1. Industrial Processes ( Case of Czech Republic) Dušan Vácha Czech Hydrometeorological Institute Fulfilling the monitoring and reporting requirements under the UNFCCC and KP 9 - 10 October 2006

2. Outline National Inventory System (NIS) Key categories 2A. Mineral Products 2B. Chemical Industry 2C. Metal Production 2F. Consumption of Halocarbons and SF 6

3. NIS In CR, the MoE is the national entity with overall responsibility for the NIS. CHMI was designated as the coordinating and managing organisation responsible for the compilation of the national greenhouse gas inventory and reporting (CRF + NIR) Responsibilities for the GHG inventory compilation from individual sectors are allocated as follows: –KONEKO marketing, Ltd. - Energy sector, stationary sources and fugitive emissions; –Transport Research Centre (CDV), Energy sector, mobile sources; –CHMI, Industrial Processes and Product Use sectors; –Institute of Forestry Ecosystem Research (IFER), Agriculture and Land Use, Land Use Change and Forestry sectors; –Charles University Environment Centre (CUEC), Waste sector.

4. NIS CHMI is responsible for Industrial Processes inventory compilation –Broad cooperation with Industrial Association (Czech Lime Association, Czech Cement Association) Ministry of Environment (EU ETS data) Czech Statistical Office (activity data) KONEKO marketing Ltd. (Energy sector and Iron and Steel Production, Ammonia Production) External Experts (Chemical Industry – nitric and adipic acid production, emissions from use of F-gases imported as bulk) Jan Evangelista Purkyně University (methodology development for emissions from use of F-gases imported in product) 13 part-time staff

5. NIS All cooperation is based on contract except –Ministry of Environment –Cooperation with Czech Statistical Office is Direct (public available data, e.g. energy statistics) Indirect (individual data, e.g. ceramics sector) mediator is Statistical Department of MoE

6. Key sources (2004, Tier 1 – Level Assessment)

7. Key sources (2004, Tier 2 – Trend Assessment)

8. 2A. Mineral Products Emissions from production of –Cement / clinker –Lime –Ceramics –Desulphurization –Limestone use (in slintering plant, emissions from liming is in LULUCF) –Glass – default EF Same methodology for all sub-categories, based on official statistics and national or default EF

9. 2A. Mineral Products National EF are based on EU ETS data (provided by the MoE) and official statistic data (Czech Statistical Office, Czech Lime Association, Czech Cement Association ) –Complete data about cement and lime production, limestone use for slintering, desulphurization –EFs (for bricks, roofing tiles and tiles) was derived from EU ETS data and production from individual installation Data from Czech Lime Association are used for emissions removal estimate (e.g. lime used in building industry)

10. 2A. Mineral Products - Recalculation Emissions from almost all sub-categories were recalculated in recent years –Desulphurization was re-allocated from category 1B to 2A –For cement production was used Tier 2 methodology instead Tier 1 –For lime production was assessed proportion of removals –Emissions from ceramics and limestone use in slintering plant were add in submission 2006 –Only emissions from glass production remain

11. 2B. Chemical Industry Emissions from production of –Nitric and Adipic Acid production (2 installation) –Ammonia production (1 installation) Emissions estimates are based on –Activity data, EF and technologies (production and abatement technology for N&A Acids/N 2 0) Cooperation with external experts (Acids) Cooperation with KONEKO marketing Ltd., which is responsible for Energy sector (non- energy use of fuel for ammonia production)

12. 2C. Metal Production Emissions from Iron & Steel Production Close cooperation with KONEKO marketing - fuel distribution between 1A2a and 2C Distribution of fuel is estimated because of missing official data, estimate is based on data about blast furnace gas and oxygen furnace gas Exact fuel distribution is impossible and every country use different approach In submission 2004 was reported emissions re- allocation from 1A2a to 2C (in 2006 whole series re- allocation), which reflect reality more exact

13. 2F. Consumption of Halocarbons and SF 6 F-gases are not produced in CR Most complex sub-category 1.SF 6 used in electrical equipment, 2.HFCs and PFCs used as refrigerants in refrigeration and air conditioning equipment, 3.SF 6 used in sound proof windows production, 4.HFCs, PFCs and SF 6 used in semiconductor manufacturing, 5.HFCs used as propellants in aerosols, 6.HFCs used as blowing agents, 7.HFCs used as extinguishing agents in fixed fire fighting systems.

14. 2F. Consumption of Halocarbons and SF 6 Since 2006 submission are reported actual emissions Methodology is based on mass balance (top-down approach) Emission = Sales – New Charge + Retiring - Destroyed 2000 GPG methodology for windows, aerosols, blowing agents and fire fighting systems Information about import and export provide Custom Office (amount and address) All importers and exporters are ask to provide more precise data about: 1.Imported and exported amounts 2.Kinds of substances (or their mixtures) 3.Areas of usage

15. 2F. Consumption of Halocarbons and SF 6 F-gases are used since approximately 1995 short period for retiring In CR exist 2 companies for refrigerator and air conditioning disposal and 2 companies for refrigerants (mainly CFC) destruction or cleaning (and re-use) All was asked to report amount of HFCs (disposal, destruct or cleaned), they together report only some kg

16. 2F. Consumption of Halocarbons and SF 6 Started cooperation with Jan Evangelista Purkyně University on methodology development for emissions from use of F-gases imported in product Provisional results will be available in next year, probably not as a part of NIR

17. Thank you ! Czech Hydrometeorological Institute http://www.chmi.cz Dusan Vacha dvacha@chmi.cz