Regulation on the allocation of greenhouse gas emission allowances in the 2005 to 2007 allotment period (allocation regulation 2007-ZuV 2007)

Unofficial table of contents

ZuV 2007

Date of completion: 31.08.2004

Full quote:

" Allocation Regulation 2007 of 31 August 2004 (BGBl. 2255), which is provided by Article 10 of the Law of 21 July 2011 (BGBl. I p. 1475).

Status:

Amended by Art. 10 G v. 21.7.2011 I 1475

For more details, please refer to the menu under Notes

Footnote

(+ + + Proof of text: 1. 9.2004 + + +) 

  

Unofficial table of contents

table of contents

Section 1
	General provisions
§ 1		Scope and purpose
§ 2		Definitions
§ 3		General requirements for allocation applications
Section 2
	General rules for the determination of carbon dioxide emissions
§ 4		Determination of emission factors
§ 5		Determination of energy-related carbon dioxide emissions
§ 6		Determination of process-related carbon dioxide emissions
§ 7		Calculation of emissions on the basis of a balance sheet of carbon content
§ 8		Determination of emissions on the basis of self-consumption
§ 9		Measurement of carbon dioxide emissions
Section 3
	Specific rules for the calculation of carbon dioxide emissions
§ 10		Allocation for existing installations on the basis of historical emissions
§ 11		Allocation for installations on the basis of declared emissions
§ 12		Allocation for additional new installations
§ 13		Early emission reductions
Section 4
	Common rules
§ 14		Requirements for verification of allocation applications
§ 15		Irregularities
§ 16		entry into force
Annexes 1 to 9

Unofficial table of contents

Input formula

Pursuant to § 7 (1) sentence 2, § 8 (1) sentence 5, § 11 (1) sentence 4 and subsection 2 sentence 4, § 12 paragraph 2 sentence 3 and section 4 sentence 3, § 13 paragraph 2 sentence 2 in connection with § 16 of the Allocation Act 2007 of 26 August 2004 (BGBl. 2211) and § 10 (5) (1) and (2) of the Greenhouse Gas Emissions Trading Act of 8 July 2004 (BGBl). I p. 1578), the Federal Government decrees:

Section 1
General provisions

Unofficial table of contents

§ 1 Scope and purpose

This Regulation shall apply within the scope of the greenhouse gas emissions trading act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163). It is used to determine the calculation of the allocation of allowances for the emission of greenhouse gases, which is used in the allocation process according to § 10 (1) of the greenhouse gas emission trading law of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), the information to be requested and the nature of the evidence to be provided and the review thereof. Unofficial table of contents

§ 2 Definitions

For the purposes of this Regulation:

1.

Capacity: the installed output per year related to the normal operation; if the requirements of the approval of the installation result in a lower maximum production output, it shall be relevant;

2.

Utilization: the quotient of the average actual production output and the capacity of a plant;

3.

Commissioning: the first-time recording of the control operation; the regular operation begins at the point in time at which the installation, in accordance with the end of the commissioning after the completion of a trial operation, for the first time the function assigned to it under the control of the control system, begins at the time The special regulations in § 10 (1) sentence 1 and § 11 (1) sentence 1 of the Allocation Act 2007 shall remain unaffected;

4.

Test operation: the temporary operation of an installation for the purpose of checking its operational capacity;

5.

Activity rate: the amount of substance used per calendar year leading to the emission of carbon dioxide;

6.

lower calorific value: the quantity of heat which is produced when a defined quantity of fuel is completely incinerated, provided that the water content of the fuel and of the water produced during combustion is in the gaseous state, the Heat recovery due to the condensation of the steam in the exhaust gas is not included;

7.

Emission factor: The quotient of the amount of unbiogenic carbon dioxide released during the handling of a substance and the amount of this substance used. In this case, the emission factor of a fuel refers to the lower calorific value of the fuel. For the purpose of the carbon balance, the emission factor also corresponds to the integration factor;

8.

biogenic carbon dioxide emissions: emissions from the oxidation of non-fossil and biodegradable organic carbon to carbon dioxide;

9.

Conversion factor: Coefficient, which indicates the degree of conversion of the carbon contained in the fuels or raw materials to carbon dioxide. If the conversion is complete, the conversion factor is 1. In combustion processes, the conversion factor corresponds to the oxidation factor; in non-combustion processes, the conversion factor corresponds to the conversion factor;

10.

Gight gas: the gas mixture emerging from the blast furnace at the gout (upper end of the blast furnace) during the production of pig iron from approx. 23 volume percent carbon dioxide, approx. 23 Volume-percent carbon monoxide, approx. 49.5 volume percent nitrogen and approx. 4.5 volume percent hydrogen;

11.

Converter gas: the gas mixture emerging from the converter in the case of crude steel production after the oxygen blowing process from approx. 15 volume percent carbon dioxide, approx. 65 volume-percent carbon monoxide, approx. 18 volume-percent nitrogen and approx. 2 volume percent hydrogen;

12.

Coupling gas: combustible process gas which is formed as a by-product in the production of basic materials, for example B. Gight gas and converter gas.

Unofficial table of contents

§ 3 General requirements for allocation applications

(1) Insofar as the provisions of Sections 2 and 3 do not contain any deviating regulations, those for the allocation of emission allowances in the allocation request according to § 10 paragraph 1 of the greenhouse gas emission trading act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), the data and information to be supplied, where available, in accordance with Commission Decision 2004 /156/EC of 29 January 2004 laying down guidelines for monitoring and reporting on Greenhouse gas emissions in accordance with Directive 2003 /87/EC of the European Parliament and of the Council (OJ L 378, 27. EU No L 59 p. 1; No L 177 p. 4). To the extent that the requirements of the guidelines referred to in the first sentence cannot be complied with, the data and information must be collected and reported with the highest attainable degree of accuracy and completeness in the individual case. (2) The Applicants are obliged to do so pursuant to Section 7 (8), § 8 (2), § 10 (5), § 11 (4), § 12 (6) and § 14 (3) of the Allocation Act 2007 as well as pursuant to § 5 sec. 2, § 6 (9), § 7 (3), § 9 (4), § 10 (7), § 11 (7), § 12 (6) or § 13 , paragraph 7 of this Regulation requires the information required in the allocation applications. In so far as these data require the prior implementation of calculations, in addition to the required information, the calculation method used must be explained in each case and the derivation of the data is to be presented in a comprehensible manner. At the request of the competent authority, the operator is obliged to show the individual evidence on which the information is based up to the end of the next allocation period following the decision to grant the allocation.

Section 2
General rules for the determination of carbon dioxide emissions

Unofficial table of contents

§ 4 Determination of the emission factors

(1) The indication of emission factors shall be based on the specific properties of the substances used. In this case, the levels of precision must be selected in accordance with the level concept of Decision 2004 /156/EC. In so far as the requirements of these guidelines cannot be complied with for technical reasons or where the necessary additional expenditure is economically unjustifiable, generally accepted default values for the emission factors of the substances , which are used in accordance with Section 20 (1) sentence 2 of the Greenhouse Gas Emissions Trading Act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), the competent authority has been published. If there are no generally accepted standard values for the substances used, a derivation of the specific emission factors with the highest degree of accuracy and determination in the individual case is required. (2) The emission factors For energy-related emissions, the quotient of the carbon content and the lower calorific value of the fuel as well as the subsequent conversion into carbon dioxide are calculated by multiplying the quotient of 44 and 12 by the quotient. The carbon content and the lower calorific value are to be determined in accordance with the generally accepted rules of technology. (3) Calculation of the carbon content from the lower calorific value of the fuels via statistical methods is in principle not allowed. Exceptionally, where the fuel is full-value hard coal, no information is available on the carbon content of the fuel and the mixture of the fuel batches is not known because of specific local circumstances, a statistical method may exceptionally be used. according to the formula in Annex 1 to this Regulation, if the methodology consistency between the determination of the emission factors for the allocation application and for reporting in accordance with § 5 of the Greenhouse Gas Emissions Trading Act of 8 May 2016. July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), it has been amended. Sentence 2 shall not apply to anthracite. (4) The emission factors for process-related emissions shall be determined from the stoichiometric analysis of the corresponding chemical reactions and the subsequent emissions, subject to the regulations in § 6 (2) to (8). Conversion of carbon dioxide into carbon dioxide by multiplying the carbon dioxide by the quotient of 44 and 12. Unofficial table of contents

Section 5 Determination of energy-related carbon dioxide emissions

(1) The energy-related carbon dioxide emissions of one plant per year are the computational product from the activity rate of the fuel, the lower calorific value, the heating-value-related emission factor and the oxidation factor of the fuel. Where more than one fuel is used in the plant, the annual energy-related carbon dioxide emissions per fuel shall be determined and added. (2) For the determination of the energy-related carbon dioxide emissions, the fuel must be determined by the Application for a grant shall contain the information on:

1.

the activity rates of fuels,

2.

the heating-value-related emission factors of fuels,

3.

the oxidation factors of fuels and

4.

the lower heating values of the fuels.

Unofficial table of contents

§ 6 Determination of process-related carbon dioxide emissions

(1) For the calculation of process-related emissions, all releases of carbon dioxide should be included in the atmosphere in which the carbon dioxide is produced as a direct product of a chemical reaction which is not combustion, or in the direct technological interconnection, indirectly and inevitably, resulting from this chemical reaction. The determination of process-related carbon dioxide emissions is generally carried out via the raw material used for the emission of carbon dioxide. The process-related carbon dioxide emissions are the computational product from the activity rate of the raw material per year, the emission factor and the conversion factor of the raw material. If more than one emission-relevant raw material is used in the plant, the annual process-related carbon dioxide emissions per raw material must be determined and added together. The specific provisions of paragraphs 2 to 8 shall remain unaffected. (2) By way of derogation from paragraph 1, the determination of process-related carbon dioxide emissions from the production of cement clinker, quicklime and dolomite may take place on the product discharge. In this case, the process-related emissions are the computational product from the activity rate of the emission-relevant product per year and the product-related emission factor. The product-related emission factors
0.53 tonnes of process-related carbon dioxide per tonne of cement clinker,
0.7848 tonnes of process-related carbon dioxide per tonne of burnt lime, or
0,9132 tonnes of process-related carbon dioxide per tonne of dolomite
in approach. If several of the products listed in the third sentence are produced in the plant, the annual process-related carbon dioxide emissions of these products shall be determined and added in detail. (3) For the blast furnace process, the whole of the total process-related carbon dioxide emissions per year on the use of raw materials and pig iron production in accordance with the formula 1 of Annex 2 to this Regulation. If the coupling gas is discharged from the blast furnace process to third parties, the amount of process-related carbon dioxide emissions attributable to the blast furnace shall be calculated from the total quantity of process-related carbon dioxide emissions in accordance with the ratio of the a total of the resulting gas and gas emissions from third parties; the process-related carbon dioxide emissions attributable to the blast furnace process are determined in accordance with the formula 2 of Annex 2 to this Regulation. If no coupling gas is released from the blast furnace process to third-party systems, the total amount of process-related carbon dioxide emissions is attributed to the blast furnace. (4) The entire process of steel production in the oxygenated steel plant will be used for the entire process. carbon dioxide emissions per year over the use of raw materials, as well as a carbon balance for the input and discharge of carbon via pig iron, scrap, steel and other substances according to the formula 1 of Annex 3 to this Regulation. If the dome gas is delivered to third party systems from the oxygenated steel plant, the amount of process-related carbon dioxide emissions from the total amount of process-related carbon dioxide emissions attributable to the Oxygen steelworks will be determined in accordance with the The ratio of the total converter gas and the converter gas levy to third party installations is determined; the process-related carbon dioxide emissions attributable to the oxygensteal plant are determined in accordance with the formula 2 of Annex 3 to this Regulation. If no coupling gas is emitted from the oxygenated steel plant to third parties, the total quantity of process-related carbon dioxide emissions is attributed to the oxygenated steelworks. (5) The operators of the blast furnaces and steelworks that emit dome gases to third parties, shall be obliged to make the process-related carbon dioxide emissions attributable to third parties as the difference between the total quantity of the process-related carbon dioxide emissions referred to in the first sentence of paragraph 3 or the first sentence of paragraph 4 and the corresponding paragraph 3 sentence 2 or 4 sentence 2 of the blast furnace and of the oxygenated steel plant in accordance with the formula in Annex 4 to this Regulation, the third party operators shall determine the result of the calculation in accordance with the formula set out in Annex 4 to this Regulation for the application of the application to the , and to inform the competent authority of the installations of third party coupling gas supplies and of the quantity of carbon dioxide emitted by the process according to this formula to be attributed to the installations concerned. (6) For the Regeneration of catalysts for crack and reform processes in Oil refineries are determined by the process-related carbon dioxide emissions per year:

1.

measurement of the carbon content of the catalyst before and after the regeneration process and the stoichiometric calculation of carbon dioxide emissions in accordance with Formula 1 of Annex 5 to this Regulation,

2.

the calculation of the carbon content of the catalyst before and after the regeneration process and the stoichiometric calculation of the carbon dioxide emissions in accordance with Formula 2 of Annex 5 to this Regulation, or

3.

Determination of carbon dioxide emissions by measuring the concentration in the exhaust gas stream and determining the total quantity of the exhaust gas stream according to the formula 3 of Annex 5 to this Regulation. Alternatively, the amount of dry exhaust gas can also be calculated from the supplied air quantity. In this case, the proportion of inert gases in the supplied air is constant 79.07 volume percent. The calculation of the amount of dry exhaust gas shall be determined in accordance with the formula 4 of Annex 5 to this Regulation.

(7) The calculation of the process-related carbon dioxide emissions per year arising from the calcination of petroleum coke is carried out by means of a complete carbon balance of the calcination process according to the formula in Annex 6 to this Regulation. (8) In the production of hydrogen from hydrocarbons, the process-related carbon dioxide emissions are determined annually by:

1.

the determination of the carbon content of the hydrocarbons used in accordance with Formula 1 of Annex 7 to this Regulation, or

2.

Determination of the amount of hydrogen production and the ratio of carbon to hydrogen in the hydrocarbons used and the water used in accordance with formula 2 of Annex 7 to this Regulation.

The method should be used in which the data on the starting materials can be determined for the calculation with a higher degree of accuracy. (9) For the determination of the process-related carbon dioxide emissions, the dispatch request must be based on the following: the information required in the preceding paragraphs shall contain:

1.

the activity rates of the raw materials or products,

2.

the emission factors of raw materials or products,

3.

the conversion factors of raw materials or products; and

4.

the individual factors of the relevant calculation formulae in Annexes 2 to 7 to this Regulation.

Unofficial table of contents

§ 7 Calculation of emissions on the basis of a balance sheet of carbon content

(1) By way of derogation from the provisions of § § 5 and 6, the determination of total carbon dioxide emissions on the basis of a balancing of the carbon content of the emission-relevant combustion and raw material use as well as of the fuel and raw materials can be determined. derived carbon in the products of the plant. Products also include by-products and waste. The annual average emissions are derived from the difference between the total carbon content of the annual use of fuel and raw materials and the raw materials used from the fuels and emission-relevant raw materials used. Carbon in the products of a plant as well as the subsequent conversion of the carbon transferred into carbon dioxide with the quotient of 44 and 12. (2) Operators of plants have process-related emissions in parallel according to the requirements of § 6 , if an assignment is requested in accordance with § 13 of the 2007 Allocation Act (Allocation Act) (3) In order to determine the carbon dioxide emissions referred to in paragraph 1, the dispatch request shall contain information on:

1.

the annual activity rates of fuel and raw materials and products,

2.

the carbon contents of the raw materials and the products and

3.

in the case of paragraph 2, in addition, the process-related emissions determined in accordance with § 6.

Unofficial table of contents

§ 8 Determination of emissions on the basis of self-consumption

The emissions of a uniform plant within the meaning of § 25 of the Greenhouse Gas Emissions Trading Act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), can be jointly identified in the context of the allocation request. For uniform installations for the processing of crude oil and petroleum products in mineral oil or lubricant refineries, the determination of the emissions according to § § 5 and 6 may be based on the activity rates of the mineral oil tax collection the non-tax-free mineral oil used by the owners of mineral oil production companies in accordance with Article 4 (1) (1) of the Mineral Oil Tax Act for the maintenance of the holding and approved by the competent principal customs office. This shall apply only to emissions recorded by the self-consumption recognised by the customs tax authorities. Unofficial table of contents

§ 9 Measurement of carbon dioxide emissions

(1) By way of derogation from the provisions of § § 5 to 7, carbon dioxide emissions can be determined directly by measurement if it is shown that this measurement results in a more accurate result than the emission determination via activity rates, lower calorific values as well as emission and conversion factors or a balance sheet of carbon content. The measurement shall also be permitted insofar as the determination of carbon dioxide emissions in accordance with the procedures of § § 5 to 7 cannot be carried out for technical reasons or would result in a disproportionate additional effort if it is ensured that the Measurement will result in a sufficiently accurate result. In doing so, the directly determined emissions must immediately be included in the scope of the greenhouse gas emission trading law of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. I p. 1163), which may be assigned to a falling installation. The operator must confirm the measurements on the basis of flanking emission calculations. (2) With regard to the measurement procedure to be used for the direct determination of emissions, § 3 applies accordingly. (3) Operators of plants have process-related To identify and specify emissions in accordance with § 6 in parallel, provided that a special allocation is requested in accordance with § 13 of the Allocation Act 2007. (4) For the emission determination referred to in paragraph 1, the allocation request shall be that referred to in paragraph 1. information required

1.

the reasons for the better suitability of the measurement in relation to the procedures of § § 5 to 7,

2.

the method and the adequate accuracy of the measurement procedure;

3.

the measure of the total directly determined annual carbon dioxide emissions in tonnes,

4.

in the case of paragraph 3, additionally the process-related emissions determined in accordance with § 6, and

5.

in the case referred to in the second sentence of paragraph 1, the technical impossibility or the unreasonable additional expenditure of a provision in accordance with § § 5 to 7.

Section 3
Specific rules for the calculation of carbon dioxide emissions

Unofficial table of contents

§ 10 Allocation for existing installations on the basis of historical emissions

(1) The carbon dioxide emissions of one plant per year shall be calculated in accordance with the provisions of Section 2 on the basis of the respective base period in accordance with § 7 of the Allocation Act 2007. The average annual carbon dioxide emissions are calculated from the calculation of the carbon dioxide emissions of one plant per year in the years to be taken in the approach to be taken. (2) To determine the carbon dioxide emissions of a Installation in the base period relevant for the allocation according to § 7 (4) and (5) of the Allocation Act 2007 shall be for installations which have been put into operation in the period from 1 January 2001 to 31 December 2002 or whose capacity in the said period is The last time period has been extended or reduced, the carbon dioxide emissions of the The calendar year of putting into service to a full operating year. Plant and sector-specific influencing factors must be taken into account. For installations which have been put into service between 1 January 2001 and 31 December 2001, the calculation shall be made for the 2001 operating year. For installations which have been put into service between 1 January 2002 and 31 December 2002, the calculation shall be made for the operating year 2002. (3) The emissions of the emissions referred to in paragraph 2 shall be made by the applicant. and are part of the allocation request in accordance with Section 7 (8) of the German Dispatch Act 2007. For the calculation, the daily average emissions of the plant are extrapolated to a full year of operation in the year of commissioning. The calculation is carried out in accordance with the formula 1 of Annex 8 to this Regulation. (4) Insofar as the operation of an installation is subject to specific plant or industry-related factors, those factors shall be used in the calculation of the emissions referred to in paragraph 2. consideration. This applies in particular to weather-dependent plant operation and seasonal production fluctuations. The consideration of the influencing factors shall be shown in the calculation of emissions in the dispatch application. The calculation for the weather-dependent plant operation is carried out in accordance with the formula 2 of Annex 8 to this Regulation, the calculation of the seasonal production fluctuations according to Formula 3 or Formula 4 of Annex 8 to this Regulation. (5) By way of derogation from the provisions of paragraphs 3 and 4 may apply to applicants other calculation methods for the high-calculation of the emissions referred to in paragraph 2, provided that the procedures for calculating the emissions of the installations referred to in paragraphs 3 and 4 are are not suitable. The reasons for the application of a system-specific calculation method and the calculation procedure for the method used are to be stated in the context of the allocation request. (6) For allocation applications pursuant to § 7 (12) of the 2007 Allocation Act (Allocation Act) § 12 para. 2 to 6 shall apply accordingly. The forecast in accordance with § 12 (5) must be carried out taking into account the historical data of the installation from the base period. In the event of deviations from these historical data, the forecast data must be duly substantiated in sufficient detail and substantiated by meaningful documents. (7) For the allocation of allowances in accordance with § 7 of the Allocation Act 2007, the Application for a grant supplementary to the information provided in Section 2 shall contain information on:

1.

the capacity of the installation,

2.

the date of entry into service,

3.

in the case of Section 7 (6) of the Allocation Act 2007, the date of re-entry after the last reduction or extension of the capacity of the installation and

4.

in the case of Article 7 (4) or (5) of the Act on Dispatch in 2007, the information required under paragraphs 2 to 5.

Unofficial table of contents

§ 11 Allocation for installations on the basis of declared emissions

(1) The average annual carbon dioxide emissions of an installation to be reported in accordance with Article 8 (1) of the Allocation Act 2007 shall be determined in accordance with the provisions of Section 2. The annual activity rates to be expected shall be determined by the following: are used as a basis for the production of fuel, raw materials or the products relevant to the emissions of carbon dioxide, as well as the respective emission factors and conversion factors. The annual activity rates to be taken result from the average annual volume of production to be expected. (2) The operator shall specify an emission value per product unit produced, the ratio of the total annual activity rate to be expressed in the annual activity rate. for the whole mass or volume-related production volume. The emission value per unit of product produced shall be determined by the quotient of the average annual carbon dioxide emissions and the expected average annual production volume of the plant. (3) In the manufacture of several Products in an installation are to form several emission values, provided that a sufficiently precise allocation of the carbon dioxide emissions to the produced product units is possible. Several products produced in one plant can be grouped into product groups, provided that the emission values of the individual products within a product group do not differ by more than 10 percent from each other. In this case, the emission value for the product groups is weighted according to the respective share of the products in the product group. The respective ratio of the product units produced or of the product groups formed to the total mass-and volume-related quantity of production shall be indicated. (4) Where different products are produced in an installation, the formation of a product shall be: If the emission value per product unit produced in accordance with paragraphs 2 and 3 is not possible, the average annual emissions may be related to a different reference quantity. In this context, it is a prerequisite that the reference quantity is in a fixed relationship to the production quantity and thus changes in the quantity of production due to lower or higher capacity utilization of the plant and the resulting changes in the production volume. average annual emissions of carbon dioxide are reproduced sufficiently accurately. The quantity of the intended combustion or raw materials is, in particular, considered as the reference value. The ratio of the reference quantity to the total mass or volume-related quantity of production shall be indicated. The absence of a possibility to form an emission value per product unit produced shall be justified in sufficient detail. (5) The calculation in accordance with the preceding paragraphs shall be carried out on the basis of a forecast to be issued by the operator for the information required. For this purpose, the operator shall use all the information and documents available at the time of the application. In the cases of Section 8 (5) of the Allocation Act 2007, the forecast of the required information shall be made taking into account the historical data of the plant. Where historical data are not available or where derogations are to be made in the case of certain information, the information which is typical of the industry and of the application is to be used. The forecast data must be duly substantiated in sufficient detail and be substantiated by meaningful documents. (6) In the case of allocation requests pursuant to § 8 (6) of the Act of Dispatch in 2007, Section 12 (2) to (6) shall apply. (7) In accordance with Section 8 (1) of the Allocation Act 2007, the allocation application must contain additional information on the corresponding forecast provided in Section 2.

1.

the expected capacity and the expected utilization of the plant;

2.

the expected average annual production volume, and the quantity and nature of the product units produced,

3.

the ratio of the product units, product groups or units of material to the total production volume of the plant;

4.

the date of entry into service,

5.

in the case referred to in paragraphs 2 and 3, the emission value per product unit produced; and

6.

in the case referred to in paragraph 4, the average annual carbon dioxide emissions of the plant.

Unofficial table of contents

§ 12 Allocation for additional new installations

(1) The average annual carbon dioxide emissions of an installation to be determined in accordance with Article 11 (4) (5) of the Allocation Act 2007 are the calculated product from the expected average annual production volume and the average annual amount of carbon dioxide. Emission value per product unit produced. The annual activity rates to be taken into account are derived from the average annual production volume of the plant, which is expected to be based on the capacity and capacity utilization of the plant. The emission value per product unit produced shall be the sum of the energy-related emission value per product unit produced and the process-related emission value per product unit produced. The emission value shall be determined in accordance with the provisions of paragraphs 2 to 4. (2) The energy-related emission value of each product unit produced shall be:

1.

in the case of electricity generating installations, not more than 750 grams of carbon dioxide per kilowatt hour of net electricity production, but not more than the emission value of the installation which is achievable when using the best available techniques, but at least an emission value of 365 Gram of carbon dioxide per kilowatt-hour of net electricity production; if the emission value in approach exceeds 365 grams of carbon dioxide per kilowatt hour of net electricity production, the plant operator shall justify the fact that it shall be based on the Best available power plant techniques and fuel (3), (3) to (5) shall apply accordingly;

2.

in the case of installations for the production of hot water (low-temperature heat), a maximum of 290 grams of carbon dioxide per kilowatt-hour, but no more than the emission value of the plant, which can be achieved when the best available techniques are used, but at least one emission value Emission value of 215 grams of carbon dioxide per kilowatt-hour; if the emission value in approach exceeds 215 grams of carbon dioxide per kilowatt-hour, the plant operator shall justify the fact that it shall be based on the best available techniques; paragraph 3, sentences 3 to 5 shall apply accordingly;

3.

in the case of installations for the production of process steam, a maximum of 345 grams of carbon dioxide per kilowatt hour, but no more than the emission value of the installation which is achievable when using the best available techniques, but at least an emission value of 225 grams Carbon dioxide per kilowatt-hour; if the emission value in approach exceeds 225 grams of carbon dioxide per kilowatt-hour, the plant operator shall justify the fact that it is derived from the best available techniques; paragraph 3 Sentence 3 to 5 shall apply accordingly;

4.

in the case of combined heat and power plants, in respect of the electricity production of the emission value per unit of product produced, electricity in kilowatt-hours of net electricity production which, in the case of a technically comparable plant for the exclusive production of electricity, shall be produced in accordance with In the case of heat production, the emission value per unit of product produced shall be subject to heat in kilowatt-hours, which shall be the exclusive product of a technically comparable plant. Production of hot water as referred to in point 2 or process steam as specified in point 3; is laid down;

5.

in the case of installations for the production of cement or cement clinker in production plants with

a)

three cyclones 315 grams of carbon dioxide per kilogram of cement clinker produced,

b)

four cyclones 285 grams of carbon dioxide per kilogram of cement clinker and

c)

five or six cyclones 275 grams of carbon dioxide per kilogram of cement clinker produced;

6.

for installations for the manufacture of glass

a)

for container glass, 280 grams of carbon dioxide per kilogram of glass produced and

b)

For flat glass, 510 grams of carbon dioxide per kilogram of glass produced;

7.

in the case of installations for the production of bricks

a)

for pre-brick tiles, 115 grams of carbon dioxide per kilogram of bricks produced,

b)

for back bricks, 68 grams of carbon dioxide per kilogram of bricks produced,

c)

for roof tiles (U cassette) 130 grams of carbon dioxide per kilogram of bricks produced and

d)

for roof tiles (H cassette) 158 grams of carbon dioxide per kilogram of bricks produced.

The emission value for process-related carbon dioxide emissions shall be determined for the products referred to in the first sentence in accordance with § 6. (3) For a plant producing products other than those referred to in paragraph 2, the operator shall give an emission value. per product unit produced. The emission value for carbon dioxide to be used is the value which can be reached on the basis of the best available techniques. The best available techniques are the production processes and modes of operation which, while ensuring a high level of protection for the environment as a whole, are the emission of climate-effective gases, in particular carbon dioxide, in the production of a reduce certain products to a level which is possible, taking into account the cost/benefit ratio, the economical use of fuels and raw materials, and the accessibility of the techniques to the operator. The operator shall state that the carbon dioxide emission value in approach is the value that can be achieved by using the best available techniques. The explanatory statement shall contain sufficiently detailed information on:

1.

the best available production methods and techniques,

2.

the possibilities of improving efficiency and

3.

the sources of information according to which the best available techniques have been identified.

(4) The emission value per product unit produced shall be determined by the quotient of the average annual carbon dioxide emissions and the expected average annual production volume of the plant. If the resulting emission value includes energy-related and process-related carbon dioxide emissions per product unit produced, then their shares shall be shown separately. If several products are to be manufactured in one plant, § 11 (3) and (4) shall apply accordingly. The expected average annual production volume, which is to be taken into account, is derived from the capacity and capacity utilization of the plant. The ratio of the product unit produced to the total mass or volume production volume shall be indicated. (5) The calculation in accordance with the preceding paragraphs shall be carried out on the basis of a forecast issued by the operator for the production of the product unit. information required. To this end, the operator must use all the information and documents available at the time of the submission of the application. In particular, the forecast is to be made primarily in the case of capacity extensions according to § 11 (6) of the Allocation Act 2007, taking into account the historical data of the plant. If historical data are not available or if deviations from certain parameters are to be presented, then the information which is typical of the industry or of an application is to be used. The forecast data must be duly substantiated in sufficient detail and substantiated by meaningful documents. (6) For the allocation of allowances in accordance with Section 11 (1) of the Allocation Act 2007, the allocation request must be supplemented with the following information: in accordance with the forecast provided for in Section 2, information on:

1.

the expected capacity and the expected utilization of the plant;

2.

the average annual carbon dioxide emissions of the plant,

3.

the expected average annual production volume, and the quantity and nature of the product units produced,

4.

the date of entry into service or planned commissioning,

5.

in the cases referred to in paragraph 2 (1) to (4) and in paragraph 3, an explanatory statement in accordance with the fourth sentence of paragraph 3,

6.

in the cases referred to in paragraph 2 (1) to (4) and in paragraph 3, the fuel and raw materials relevant to the emission of carbon dioxide, and

7.

in the cases referred to in paragraph 4, the ratio of the product units, product groups or units of substance to the total production volume of the plant.

Unofficial table of contents

Section 13 Early emission reductions

(1) For the calculation of early emission reductions, the energy-related annual emissions of carbon dioxide from an installation shall be based on the provisions of Section 2, on the basis of the relevant information for the years to be taken into account of the reference period and of the base period. The average annual energy-related emissions of carbon dioxide from the computational means of the energy-related carbon dioxide emissions of the plant per year shall be expressed in the years of the reference period, respectively, which are to be applied in accordance with the approach, or (2) The operator shall indicate the average annual energy-related carbon dioxide emissions of the installation per product unit produced in the reference period and in the base period. This information shall be determined by the quotient of the average annual energy-related carbon dioxide emissions and the annual average annual production volumes of the plant. The respective production quantities are derived from the capacity and utilization of the plant in the years to be carried out in each case. The ratio of the product units produced to the total mass or volume-related amounts of production shall be indicated. (3) Several products manufactured in one plant may be grouped into product groups, provided that: a sufficiently precise allocation of the average annual energy-related carbon dioxide emissions to the product units produced is possible and the average annual energy-related carbon dioxide emissions of the individual products No more than 10 percent differ from each other. The average annual energy-related carbon dioxide emissions for the product group shall be determined according to the respective share of the products in the product group. The respective ratio of the product units produced or the product groups formed to the total mass or volume-related production quantities shall be indicated. (4) The average annual energy-related carbon dioxide emissions may be: to a different reference quantity, provided that it is not possible to assign to the product units produced in accordance with the first sentence of paragraph 3. In this context, it is a prerequisite that the reference quantity is in a fixed relationship to the production quantity and thus changes in the quantity of production due to lower or higher capacity utilization of the plant and the resulting changes in the production volume. average annual emissions of carbon dioxide are reproduced sufficiently accurately. The quantity of the intended combustion or raw materials is, as a matter of priority, considered as the reference value. The ratio of the reference quantity to the total mass or volume-related production volumes shall be indicated. (5) The emission reduction shall be the difference between the average annual energy-related carbon dioxide emissions of the plant. the product unit produced in the reference period and the average annual energy-related carbon dioxide emissions of the installation per product unit produced in the base period. In this case, the selected reference variable must be identical in the reference period and in the base period. (6) The generated heat quantity in megajoules shall be considered to be the product unit produced for combined heat and power plants. The electricity and heat production of the combined heat and power plant will be given as heat equivalent. To the extent that an installation exclusively produced electricity before the modernization, the product unit generated is electricity in kilowatt hours. In this case, the power and heat production of the combined heat and power plant will be indicated as the current equivalent. The relative reduction of the determined carbon dioxide emissions per product unit produced for combined heat and power plants is determined in accordance with Formula 1 or 2 of Annex 9 to this Regulation. (7) For the allocation of allowances in accordance with § 12 para. 4 of the 2007 Allocation Act must include the dispatch application in addition to the information provided in Section 2

1.

on the calculation of the average annual emissions of carbon dioxide, the average annual production volumes and the labour-related loss of electricity losses of the combined heat and power plant in the base period and in the plant before the Modernisation in the reference period and

2.

for the calculation of the emission reduction, the factors of the calculation formulae in Annex 9 to this Regulation.

Section 4
Common rules

Unofficial table of contents

§ 14 Requirements for the verification of allocation applications

(1) As part of the verification of the dispatch requests, the expert has pursuant to § 10 paragraph 1 sentence 3 of the greenhouse gas emission trading law of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), it has been amended to check the factual information in the allocation request for the accuracy of the information. Insofar as this is justifiable in particular with regard to the number of authorizations requested and corresponds to a regular task performance, the expert may check the submitted evidence in a random manner. (2) From verification Except for assessments with a significant margin of assessment, the expert shall check only the facts-related information referred to by the operator in his or her derivation. In the cases of Section 12 (2) Nos. 1 to 4 and Section 12 (3), the expert has to confirm that, according to his assessment of the emission value for carbon dioxide shown in the allocation request, the value is the value of the best value on the basis of the allocation of the best value for the carbon dioxide. available techniques. (3) For the verification of correctness, the expert has the information provided in the application or its derivation with the evidence to be submitted by the operator, as well as the approval pursuant to § 4 of the Federal Immission Protection Act or § 4 of the Greenhouse Gas Emissions Trading Act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. I p. 1163). In addition to examining the facts-related information, the expert has to examine the application as a whole and the evidence submitted to him, in each case, on their internal consistency and credibility. (4) The expert has significant Perform audit activities yourself. In so far as he delegates ancillary activities, he shall indicate this in his audit report. (5) In so far as a review is not possible or only conditionally possible for the expert, he shall state in his audit report the extent to which proof has been conducted and to the extent to which it is to be carried out. (6) The expert has to declare in his audit report that the verification of the application is based on the independence of its activities in accordance with the requirements of the the relevant provisions of its authorisation as environmental verifier or its Appointment as an expert in accordance with § 36 of the Commercial Code and he did not participate in the preparation of the application. For others according to § 10 paragraph 1 of the Greenhouse Gas Emissions Trading Act of 8 July 2004 (BGBl. I p. 1578), most recently by Article 9 of the Law of 11 August 2010 (BGBl. 1163), the provisions of the first sentence of paragraph 1 shall apply mutaly to the provisions of the first sentence. Unofficial table of contents

§ 15 (omitted)

- Unofficial table of contents

Section 16 Entry into force

This Regulation shall enter into force on the day after the date of delivery. Unofficial table of contents

Annex 1 (to section 4 (3))
Determination of the specific carbon dioxide emission factor for full-value hard coal over the lower calorific value

Site of the (original text: BGBl. I 2004, 2264)

Formula 
 0,054829 + H (deep) u x 0,023736 44 
EF = ------------------------------ x -- 
 H (deep) u 12 
EF heating-value-related CO (low) 2-emission factor in t CO (deep) 2/GJ 
H (deep) u lower calorific value of the fuel in GJ/t   

Unofficial table of contents

Annex 2 (to section 6 (3))
Calculation of process-related carbon dioxide emissions for the blast furnace process

Source of the original text: BGBl. I 2004, 2264

Formula 1 
 44 
E (deep) HO; proz = P (deep) RE x (0.3565-0.047) x -- + E (deep) RS 
 12 
E (deep) HO; proz whole special process-related process-related 
 CO (deep) 2-emissions from blast furnace process in t CO (deep) 2 
P (deep) RE Roheisenproduktion in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials (limestone, dolomite) in t 
  
Formula 2 
 (44)  G (deep) ges-Gabg 
E (deep) ges; proz = (PRE x (0.3565-0.047) x -- + E (deep) RS) x ---------------- 
 (12)  G (deep) ges 
E (deep) ges; proz entire probe-relevant process-related CO (deep) 2- 
 Emissions to be attributed to the blast furnace process in 
 t CO (deep) 2 
P (deep) RE Roheisenproduktion in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials (limestone, dolomite) in t 
G (deep) total gland gas attack 
G (deep) disposination of Gichtgas to third party installations   

Unofficial table of contents

Annex 3 (to § 6 (4))
Calculation of process-related carbon dioxide emissions for oxygenated steel plants

Source of the original text: BGBl. I 2004, 2265

Formula 1 
 ()  44 
Eges; proz = (REin x 0,047 + sum of Cin; and-sum of Cout) x -- + ERS 
 ()  12   
E (deep) ges; proz whole special process-related process-related 
 CO (deep) 2-emissions from steel production in the 
 Oxygenated steel plant in t (CO (deep) 2) 
RE (deep) in pig iron used in steel plant in t 
C (deep) in; and input other carbon from scrap, etc. in t 
C (deep) out Output of carbon in steel etc. in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials in t 
  
Formula 2 
 (44) 
Eges; proz = ((RAn x 0.047 + sum of Cin; and-sum of Cout) x -- + ERS) 
 (12) 
 Gges-Gabg 
 x ----------- 
 Gges 
E (deep) ges; proz whole special process-related process-related 
 CO (deep) 2 emissions to be attributed to the oxygenated steel plant 
 , in t CO (deep) 2 
RE (deep) in pig iron used in steel plant in t 
C (deep) in; and input other carbon from scrap, etc. in t 
C (deep) out Output of carbon in steel etc. in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials in t 
G (deep) total converter gas attack 
G (deep) abg dispensing of converter gas to third party equipment   

Unofficial table of contents

Annex 4 (to section 6 (5))
Calculation of process-related carbon dioxide emissions for plants using dome gases from blast furnace plants and oxygenated steelworks

Source of the original text: BGBl. I 2004, 2266

Formula 
 (44)  GGichtG;abg 
Eges; proz = (PRE x (0.3565-0.047) x -- + ERS) x ----------- 
 (12)  GGichtG; ges 
  
 (44) 
 + ((RAn x 0.047 + sum of Cin; and-sum of Cout) x -- + ERS) 
 (12) 
 GKonvG;abg 
 x ---------- 
 GKonvG; ges 
  
E (deep) ges; proz whole son-to-day-relevant 
 process-related CO (deep) 2-emissions from the 
 High-furnace process and steel production in 
 Oxygenated steelworks used in the supply of coupling gases 
 Third-party systems are to be attributed to third parties, 
 in t CO (deep) 2 
P (deep) RE Roheisenproduktion in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials (limestone, dolomite) in blast furnace in t 
RE (deep) in pig iron used in steel plant in t 
C (deep) in; and input other carbon from scrap, etc. in the 
 Steelworks in t 
C (deep) out Output of carbon in steel etc. at the steel plant in t 
E (deep) RS process-related CO (deep) 2-emissions from the other 
 Use of raw materials in t 
G (deep) KonvG; ges total converter gas attack in steelworks 
G (deep) KonvG;abg delivery of converter gas to the respective third party 
G (deep) GichtG; ges total gland gas attack in blast furnace 
G (deep) GichtG;abg levy of Gichtgas to the respective third party   

Unofficial table of contents

Annex 5 (to § 6 (6))
Determination of process-related carbon dioxide emissions from the regeneration of catalysts in oil refineries

Source of the original text: BGBl. I 2004, 2267

Formula 1 
 ()  44 
E (deep) ges; proz = (C (deep) gem; t0-C (deep) gem; t1) x -- 
 ()  12 
  
E (deep) ges; proz whole process-related CO (deep) 2-emissions in t CO (deep) 2 
C (deep) gem; t0 measured carbon content of the catalyst immediately before 
 the regeneration process in t 
C (deep) common; t1 measured carbon content of the catalyst immediately after 
 the regeneration process in t 
  
Formula 2 
 ()  44 
E (deep) ges; proz = (C (deep) ber; t0-C (deep) ber; t1) x -- 
 ()  12 
  
E (deep) ges; proz whole process-related CO (deep) 2-emissions in t CO (deep) 2 
C (deep) ber; t0 calculated carbon content of the catalyst immediately before 
 the regeneration process in t 
C (deep) ber; t1 calculated carbon content of the catalyst directly 
 after the regeneration process in t 
  
Formula 3 
 44 
E (deep) ges; proz = V (deep) ber x a (deep) CO2 x ------------ 
 22.4 x 1,000 
  
E (deep) ges; proz whole process-related CO (deep) 2-emissions in t CO (deep) 2 
V (deep) from the quantity measurement of the gas stream of certain 
 Annual volume flow of the exhaust gas (converted into dry 
 Exhaust gas) in Nm (high) 3 
a (deep) CO2-measured carbon dioxide content of the dry exhaust gas 
 in proportions (concentration in Vol-%/100) 
  
If a measurement of the carbon monoxide before conversion into carbon dioxide 
, carbon monoxide shall be included in the invoice.  Where 
shall be subject to the carbon monoxide being completely carbon dioxide 
is implemented. 
  
Formula 4 
Calculation of the dry exhaust gas quantity from the supplied air quantity at 
constant inert gas content of 79.07% by volume. 
  
 V (deep) air, tr x 79,07 
V (deep) ber = ---------------------------------------- 
 100-a (deep) CO2-b (deep) CO-c (deep) O2 
  
V (deep) air, tr volume flow of air supplied (converted into 
 dried air) in Nm (high) 3 per time unit 
a (deep) CO2 measured carbon dioxide content of the dry exhaust gas in Vol-% 
b (deep) CO measured carbon monoxide content of the dry exhaust gas in Vol-% 
c (deep) O2 measured oxygen content of the dry exhaust gas in Vol-%   

Unofficial table of contents

Annex 6 (to § 6 (7))
Determination of process-related carbon dioxide emissions from the calcination of petroleum coke in petroleum refineries

(Fundstelle: BGBl. I 2004, 2268)

Formula
E (deep) ges; proz =	(		)		44
	(	C (deep) in; ges-C (deep) out; coke	)	X	--
	(		)		12
E (deep) ges; proz	Total process-related CO (deep) 2-emissions in t CO (deep) 2
C (deep) in; ges	total carbon input of the calcination process in t
C (deep) out; coke	Carbon-output of the calcination process in the coke in t

Unofficial table of contents

Annex 7 (to § 6 (8))
Determination of process-related carbon dioxide emissions from hydrogen production in oil refineries

Source of the original text: BGBl. I 2004, 2268

Formula 1 
 44 
E (deep) ges; proz = sum of C (deep) in; KW x -- 
 12 
  
E (deep) ges; proz whole special process-related process-related 
 CO (deep) 2-emissions in t CO (deep) 2 
C (deep) in; KW Input to carbon in the processed hydrocarbons 
 in t (without fuel use) 
  
Formula 2 
 ()  44 
E (deep) ges; proz = (H (deep) out; H2-H (deep) in; H2O) x 2 x k (deep) C/H x -- x 1,000 
 ()  12 
  
E (deep) ges; proz whole process-related CO (deep) 2-emissions in t CO (deep) 2 
H (deep) out; H2 Output to hydrogen in kmol 
H (deep) in; H2O Input to hydrogen in water vapour in kmol 
k (deep) C/H carbon-hydrogen ratio of the used 
 Total hydrocarbons in mol/mol   

Unofficial table of contents

Annex 8 (to § 10)
Emission shoting without additional influences

(Fundstelle des Originaltextes: BGBl. I 2004, 2269-2270)

Formula 1
E (deep) H =	E (deep) t x 375 and E (deep) t = E (deep) Bz: t (deep) B
E (deep) H	Emissions reporting for full operating year
E (deep) t	daily average emissions during the operating period of the calendar year of commissioning
t (deep) B	Number of calendar days of the operating period in the calendar year of entry into service
E (deep) Bz	Emissions from the plant during the operating period in the calendar year of commissioning
	Emission shocketing calculation for weather-dependent plant operation (consideration of heating periods)

In this case, the emissions of the plant will be extrapolated the full year in the year of commissioning, taking into account the weather-dependent production of the plant. The number of grads is determined according to VDI 3807 (VDI 3807, sheet 1: energy consumption values for buildings, basic principles). The location-specific data of the German Weather Service are relevant. Alternatively, the data of the German Weather Service may be used for a test reference year provided by the competent authority on its website.

Formula 2
E (deep) H =	E (deep) Bz x G (deep) 15: GTZ
GTZ	cumulative number of grads for the operating life of the plant during the first year of operation
G15	Gradday number of the calendar year according to VDI 3807, sheet 1
EH	Emissions reporting for full operating year
EBz	Emissions from the plant during the operating period in the calendar year of commissioning
Emission reporting for seasonal production fluctuations (campaign operation)
In this case, the emissions from the plant will be extrapolated to the full year, taking into account seasonal fluctuations in production.
Formula 3
For the cases of Section 7 (4) of the German Dispatch Act 2007
	(	)	(	)
E (deep) H =	(E (deep) Bz: PM1	) X	((PM2 + PM3)	) : 2)
	(	)	(	)
Formula 4
For the cases of Section 7 (5) of the Allocation Act 2007
	(	)
E (deep) H =	(E (deep) Bz: PM1	) X	PM2
	(	)
PM1	Production volume within the first year of operation
PM2	Production volume within the second year of operation
PM3	Volume of production within the third operating year, 2003
E (deep) H	Emissions reporting for full operating year
E (deep) Bz	Emissions from the plant during the operating period in the calendar year of commissioning

Unofficial table of contents

Annex 9 (to section 13 (6))
Calculation of the relative emission reduction for combined heat and power plants

Source of the original text: BGBl. I 2004, 2271-2272In the calculation of the specific emissions, in addition to the heat actually produced, the heat equivalent of the generated stream as a generated product quantity is also taken into account.
In addition to the product quantities and emissions during the reference period and the base period, the operator shall be responsible for the mean work-related loss of electricity losses on the basis of specific, sufficiently accurate and verified time series for the energy flows to be imaged Proof.

 Heat reference 
Formula 1 
 W (deep) Predecessor 
 Q (deep) predecessors + --------------------- 
 E (deep) Stock Beta (deep) a, Predecessor 
Delta e (deep) r = 1--------------- x -------------------- 
 E (deep) predecessor W (deep) inventory 
 Q (deep) Inventory + --------------------- 
 Beta (deep) a, Stock 
  
Delta e (deep) r specific emission reduction 
E (deep) stock Total emissions of the combined heat and power plant in the 
 Base period in t CO (deep) 2 
E (deep) Predecessor total emissions of the plant prior to modernization in the 
 Reference period in t CO (deep) 2 
Q (deep) stock of the combined heat and power plant in the base period 
 Thermal energy provided in MJ 
Q (deep) predecessor of the plant prior to modernization in the reference period 
 Thermal energy provided in MJ 
W (deep) inventory of the combined heat and power plant in the base period 
 Electrical energy provided in MJ 
W (deep) Predecessor if the plant before the modernization power in 
 Combined heat and power generation: from the plant before the 
 Modernization provided in the reference period 
 electric energy in MJ 
Beta (deep) a, labour-related power loss index of the 
Fleet of combined heat and power plants in the base period 
 by FW 308 (11/2002) 
Beta (deep) a, provided that the plant before the modernization of electricity in 
Predecessor combined heat and power generation: 
 asset-related power loss characteristics of the asset 
 the modernization in the reference period according to FW 
 308 (11/2002) 
  
 Current reference 
Formula 2 
 EInventory Wpredecessors 
Delta e (deep) r = 1------------------ x ------------------------------- 
 Epredecessors Wstock + Qinventory x Beta a 
  
Delta e (deep) r specific emission reduction 
E (deep) stock Total emissions of the combined heat and power plant in the 
 Base period in t CO (deep) 2 
E (deep) Predecessor total emissions of the plant prior to modernization in the 
 Reference period in t CO (deep) 2 
Q (deep) stock of the combined heat and power plant in the base period 
 Thermal energy provided in MJ 
W (deep) predecessor of the plant prior to modernization in the reference period 
 Electrical energy provided in MJ 
W (deep) inventory of the combined heat and power plant in the base period 
 Electrical energy provided in MJ 
Beta (deep) a labour-related power loss measure of the 
 Power-to-heat coupling system in the base period after 
FW 308 (11/2002)