Contribution to the Workshop on
Photochemical Oxidants and Aerosols in Lombardia,
21st - 22nd June 1999
Some current problems in the atmospheric environment; the potential contribution
of EUROTRAC-2
Peter Borrell
(formerly Executive Secretary of EUROTRAC-2)
P&PMB Consultants, Ehrwalder Straße 9, D-82467 Garmisch-Partenkirchen
1. Abstract
Current environmental concerns include the increase in free-tropospheric
ozone levels over the past 50 years, the difficulties caused by non-linearity
in devising strategies to ameliorate ozone concentrations under NOx controlled
conditions, the health effects of particulates and the possible synergism
between pollutants. The environmental issues are paralleled by scientific
problems, particularly those of the description and analysis of heterogeneous
atmospheric components, the adequacy and representativeness of measurements,
the difficulties of modelling complex heterogeneous chemistry in turbulent
situations and the validation of the current models.
The EUREKA environmental project, EUROTRAC-2, was established in 1996
to provide some solutions to the scientific problems. Particularly appropriate
to the Lombardy region is the work of the "urban" subprojects, LOOP and
SATURN, as well as in the modelling subproject, GLOREAM, and the emission
subproject, GENEMIS.
2. Introduction: the environmental problem
Despite the measures taken under the Convention on the Long Range Transport
of Air Pollutants (ECE, 1994) and by the European Commission (Lutz, 1999)
there is continuing public concern about the concentrations of ozone and
other photo-oxidants throughout Europe. In addition there are worries about
the health effects of emissions within urban areas, particularly aromatic
hydrocarbons and particulate matter of all types. The environmental problems
are closely inter-related because photo-oxidant precursors are emitted
by road traffic and by industrial and domestic activities which occur mainly
within urban areas.
A complication for the policy maker is the variety of effects that have
to be taken into account in formulating appropriate measures (Borrell et
al., 1996). On a regional scale, the background concentration of ozone
throughout the region has apparently increased, from the turn of the century
until the nineteen eighties, to a level which is now close to concentrations
which are believed to inhibit crop growth. Some indication of the changes
that took place in Europe between 1950 and the 1980 can be seen in figure
1 which shows that at all altitudes, there has been an appreciable increase
in average ozone concentrations (Staehelin et al., 1994). The increase
appears to have levelled off at the moment but the general levels of ozone
and photo-oxidants are still too high.
Under sunny stagnant atmospheric conditions, ozone episodes occur which
produce over the course of several days concentrations which lead to ozone
exposures well in excess of the WHO health guidelines. In the centre of
many conurbations, the production of ozone is limited by the concentrations
of volatile organic compounds (VOC) in the air while in the hinterland
of cities and throughout most of the region the production is limited by
concentrations of nitrogen oxides, NOx. However the non-linearity in the
ozone chemistry can actually, under appropriate conditions, lead to increasing
ozone concentrations if the NOx is reduced. This is demonstrated by the
anomalous "weekend" effect observed in Belgium for example where, although
the emissions decrease over the weekend, ozone concentrations actually
increase (Dumollin et al., 1999). In Vienna on the other hand ozone
decreases slightly (Schneider, 1998).
The progress in legislation has gone hand in hand with progress in the
science of the troposphere. The realisation that international policy development
requires an international scientific consensus led to the formation in
1986 of the EUREKA project, EUROTRAC. It came to an end in 1995 with the
publication of a final report which contained not only a plethora of scientific
results (Borrell et al., 1999) but also an assessment of the environmental
situation in the troposphere (Borrell et al., 1996).
However, despite the scientific progress, a number of substantial problems
remained, leading to the formation in 1996 of a new project, EUROTRAC-2,
which is tackling these problems on a broad front (EUROTRAC-2, 1999). The
purpose of the present paper is to outline some of the problems and to
indicate how the project is attempting to solve them.
3. Scientific uncertainties
To support cost-effective measures to reduce concentrations of harmful
pollutants, a suite of reliable validated models is required that encompass
the scientific understanding of the problem. These can then be used to
create regional and local scenarios and subsequently, when used with the
monitored concentrations, to ensure legal compliance with the agreed emission
reduction targets.
Much scientific progress has been made over the last twenty five years
in building, from countless experiments, a general understanding the processes
leading to photo-oxidant formation. The major chemical processes have been
characterised in laboratory work; the processes by which pollutants reach
their sink in the biosphere have been studied; emissions both anthropogenic
and biogenic have been estimated, models for all scales have been developed
and many field campaigns have been used both to validate particular models
and to provide indications of unexpected processes occurring in the atmosphere
(Borrell, 1999). However, despite the progress, substantial uncertainties
still remain in the components required for reliable modelling.
There are uncertainties:
-
In the type and in the spatial and temporal distribution of the emissions
themselves (Eliassen 1999, Friedrich, 1999). There is also a fundamental
question concerning the possible limits placed on the resolution of the
modelling because of the impossibility of providing sufficiently detailed
information about the emissions.
-
In the chemical processes occurring. While the homogeneous reactions of
simple species are reasonably well understood, there are still appreciable
gaps in our knowledge about the oxidation processes associated with aromatic
hydrocarbons and biogenic species. The heterogeneous reactions leading
to the formation of particles in the atmosphere, their chemical processing
in cloud and fog droplets and in their ultimate fate is still largely a
closed book (Fuzzi, 1999;Schurath, 1999).
-
In the measurement of the appropriate chemical components in the atmosphere.
Measurement techniques themselves, particularly for photo-oxidant precursors
and particulates, frequently require much expertise to obtain reliable
results and cannot therefore be easily used for the necessary monitoring
(Bösenberg et al., 1997). There is the additional difficulty
of the representativeness of a measuring site, i.e. in comparing the measurements
made at a particular point with the predictions of a model for a particular
grid square; the problem applies at all scales whether one is modelling
a street canyon or a large geographical region.
-
In the modelling of the dynamics of the transport processes. The dispersion
of urban pollutants involves circulation in street canyons, crossing the
internal boundary layer, circulation within the boundary layer itself,
advection to the surrounding region and handover to the free troposphere.
All of these involve turbulent processes which, despite the advances in
computation and in simulation, are still difficult to characterise and
model on any scale. The problem is exacerbated for photo-oxidant episodes
since they occur mainly under stagnant atmospheric conditions where turbulence
while still dominating the dispersion, is at its most difficult to observe
and model (Builtjes, 1999).
Some of the general questions to which answers should be sought in an urban
context are as follows.
-
Can the regimes of VOC - limited and NOx - limited ozone production be
fully characterised? Is it possible to use empirical indicators to determine
areas of NOx - and VOC - limited ozone production throughout Europe? Is
the "weekend effect" such an indicator?
-
Is it possible to obtain an improved understanding of the temporal evolution
and the spatial extent of the different photo-oxidant production regimes
in the planetary boundary layer in order to assess the effectiveness of
reduction strategies towards ground level ozone?
-
Are there limits imposed on the scales which can be reliably modelled,
by the inevitable lack of detail in our knowledge of emissions and the
uncertainties in other parameters?
-
Is it possible to define a realistic minimum network of measurements which,
with suitable model support, would be needed to monitor the emissions within
a conurbation and determine whether they comply with the statutory requirements?
4. The role of EUROTRAC-2
EUROTRAC-2 is a co-ordinated research project within the EUREKA initiative,
studying the transport and chemical transformation of pollutants and trace
substances in the troposphere over Europe. Since the inception of the first
phase some thirteen years ago the project achieved a remarkable success
in bringing together groups of European scientists to study scientific
problems related to the development of environmental policy in Europe.
The project now entirely reconstituted, began a second phase, EUROTRAC-2
in 1996. The project started again from scratch: new committees were appointed
and groups of scientists were encouraged to propose the formation of new
subprojects.
The overall objective of EUROTRAC-2 (The Transport and Chemical Transformation
of Environmentally Relevant Trace Constituents in the Troposphere over
Europe; Second Phase) is to support the further development of abatement
strategies within Europe by providing an improved scientific basis for
the quantification of source-receptor relationships for photo-oxidants
and acidifying substances. In 1997 the IEC decided to extend the project
to include mercury and persistent organic pollutants (POPs), since it recognised
the increasing concern over these pollutants in Europe and was persuaded
that EUROTRAC could contribute scientifically to understanding the problems
associated with their transport and distribution.
The specific objectives of the project are
-
Quantification of atmospheric interactions . To quantify the anthropogenic
and natural contributions of relevant emissions and atmospheric processes
to the abundance and the long term changes of photo-oxidants and acidifying
substances in the planetary boundary layer and free troposphere.
-
Evaluation of feedback mechanisms . To evaluate the consequences
of feed-back mechanisms, for example: the feed-back between the concentrations
of tropospheric photo-oxidants and biogenic emissions; the feed-back between
the concentrations of photo-oxidants and those of climatically relevant
atmospheric constituents; and the feed-back between the changing intensity
of ultraviolet radiation and photo-oxidant production.
-
Contribution to the formulation of abatement strategies and future air
quality . To contribute to the formulation and improvement of strategies
for reducing the anthropogenic contribution to the abundance of photo-oxidants
and acidifying substances and to the prediction of future air quality on
shorter and longer time scales.
In these objectives there is the recognition that, although much was achieved
in the first phase, there is still much to do before the scientific understanding
is good enough for modern policy development. The authorities responsible
for implementing environmental policy must have confidence in the predictions
of the models before they will be prepared to enact the necessary but expensive
abatement measures that are likely to be needed to deal with the present
environmental situation.
5. The new subprojects
Fourteen subprojects shown in Table 1 have been approved for inclusion
in EUROTRAC-2 by the Scientific Steering Committee (SSC). Most started
work in 1997 and the current annual reports suggest that much scientific
work has already been done.
Table 1: EUROTRAC-2 Subprojects
AEROSOL |
Aerosol balance in Europe |
Harry ten Brink |
ECN, Petten |
BIATEX-2 |
Biosphere/Atmosphere exchange of pollutants |
David Fowler |
ITE, Edinburgh |
CAPP |
Coastal air pollution processes |
Gary Geernaert |
DEAP, Roskilde |
CMD |
Chemical mechanism development |
Ulrich Schurath |
FZK, Karlsruhe |
GENEMIS |
Generation and evaluation of emission data |
Rainer Friedrich |
IER, Stuttgart |
GLOREAM |
Global and Regional Atmospheric Modelling |
Peter Builtjes |
TNO, Apeldoorn |
LOOP |
Limitation of oxidant production |
Albrecht Neftel |
FAL, Berne |
MEPOP |
Research on mercury and POPs |
John Munthe |
IVL, Göteborg |
PROCLOUD |
Processing of trace constituents in clouds over Europe |
Sandro Fuzzi |
CNR, Bologna |
SATURN |
Studying atmospheric pollution in urban areas |
N. Moussiopoulos |
U. of Thessaloniki |
TOR-2 |
Tropospheric Ozone Research |
Anne Lindskog |
IVL, Göteborg |
TRAP45 |
Trends in air pollution since 1945 |
P. Brimblecombe |
UEA, Norwich |
Of particular interest in the context of the urban environment are the
two "urban" subprojects, LOOP and SATURN, the aims of which are given in
Table 2
LOOP carried out an extensive field campaign in 1998 to study the plume
from Milan. The results are presently being evaluated and the first publications
will appear in the near future. SATURN is an ambitious project involving
a host of modelling activities to try to take advantage of the field measurements
being made at all scales in cities throughout Europe.
Table 2: The aims of the EUROTRAC-2 "urban" subprojects
LOOP: Limitation of oxidant production (Neftel, 1999).
-
To investigate the photo-oxidant formation in heavily polluted areas of
Europe; focusing on the question of VOC versus NOx sensitive ozone production.
-
To evaluate the temporal and spatial behaviour of photo-chemical regimes.
-
To provide improved tools for the assessment and development of efficient
and cost-effective ozone management strategies.
-
To provide information on the NOx/VOC regime that can be compared to source
estimates.
SATURN: A study of atmospheric pollution in urban areas (Moussiopoulos,
1999)
-
To improve substantially the ability to establish source-receptor relationships
at the urban scale. To meet this aim, the following sequence of activities
is planned:
-
To develop an appropriate model hierarchy, also covering the sub-urban
(local) scales to the extent necessary to establish source-receptor relationships.
-
To evaluate individual models with suitable procedures.
-
To support such procedures, the creation of proper validation datasets
from observations and experimental results originating from field campaigns
and laboratory studies will be necessary
Two other subprojects of interest in the urban field are GENEMIS and GLOREAM.
Emissions are the principal uncertainty in models at almost all scales
and the methods for obtaining spatial and temporal resolution and the validation
of emissions, started by GENEMIS in the first phase and being continued
today, are essential for the success of nearly all the subprojects in EUROTRAC-2,
(Friedrich, 1999). Similarly the model development work being undertaken
in GLOREAM should assist all modellers in dealing with problems of the
scale interactions which abound in urban situations (Builtjes, 1999).
6. Conclusions
The work being undertaken in EUROTRAC-2 should go some way to providing
some solutions to the problems and questions outlined in section 2. However
the environmental problems remain with those actually responsible for developing
policy for the atmospheric environment but, from past experience, but we
can be sure that the measures proposed will have a good scientific foundation.
However one problem remains which is neither scientific nor legislative
but concerns our society as a whole: Are we as a developed society prepared
to pay for and if necessary be limited by the measures necessary to ameliorate
the problems in the atmospheric environment? The major cause of our present
troubles is the expanding industrialisation and the ever-increasing amounts
of road traffic. At the moment we are engaged in doing the easier and cheaper
things to improve matters. But in the future, draconian reductions in pollutants
may be necessary in many places, and technical "fixes" may not be enough.
Then the crunch may come not only in terms of cost but also in limitations
on our freedom to travel wherever and whenever we want. The new millennium
certainly promises to be an "interesting" century!
7. Acknowledgements
It is a pleasure to thank the organisers of the meeting for inviting me
to give this paper and for their support to enable me to attend. I would
also like to thank Dr. Pauline Midgley, the Executive Secretary of EUROTRAC-2,
for her encouragement.
8. References
P. Borrell (editor), 1999, Transport and Chemical Transformation
of Pollutants in the Troposphere: an Overview of the work of EUROTRAC ,
, Springer Verlag, Heidelberg (in preparation). The other volumes of the
final report of the first phase are: Borrell P, Borrell P M, Cvitas T,
Kelly K, Seiler W, 1997, editors, Transport and Chemical Transformation
of Pollutants in the Troposphere, Springer Verlag, Heidelberg, Vols 2,
3, 4 &10 (1996); vols 5, 6, 7 & 8 (1997); vols 1 & 9 (in preparation).
P. Borrell, P. Builtjes, P. Grennfelt, Ø. Hov (editors),
1996, Photo-oxidants, Acidification and Tools, Policy Applications of
the EUROTRAC Results , Springer Verlag, Heidelberg.
J. Bösenberg, D. Brassington and P. Simon (Editors),
1997; Instrument Development for Atmospheric Research and Monitoring
, Springer Verlag, Heidelberg (1997)
P. Builtjes, 1999, GLOREAM Project Description ,
EUROTRAC-2 ISS, München.
J. Dumollin, A. Derouane and G. Dumont, 1999, Assessing
ozone in ambient air in Belgium , International Conference on Air Quality
in Europe: Challenges for the 2000s, Venice, May 1999.
ECE, 1994: The Economic Commission for Europe (ECE), Convention
on Long-Range Transboundary Air Pollution (LRTAP), United Nations, Geneva,
1994.
EUROTRAC-2, 1999: EUROTRAC-2 Project Description and
Handbook , EUROTRAC-2 ISS, München.
A. Eliassen, 1999, Policy-related tasks for EUROTRAC-2
, EUROTRAC-2 Project Description and Handbook, EUROTRAC-2 ISS, München,
32-38.
R. Friedrich, 1999, GENEMIS Project Description ,
EUROTRAC-2 ISS, München.
S. Fuzzi, 1999, PROCLOUD Project Description ,
EUROTRAC-2 ISS, München.
M. Lutz, 1999, private communication.
N. Moussiopoulos, 1999, SATURN Project Description
, EUROTRAC-2 ISS, München.
A. Neftel, 1999, LOOP Project Description , EUROTRAC-2
ISS, München.
J. Schneider, 1999, An assessment of Austrian Ozone Data
based on different indicators, Bericht des Umweltbundesamts , Wien,
BE 106.
U. Schurath, 1999, CMD Project Description , EUROTRAC-2
ISS, München.
J. Staehelin, J. Thudium, R. Buechler, A. Volz-Thomas
and W. Graber, 1994, Trends in surface ozone concentrations at Arosa
(Switzerland) , Atmos Environ, 28, 75-87.