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ANNEX A: CORINAIR 90 QUESTIONNAIRES
ANNEX B: CHARACTERISTICS OF CORINAIR 90 DATABASES
ANNEX C: NATIONAL CONFIDENTIALITY REQUIREMENTS
ANNEX D: PROPOSED SOFTWARE CHANGES FOR AIR EMISSIONS
ANNEX A CORINAIR 90 QUESTIONNAIRES
A questionnaire on the CORINAIR 90 methodology was sent out in early 1994. 16 out of the 30 participants returned completed questionnaires to the EEA:
EEA Members:
Belgium (Flemish)
Belgium (Walloon)
Germany
Spain
France
Luxembourg
Portugal
Finland
Norway
Sweden
UK
Eastern European Countries:
Bulgaria
Czech Republic
Hungary
Poland
Slovenia
In 1995 the Air Emissions Topic Centre contacted seven countries who had not completed the questionnaire to establish their general views on the CORINAIR 90 methodology. The countries contacted were:
Greece
Ireland
Italy
Switzerland
Croatia
Slovakia
Romania
Russia
The main results of the questionnaire are discussed below. As only just over half of participants replied to the questionnaire in full the results can only be taken as indicative.
1. Resources
Between 1 to 2 man-years were generally required to compile CORINAIR 90, although some of the Eastern European countries compiling CORINAIR for the first time took 4 to 5 man-years.
2. Relationships with National Inventories and International Reporting Requirements
Only four countries used the CORINAIR database as the basis of a national methodology; in addition in Germany CORINAIR was used to help complete the national inventory, and in France, CORINAIR is initially developed in parallel with rough national estimates, and is then used as the national inventory as it is developed further. In six countries CORINAIR is used to reproduce estimates made in the national emissions inventory, and in the remaining four countries the two inventories are completely independent.
Just over half of countries (10) used the 11 main CORINAIR/EMEP source sectors to report to LRTAP, and half were planning for CORINAIR data to be used by EEA-TF in the preparation of EMEP data. Just under half were preparing greenhouse gas emissions data for the Framework Climate Change Convention using CORINAIR methodology and the proposed IPCC reporting format.
3. Reasons for Delay in Completing CORINAIR 90
The most common reported reasons for delay which were reported were all linked to data requirements (Table 1). Data was seen as difficult to find and data requirements as demanding; in addition waiting for the publication of official statistics and for data from various source sectors caused delay. For some countries official statistics for 1990 were not available until the end of 1992 or mid 1993, and in France and Germany, source data for some activities was not available until 1994. In some countries, data was only available in socio-economic categories and additional work was required to extract data in the technological categories required for CORINAIR. This was a particular problem in countries completing CORINAIR for the first time.
A lack of priority for CORINAIR work was also identified as a cause for concern. In some countries there is an emphasis on producing a top down national inventory quickly first, before beginning work on CORINAIR.
Table 1 Reported Reasons for Delay in Completing CORINAIR 90*
Reason | No. of countries | No. of countries as % of those responding (20) |
Data difficult to find | 15 | |
Data requirements very demanding | 13 | 65% |
Dependent on data supply from various source sectors | 13 | 65% |
Dependent on publication of official statistics | 11 | 55% |
Priority given to other work | 10 | 50% |
Shortage of national funding | 10 | 50% |
Needed training in use of software | 9 | 45% |
Data requirements very complicated | 8 | 40% |
Software difficult to understand | 7 | 35% |
Shortage of CEC funding | 7 | 35% |
Late receipt of contract from national/regional customer | 7 | 35% |
Shortage of (experienced) staff | 6 | 30% |
Changes in software/data requirements lead to duplication of effort | 5 | 25% |
Late entry into CORINAIR programme | 5 | 25% |
Dependent on completion of emission estimates using national methodology | 4 | 20% |
Late reply from EEA-TF following request for help | 3 | 15% |
Late receipt of contract from CEC (EEA-TF or PHARE) | 2 | 10% |
Need to completely verify database before sending to CITEPA or Zierock/Samaras | 2 | 10% |
Staff switched/lost from CORINAIR during data build | 2 | 10% |
Late reply from CITEPA or Zierock/Samara with consistency check reports | 0 | 0% |
Late reply from CITEPA or Zierock/Samara following request for help | 0 | 0% |
*
Based on replies from 16 countries returning questionnaire plus information from Croatia,
4. Inconsistencies
The questionnaire revealed inconsistencies in the way that CORINAIR is compiled. Half of countries submitted estimates of CO2 emissions as the actual emissions from the exhaust, and half as ultimate CO2 which assumes that all the carbon in the exhaust will eventually be converted to CO2. Similarly, about half of countries included CO2 emissions from biomass burning and half excluded them.
5. Verification
The most common sources of information for verifying CORINAIR were emissions estimates made using the national methodology and emission factors in the Default Emission Factor Handbook (Table 2). National energy statistics and emission estimates from point source operators were also used in many countries.
Table 2 Other Information used to Verify CORINAIR 90
Verification against: | No. of countries | No. of countries as % of those responding (16) |
National methodology emissions estimates | 14 | 87% |
Emission factors in Default Emission Factor Handbook | 13 | 81% |
National energy statistics | 11 | 69% |
Point source operators emissions estimates | 10 | 62% |
Emissions estimates from local/urban/regional inventories | 7 | 44% |
Other international energy statistics | 5 | 31% |
Eurostat emissions estimates | 4 | 25% |
EMEP emissions estimates | 3 | 19% |
OECD emissions estimates | 3 | 19% |
Eurostat energy statistics | 1 | 6% |
UNECE emission estimates | 1 | 6% |
6. CORINAIR Material and Software
CORINAIR and COPERT material (software and manuals/instructions) were rated as average, and additional information, check reports, progress meetings etc. as good. Although the use of English for all printed material caused few difficulties on average, 7 participants asked for material in an alternative language - French (3), German (2), Russian (1) and Portuguese (1).
The various aspects of the CORINAIR software were rated as average or good:
Average | Good |
Screen data entry | Overall design |
Speed of response | Data Build - emissions calculations |
File transfer (without screen
interface) Data Build Data Edit |
Initialisation Options - indexing Options - backup/restore Options - COPERT import Options - empty temp files (very good) |
There were also a number of specific comments on individual aspects of the softwares usability (Table 3).
With regard to the overall design, there were several calls for a Windows-based application of the software - the system was not felt to be user friendly by todays standards, and data entry in the current software was found to be very time consuming, with a lot of duplication (e.g. area sources, ratio and emission factors have to be filled in one by one, fuel emission factors for point sources have to be repeated many times). These aspects could be remedied by using spreadsheets for data entry. It was also felt that it was not easy to aggregate data and to produce summary tables, or e.g. to produce tables giving all the data on one particular point source, or one SNAP code. At least two countries had transferred data from CORINAIR files to their own database systems to allow them to produce tables, cross-check data, and edit results.
Table 3 Comments on Aspects of the CORINAIR and COPERT Software*
CORINAIR | Comments | |
Screen data entry | very slow, lot of duplication; too many keystrokes necessary to enter data; problem with numeric fields which do not have decimal places; | |
Speed of response | calculations take too much time; | |
File transfer (without screen interface) | non-existent; | |
Data build - data files | for some classification groups it is impossible to add new items such as types of units; for area activities when the default socio-economic variable (BASEA) is not used, problems with the conversion ration which must be defined; | |
Data build - allocation procedures | time consuming, very slow to update; slow; needs error messages stored simply; incomplete- lacks a good facility to aggregate data; | |
Data build - emissions calculations | very slow - need to process after each correction to view the result; slow and old fashioned; | |
Data build - checking procedures | very slow - need to process after each correction to view the result; not possible to choose printer ports; too many messages, many of which have little information value; | |
Data edit - data files | large number of codes make the screens difficult to understand; impossible to do some types of queries (e.g. to view LPSs with an activity rate above a certain level); | |
Data edit - emission files | not possible to look at emissions from separate parts of an LPS; | |
Initialisation | problems when CORINAIR is in use on a PC in network (LAN); need to change parameters and reboot at start of each session; | |
Options - backup/restore | backup is only possible to diskette; not operational with DOS 6; problems -does not work properly; | |
COPERT | In COPERT there is no clear differentiation between data and procedure files (except for COPERT/CORINAIR transfer) - this applies to file transfer, data build, definitions and data files , data edit files and emission files; Screen data entry - spreadsheet design not so good; |
* Each of the comments in the Table were made by one expert only
One country felt that CORINAIR should allow more flexible input of data on point sources; it suggested point source data should be entered whatever the size of the source, and CORINAIR should then have the capability to select large point sources through a given selection criteria.
Other comments included:
6. Surrogate Definitions
Table 4 Surrogate Parameters provided for CORINAIR 90
Type of surrogate data | Provided | Not available | Not provided but available |
Provided | Not available | Not provided but available |
Nos. of road vehicles | 8 | 1 | 5 | 50% | 6% | 31% |
Distances travelled by road vehicles | 4 | 2 | 7 | 25% | 13% | 44% |
Nos. of non-road vehicles | 6 | 4 | 2 | 38% | 25% | 13% |
Forest area | 9 | 0 | 5 | 56% | 0% | 31% |
Agricultural area | 10 | 1 | 3 | 63% | 6% | 19% |
Other land use | 4 | 2 | 5 | 25% | 13% | 31% |
Nos. of households | 4 | 1 | 9 | 25% | 6% | 56% |
Nos. of employees/workers | 5 | 0 | 8 | 31% | 0% | 50% |
7. COPERT
6 countries directly used COPERT, 2 used it to cross check data, and 8 did not use it all. Some countries expressed difficulty in obtaining data in the format required for inclusion in COPERT e.g. mileage per vehicle.
8. SNAP Codes
Suggestions for SNAP codes which should be subdivided, added, or aggregated or deleted are shown in Tables 5a, 5b and 5c. More general comments included:
Additions/completeness
Areas for improved clarity/definitions
- NAPACT (ISIC, NACE...) economic-sectoral
- NAPTEC -techniques
- NAPCONT - control reduction technologies
- NAPFUE - fuels
Deletion/Aggregation
Table 6 shows reasons why it was not possible for countries to complete the CORINAIR database - either because the activity definition was unclear, or activity data or emission factors were unavailable. Some of the comments reflect ambiguities already mentioned above (e.g. the split between combustion and process dependent emissions in some industries); other problems are probably particular to one country. The main areas where several countries experienced problems were solvent use (06), other transport (08), and nature (011) .
In some countries, the mismatch between SNAP codes and categories used for socio-economic data had caused some problems in data collection for some sectors.
Table 5a SNAP codes to be Sub-divided
Code | Description | To be split into: |
02 | Commercial, institutional and residential combustion plants | commercial residential tertiary |
02.00.02 | Commercial, institutional and residential combustion plants - combustion plants <50 MW | residential
non-residential |
03.03.11 | Processes with contact - cement | dry
method wet method |
04.07 | Cooling plants | ammonia
plants freon plants |
04.02.08 | Iron and steel processes - rolling mills | hot
rolling cold rolling |
05.01.02 | Underground coal mining | with
methane emission reduction without methane emission reduction |
05.05.01 | Refinery dispatch station | railway
tanker pipeline tanker |
06.01.01 to 06.01.04 | Solvent use paint application | using
water solvent using non-water solvent |
06.01.02 | Other industrial paint application | automobile repair |
06.04.02 | Other uses of solvents -fat, edible and non-edible oil extraction | grinding |
06.04.03 | Other uses of solvents -printing | packaging edition printing |
06.04.04 | Other uses of solvents - fat, edible and non-edible oil extraction | grinding degreasing |
06.04.06 | Other uses of solvents - preservation of wood | impregnation coating |
06.04.07 | Underseal treatment of vehicles | undersealing treatment of hollow spaces |
06.04.06 | Domestic use of solvents | use of cosmetics |
06.04.09 | Vehicle dewaxing | vehicle
dewaxing vehicle waxing |
08.03 | Inland waterways | inland
waterways coastal navigation |
09.01 | Waste water treatment | refinery
industry municipal |
09.07 | Open burning of agricultural waste | open
burning of agricultural waste open burning of forestry wastes |
Table 5b Activities to be Added
To Code | Description | Add |
03.02 | Process Furnaces without Contact | drying kilns (e.g. in car manufacture) |
03.03 | Process with contact | sugar |
04.03 | non-combustion processes in ferrous metal industries | production of silicon carbide |
04.05 | Production processes- organic chemical industry | ethylene
glycol aniline cyclohexane ethylene dichloride |
06.03 | Chemical products manufacturing or processing | additional
substances for chemical production processing of synthetic materials (excluding 06.03.02) |
06.04 | Other uses of solvents and related activities | other
industrial cleaning protective coatings for the construction industry (excluding O6.04.06) metal treatment pesticides other industrial applications |
10.04 | Animal breeding | poultry |
10.04 | Animal breeding (enteric fermentation) | tame reindeer |
10.05 | Animal breeding (excretion) | tame reindeer |
11 | Nature | Land
use changes Others? (as relevant to IPCC/OECD reporting format) |
? | not specified by respondent | charcoal production |
? | not specified by respondent | nickel or other non-ferrous metal production |
? | not specified by respondent | production of soda fluffy |
? | not specified by respondent | furnace induction for cast iron |
? | not specified by respondent | coal drying |
? | not specified by respondent | caprolactam |
? | not specified by respondent | well testing |
Table 5c Activities to be Deleted or Aggregated
Code | Description | |
04.04.11 | graphite | delete |
04.06.09 | bark gasifier | delete |
04.06.12 04.06.13 04.06.14 |
Cement Lime Glass |
aggregate |
09.08.00 | Latrines | delete |
11.07.02 | termites | delete |
Table 6 Reasons for Incomplete
Database
SNAP code |
Activity definition | Activity definition unclear | Activity data unavailable | Emission factors unavailable |
Note |
1 | PUBLIC POWER, COGENERATION AND DISTRICT HEATING PLANTS | ||||
10104 | GAS TURBINES | * | |||
10105 | STATIONARY ENGINES | * | |||
10204 | GAS TURBINES | * | |||
10205 | STATIONARY ENGINES | * | |||
2 | COMMERCIAL, INSTITUTIONAL AND RESIDENTIAL COMBUSTION PLANTS | ||||
20003 | GAS TURBINES | * | |||
20004 | STATIONARY ENGINES | * | |||
3 | INDUSTRIAL COMBUSTION PLANTS AND PROCESSES WITH COMBUSTION | ||||
30104 | GAS TURBINES | * | |||
30105 | STATIONARY ENGINES | * | |||
30311 | CEMENT | * | Confusion with 40612 and 40613, cement and glass, non combustion processes | ||
30314 | FLAT GLASS | * | |||
30318 | MINERAL WOOL | * | |||
30320 | FINE CERAMICS MATERIAL | * | |||
4 | NON COMBUSTION PROCESSES | ||||
40100 | PRODUCTION PROCESSES - PETROLEUM INDUSTRIES | * | Difficult to differentiate between emissions from constituent parts and overlap with refinery furnaces (30201) | ||
40302 | FERRO ALLOYS | * | * | unclear | |
40406 | AMMONIUM PHOSPHATE | * | |||
40411 | GRAPHITE | * | |||
40500 | PRODUCTION PROCESSES -ORGANIC CHEMICAL INDUSTRY | In addition to the problems reported below one country reported general difficulties with activity data and emissions factors for all 405XX codes | |||
40503 | 1,2 DICHLOROETH (EXCEPT 040505) | * | |||
40505 | 1,2 DICHLOROETH + VINYLCHL (BALANCED PROCESS) | * | |||
40513 | STYRENE-BUTADIENE LATEX | * | |||
40514 | STYRENE-BUTADIENE RUBBER (SBR) | * | |||
40515 | ACRYLONIT. BUTADIENE STYRENE (ABS) RESINS | * | |||
40522 | STORAGE AND HANDLING OF CHEMICAL PRODUCTS | * | ** | ** |
Key: * reported by one country; ** reported by two countries
Table 6 Reasons for Incomplete Database (contd)
SNAP code | Activity definition | Activity definition unclear | Activity data unavailable | Emission factors unavailable | Note |
40601 | CHIP BOARD | * | |||
40606 | WINE | * | * | ||
40607 | BEER | * | * | ||
40608 | SPIRITS | * | * | ||
40609 | BARK GASIFIER | * | ** | ** | |
40610 | ASPHALT ROOFING MATERIALS | ** | ** | ||
40611 | ROAD PAVING WITH ASPHALT | * | * | ||
40612 | CEMENT | * | Confusion with 30311 and 30314 | ||
40613 | GLASS | * | |||
40700 | PRODUCTION PROCESSES - COOLING PLANTS | * | * | * | |
5 | EXTRACTION AND DISTRIBUTION OF FOSSIL FUELS | ||||
50103 | STORAGE OF SOLID FUELS | * | |||
50201 | LAND BASED EXTRACTION, 1ST TREATMENT AND LOADING OF LIQUID FUELS | * | |||
50502 | OFF-SHORE EXTRACTION, 1ST TREATMENT AND LOADING OF LIQUID FUELS | * | |||
50302 | OTHER LAND BASED EXTRACTION, 1ST TREATMENT AND LOADING OF GASEOUS FUELS | * | |||
50303 | OFF-SHORE EXTRACTION, 1ST TREATMENT AND LOADING OF GASEOUS FUELS | * | |||
50502 | TRANSPORT AND DEPOTS FOR GASOLINE DISTRIBUTION | * partially | |||
50602 | PIPELINE COMPRESSOR STATIONS | * partially | |||
6 | SOLVENT USE | ||||
60101 | MANUFACTURE OF AUTOMOBILES | * | |||
60102 | OTHER INDUSTRIAL APPLICATIONS | ** | |||
60103 | CONSTRUCTION AND BUILDINGS | * | |||
60104 | DOMESTIC USE | * | |||
60201 | METAL DEGREASING | ** | |||
60202 | DRY CLEANING | * | |||
60300 | SOLVENT USE -CHEMICAL PRODUCTS MANUFACT/PROCESSING | In addition, one country reported general difficulties with activity data and emissions factors for all 603XX codes. | |||
60301 | POLYESTER PROCESSING | * |
Key: * reported by one country; ** reported by two countries
Table 6 Reasons for Incomplete Database (contd)
SNAP code | Activity definition | Activity definition unclear | Activity data unavailable | Emission factors unavailable | Note |
60302 | POLYVINYLCHLORIDE PROCESS | * | |||
60303 | POLYURETHANE PROCESSING | * | |||
60304 | POLYSTYRENE FOAM PROCESS | * | |||
60305 | RUBBER PROCESSING | * | |||
60305 | PHARMACEUTICAL PRODUCTION MANUFACTURING | ** | |||
60310 | ASPHALT BLOWING | * | |||
60311 | ADHESIVE TAPES MANUFACTURE | * | * partially | * | |
60401 | GLASS WOOL ENDUCTION | * | |||
60402 | MINERAL WOOL ENDUCTION | ** | |||
60404 | FAT EDIBLE AND NON-EDIBLE OIL EXTRACTION | * | |||
60405 | APPLICATION OF GLUES AND ADHESIVES | * | * | ||
60406 | PRESERVATION OF WOOD | * | |||
60407 | UNDERSEAL TREATMENT OF VEHICLES | ** | * | ||
60408 | DOMESTIC SOLVENT USE (OTHER THAN PAINT) | ** | * | ||
8 | OTHER TRANSPORT | ||||
80100 | OFF ROAD VEHICLES AND MACHINES | One
country reported unclear activity definitions for all 801XX codes; two countries reported that activity data and emissions factors were partially or wholly unavailable |
|||
80103 | INDUSTRY | ** | |||
80104 | MILITARY | * | |||
80105 | HOUSEHOLD/GARDENING | ** | * | ||
80400 | MARINE ACTIVITIES | *unclear | * | ||
80401 | HARBOURS | * | |||
80500 | AIRPORTS (LTO CYCLES AND GROUND ACTIVITIES) | * | * | * | For ground activities |
9 | WASTE TREATMENT AND DISPOSAL | One country reported that data was incomplete and unavailable and that emissions factors were unavailable for all code 9 data | |||
90100 | WASTE WATER TREATMENT | * | |||
90203 | FLARING IN OIL INDUSTRY | * | * | ||
90204 | FLARING IN CHEMICAL INDUSTRIES | * | * | * | |
90300 | SLUDGE SPREADING | * | * |
Key: * reported by one country; ** reported by two countries
Table 6 Reasons for Incomplete Database (contd)
SNAP code | Activity definition | Activity definition unclear | Activity data unavailable | Emission factors unavailable | Note |
90600 | BIOGAS PRODUCTION | * | |||
90700 | OPEN BURNING OF AGRICULTURAL WASTES | * | |||
90800 | LATRINES | * | * | ||
10 | AGRICULTURE | One country reported that emission factors for methane and NMVOCs were unavailable for all SNAP code 10 activities | |||
100100 | CULTURES WITH FERTILISERS | One country reported that it was not possible to distinguish between data for 10100 and 10200 | |||
100200 | CULTURES WITHOUT FERTILISERS | ||||
100510 | FUR ANIMALS | * | * | ||
11 | NATURE | One country reported that an emission factor for methane was unavailable for all SNAP code 11 activities. Another country queried where scrublands and open forests should be included. | |||
110501 | UNDRAINED AND BRACKISH MARSHES | * | |||
110502 | DRAINED MARSHES | * | |||
110602 | RAISED BOGS | * | * | * | |
110603 | SHALLOW SALTWATERS | * | * | * | |
110604 | GROUND WATERS | * | * | * | |
110605 | DRAINAGE WATERS | ** | ** | ||
110606 | RIVERS | * | |||
110607 | DITCHES AND CANALS | * | * | ||
110701 | OPEN SEA | * | |||
110702 | TERMITES | * | * | ||
110800 | MAMMALS | * | |||
110900 | NEAR SURFACE DEPOSITS | ** | * | * |
Key: * reported by one country; ** reported by two countries
ANNEX B CHARACTERISTICS OF CORINAIR 90 DATABASES
Table B.1 The number of area source data defined by each country in CORINAIR 90 is given below. They show the range of approaches adopted to completing CORINAIR 90 by individual countries.
Rubrics | Fuels | Activities | Territorial units | Activity rates | Emission factors | |
Belgium (Flemish Region) | 20 | 62 | 184 | 29 | 2297 | 2705 |
Belgium (Wallonie region) | 29 | 32 | 153 | 28 | 2884 | 1232 |
Germany (former west) | 10 | 84 | 268 | 366 | 16405 | ? |
Germany (former east) | 12 | 84 | 182 | 229 | 4829 | 5060 |
Denmark | 17 | 64 | 175 | 21 | 3642 | 952 |
Spain | 200 | 142 | 509 | 78 | 39702 | 3616 |
France | 109 | 260 | 516 | 128 | 50335 | 5316 |
Greece | 0 | 12 | 228 | 67 | 12568 | 1665 |
Ireland | 0 | 28 | 95 | 12 | 1140 | 683 |
Italy | 4 | 20 | 242 | 127 | 17134 | 3491 |
Luxembourg | 11 | 22 | 124 | 1 | 124 | 579 |
Netherlands | 48 | 25 | 683 | 57 | 15702 | 683 |
Portugal | 22 | 65 | 170 | 38 | 5780 | 2256 |
United Kingdom | 1 | 22 | 173 | 95 | 16340 | 573 |
Austria | 27 | 19 | 115 | 10 | 1150 | 549 |
Finland | 27 | 18 | 229 | 14 | 836 | 894 |
Norway | 76 | 21 | 187 | 23 | 4301 | 1559 |
Sweden | 2 | 91 | 124 | 25 | 1708 | 1836 |
Bulgaria | 44 | 29 | 283 | 11 | 2322 | 1507 |
Czech Republic* | 1 | 177 | 188 | 10 | 1276 | 4202 |
Hungary | 2 | 34 | 144 | 147 | 2823 | 438 |
Poland | 18 | 148 | 164 | 51 | 8364 | 761 |
Romania | 8 | 14 | 171 | 44 | 4284 | 15643 |
Slovak Republic | 22 | 48 | 138 | 43 | 5680 | 862 |
Estonia | 3 | 18 | 86 | 19 | 1126 | 2322 |
Latvia | 8 | 24 | 162 | 12 | 1104 | 3158 |
Lithuania | 8 | 13 | 99 | 12 | 1032 | 3900 |
Slovenia | 58 | 17 | 57 | 75 | 58 | 185 |
ANNEX C NATIONAL CONFIDENTIALITY REQUIREMENTS
Country | All Open | SNAP Groups restricted | 1 Loca- tion |
2 Source data | 3 Opera- tions |
4 Activity data |
5 Emiss- ions |
Comments |
Belgium-Flemish | YES | |||||||
Belgium-Walloon | ? | |||||||
Denmark | YES | |||||||
Germany | ? | |||||||
Greece | NO | Refineries | O | X | X | X | X | |
Spain | NO | LPS | O | O | X | X | O except LCPs | LCP data more restricted |
France | NO | ALL LPS | O | X | X | X | O | |
Ireland | YES | |||||||
Italy | ALL LPS | O | O | O | X | O | ||
Luxembourg | YES | |||||||
Netherlands | NO | ALL LPS | O | X | X | X | O | |
Portugal | NO | ALL LPS | X | X | X | X | O | Coordinates restricted |
United Kingdom | YES | |||||||
Austria | ? | |||||||
Finland | ? | |||||||
Norway | NO | 3 & 4 | O | X | X | X | O | Area source activity/emission factor restrictions |
Sweden | O LPS | |||||||
Switzerland | ? | |||||||
Albania | ? | |||||||
Bulgaria | YES | |||||||
Croatia | ? | |||||||
Czech Republic | NO | All LPS | X | X | O | X | O | Coordinates restricted |
Estonia | YES | |||||||
Hungary | NO | All LPS | O | X | O | O | O | Capacity restricted |
Latvia | YES | |||||||
Lithuania | ? | |||||||
Poland | All LPS | X | X | X | X | O | Coordinates restricted | |
Romania | ? | |||||||
Russia | ? | |||||||
Slovakia | All LPS | O | X | X | X | O | ||
Slovenia | YES |
Key X confidential
O unrestricted
? No reply received to questionnaire
ANNEX D
PROPOSED SOFTWARE CHANGES FOR AIR EMISSIONS 94
1 Proposed Changes
It is proposed that the following changes are made to the CORINAIR 90 software by the end of 1995.
1.1 Data model
Two new elements will be introduced:
1.2 Inventory Specifications
New pollutants (heavy metals, POPs and possibly others) will be included. SNAP 90 will be modified to include sources of the new pollutants and to ensure as good a compatibility with IPCC requirements as possible.
1.3 Software Facilities
Default emissions factors from the UNECE guidebook will be included in the revised software.
Some data handling and input facilities will be improved:
2. Benefits of the Proposed Approach
The main benefits of the proposed changes are:
This compatibility with the existing CORINAIR 90 structure will have other advantages. Firstly, countries which have already developed a procedure to transfer their national inventories into a CORINAIR 90 format, will not have to undertake major revisions to the procedure. Secondly, it will be possible to provide a starting point for the Air Emissions 94 inventory by prefilling the revised software with the CORINAIR 90 data.
3. Conclusions
The proposed changes take into account the main issues identified in this scoping study:
The revised version of the CORINAIR software will be distributed to national experts at the end of 1995.
For references, please go to https://eea.europa.eu./publications/92-9167-022-7/page011.html or scan the QR code.
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