Table1. Planned anthropogenic emissions of greenhouse gases, Gg
Year
|
2007
|
2008
|
2009
|
2010
|
2011
|
2012
|
Overall anthropogenic GHG emissions in the country, Gg CO2 eqv.
|
80 135,78
|
84 305,74
|
89 382,27
|
98 268,94
|
102 274,72
|
103 826,91
|
Overall GHG emissions from sectors, not covered by the Scheme, Gg CO2 eqv
|
24 815,00
|
26 501,00
|
27 424,00
|
28 523,00
|
29 181,00
|
29 778,00
|
Overall GHG emissions from sectors, covered by the Scheme, Gg CO2 eqv
|
55 320,78
|
57 804,74
|
61 958,27
|
69 745,94
|
73 093,72
|
74 048,91
|
Overall CO2 emissions from sectors covered by the Scheme, Gg CO2
|
50 743,95
|
53 020,62
|
56 814,08
|
63 927,82
|
66 935,58
|
67 834,47
|
Energy activities, including:
|
|
|
|
|
|
|
-electric power
|
22 326,04
|
22 415,13
|
24 028,10
|
27 580,62
|
30 252,25
|
29 086,36
|
-combined production of heat and electric power
|
9 123,85
|
9 210,26
|
9 299,67
|
9 494,08
|
7 884,58
|
8 002,88
|
-heating – public sector
|
905,77
|
953,17
|
1 000,57
|
1 047,97
|
1 095,37
|
1 142,77
|
-heating for industrial purposes and other CP, incl.:
|
|
|
|
|
|
|
Production of chemical products and rubber
|
432,05
|
452,96
|
473,37
|
493,35
|
512,98
|
532,31
|
Production of food and beverages
|
601,31
|
630,16
|
658,91
|
687,39
|
715,96
|
744,34
|
Production of wood material and wood articles (expect wood furniture)
|
208,52
|
225,68
|
242,84
|
260,00
|
277,15
|
294,31
|
Production of textile and textile articles (except for apparel)
|
188,31
|
201,05
|
213,80
|
226,55
|
239,30
|
252,04
|
Production and casting of non-ferrous metals
|
156,68
|
160,29
|
163,63
|
166,74
|
169,65
|
172,39
|
Production of machines, equipment and household appliances
|
105,21
|
108,86
|
112,28
|
115,51
|
118,56
|
121,46
|
Healthcare and social activities
|
353,20
|
371,68
|
390,17
|
408,65
|
427,13
|
445,62
|
Agriculture and hunting and related to them services
|
219,18
|
230,65
|
242,12
|
253,59
|
265,06
|
276,53
|
Distribution of natural gas
|
219,00
|
219,00
|
219,00
|
219,00
|
219,00
|
219,00
|
Refineries and oil products
|
2 389,74
|
2 533,13
|
2 685,11
|
2 846,22
|
3 017,00
|
3 198,01
|
Cement production
|
4 588,08
|
4 933,63
|
5 376,48
|
7 139,70
|
7 359,82
|
7 579,94
|
Lime production
|
1 596,71
|
1 692,56
|
1 779,31
|
1 866,07
|
1 952,82
|
2 039,57
|
Cellulose and paper production
|
530,72
|
582,32
|
663,69
|
706,58
|
748,70
|
788,49
|
Glass production
|
371,94
|
375,68
|
379,81
|
383,57
|
387,04
|
388,42
|
Ceramics production
|
199,20
|
202,96
|
206,90
|
210,12
|
213,12
|
215,95
|
Ferrous metallurgy
|
5 897,92
|
6 045,62
|
6 166,23
|
6 261,12
|
6 350,20
|
6 434,28
|
Unknown new entrants
|
0,00
|
1 000,00
|
2 000,00
|
3 000,00
|
4 000,00
|
5 000,00
|
Correction compulsory measures
|
330,53
|
475,82
|
512,08
|
560,99
|
729,91
|
899,81
|
Correction JI
|
|
3 200,87
|
3 200,87
|
3 200,87
|
3 200,87
|
3 200,87
|
1.2 Principles, assumptions and data applied to determine the contribution of installations covered by the Directive
1.2 What principles, assumptions and data have been applied to determine the contribution of the installations covered by the emissions trading Directive (total and sector historical emissions, total and sector forecast emissions, least-cost approach)? If forecast emissions were used, please describe the methodology and assumptions used to develop the forecasts.
| Determination of the total quantity of allowances to be allocated
Figures in row “Overall CO2 emissions from sectors covered by the Scheme” in Table 1 and the next rows represent basic information for determination of emission allowances. Those emissions are allocated to participant and not participating installations, and from them allowances are set aside for both a part of necessary calculative reserves and reserves of emission allowances for later allocation, and the allowances to be allocated under the current allocation plan. In accordance with the requirements of the EU, the NAP plans for equal effort, equal right and equal obligation to changes (increase or reduction) in emission levels for the two groups of emission sources (participants and not participants) and preservation of the correlation of their emissions.
In determining the emissions from sectors covered by the Scheme and installations participating and not participating in the Scheme, the proportion of emissions from installations covered by the Scheme for each sector to the total quantity of emissions from all installations in the respective sectors for the country in 2003 is determined. This proportion is defined as (share) of participants in the scheme for 2003 from total sector emissions. By multiplying emissions planned for the period 2007–2012 (Table 1) by the shares by sectors, the volume of emissions by sectors and total for the county are determined that could be covered by the Scheme from a macroeconomic viewpoint (Table 2). The table shows the two corrections – for early credits and compulsory measures – by which the quantity of allocated allowances is reduced.
Table 2. Quantity of emissions by sectors total for the country, which could be covered by the Scheme from a macroeconomic viewpoint, Gg
Year
|
2007
|
2008
|
2009
|
2010
|
2011
|
2012
|
Total emissions of GHG from sectors covered by the scheme, Gg CO2
|
50 743,95
|
53 020,62
|
56 814,08
|
63 927,82
|
66 935,58
|
67 834,47
|
Total CO2 emissions from installations participating in the scheme, Gg CO2
|
49 470,56
|
51 669,22
|
55 486,21
|
62 616,48
|
65 755,27
|
66 596,14
|
Energy activities, including:
|
|
|
|
|
|
|
-electric power
|
22 326,04
|
22 415,13
|
24 028,10
|
27 580,62
|
30 252,25
|
29 086,36
|
-combined production of heat and electric power
|
8 061,03
|
8 161,78
|
8 240,50
|
8 411,68
|
6 994,50
|
7 097,19
|
-thermal energy – public sector
|
828,19
|
871,53
|
914,87
|
958,21
|
1 001,55
|
1 044,89
|
-thermal energy for industrial purposes and other CP, incl.:
|
|
|
|
|
|
|
Production of chemical products and rubber
|
324,65
|
340,37
|
355,70
|
370,72
|
385,47
|
399,99
|
Production of food and beverages
|
39,74
|
41,79
|
43,87
|
45,80
|
47,90
|
49,91
|
Production of wood material and articles thereof (except for wooden furniture)
|
92,31
|
99,90
|
107,50
|
115,10
|
122,69
|
130,29
|
Production of textile and textile articles (except for apparel)
|
23,87
|
25,48
|
27,10
|
28,71
|
30,33
|
31,95
|
Production and casting of non-ferrous metals
|
129,87
|
132,86
|
135,63
|
138,20
|
140,62
|
142,89
|
Production of machines, equipment and household appliances
|
28,83
|
29,84
|
30,77
|
31,66
|
32,49
|
33,29
|
Healthcare and social activities
|
3,77
|
3,96
|
4,16
|
4,36
|
4,55
|
4,75
|
Agriculture, hunting and related services
|
7,18
|
7,56
|
7,94
|
8,31
|
8,69
|
9,06
|
Distribution of natural gas
|
182,49
|
182,49
|
182,49
|
182,49
|
182,49
|
182,49
|
Refineries and oil products
|
6 752,93
|
7 158,11
|
7 587,59
|
8 042,85
|
8 525,42
|
9 036,94
|
Cement production
|
4 236,39
|
4 559,84
|
4 980,58
|
6 721,71
|
6 919,72
|
7 117,74
|
Lime production
|
562,87
|
593,75
|
615,53
|
637,31
|
659,09
|
680,88
|
Production of cellulose and paper
|
375,46
|
412,98
|
480,26
|
509,05
|
537,08
|
562,77
|
Glass production
|
354,05
|
357,45
|
361,26
|
364,73
|
367,93
|
369,07
|
Ceramics production
|
154,33
|
157,21
|
160,34
|
162,80
|
165,11
|
167,27
|
Ferrous metallurgy
|
4 986,56
|
5 117,20
|
5 222,02
|
5 302,16
|
5 377,39
|
5 448,42
|
Unknown new entrants
|
0,00
|
1 000,00
|
2 000,00
|
3 000,00
|
4 000,00
|
5 000,00
|
Correction JI
|
|
3 200,87
|
3 200,87
|
3 200,87
|
3 200,87
|
3 200,87
|
Correction compulsory measures
|
330,53
|
475,82
|
512,08
|
560,99
|
729,91
|
899,81
|
In accordance with the requirements of the EU, the NAP plans for equal effort, which means equal right and equal obligation to changes (increase or reduction) in emission levels for the two groups of emission sources (participants and non participants) and preservation of the correlation of their emissions (Table 2, p.1.1.). After the determination of the various types of reserves for later allocation and the calculative reserves, a table is structured that contains the overall quantity of emission allowances by sectors and reserves for the country, which could be allocated within the Scheme from a macroeconomic viewpoint.
The overall volume of allowances to be allocated to registered participants is determined by recalculating the projected and corrected quantity of sectors emissions (Table 2) is re-calculated through setting aside out of the allowances of electric power sub-sector the quantity of emission reductions for cancellation of allowances for indirect double counting of emission reductions as a result of JI projects that were not accounted for in the macroeconomic forecast.
As a result of the "top-down” emission projections, after forming the respective reserves of emission units and their subtraction from , the overall amount of emissions which, from a macroeconomic viewpoint can be allocated between participants in the Scheme for the period 2007–2012 – (j=2007 - 2012) and the various types of reserves are determined. In Table 3, the preliminary allocation of those allowances among sectors is determined (from a macroeconomic viewpoint).
Table3. Volumes of allowance by sectors and total reserves for the country, which could be allocated in the Scheme from a macroeconomic viewpoint, Gg
№
|
Year
|
2007
|
2008
|
2009
|
2010
|
2011
|
2012
|
1
|
Total allowances for registered installations
|
49 470 560
|
50 161 260
|
52 583 634
|
58 304 621
|
60 343 473
|
59 864 886
|
2.1
|
Energy activities, including:
|
|
|
|
|
|
|
2.1.1
|
-electric power
|
22 326 044
|
21 907 164
|
23 125 522
|
26 268 762
|
28 840 447
|
27 355 107
|
2.1.2
|
-combined production of heat and electric power
|
8 061 028
|
8 161 776
|
8 240 503
|
8 411 681
|
6 994 499
|
7 097 189
|
2.1.3
|
-thermal energy – public sector
|
828 190
|
871 531
|
914 871
|
958 212
|
1 001 552
|
1 044 893
|
2.1.4
|
-thermal energy for industrial purposes and other CP, incl.:
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Production of chemical products and rubber
|
324 655
|
340 368
|
355 702
|
370 719
|
385 469
|
399 989
|
|
Production of food and beverages
|
39 739
|
41 792
|
43 872
|
45 801
|
47 903
|
49 909
|
|
Production of wood material and wood articles thereof (except for wooden furniture)
|
92 309
|
99 905
|
107 500
|
115 095
|
122 691
|
130 286
|
|
Production of textile and textile articles (except for apparel)
|
23 867
|
25 483
|
27 098
|
28 714
|
30 330
|
31 945
|
|
Production and casting of non-ferrous metals
|
129 870
|
132 863
|
135 629
|
138 204
|
140 617
|
142 888
|
|
Production of machines, equipment and household appliances
|
28 835
|
29 836
|
30 773
|
31 657
|
32 493
|
33 289
|
|
Healthcare and social activities
|
3 765
|
3 962
|
4 159
|
4 356
|
4 553
|
4 750
|
|
Agriculture, hunting and related services
|
7 185
|
7 561
|
7 937
|
8 313
|
8 689
|
9 065
|
|
Distribution of natural gas
|
182 488
|
182 488
|
182 488
|
182 488
|
182 488
|
182 488
|
3.
|
Refineries and oil products
|
6 752 931
|
7 158 107
|
7 587 593
|
8 042 849
|
8 525 420
|
9 036 945
|
4.
|
Cement production
|
4 236 386
|
4 559 839
|
4 980 585
|
6 721 709
|
6 919 724
|
7 117 740
|
5.
|
Lime production
|
562 869
|
593 746
|
615 529
|
637 312
|
659 094
|
680 877
|
6.
|
Cellulose and paper production
|
375 463
|
412 976
|
480 258
|
509 054
|
537 076
|
562 773
|
7.
|
Glass production
|
354 053
|
357 450
|
361 257
|
364 733
|
367 930
|
369 065
|
8.
|
Ceramics production
|
154 328
|
157 212
|
160 342
|
162 805
|
165 106
|
167 268
|
9.
|
Ferrous metallurgy
|
4 986 555
|
5 117 201
|
5 222 016
|
5 302 157
|
5 377 393
|
5 448 420
|
10.
|
Reserve of allowances for delayed installations
|
2 473 528
|
2 583 461
|
2 774 311
|
3 130 824
|
3 287 764
|
3 329 807
|
11.
|
Reserve of allowances for unknown new entrants
|
0
|
1 000 000
|
2 000 000
|
3 000 000
|
4 000 000
|
5 000 000
|
12.
|
Reserve of allowances for new cogeneration
|
73 957
|
178 057
|
334 975
|
481 172
|
573 420
|
932 252
|
13.
|
Calculative reserve for standardization of degrees/day
|
148 686
|
148 686
|
148 686
|
148 686
|
148 686
|
148 686
|
14.
|
Calculative reserve for compulsory measures
|
330 530
|
475 820
|
512 080
|
560 990
|
729 910
|
899 810
|
15.
|
Allowances set aside for cancellation of allowances for indirect double counting as a result of JI projects
|
0
|
3 022 740
|
3 654 029
|
4 321 929
|
4 494 430
|
4 881 861
|
If the draft Decision of the European Commission regarding avoidance of double counting of GHG emission reductions is approved, then, in compliance with the requirements laid down in the Decision, the respective quantity of allowances will be set aside for JI projects with a direct double counting effect.
In determining the total quantity of allowances for allocation to installations, Bulgaria applies a combination of two approaches – the “historical emissions level” approach and the “forecast” approach.
Historical emissions level – under this approach, the total number of allowances is determined as the share of emissions emitted to the ambient air from installations covered by the Scheme in the respective country. For Bulgaria, the historical emissions level approach is used to define the base year.
The determination of the quantity of allowances and their relation to the emissions of the sources outside the Scheme is based on the following sources of information:
-
National GHG Inventory for the year 2003;
-
Company data based on a questionnaire, filled in by the operators of the installations;
-
Data on sectors and installations from the National Statistical Institute;
-
Data from the EEA on issued integrated permits and submitted requests for issuing an integrated permit.
The National GHG Inventory for the year 2003 is an official document and the operators sign a Declaration on the accuracy of data. Those data is compared to data from the National Statistical Institute, the integrated permits and other available documents.
Data about installations is collected pursuant to the EPA (SJ 75/27.09.2005). The MOEW, in cooperation with the EEA, the RIEWs, other ministries and stakeholders, has compiled a list of potential participants on the basis of available information. Announcements have been published in the mass-media and at the MOEW web-page.
The questionnaire used to collect data about installations has been developed by the consultants and approved by members of the Working Group. Gathered information has been used by the consultants from the Energy Institute, PLC to calculate the CO2 emissions of installations covered by the Scheme based on data on fuel and raw materials consumption and production outputs.
Installations whose operators have provided sufficient and correct data in the questionnaire are included in a list of participants and receive allowances in the current plan. The total volume of emissions of registered installations for 2003 is calculated as a sum of the volumes of emissions from registered individual installations for 2003 (as provided in the questionnaire and corrected during the verification process).
,
where “i” is the serial number of the installation in the Scheme.
The volume of the reserve for not registered (delayed) installations is defined as 5% of emissions from registered installations:
Such a reserve is included for each year of the period 2007-2012, in order to allocate emission allowances to installations, which will register after 30 November 2005.
Apart from determining the overall volume of emissions of the installations in 2003, data from the registered installations is also used to determine the volumes of emissions by sectors, according to the classification of the International Panel on Climate Change in order to compare those volumes with the volumes received during the inventory of GHG emission for 2003.
Emissions from the following groups of sources have been determined:
-
Condensing TPP;
-
District Heating Cogeneration Plants;
-
District Heating Boilers
-
Auto-generation;
-
Refineries;
-
Ferrous metallurgy (fuels);
-
Production of cellulose and paper (fuels);
-
Other productions (fuels);
-
Production of ferrous metals (process emissions);
-
Cement production (process emissions);
-
Lime production (process emissions);
-
Glass production (process emissions);
-
Ceramics production (process emissions);
-
Cellulose and paper production (process emissions).
The emissions calculated in this manner by groups of sources, are compared with the emissions in the 2003 inventory (Table 4).
Table 4. Emissions of participating sectors and participating installations for 2003, kt CO2
Sector
|
All installations
|
Registered installations
|
Share
|
-electric power
|
19 986,32
|
19 986,32
|
1,000
|
-combined production of heat and electric power
|
9 048,00
|
7 966,831
|
0,881
|
-heating – public sector
|
736,00
|
672,96
|
0,914
|
-heating for industrial purposes and other CP, incl.:
|
2 022,11
|
699,39
|
0,346
|
Production of chemical products and rubber
|
328,32
|
246,71
|
0,751
|
Production of food and beverages
|
485,00
|
31,43
|
0,065
|
Production of wood material and wood articles thereof (except for wooden furniture)
|
152,60
|
67,55
|
0,443
|
Production of textile and textile articles (except for apparel)
|
138,80
|
17,59
|
0,127
|
Production and casting of non-ferrous metals
|
145,60
|
120,69
|
0,829
|
Production of machines, equipment and household appliances
|
87,69
|
24,03
|
0,274
|
Healthcare and social activities
|
287,00
|
3,06
|
0,011
|
Agriculture, hunting and related services
|
178,10
|
5,84
|
0,033
|
Distribution of natural gas
|
219,00
|
182,49
|
0,833
|
Refineries and oil products
|
1 892,90
|
5 348,952
|
2,826
|
Cement production
|
2 622,10
|
2 358,82
|
0,900
|
Lime production
|
1 033,44
|
259,48
|
0,251
|
Cellulose and paper production
|
279,20
|
180,32
|
0,646
|
Glass production
|
206,73
|
190,81
|
0,923
|
Ceramics production
|
173,01
|
132,48
|
0,766
|
Ferrous metallurgy
|
5 344,20
|
4 513,031
|
0,844
|
The discrepancies in the aggregated overall volumes of emissions by groups of sources compared to the 2003 inventory have been assessed and, where necessary and possible, the reasons for such discrepancies were eliminated. Examples of such reasons include:
-
Considerable number of not registered installations;
-
Unconformity of emission factors;
-
Incorrect data on production volumes;
-
Incorrect data on fuels volumes.
both in the inventory and in the installation data.
Therefore, some operators of installations were invited to correct submitted data.
As a result, the total volume of emissions from installations registered in the Scheme for 2003 () and the volume of the reserve for delayed installations () have been determined.
It is expected that the total volume of emissions covered by the Scheme for 2003 is equal to the sum of the volume of emissions from registered installations () and the reserve ().
“Forecast” approach, where the total volume of emissions of installations is determined on the basis of their share of projected development based on “business as usual”.
In applying the forecast approach, the “top-down” and “bottom-up” principles are applied. “Top-down” forecasts include official data on the expected GDP and GVA growth by sectors. Based on those data an assessment is carried out of the relation between the growth of the GVA and the change in the production volumes in the sectors, covered by the Scheme. Another important component of the forecasting approach is the projection of the fuel and energy balance of the country (final consumption of fuels and energy by sectors, least costs development of the energy sector, primary gross consumption of fuels and energy). The described forecasts are developed using the “business as usual” scenario.
Projections take into account important policies with impact on climate change, such as policies laid down in the Second National Plan on Climate Change 2005-2008, the Strategy on Energy of Bulgaria, the National Long-term Programme on Energy Efficiency until 2015, the National Long-term Programme on Promotion of Renewable Energy Sources 2005-2015 (in a process of development), approved and supported joint implementation projects. Applicable Directives 2003/96/ЕС, 96/61/ЕС, 2003/17/ЕС, 2002/91/ЕС, 2001/80/ЕС, 1999/13/ЕС, 2001/77/ЕС are taken into account, with the respective implementation timeframes and agreed transition periods.
The projection of the trends in emissions of carbon dioxide and other greenhouse gases has been taken into consideration in the process of developing the NAP, as shown in Figure 1 below:
Figure 1
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