere of background regions. It can cause increasing
of concentrations up to 5-10 times. Influence of regional sources can also
appear in formation of pollution clouds over cities which are then transported
to background territories and deposed with precipitation.
References
Atmospheric emission inventory guidebook
(1999). Second Edition. Edited by S.Richardson. Joint EMEP/CORINAIR, Vol.1-3.
EMEP report (1999). Monitoring and modelling of
lead, cadmium and mercury transboundary transport in the atmosphere of Europe.
Joint report of EMEP Centres: MSC-E and CCC 3/99
Review of the state of background environment
over the territory of CIS countries and its dynamic during the last ten years.
Edited by Izrael YuA, Rovinskiy F.Ya (1999). St.Peterburg: Gidrometeoizdat (In
Russian).
General report on protection of the atmosphere
in 1993 (Statistic data) (1994) Russian State Comittee for Statistics,
Moscow.(In Russian)
Yearbook on pollution emissions into the
atmosphere of cities and regions of Russia in 1995. Edited by Milyaev VB,
Nikolaev VD, Yasenskiy AN. (1997). St.Peterburg (in Russian).
Year book on pollution emissions into the atmosphere
of cities and regions of Russia in 1997. Edited by Milyaev VB, Nikolaev VD,
Yasenskiy AN. (1998). St.Peterburg (in Russian).
Yasenskiy AN, Yacenko-Hmelevskaya MA. (1998)
Emissions of heavy metals over European part of Russia according to statistical
data and expert evaluations. Proceedings of EMEP workshop on heavy metals and
POPs emissions inventory.
List
of figures:
Figure 1. Time trend of Pb,
Cd and Hg emissions.
Figure
2. The share of economic regions in total industrial emissions of lead, cadmium
and mercury and vehicle emissions of lead in Russia, %
Figure
3. Contribution of various industries in total lead and mercury emissions in
Russia, %

Figure 1. Time trend of Pb, Cd and Hg emissions





Figure
2. The share of economic regions in total industrial emissions of lead, cadmium
and mercury and vehicle emissions of lead in Russia, %


Figure 3. Contribution of various industries in total
lead and mercury emissions in Russia, %