Implementation of the Environmental Action Programme for CEE

 

Sofia Initiative
Local Air Pollution

 

 

 

Meeting Minutes

 

 

 

Regional Workshop for Reducing SOx and Particulate Emissions
Bratislava, Slovakia; January 20-22, 1998

 

 

Submitted by the Secretariat

 

Chair:  Secretariat:
Bulgaria
Dr. Dimitar Kantardjiev, Director General
The National Center for Environment and
Sustainable Development to the Ministry of
Environment and Waters
136, Tzar Boris III blvd
1618 Sofia, Bulgaria
Tel.: (359 2) 955 90 11
Fax: (359 2) 95590 15
E-mail: ncesd@online.bg

Mr. Miroslav Chodák, Project Manager
The Regional Environmental Center
Ady Endre út 9-11, 2000 Szentendre, Hungary
Tel.: (36-26) 504-000; Fax: (36-26) 311-294
http://www.rec.org/ E-mail: mchodak@rec.org

Mr. Mihail Staynov, Liaison Officer
REC Local Office Bulgaria
42, Alabin Str., 1000 Sofia, Bulgaria
Tel./Fax.: (359 2) 980 37 30
E-mail: mstaynov@bulnet.bg


Introduction

1. The Workshop for Reducing SOx and Particulate Emissions is one of components of the Sofia Initiative: Collaborative Programme on Improving Local Air Quality in Central and Eastern Europe (SILAQ). The workshop was organized by the Regional Environmental Center for Central and Eastern Europe (REC), Local Office Bulgaria and hosted by the REC, Local Office Slovakia.

2. The Workshop took place on 20-22 January 1998 in Bratislava, Slovakia according to an agenda preliminary coordinated by SILAQ Working Group members.

3. The goal of the Workshop was to exchange information on the impact of airborne Sulfur and Particulate Matter and on the different approaches to reducing SOx and particulate emissions.

4. The representatives of all SILAQ countries, as well as consultants from Austria, Denmark, Germany, and USA were invited to participate. The Workshop was attended by representatives from Bulgaria, Czech Republic, Poland, Romania and Slovakia, and consultants from Denmark, Germany and USA. For logistical reasons, the representatives from other SILAQ countries (Hungary and Slovenia) were not able to attend.

5. Different sessions of the Workshop were chaired by the different SILAQ delegates in rotation. The participants were welcomed by Mr. Vladimir Hudek, Local Representative of REC Slovakia, who was responsible for the logistics of the Workshop.

Day One

6. The Chairman of the SILAQ Working Group - Dr.Dimitar Kantardjiev, Bulgaria, opened the Workshop and welcomed all participants.

7. Ms. Petra Sanches, from the US EPA, led the session on the consequences of particulate matter and sulfur on human health. A general overview of scientific data illustrated a strong relationship between high mortality rates with exposure to fine particulate matter (PM 2.5) in both long and short term studies. The fine particles cause more damage to human health because they are more likely to be deposited into the lower cilia of the lungs, as opposed to more coarse particles that are often emitted by the respiratory system. Concerning SO2, the EPA concluded that short-term peak concentrations do not constitute the type of public health concern for which establishing national ambient air quality standards would be appropriate. The presentation was illustrated with specific data on research that was conducted on mild asthmatics regarding the minimum amount of these substances that would cause adverse health effects, criteria used, types of sources, groups of recipients. (List of presentations, 1).

8. The session highlighting the adverse health effects that are caused by these two pollutants was followed by a discussion which brought up different specific points.

  • Czech Republic: Two major collaborative projects developed together with USEPA evaluated the health impacts of airborne pollutants (SOx and PM). Extensive monitoring is required, but real difficulties result. Lifestyle in the Czech Republic (and elsewhere) is a more important factor with regard to health than the level of pollutants (especially SOx) in the air.
  • Denmark: There are many environmental projects supported by Denmark and the reduction of SOx/PM is regarded a priority for improvement in the CEE countries. Even though the quantity of these pollutants is very low in Denmark, research corroborates the evidence given. The State focuses its activities on VOCs and organics.
  • Germany: Pollution levels in Eastern Germany used to be high, but since 1990 there has been a sharp decrease of particulates owing to industrial and domestic standard increases. All power stations were force to apply the new standards, to change to gas or to be closed.
  • Poland: The energy sector in Poland is based on hard coal, and the pollution norms are exceeded. Upper Silesia is still recognised as one of the most polluted area in Europe, however due great effort in the industry modernisation some improvement in air quality is achieved. The impact of SOXPM on the health of the people is not an issue of the Ministry of the Environment, but of the Ministry of Health and Social Welfare.
  • In Romania, SO2 is one of the most effectively monitored pollutants. RomEPA controls 115 monitoring points.
  • Slovakia: Health effects of particulates is a concern of the Ministry of Health, but the health issues considered in environmental policy-making and the cooperation between these two ministries is currently improving. Fine and course particulates were just recently differentiated, so new information on their levels is forthcoming. The most polluted areas are monitored.
  • World Bank: It is very important to include such studies (on the relationship between air pollution and health) in the reduction programmes. The World Health Organization should be involved in developing public policy for environmental standards considering ambient air quality (for example, through NEHAPs - National Environmental and Health Plans, collaborations between MoE and MoH, monitoring/assessment of PM 2.5 pollution and health effect, measuring methods and devices, public policy, etc.).
  • U.S.A.: The EPA has two different approaches. Concerning controls of particulate matter and SOx, new sources are controlled more strictly than existing sources. The new sources must have the Best Available Control Techniques (BACT). Existing sources, because it is less economically feasible, are required to have a less stringent Reasonably Available Control Technique (RACT), which are designed by a team of engineers, economists and consultants. To shut sources down is a less popular approach in the US.
  • To summarize, it is necessary to answer the following questions: Can the countries show that there is an improvement of public health correlating with a decrease in particulates and SO2? This must be proved in order to justify international funding in this area. Can these countries collaborate and correlate (calibrate) certain standards so that they can be measured and compared? Air quality data are indicators of air quality, but what is needed are health indicators. Health indicators are difficult to attain because when a project deals with comparison internationally, cultural issues need to be taken into account as well. Developing these indicators will also require cooperation with health experts who can compare the changes in the Health Sector during the transition in CEE. There does need to be a much closer relationship between environmental and health officials. The programme should focus not only on the national levels of pollution but on the most polluted areas which should be assessed, improved and compared (maybe as a case study).
  • 9. The World Bank's Approach to Air Quality Management was presented by Ms. Magda Lovei. The environmental sustainability is a focus of the World Bank, whose goal is to fund only those projects that result in no environmental damage. Since the Rio conference, the Bank has funded 24% win-win projects, 8% environmental projects, 52% environmentally neutral projects, and 16% of the funded projects do damage to the environment. In Central and Eastern Europe, pollution management is a main focus of the WB, and the strategy has shifted from funding end of pipe technologies to pollution prevention and flexible plans that focus on partnerships between government and industry. What are currently the most serious problems? According to the risk assessment studies:

  • lead and particulates present a high risk
  • carbon monoxide, other metals, and ground level ozone are a medium risk
  • nitrogen oxide and other airborne pollutants present a lower risk
  • The least-cost approach would be used as opposed to cost-benefit analysis, and the role of the governments would be to provide a policy framework.
  • Further the main sources of pollution were described. The estimate cost of damage and cost/benefit analysis of fuel conservation was illustrated by Polish and Slovenian experience where the role of Government and the role of private sector in the environmental projects were highlighted. The role of the World Bank was synthesized to:
  • identify the benefits,
  • work with Government on policy measures, work with other IFIs to earn financing, based on politically acceptable strategies, action plans, risk assessment and health studies, least-cost and feasibility studies, integrated urban Air quality studies and cross-sectoral discussion. (List of presentation, 2).

  • 10. Control Measures for Particulate Matter and Sulfur were presented by Mr. James Yarbrough of the U.S. EPA. Among the first measures that need to be taken when considering control measures for particulate matter and sulfur is prioritizing the problems, emission inventorying, and introducing dispersion models to estimate the amount of emissions and the reduction needed. Most air models require source emissions in grams/second, stack height, gas exit velocity, gas exit temperature, and hourly meteorological data (wind direction, wind speed, atmospheric mixing height, and atmospheric stability class). A good, conservative air model to use is SCREEN. (an example of the air model is in the hand-out and it gives specific values and statistics). The Control Strategies for SO2 and PM were presented in five groups:

  • Air pollution control plans: In the U.S., State Implementation Plans (SIPs) are required by EPA for non-attainment areas, which are geographic areas that fail to meet the U.S. National Ambient Air Quality Standards (NAAQS). A SIP is a state plan with all of the enforceable regulations, approved by EPA, which enables EPA to confront industries that violate those regulations. EPA sets specific standards for SIPs where existing industrial sources must employ Reasonably Available Control Techniques (RACT), new sources must employ Best Available Control Techniques (BACT) and new sources in non-attainment areas must employ Lowest Achievable Emissions Rate (LAER) which is the strictest possible control.
  • Strict control of new sources: The EPA determines the BACT and LAER for specific industries, while a pre-construction permit program exists for large industrial sources. The Prevention of Significant Deterioration (PSD) Program specifically targets non-attainment areas.
  • Expensive SO2, PM industrial controls: The expensive industrial controls are flue-gas desulfurization (FGD), which is also known as scrubbing, and the so-called wet and dry method. The wet method entails the use of an electrostatic precipitator (ESP) or baghouse followed by a "scrubbing liquor". The particulate matter and slurry are filtered out when passing through the entrainment separator. The cost of this method is approximately $225/kw. Dry scrubbing employs an absorbing agent that removes pollutants. Natural gas burning is a very effective way of reducing SO2 and particulates, but the availability and costs are key issues.
  • Some cost-effective industrial controls include cyclones, ADVACATE, coal-cleaning, natural gas co-firing or re-burning, higher BTU coal/seasonal use, enclosing industrial processes/good O&M, increasing flue gas temperature/raising the stacks, and opacity reading/citizen volunteers. These methodologies are described in a handout which was distributed to participants. The importance of maintenance to combat fugitive emissions was also mentioned.
  • Cost-effective area source controls: These controls include road-paving, street sweeping/vacuuming, temporary controls based on meteorological data, open space and trees, zoning, efficient residential heaters, and discouraging of outside burning/securing dumps. These measures are also described in more detail in the handout that was distributed to participants (List of presentations, 3).

  • 11. Country Reports of Bulgaria and Romania were presented by the Working Group members. In Bulgaria pollution levels are close to the previous year's. The power sector accounts for almost 85% of particulate and 84% of SO2 annual emissions in 1996. More than a half from these SO2 emissions (approximately 51%) come from the Maritza East Thermal power plants due to lack of abatement equipment and an extremely high sulphur and ash content in the local lignites which they are using. There is not a strategy adopted but it is in a preparation phase and will be based on the least cost approach, cost and benefit analysis and global strategic directions (energy production, energy consumption and fuels). An action plan will focus on EU accession and on the implementation of the Clean Air Act and the Convention of LRTAP. In Romania the short term and medium term targets are established according to the LRTAP. Specific studies and measures, including economic incentives, technical guidelines and standards, public information and education, are included. (List of presentations, 4 and 5).

    Day Two

    12. The session concerned economic incentive programs that would encourage industries to be more efficient in their pollution control with the promise of financial benefit was presented by Mr.Yarbrogh (USEPA). These programs include air pollution control plans, marketable allowances, offsets program, netting, bubbles/alternative RACT, Supplementary Environmental Projects (SEPs), and the clean air investment fund. All of these programs are described in detail in the handout distributed by Mr.Yarbrogh. (List of presentations, 3). Clean Air Funds, Economic Incentives, and NAAQS Attainment Strategies were presented by James Yarbrough beginning from the various strategies that governments can take to encourage industries to maintain the lowest possible emissions of particulates and SO2. National Ambient Air Quality Standards (NAAQS) compliance programs in the United States are expected to fully utilize economic incentive programs. These programs include clean air funds, cap and trade programs, emissions averaging, emissions banking, and emissions taxes or fees. All of these programs are described in detail in the handout that was distributed during the presentation. Several examples were given of incentive programs that have been instituted in the United States. These program successes included the acid rain allowance system, the NOx averaging system, the lead trading and banking program, and the opt-in program, and Mr. Yarbrough also went into more detail concerning the benefits and liabilities of clean air funds. In the description of clean air funds, he provided many specific examples of funds, how to set them up, and how they work. The specifics of these programs are also provided in the handout (List of presentations, 3)

    13. Country Reports of Czech Republic, Poland and Slovakia were presented by the SILAQ Working Group members. In the Czech Republic the levels of SO2 levels in Northern Bohemia and Prague have decreased since the implementation of new legislation. There is no information about individual contributors. Low quality brown coal is widely used in the Czech Republic. Residential use is about 15-20%. In some districts conversion to natural gas has been about 7%. The Czech Power Company is producing about 75% of SOx emissions, there is only one private power plant (owned by a British company). According to the National programme by the year 2000 SOx emissions should be reduced by 90% and NOx emissions by 60% - in comparison to 1993. In May of 1997, the Ministry of the Environment set a limits decree defined by the Air Protection Legislation (158, 1994). In Poland the SO2 concentration on the border between the Czech Republic and Germany is the highest in Europe, and in some mountain areas, acid rain has killed most of the trees. These are problems that are of great concern to the ministry. Poland has a state administrative authority, and the Ministry of the Environment is the chief organization for environmental law and protection. The state environmental inspectorate issues punishments and fines and deals with economic instruments. Five state research institutions serve under the Ministry of the Environment in Poland as well. The Ministry of Health and Social Welfare is concerned with public health. There are three main legislative acts which creates system of law in Poland concerning air pollution: 1) the Act on Protection and Management of the Environment of 31st January, 1980 - a base for regulating air quality; 2) the Act on Spatial Management of July 7th, 1994; and 3) the Building Act. In a few years, laws should change as a result of implementation of the EU directives, and there will be big changes. Right now in Poland the environmental policy goals are 3-4 years in the short term goals, the year 2000 is the date set for medium term goals, and long term priorities have a date of 2010. The graphs showed that SO2 standards are exceeded, and it was stressed that Polish standards are more strict than European Union standards. SO2, NO2, and PMs are all decreasing over time. The Executive Programme to the National Environmental Policy for the years 1994-2000 aims to reduce SOx annual emissions to 1.0 million tonnes and PM to 0.7 million tonnes till year 2000. The government has already issued criteria for projects resulting in abatement of lower emissions from dispersed small sources. This document has been helping self-governments, the banks and Environmental Funds (National, Voivodeships, and Gminas Fund for Environmental Protection and Water Management) to implement National Environmental Policy. The results of the implementation of the policy is that the SO2 levels have decreased significantly. The basic differences between the countries in transition compared to the West are democracy. In Poland the citizens are not always involved in decisionmaking process. There is rare opportunity for the public (NGO's) to give comments on pending legislation. In Slovakia about 24% of the population is living in heavily polluted areas. Bratislava and Kosice are the two most polluted cities. There are 32 monitoring stations located in the most heavily polluted areas, and it has been determined that the ambient air standard for SO2 is not exceeded, but the standard for particulates is often exceeded. Slovak standards are very close to EU standards. The SO2 inventory is updated yearly. Both particulates and SO2 levels have decreased partly due to recession and partly due to new legislation. The consumption of brown coal has been reduced, and the use of natural gas has increased. After 1989, legislation was created to lower emissions. In 1996 the National Environmental Action Plan was enacted and includes both long and short term goals. Since implementation of the plan, both SO2 and Particulate emissions have decreased drastically. Fuel quality requirements are mandatory on a national level. Hungary was not represented at the workshop, but the country status report prepared especially for the SILAQ purposes was distributed. (List of presentations, 6, 7, 8 and 9).

    14. The representative of COWI Consult, Denmark, Mr.Douglas Clark presented the Danish Environmental Support Fund (DESF). The DESF supports air quality projects in Central and Eastern Europe and serves under the auspices of the Danish EPA. 380 projects were funded, 76 of those are air quality projects (total cost $150 million). The Agency looks for projects where the benefit to the environment would be the greatest, with visible results, that require only a short time for implementation. Investment projects are becoming more common as opposed to technical assistance. Who are the recipient countries? - Poland 40%, Czech/Slovak 18%, Baltics 12%, Russia 14%, CIS Countries 6%.
    The Project Evaluation Criteria are ordered: 1. priority of government, 2. local recipients, 3. Danish proponent (manager), 4. transfer of Danish "know-how", 5. pollution reduction, 6. co-financing (maybe matching funds), 7. sustainability and dissemination of results (good public relations for the Danish). The Danes offer district heating, energy conservation, emission control - large ESP's, bag houses, FGD, DeNOx, vapor recovery, catalytic incineration, coal fired plants, boiler replacements, incineration plants (municipal and hazardous waste), alternative energy sources. (List of presentation, 10)

    15. Mr.Dietmar Heinze from Vereinigte Energiewerke AG (VEAG),Germany presented their experience. The company was set up in 1990 to provide public power supply for the five new Bundeslaender (the former GDR). The briquetting, cocking, gas-making and power plants were operated until 1990 at the Schwartze Pumpe location. Their operation caused major environmental impact due to emissions of lignite dust, ash, odorous substances, hydrocarbons, SO2 and NOX. The cocking plant was closed, while a modernization programme was initiated for other plants. Due to the use of novel materials, supercritical steam parameters, utilization of hot flue gasses, use of eight preheating stages, etc. it has been possible to increase the net energetic efficiency and to reduce the specific CO2 emissions to 0.995 kg/kWh net. The electrostatic precipitators ensure that the dust burden does not exceed 50 (5 to 15 under operating) mg/Nm3, dry, 6% O2. Wet flue-gas desulphurization is based on the two-circuit process, using limestone as a sorbent, with 98% or 99% of sulphur removed under operation conditions. Six gypsum building-material factories are processing FGD gypsum to sandwich-type plasterboard, binder for flowable floor screed, gypsum wallboards and gypsum plaster. The effluent from the FGD unit is mixed with ash to produce a stabilizer that is dumped in the open-cast mine. In the FGD plant the SO2 raw-gas concentrations of 2,500 to 5,000 mg/m3 are reduced to quantities of 30 to 60 mg/m3. An emergency programme was initiated in 1990 aimed to rapidly and efficiently reducing dust from the old power plants. Attention was given to measures that could be carried out by the repair personnel at the site, which helped to essentially cut costs. (List of presentations, 11)

    16. The sessions on the SILAQ Synthesis Reports and on the Further SILAQ Activities was facilitated by Mr.Miroslav Chodak from the REC. He described the process of SILAQ: 1. Questionnaire, 2. Country Reports, 3. Structure of Region, 4. Draft Report, 5. Comments, 6. Final Version and the role of the REC - in its capacity to support as Secretariat.

    17. The discussion on the Synthesis Report on the Reduction of SOx and Particulate Emissions (SOXP) begun with a short presentation of the work on the draft by Mr.Yoncho Pelovski, leader of the consulting team who prepared the reports. The presented draft synthesis report on SOXP is based on the data sheets provided by Bulgaria, Romania, Slovakia and Slovenia. The Czech Republic, Hungary and Poland are included on the base of information collected by other sources (not through the Working Group members). The country reports, presented on the workshop, and data which will be presented till the end of January will be included in the next draft. In the report, objectives that need to be focused on are addressed. Of specific importance is transboundary pollution, and there is a clear trend of Environmental Authorities introducing stronger and stricter standards throughout Central and Eastern Europe.

    18. The comments of the participants were focused on content (not editorial). Czech Republic: Will send data sheets in the next few days. The report may use the data from the Internet pages. Recommend to include data for residential heating and public awareness with it. Slovakia: In general, likes report, there is a good, clear overview and it allows for a good orientation of the issues. Some figures should be correct according to the written comments which will be presented later. Bulgaria, Poland and Romania confirmed the evaluation given by Slovakia. Poland recommended to include more information for the economic incentives and instruments in the policy section. Germany commented that EU accession requires to use taxation and fees only. The World Bank acknowledged the quality of the report and mentioned that it is strong on the technical side, but might more emphasize the policy-side, stress more policy and legislative measures, reflect on the impact of enforcement mechanisms, taxes and charges, include more data on small source of pollution (traffic, etc..), and include more health impact data. The World Bank added that the OECD is preparing a paper for Aarhus. The main trend identified is that the economic growth and the environmental factors (emissions) tendencies are not similar.The US EPA evaluated the report as good work and recommended broadening the health impact section (to include and comment the existing health data). Denmark agreed that the report is important and serves as useful input to the Aarhus Conference. It also recommended caution be exercised with regard to the comments on trends in emissions and to give more explanation for GNP, change of fuel, separating countries that changing their fuels and those which are changing their technologies, as well as transboundary pollution, SO2 emissions from vehicles, and effectiveness of generation. Preventative measures need to be included in the catalog of control mechanisms, and also, if is it possible, to distinguish in the tables how much pollution is originated from high emissions and how much is from low emissions. It is necessary to point out that not only pollution control, but technological strategies, waste management, energy conservation, high and low emissions are important. The REC recommended to stress the attention not only to end-of-pipe solutions, but also to win-win and preventing measures.

    19. The reviewer of the report (Mr.Milos Tichy) suggested that there is a need to include government measures, and it needs to concentrate more on the effects rather than specific pollutants. Graphs in the report should show development in desulphurization, and what is the factor for reducing emissions - if it is a result of decreased economic activity or from implementation of new technologies. One paragraph should mention Country standards compared with EU standards. The approach should be geared toward government measures (fines should go to environmental fund). The success story where a regeneration plant replaced heater should not be highlighted as a special project. The fact that the role of government is limited to subsidiaries with respect to small pollution sources should be referenced.

    Day Three

    20. The discussion on the Synthesis Report on the Phase Out of Lead in Gasoline (POLG) begun with a short presentation of the work on the draft by Mr.Yoncho Pelovski. The presented final draft of the synthesis report on POLG is based on four things: the data sheets provided by Bulgaria, Czech Republic, Hungary, Poland, Romania, Slovakia and Slovenia, the country status reports of Bulgaria, Hungary, Romania, Slovakia and Slovenia, the information provided at the SILAQ workshop on POLG in June '97 in Bourgas and the materials prepared for the UNECE Task Force for POLG in Europe. The first draft included comments received from Bulgaria, Czech Republic, Hungary, Romania, Slovakia, Slovenia, Denmark, HIID and the World Bank. The comments, presented here at the workshop, will be included in the final copy.

    21. The Czech Republic (more recently involved) presented data sheets. Much data is missing. The SILAQ synthesis report is more tailored to the needs of CEE than the new pan-European strategy proposal. Other problems which, such as neglecting the possibility of an increase in benzene might be considered. In the paragraph on page 36, "some cars in many countries do need lubricants", the statement is correct, but LADA cars can use unleaded gasoline without any problem. More references are also needed at the end of the report and the pan-European strategy should be referenced, too. Add a list of references. The other SILAQ country representatives expressed their satisfaction with the report. Denmark recommended a three page executive summary.

    22. The Roundtable Discussion on SILAQ Activities until and after Aarhus focused on: 1) What needs to be done before Aarhus? New ideas for projects, elaborate and check on the feasibility with donors, finalize at next SILAQ working group meeting - 1st half of May; and 2) What should be presented as SILAQ contribution at Aarhus? Ministerial report submitted from Bulgaria by the name of all SILAQ countries, full set of country reports, synthesis papers, a glossy brochure - including results written in clear, easy to understand language and press release - written by a journalist and given to media. The flipcharts "What to do before Aarhus/in Aarhus?" and "What to do after Aarhus?" were elaborated on the basis of the opinions, statements and suggestions of the participants (The representatives of USEPA, WB and Germany do not participate in this session.). Denmark recommended the executive summary of the synthesis paper be published. The Czech Republic suggested the synthesis papers be submitted as background documents, while the ministerial document needs to be finalized before the next working group meeting.

    23. Proposals for post-Aarhus: Bulgaria: main goal for Bulgaria is SO2 and particulate matter reduction and would request European assistance in the preparation of the National programme on reduction of SOX and PM emissions (because it is only just beginning). Czech Republic: all countries are taking conclusions of SILAQ as a guide, next activity SILAQ could be how synthesis papers have been applied to the elaboration or implementation of National Air Quality Programmes. Monitoring and evaluation of the Czech programme (adopted in '91) by the group could be very useful. The Czech Republic is going to reduce SOX/PM from the power sector in a short time, but they should move their attention to residential sources. SILAQ programme is a means to activate work on the air-quality programmes on the National level also. Poland: Every international meeting is useful for the participants, and it gives inspiration for future activities. Within the SILAQ programme there is a possibility to compare our activities and assess the differences as well as similarities. The continuation of SILAQ programme was suggested. Romania: A national environmental strategy for reduction of the industrial pollution is being developed. SILAQ is very useful and inclusion of on both hydro carbons and NOx should be considered. Slovakia: SILAQ provides a good opportunity for the exchange of experience. Approaches and achievements can be compared. Successful programs can be presented and reviewed. It helps concentrate the efforts and harmonize our legislation and environmental statistics. The consultants (Y.Pelovski and D.Clark): Multi-country projects, environmental risk assessments, human health assessments, and cost benefit analysis could be very interesting to donors. Also, the identification of hot spots and projects, which might be supported by the ministries, the improvement of the monitoring of emissions in this areas, inventory studies - the main sources of pollution, visibility studies, etc. Some of the recommendations to the synthesis paper could not be included now, since they require additional data, inventorying, etc. The continuation of SILAQ programme should include an elaboration of the synthesis papers, development of criteria on changing fuel for instance. Specific targets for specific industry (wood products for example) should be elaborated which would later serve as basis for the development of indicators and statistics.

    24. Conclusions regarding the future of SILAQ: If the SILAQ programme continues after Aarhus, which was recommended by all participants, the programme should be oriented towards the harmonization of data and statistics (hot spots are often relative and comparison of levels of air pollution could be useful); transboundary pollution (case studies for local air pollution); risk assessment; cost-benefit; inventory studies (utilize and improve the inventory systems, where it is needed); feasibility studies; pilot projects are; compare legislation and policy measures; and other pollutants. The main decisionmaking body of SILAQ should be the existing Working Group consisting of delegated members of each participating country (Bulgaria, Czech Republic, Hungary, Poland, Romania, Slovakia, Slovenia). It will continue to identify projects, evaluate progress, and review the results. In order to meet the new specific tasks of the programme Expert Working Group(s) should be established which will be the implementing body of SILAQ. For certain purposes different countries might establish National Expert Working Group(s) which will be facilitated or supported by the programme. The REC might continue to provide secretarial support directly and by hiring specific consultants. All members and the REC shall do their best to reinforce the Support Panel to the programme.

    25. The Workshop closed with the conclusion that it was both useful and beneficial. The presented materials will be copied and disseminated to the participants later. A list of the materials presented and additional late materials will be attached to the report from the meeting.

    Attachments:

    a) List of participants
    b) List of presentations (available on hard copy)
    c) List of presentation (distributed during the workshop)
    d) List of materials available at the coordinator
    e) Flipcharts from the last two sessions

     


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