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Seventeenth Ordination on the Implementation of the Federal Immission Protection Act

Original Language Title: Siebzehnte Verordnung zur Durchführung des Bundes-Immissionsschutzgesetzes

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Seventeenth Regulation implementing the Federal Immission Control Act (Regulation on the incineration and co-incineration of waste-17). BImSchV)

Unofficial table of contents

17. BImSchV

Date of completion: 02.05.2013

Full quote:

" Regulation on the incineration and co-incineration of waste of 2 May 2013 (BGBl. I p. 1021, 1044, 3754) "

Footnote

(+ + + Text proof: 2.5.2013 + + +) 

The V was referred to as Article 3 of the V v. 2.5.2013 I 1021 by the Federal Government and the Federal Ministry of Transport, Building and Urban Development, after consultation of the parties involved, in agreement with the Federal Ministry of Finance and the Federal Ministry of Economics and Technology, with due regard for the rights of the Bundestag pursuant to § 48b of the Federal Immission Protection Act and with the consent of the Federal Council. She's gem. Article 10 (1) of this V entered into force on 2 May 2013. Unofficial table of contents

Content Summary

Section 1General provisions
§ 1 Scope
§ 2 Definitions
Section 2Requirements for the establishment,
the nature and operation
§ 3 Requirements for the delivery, acceptance and interim storage of the starting materials
§ 4 Construction and nature of the installations
§ 5 Operating conditions
§ 6 Combustion conditions for waste incineration plants
§ 7 Combustion conditions for waste co-incineration plants
§ 8 Emission limit values for waste incineration plants
§ 9 Emission limit values for waste co-incineration plants
§ 10 Emission limit values to be observed in the annual budget
§ 11 Discharge conditions for exhaust gases
§ 12 Treatment of residues resulting from the incineration of waste and waste co-incineration
§ 13 Heat Usage
Section 3Measurement and monitoring
§ 14 Measuring stations
§ 15 Measuring methods and measuring equipment
§ 16 Continuous measurements
§ 17 Evaluation and evaluation of continuous measurements
§ 18 Single measurements
§ 19 Reports and assessment of individual measurements
§ 20 Special monitoring of emissions of heavy metals
Section 21 Malfunction of the holding
Section 22 Annual reports on emissions
Section 4Common provisions
Section 23 Publication obligations
§ 24 Approval of exceptions
Section 25 More stringent requirements and significant changes
Section 5Final provisions
Section 26 Accessibility and equivalence of standards and worksheets
§ 27 Irregularities
§ 28 Transitional arrangements
Appendix 1
(in accordance with Article 8 (1)),
Section 18 (5) and
Section 20 (1))

Emission limit values for carcinogenic substances
Appendix 2
(relating to Annex 1 (d))

Equivalence factors
Appendix 3
(on § 9,
Section 10 (2),
Section 16 (1) and (4),
Section 17 (1) and (5),
Section 18 (2),
Article 19 (2),
Section 21 (3),
Section 22 (1) and
Section 28 (5) and (6)

Emission limit values for co-incineration of waste
Appendix 4
(in accordance with Article 15 (1)),
Section 16 (1) and
Section 17 (5))

Requirements for the continuous measuring equipment and the validation of the measurement results

Appendix 5
(to § 2 (10))
Conversion formula

Section 1
General provisions

Unofficial table of contents

§ 1 Scope

(1) This Regulation shall apply to the establishment, nature and operation of waste incineration plants and waste co-incineration plants which, in accordance with Article 4 of the Federal Immission Control Act, in conjunction with the Regulation referred to in point 2 above, shall: need to be approved and in which the following waste and substances are used:
1.
solid, liquid or gaseous wastes in containers, or
2.
similar solid or liquid combustible substances other than those specified in points 1.2.1, 1.2.2 or 1.2.3 of Annex 1 to the Regulation on approved installations of 2 May 2013 (BGBl. 973), with the exception of similar liquid combustible substances, provided that no other or no higher emissions can occur during their combustion than in the case of the combustion of light heating oil, or
3.
solid, liquid or gaseous substances which are produced during the pyrolysis or gasification of waste.
This Regulation shall not apply to waste incineration or co-incineration plants or to individual waste incineration or co-incineration lines which, apart from the use of those set out in points 1.2.1, 1.2.2 and 1.2.3 of Annex 1 to the Regulation, shall apply: Substances listed in need of approval are intended solely for the use of
1.
Bioliquids according to § 2 (6) (2) of the Ordinance on Large Fire, Gas Turbine and Combustion Engines of 2 May 2013 (BGBl. 1021, 1023), as amended,
2.
Animal bodies within the meaning of Regulation (EC) No 1069/2009 of the European Parliament and of the Council of 21 June 2009 Directive on animal by-products not intended for human consumption, and repealing Regulation (EC) No 1774/2002 (Regulation on animal by-products) (OJ L 327, 31.12.2002, p. 1), as defined by Directive 2010 /63/EU (OJ L 327, 22.12.2010, p. OJ L 276, 20.10.2010, p. 33), or
3.
Wastes arising from the exploration of oil and natural gas deposits and their extraction on drilling rigs, where they are incinerated.
(3) The Regulation shall not apply to:
1.
waste incineration or co-incineration lines, which treat less than 50 megagrams of waste per year for research, development and testing purposes to improve the combustion process; and
2.
gaseous substances referred to in paragraph 1 (3) which are used in waste co-incineration plants if their combustion causes no other or higher emissions than the combustion of natural gas due to their composition.
(4) This Regulation lays down requirements for waste incineration plants and waste co-incineration plants,
1.
According to § 5 (1) (1) (1) to (4) of the Federal Immission Control Act (Federal Immission Control Act), the installation and operation of the plants shall be fulfilled
a)
the fight against fire hazards,
b)
Prevention of adverse environmental impacts,
c)
Treatment of waste and
d)
Use of the resulting heat as well as
2.
for the fulfilment of air quality requirements of the European Communities or of the European Union pursuant to § 48a (1) and (3) of the Federal Immission Control Act.
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§ 2 Definitions

(1) "waste" within the meaning of this Regulation shall be substances or objects which, in accordance with the provisions of the Circular Economic Law of 24 February 2012 (BGBl. 212) in the version in force in each case. (2) "Large combustion plant waste co-incineration plant" within the meaning of this Regulation is a waste co-incineration plant with a thermal output of 50 megawatts or more. (3) For the purposes of this Regulation, 'waste co-incineration plant' means a combustion plant, the main purpose of which is the supply of energy or of the production of material products, and in which waste or substances are mixed in accordance with Article 1 (1), Settlement waste only as far as processed mixed municipal waste is concerned,
1.
are used as regular or additional fuels, or
2.
are thermally treated with the aim of eliminating them.
The plant in this sense shall cover the entire waste co-incineration plant, including all waste co-incineration lines, the acceptance and storage of the waste and the substances referred to in Article 1 (1), which are located on the site. Pre-treatment plants, the supply system for waste and substances in accordance with Article 1 (1), for fuels and air, the boiler, the exhaust gas treatment plants, the facilities located on the site for the treatment and storage of waste and waste water, which shall be of the waste co-incineration, the chimney, the devices and systems for controlling the Combustion processes, for recording and for monitoring combustion conditions. If waste co-incineration is carried out in such a way that the main purpose of the plant is not in the energy supply or production of material products but in the thermal treatment of waste, the installation shall be deemed to be: Waste incineration plant within the meaning of paragraph 4. (4) "waste incineration plant" within the meaning of this Regulation is a combustion plant, the main purpose of which is to provide thermal processes for the treatment of waste or substances in accordance with Article 1 (1) of this Regulation. . These methods shall include the incineration by oxidation of the abovementioned substances and other comparable thermal processes, such as pyrolysis, gasification or plasma processes, to the extent that the resulting thermal processes result from waste solid, liquid or gaseous substances. The plant in this sense shall cover the entire waste incineration plant, including all waste incineration lines, the acceptance and storage of the waste and substances in accordance with Article 1 (1), the pre-treatment facilities on the site, the System for the supply of waste and substances according to Article 1 (1), for fuels and air, the boiler, the exhaust gas treatment plants, the facilities located on the site for the treatment and storage of waste and waste water used in the incineration of waste , the chimney, the devices and systems for controlling the Incineration operations, recording and monitoring of combustion conditions. (5) "Waste incineration or co-incineration line" within the meaning of this Regulation is the technical equipment of the waste incineration or incineration plant; or -co-incineration plant, which includes a combustion chamber, a burner where appropriate, and the associated control unit, an exhaust gas purification device and other subsidiary equipment in accordance with Article 1 (2) (2) of the Regulation on (6) "exhaust gas" within the meaning of this Regulation shall be the carrier gas with the solid, liquid or gaseous emissions, expressed as a volume flow rate in the unit of cubic metres per hour (m 3 /h) and with respect to the exhaust gas volume in the normal state (temperature 273.15 Kelvin (K), pressure 101.3 kilopascals (kPa)) after deduction of the moisture content of water vapour. (7) "processed mixed municipal waste" within the meaning of this Regulation are mixed Municipal waste for which measures have been taken for the purpose of co-incineration which significantly reduce exposure to inorganic pollutants, in particular heavy metals; drying, pressing or mixing are generally not included in these wastes Measures. (8) "Existing waste-co-incineration large combustion plant" in the sense of this Regulation shall be a large combustion plant which is co-incinerated with waste;
1.
which was to be reported in accordance with § 67 (2) or § 67a (1) of the Federal Immission Protection Act or before the entry into force of the Federal Immission Protection Act pursuant to Section 16 (4) of the Industrial Code,
2.
for which the first permit for the erection and operation according to § 4 or § 16 of the Federal Immission Protection Act was granted before 7 January 2013 and which went into operation before 7 January 2014, or
3.
For which the operator has submitted a complete permit for the establishment and operation according to § 4 or § 16 of the Federal Immission Protection Act before 7 January 2013 and which went into operation before 7 January 2014.
(9) 'Existing waste incineration or co-incineration plant' within the meaning of this Regulation is a waste incineration or co-incineration plant, with the exception of large combustion plants which are co-incinerated and approved or built before 2 May 2013 (10) 'Reference oxygen content' within the meaning of this Regulation shall be the volume content of oxygen in the exhaust gas given or to be calculated in each case, to which the respective emission limit value is to be obtained, taking into account Annex 5. (11) "biofuels" for the purposes of this Regulation shall be bio-fuels according to § 2 (12) "emissions" within the meaning of this Regulation are the air pollutants emitted by an installation; expressed as a mass concentration in the milligram unit per unit of time, Cubic meter exhaust gas (mg/m 3 ) or nanogram per cubic meter of exhaust gas (ng/m 3 ) or mass flow in the unit Megagramm per year (Mg/a). (13) "emission limit value" for the purposes of this Regulation is the emission of an installation which may be allowed to be discharged into the air, expressed as a mass concentration and referred to the relevant reference oxygen content. (14) "natural gas" within the meaning of this Regulation
1.
naturally occurring methane gas with no more than 20% by volume of inert gases and other constituents which corresponds to the requirements of the DVGW Working Sheet G 260 of May 2008 for gases of the 2nd gas family, and
2.
Clarifying, bio-and mine gases according to DVGW worksheet G 262 of September 2011, which meet the conditions of the DVGW working sheet G 260 as an exchange gas or as an additional gas for conditioning, and in so far as the basic gases of the 2nd gas family in the public Replace or supplement gas supply.
(15) "combustion plant" within the meaning of this Regulation means any installation in which fuel is oxidised for the use of the heat produced. (16) "Thermal heat output" for the purposes of this Regulation is the heat content of the fuel used for the lower calorific value; (17) "Mixed municipal waste" within the meaning of this Regulation shall be waste from domestic and industrial waste and industrial waste and waste; from establishments which, by virtue of their nature or composition, have wastes from household appliances are similar. The mixed municipal waste within the meaning of this Regulation shall not include those under the waste group 20 01 of the Waste List Regulation * (18) 'Hazardous waste' within the meaning of this Regulation shall be hazardous waste in accordance with the provisions of this Regulation, which shall be subject to the following conditions: Waste-directory regulation. (19) "Light heating oil" for the purposes of this Regulation is heating oil EL according to DIN 51603-1, edition August 2008.
*
Note to the written instructions:
Waste List-Regulation of 10 December 2001 (BGBl. 3379), as last amended by Article 5 (22) of the Law of 24 February 2012 (BGBl). 212) has been amended.

Section 2
Requirements for the establishment, quality and operation of the system

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§ 3 Requirements for the delivery, acceptance and interim storage of the starting materials

(1) The operator of a waste incineration or co-incineration plant shall take all the necessary precautions with regard to the delivery and acceptance of the waste, in order to prevent pollution of the air, soil, surface water and of groundwater, other pressures on the environment, odour and noise nuisances as well as direct risks to human health, or to limit them as far as possible. (2) The operator shall contribute to the adoption of hazardous waste in the Waste incineration or co-incineration plant, the information available on the wastes together to determine whether the conditions of the permit are met. This information shall include:
1.
all administrative information relating to the production process of the waste contained in the documents referred to in point 1 of the first sentence of paragraph 3,
2.
the physical and, as far as practicable, the chemical composition of the waste,
3.
any other information required for the assessment of the suitability of the waste for the incineration process,
4.
Hazard characteristics of the waste, substances with which they cannot be mixed, and precautions for handling such waste.
(3) Before the adoption of hazardous waste in the waste incineration or co-incineration plant, the operator shall carry out at least the following measures:
1.
Examination of the documents provided for in Directive 2008 /98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives (OJ L 327, 30.12.2008, p. 24) (Waste Framework Directive) and, where appropriate, Regulation (EC) No 1013/2006 of the European Parliament and of the Council of 14 June 2006 on shipments of waste (OJ L 327, 22.12.2006, p. 1, L 318, 28.11.2008, p. 15), as last amended by Regulation (EU) No 135/2012 (OJ L 327, 28.11.2008, p. 30), as well as the legislation on the transport of dangerous goods, as well as
2.
Sampling and control of samples taken from samples to verify that the waste complies with the information referred to in paragraph 2 and to enable the competent authorities to establish the type of waste treated; the samples shall be to be removed prior to loading, provided that this does not involve a disproportionate effort.
The samples referred to in point 2 of the first sentence shall be kept for at least one month after the incineration or co-incineration of the waste in question. (4) The operator of the plant shall have a waste incineration or waste incineration plant prior to the acceptance of the waste. (5) The competent authority may, at the request of the operator, for waste incineration or co-incineration plants, derogations from paragraphs 2 to 4. , if these installations are
1.
are part of an installation marked with the letter E in Annex 1 to the Regulation on installations in need of approval in column d;
2.
only incinerate or co-incinerate waste generated within the plant.
(6) Liquid wastes or substances according to § 1 (1) shall be stored in closed containers, which are secured against overpressure. When filling the containers, the gas-pendulating method is to be used or the displacement air is to be detected. The operator shall have to equip open transfer points with an air suction before the commissioning of a waste incineration or co-incineration plant. The displacement air from the containers as well as the sucked-off air must be supplied to the firing. When the firing is at a standstill, an acceptance at open transfer points or a filling of storage tanks is only permissible if emission reduction measures, in particular the gas treatment or an exhaust gas purification, are used. Unofficial table of contents

§ 4 Installation and nature of the plants

(1) Waste incineration or co-incineration plants shall be designed, constructed and operated in such a way as to prevent unauthorised and unintentional release of harmful substances into the soil, surface water or groundwater. In addition, sufficient storage capacity shall be required for the polluted rainwater produced on the site of the waste incineration or co-incineration plant and for polluted water to be used in the event of disturbances or fire-fighting. shall be provided. It is sufficient if the water obtained can be tested and, if necessary, treated before discharge. (2) The operator has a waste incineration plant for solid waste or substances according to § 1 (1) before putting into service with a waste incineration plant. To equip bunkers, which is to be provided with a suction and whose sucked-off air is to be supplied to the firing. In the event that the firing is not in operation, measures must be taken to clean and discharge the air drawn off. (3) The operator shall have a waste co-incineration plant for solid waste or substances in accordance with Article 1 (1) before commissioning. to equip closed storage facilities for these substances. (4) Paragraphs 2 and 3 shall not apply to waste incineration or co-incineration plants to the extent that the waste or substances referred to in Article 1 (1) of the waste incineration or waste co-incineration plant (5) For waste incineration or co-incineration plants, provision should be made for measures and facilities for the detection and control of fires. The fire protection facilities and measures must be designed in such a way that fires arising or registered in the waste bunker can be detected and combated. (6) Explosions based on the composition of the waste or substances according to § 1 paragraph 1 in the storage sector, other appropriate measures shall be implemented by way of derogation from paragraph 4. The measures shall be determined by the competent authority more closely. (7) Before the entry into service, the operator shall have each waste incineration or co-incineration line of a waste incineration or co-incineration plant with one or more burners. to equip. Sentence 1 shall not apply provided that the conditions laid down in Article 9 (1), first sentence, point 1 are met. (8) The operator must equip a waste incineration or co-incineration plant with automatic devices prior to entry into service, by means of which the operator shall: ensuring that
1.
the installation of waste or substances in accordance with Article 1 (1) is only possible if the minimum temperature has been reached during start-up,
2.
a loading of the waste or substance installations referred to in Article 1 (1) can only be carried out for as long as the minimum temperature is maintained,
3.
a charge of waste or substances in accordance with § 1 (1) shall be interrupted if, as a result of a failure or disturbance of exhaust gas purification devices, a continuously monitored emission limit value is exceeded , safety-related aspects of fire and explosion protection must be taken into account.
(9) Waste incineration or co-incineration plants shall be equipped with recording equipment which shall register locking or shutdowns by means of the automatic devices referred to in paragraph 8. (10) Other requirements which may be from the regulation on large-scale fire, gas turbine and internal combustion engine systems or from § 5 (1) (2) of the Federal Immission Protection Act in compliance with the First General Administrative Regulation on the Federal Immission Control Act (Technical and Technical Assistance Act) Guidance on air pollution-TA Luft) of 24 July 2002 (GMBl. 511), as amended, shall remain unaffected.

Footnote

Section 4 (1) Sentence 1 Italics: Should "waste incineration or co-incineration plants" be correct
§ 4 (5) sentence 2 italic print: superfluous word Unofficial table of contents

§ 5 Operating conditions

(1) A waste incineration plant shall be constructed and operated in such a way as to ensure that:
1.
a major burn-out of the waste or of the substances referred to in Article 1 (1) is achieved; and
2.
in the slag and in the rust ash, a content of organically bonded total carbon of less than 3 per cent or a loss of ignition of less than 5 per cent of the dry weight is maintained.
(2) Where necessary for the fulfilment of the requirements referred to in paragraph 1, the waste or substances shall be pre-treated in accordance with § 1 (1) (1). The pre-treatment is usually carried out by crushing or mixing or by opening disposable containers. (3) Contrary to the requirements of paragraph 2, infectious disease-specific waste is to be brought into the firing, without first (4) The waste co-incineration plants shall be operated in such a way as to achieve the most complete incineration of waste and substances in accordance with Article 1 (1). (5) Flight-ash deposits shall be kept as low as possible, in particular by appropriate means Exhaust gas flow as well as frequent cleaning of boilers, heating surfaces, boiler feed water preheaters and exhaust gas trains. Unofficial table of contents

Section 6 incineration conditions for waste incineration plants

(1) Waste incineration plants shall be constructed and operated in such a way that, for the combustion gases resulting from the incineration of waste or substances as defined in Article 1 (1), after the last combustion air supply, a minimum temperature of 850 shall be: (2) In the case of the incineration of hazardous waste with a halogen content of more than 1 per cent of the weight, calculated as chlorine, the operator shall ensure that, by way of derogation from paragraph 1, 1 a minimum temperature of 1 100 degrees Celsius is maintained. (3) Minimum temperature must also be maintained under unfavourable conditions with uniform mixing of the combustion gases with the combustion air for a residence time of at least two seconds. (4) The measurement of the minimum temperature has to be carried out in accordance with the following conditions: the proximity of the inner wall of the combustion chamber. The competent authority may authorise the measurement to be carried out at another representative point in the combustion chamber or in the afterburning area. The verification and, where appropriate, the adjustment of the representative body shall be carried out with the agreement of the competent authority within the framework of the commissioning of the installation. (5) Compliance with the minimum temperature and the minimum residence time shall be at least once (6) By way of derogation from paragraphs 1 to 3, the competent authorities may have other minimum temperatures or minimum residence times. (combustion conditions), provided that:
1.
the other requirements of this Regulation are complied with, and
2.
it is established that the change in combustion conditions does not contain any major waste quantities and no waste with a higher content of organic pollutants, in particular polycyclic aromatic hydrocarbons, polyhalogenated Dibenzodioxins, polyhalogenated dibenzofurans or polyhalogenated biphenyls, may be expected to be obtained under the conditions laid down in paragraphs 1 to 3.
The proof referred to in the first subparagraph of point 2 shall be provided at least once when the waste incineration plant is put into service under the modified combustion conditions by means of measurements or by an opinion recognised by the competent authority. The competent authorities shall submit a derogation in accordance with the first sentence of the first sentence to the competent authorities of the competent authorities of the Member States for transmission to the European Commission. (7) Existing installations shall be subject to proof of sufficient proof of Combustion conditions shall also be deemed to be provided, provided that, at least once after the plant has been put into service, it is demonstrated by measurements that no higher emissions, in particular polycyclic aromatic hydrocarbons, are polyhalogenated Dibenzodioxins, polyhalogenated dibenzofurans or polyhalogenated dibenzodioxins (8) During start-up and in the event of a threat of undershooting of the minimum temperature, the burners must be used with natural gas, liquefied petroleum gas, hydrogen, gaseous Fuels referred to in point 1.2.2 of Annex 1 to the Regulation on installations in need of approval, light heating oil or other liquid substances in accordance with Article 1 (1), provided that their composition does not contain any other or higher emissions than those of the Combustion of light heating oil can occur, operated. (9) Waste incineration plants or individual waste incineration lines shall be used to operate the burners in order to maintain the combustion conditions until such time as no waste or substances in accordance with § 1 (1) are found in the firebox. The distillers shall be operated exclusively with the fuels referred to in paragraph 8. Sentence 1 shall not apply to the other liquid substances referred to in Article 1 (1) where, because of their composition, no other or no higher emissions may occur than in the case of the combustion of light heating oil, and to the extent that they are Maintenance of combustion conditions will be used. Unofficial table of contents

Section 7 incineration conditions for waste co-incineration plants

(1) Waste co-incineration plants shall be constructed and operated in such a way as to comply with a minimum temperature of 850 degrees Celsius for the combustion gases produced in the case of waste co-incineration. (2) Waste with a halogen content of more than 1% by weight of halogen-organic substances, calculated as chlorine, shall ensure that, by way of derogation from paragraph 1, a minimum temperature of 1 100 degrees Celsius is maintained. (3) The minimum temperature must also be kept under the most unfavourable conditions for a residence time of at least two seconds. (4) The measurement of the minimum temperature shall be carried out on a representative site of the combustion chamber or post-combustion chamber, as defined by the competent authority in the permit. The verification and, where appropriate, the adjustment of the representative body shall be carried out with the agreement of the competent authority within the framework of the commissioning of the installation. (5) Compliance with the minimum temperature and the minimum residence time shall be at least once (6) by way of derogation from paragraphs 1 to 3, the competent authority may authorise other combustion conditions, provided that:
1.
the other requirements of this Regulation are complied with, and
2.
the emission limit values set out in Article 8 (1) for organic substances, indicated as total carbon, and for carbon monoxide are complied with.
The competent authorities shall provide the competent supreme immission protection authorities of the countries for transmission to the European Commission, in accordance with the first sentence of the first sentence. Unofficial table of contents

Section 8 Emission limit values for waste incineration plants

(1) Waste incineration plants shall be constructed and operated in such a way as to ensure that:
1.
no daily average value exceeds the following emission limit values:
a)
Total dust 5 mg/m 3 ,
b)
organic substances, expressed as total carbon, 10 mg/m 3 ,
c)
gaseous inorganic chlorine compounds,
specified as hydrogen chloride,
10 mg/m 3 ,
d)
gaseous inorganic fluorine compounds,
specified as hydrogen fluoride,
1 mg/m 3 ,
e)
Sulphur dioxide and sulphur trioxide,
specified as sulphur dioxide,
50 mg/m 3 ,
f)
nitrogen monoxide and nitrogen dioxide,
specified as nitrogen dioxide,
150 mg/m 3 ,
g)
mercury and its compounds,
indicated as mercury,
0.03 mg/m 3 ,
h)
Carbon monoxide 50 mg/m 3 ,
i)
Ammonia, provided that the emissions are reduced by
Nitrogen oxides, a process for selective catalytic
or non-catalytic reduction is used
10 mg/m 3 ;
2.
no half-hourly average value exceeds the following emission limit values:
a)
Total dust 20 mg/m 3 ,
b)
organic substances, expressed as total carbon, 20 mg/m 3 ,
c)
gaseous inorganic chlorine compounds,
specified as hydrogen chloride,
60 mg/m 3 ,
d)
gaseous inorganic fluorine compounds,
specified as hydrogen fluoride,
4 mg/m 3 ,
e)
Sulphur dioxide and sulphur trioxide,
specified as sulphur dioxide,
200 mg/m 3 ,
f)
nitrogen monoxide and nitrogen dioxide,
specified as nitrogen dioxide,
400 mg/m 3 ,
g)
mercury and its compounds,
indicated as mercury,
0.05 mg/m 3 ,
h)
Carbon monoxide 100 mg/m 3 ,
i)
Ammonia, provided that the emissions are reduced by
Nitrogen oxides, a process for selective catalytic
or non-catalytic reduction is used
15 mg/m 3 ;
3.
no mean value calculated over the sampling period in question exceeds the emission limit values set out in Appendix 1.
(2) For waste incineration plants with a thermal output of less than 50 MW, the following shall apply:
1.
by way of derogation from paragraph 1 (1) (a), an emission limit value for total dust of 10 mg/m 3 for the daily average value and
2.
by way of derogation from paragraph 1 (1) (f), an emission limit value for nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, of 200 mg/m 3 for the daily average.
The emission limit values referred to in paragraph 1 shall relate to a reference oxygen content of 11 per cent. To the extent exclusively gaseous substances produced during the pyrolysis or gasification of waste, or waste oils within the meaning of Article 1a (1) of the Waste Oil Regulation as amended by the Federal Law Gazette of 16 April 2002 (BGBl I). I p. 1368), most recently by Article 5 (14) of the Law of 24 February 2012 (BGBl. 212), the reference oxygen content shall be 3 per cent. Unofficial table of contents

Section 9 Emission limit values for waste co-incineration plants

(1) Waste co-incineration plants shall be constructed and operated in such a way as to comply with the following emission limit values in the exhaust gases:
1.
the emission limit values set out in Annex 3, where:
a)
the plant does not produce more than 25 per cent of the respectively driven thermal output of a co-incineration plant waste co-incineration line; and
b)
if mixed municipal waste is used, only mixed municipal waste is used, and
2.
the emission limit values referred to in Article 8 (1) and Article 10 (1), provided that:
a)
the plant generates more than 25 per cent of the respectively driven thermal output of a waste co-incineration line from co-incineration plants, or
b)
in the case of mixed municipal waste, no processed mixed municipal waste is used.
Co-incineration substances are the waste and substances used in accordance with § 1 (1) and the fuels additionally required for their co-incineration. (2) For plants for the production of cement clinker or cements or for installations for burning of Limestone referred to in point 2.3 or 2.4 of Annex 1 to the Regulation on installations in need of approval shall be subject to the provisions of Annex 3, point 2, even if, by way of derogation from the first sentence of paragraph 1, point 1 (a), the share of co-incineration substances (3) become available in plants , by way of derogation from paragraph 2, the limit values laid down in Article 8 (1) shall apply by way of derogation from paragraph 2, in accordance with paragraph 2, which produces more than 40 per cent of the total heat output of hazardous waste, including the fuel additionally required for incineration. and § 10 (1). For the determination of the percentage of the percentage referred to in the first sentence, liquid combustible waste and substances shall remain in accordance with Article 1 (1) if:
1.
their mass content of polychlorinated aromatic hydrocarbons, such as, for example, polychlorinated biphenyls or pentachlorophenol, less than 10 milligrams per kilogram, and the lower calorific value of which is at least 30 megajoules per kilogram, or
2.
on the basis of their composition, no other or higher emissions may occur than in the case of the combustion of light heating oil.
(4) The emission limit values shall be based on a volume content of oxygen in the exhaust gas as determined in Appendix 3 or determined in accordance with the procedure specified in Appendix 3. Unless otherwise specified in Appendix 3, the half-hourly average values shall not exceed twice the daily average values laid down. To the extent that the emission limit values set out in Annex 3, point 3 are dependent on the thermal output, the thermal output of large combustion plants shall be the thermal output of large combustion engines, gas turbines and gas turbines in accordance with Article 3 of the Regulation on waste co-incineration plants, and (5) The competent authority shall have the relevant emission limit values, in particular where they can be determined by computer or by way of derogation, in accordance with Annex 3, in the approval certificate or in a to fix retrospective arrangement. Unofficial table of contents

Section 10 Emission limit values to be observed in the annual budget

(1) Waste incineration plants shall be constructed and operated in such a way that no annual average value exceeds the following emission limit values:
1.
nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, 100 mg/m 3 ,
2.
mercury and its compounds, indicated as mercury, 0.01 mg/m 3 .
(2) Waste co-incineration plants shall be constructed and operated in such a way that no annual average value exceeds the emission limit values set out in Annex 3, point 2.3, 3.7 or 4.3. (3) Paragraphs 1 and 2 shall be for existing installations with a Thermal power of 50 MW or less shall not be used. Unofficial table of contents

Section 11 Conditions of discharge for exhaust gases

The exhaust gases are to be diverted in a controlled manner in such a way that an undisturbed transport with the free air flow is made possible. For the determination of the discharge heights, the requirements of the technical instructions for the clean-keeping of the air must be taken into account. The more detailed provisions shall be laid down in the permit. Unofficial table of contents

Section 12 Treatment of residues resulting from the incineration of waste and waste co-incineration

(1) Residues, such as slag, rust ash, filter and boiler dusts, as well as reaction products and other waste of the exhaust gas treatment, shall be avoided, used or eliminated in accordance with Section 5 (1) (3) of the Federal Immission Control Act. Where the recycling of residues is not technically possible or unreasonable, they shall be removed without prejudice to the good of the general public. (2) The operator shall ensure that filter and boiler dusts used in exhaust gas dust removal as well as for the cleaning of boilers, heating surfaces and exhaust gas trains, separate from other solid wastes. The first subparagraph shall not apply to installations with fluidized bed firing. (3) Where necessary for the performance of the obligations referred to in paragraph 1, the constituents of organic and soluble substances in the waste and other substances shall be reduced. (4) The Conveying and storage systems for debris-containing, dust-like residues shall be designed and operated in such a way as to ensure that no relevant diffuse emissions can be emitted. This is particularly the case with regard to the necessary maintenance and repair work on plant parts susceptible to wear. The operator shall ensure that dry filter and boiler dusts, reaction products of the waste gas treatment and dry slag are transported or stored in closed containers. (5) Before determining the procedures, the operator shall ensure that the following conditions are applied. for the recovery or disposal of waste resulting from the incineration or co-incineration of waste, in particular the slag, rust ash and filter and boiler dusts, their potential for pollution, in particular their physical and chemical properties and their content of harmful impurities, by means of appropriate analyses. The analyses are to be carried out for the whole soluble fraction and the heavy metals in the soluble and insoluble part. Unofficial table of contents

§ 13 Heat use

Heat which is produced in waste incineration or co-incineration plants and which is not delivered to third parties shall be used in equipment of the operator, insofar as this is technically possible and reasonable according to the type and location of these plants. The operator shall, in so far as the resulting heat, which is not delivered to third parties or which is not used in equipment of the operator, has an electrical terminal power of more than half a megawatt, can be generated, to generate electricity.

Section 3
Measurement and monitoring

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§ 14 Measuring stations

The operator must set up measuring stations prior to the commissioning of an installation for the measurements to determine the emissions or the combustion conditions as well as for the determination of the reference or operating variables. The measuring sites in accordance with the first sentence shall be sufficiently large, easily accessible and so obtained, and shall be selected in such a way that representative and impeccably accurate measurements are ensured. Details shall be determined by the competent authority. Unofficial table of contents

§ 15 Measuring methods and measuring equipment

(1) The operator shall ensure that measurements are carried out using the measurement procedures corresponding to the state of measurement technology and that appropriate measuring equipment which meets the requirements of Annex 4, points 1 to 4, is used. (2) The operator shall ensure that the sampling and analysis of all pollutants, as well as the quality assurance of automatic measuring systems and the reference measurement methods for calibration, are automatically carried out automatically. Measurement systems are carried out in accordance with CEN standards of the European Committee for Standardization. If no CEN standards are available, ISO standards, national standards or other international standards shall be applied to ensure that data of equivalent scientific quality are identified. (3) The operator shall have the proper Installation of measuring and evaluation equipment for continuous monitoring prior to the commissioning of the waste incineration or co-incineration plant of the competent authority by means of the certificate of a unit for calibrations which shall be provided by: of the competent State authority or of the national law (4) The operator has measuring equipment for the continuous determination of the emissions or the combustion conditions as well as for the determination of the reference or Operating variables shall be used by a body which has been notified by a competent authority in accordance with national law pursuant to Section 29b (2) of the Federal Immission Protection Act, in accordance with paragraph 5
1.
calibrate and
2.
to be checked for functionality.
(5) The functional capability shall be checked annually by means of parallel measurement using the reference method. The calibration shall be carried out in each case after the establishment and any substantial modification, as soon as the undisturbed operation has been reached, but at the earliest three months and no later than six months after the start of operation. The calibration shall be repeated at least every three years. (6) The operator shall have the reports on the outcome of the calibration and the verification of the functioning of the competent authority within twelve weeks after calibration and verification .

Footnote

Section 15 (4) italics: would have to be correctly "given" Unofficial table of contents

§ 16 Continuous Measurements

The operator shall, taking into account the requirements of Appendix 4, continuously determine, register and evaluate the following parameters:
1.
the mass concentration of the emissions in accordance with Article 8 (1) (1) and (2) and points 2.1, 2.2, 2.3, 3.1 to 3.6, and 4.1 and 4.2 in accordance with Annex 3,
2.
the volume content of oxygen in the exhaust gas,
3.
the temperatures referred to in Article 6 (1) or (2), and Article 7 (1) or (2), and
4.
the operating parameters necessary for the assessment of the proper operation, in particular the exhaust gas temperature, the exhaust gas volume, the moisture content and the pressure.
For this purpose, the operator must equip the waste incineration or co-incineration plants with suitable measuring devices and measuring data computers before they are put into operation. Sentence 1 (1) in conjunction with the second sentence shall not apply in so far as emissions of individual substances in accordance with Article 8 (1) (1) or (2.1), (2.3), (3.1) to (3.5) and (4.1) of Appendix 3 can be proven to be excluded or, if appropriate, in low concentrations. (2) Moisture content measuring equipment is not necessary if the exhaust gas is dried before determining the mass concentration of the emissions. (3) because of the waste or substances used in accordance with Article 1 (1), the type of construction, The competent authority shall waive the continuous measurement of nitrogen dioxide and the determination of the nitrogen dioxide content of nitrogen dioxide emissions of less than 10% of the nitrogen dioxide emissions, or of individual measurements. Allow share by calculation. In this case, the operator shall keep evidence of the proportion of nitrogen dioxide in the calibration and shall submit it to the competent authority upon request. The operator must keep the evidence five years after calibration in each case. (4) Paragraph 1, first sentence, point 1 is not to be applied to gaseous inorganic fluorine compounds, if purification stages for gaseous inorganic chlorine compounds which ensure that the emission limit values referred to in Article 8 (1) (1) (c) and (2) (c) or in point 2.1, 2.2, 3.5, 3.6, 4.1 and 4.2 shall not be exceeded in accordance with Appendix 3. Require the competent authority to collect mass concentrations of emissions in accordance with Article 8 (1) (3) (6) By way of derogation from the first sentence of paragraph 1, the competent authorities may, at the request of the operator, make individual measurements for hydrogen chloride, hydrogen fluoride, sulphur trioxide, and If the operator ensures that the emissions of these pollutants are not higher than the emission limit values laid down for this purpose, sulphur dioxide shall be permitted. (7) The operator has to determine the sulphur content of the sulphur dioxide, in addition to the Measurement of emissions of sulphur dioxide and sulphur trioxide in the exhaust gas the sulphur content of the fuel used should be determined on a regular basis. In doing so, the competent authority shall determine in more detail how it is demonstrated that the levels of sulphur separation are complied with as the daily average. (8) For mercury and its compounds, identified as mercury, the competent authority shall, upon request, be without continuous measurement, where it is reliably demonstrated that the emission limit values referred to in Article 8 (1) (1) (g) and (2) (g) or in Annex 3, points 2.1, 2.2, 3.5, 3.6, 4.1 and 4.2 shall be less than 20 of the emissions limit values of A hundred are taken up. Unofficial table of contents

§ 17 Evaluation and evaluation of continuous measurements

(1) During the operation of the waste incineration or co-incineration plants, the half-hourly average value for each successive half-hour shall be made up of the measured values determined in accordance with § 16 and shall be based on the value of the half-hourly average value for each successive half hour. Convert the reference oxygen content. For substances whose emissions are reduced and limited by means of exhaust gas purification devices, the conversion of the measured values may only be carried out for the periods in which the measured oxygen content is higher than the reference oxygen content. For each day, the average daily average shall be calculated from the half-hourly average values, with reference to the daily operating time, including the starting or departure operations. (2) The operator has for each of the results of the continuous measurements for each The calendar year shall be drawn up and submitted to the competent authority by 31 March of the following year. The operator shall keep the report referred to in the first sentence and the associated records of the measuring instruments five years after the end of the reporting period after the first sentence. In so far as the measurement results of the competent authority are due to appropriate telemetric transmission, the obligation set out in the first sentence shall not be required to submit the measurement report. (3) The operator shall include in the measurement report referred to in paragraph 2:
1.
the frequency and duration of non-compliance with the requirements laid down in Article 6 (1) to (3) or in accordance with Article 7 (1) to (3) and
2.
the records of the registrants in accordance with Article 4 (9).
(4) The operator shall calculate the annual average values in accordance with § 10 on the basis of the daily average values validated in accordance with Appendix 4; for this purpose, the daily average values of a calendar year are to be counted together and by the number of daily average values . The operator shall, for each calendar year, provide proof of the annual average values and shall submit to the competent authority, on request, by 31 March of the following year. Proof of proof shall be kept five years after the end of the detection period. (5) The emission limit values shall be complied with if:
1.
no result of a daily average value validated in accordance with Appendix 4 exceeds the relevant emission limit value in accordance with section 8 (1) (1) and Appendix 3, points 2.1, 2.3, 3.1 to 3.5, and 4.1,
2.
no result of a half-hourly average value validated in accordance with Annex 4 shall exceed the relevant emission limit value in accordance with section 8 (1) (2) and 3 (2.2), 2.3, 3.4, 3.6 and 4.2,
3.
no result falls below the relevant sulphur separation level in accordance with Annex 3, points 3.1 and 3.3, and
4.
no annual average value as determined in accordance with paragraph 4 exceeds the respective emission limit value according to § 10 and Appendix 3, points 2.3, 3.7 and 4.3.
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§ 18 Individual measurements

(1) The operator, after the installation or substantial modification of a waste incineration plant or co-incineration plant, has been notified of the installation by measurements of a waste incineration plant or co-incineration plant according to § 29b (2) in conjunction with § 26 of the Federal Immission Protection Act (Bundes-Immissionsschutzgesetz) (2) The operator has, after the establishment or substantial modification of a waste incineration or waste incineration plant, a waste incineration plant, or a waste incineration plant, or a waste incineration plant, or a waste incineration plant. -co-incineration plant Measurements of a plant according to § 29b (2) in conjunction with § 26 of the Federal Immission Protection Act (Federal Immission Protection Act) to determine whether the requirements of Section 8 (1) (3) or, in the case of the existence of the requirements pursuant to § 16 (6), in accordance with § 8 (1) (1) and (2) or Annex 3 (3) (2.1), (2.2), (3.1) to The measurements shall be carried out in accordance with paragraphs 3 and 4. (3) The measurements shall be carried out every two months at least one day after the date of entry into service of the twelve months following the date of entry into service, followed by recurrent periods of time. shall be carried out at least every twelve months at least on three days. (4) The measurements shall be if the plant is operated with the highest performance for which it is authorised for continuous operation in the case of the waste or substances used during the measurement in accordance with Article 1 (1). (5) For the purpose of monitoring the requirements of § 8 (1) Point 3 shall be the sampling time for measurements for the determination of emissions of substances
1.
Appendix 1 (a) to (c) other than benzo (a) pyrene shall be at least half an hour; it shall not exceed two hours,
2.
Appendix 1 (d) and benzo (a) pyrene shall be at least six hours and shall not exceed eight hours.
For the substances referred to in Annex 1 (d) or Annex 2, the limit of detection of the analytical method used shall not be greater than 0.005 nanograms per cubic metre of exhaust gas. Unofficial table of contents

Section 19 Reports and evaluation of individual measurements

(1) The operator shall draw up a measurement report on the results of the individual measurements in accordance with § 18 and submit it to the competent authority no later than eight weeks after the measurements. The measurement report must contain the following:
1.
Information about the measurement planning,
2.
the result of each individual measurement,
3.
the measurement procedure used, and
4.
the operating conditions which are of importance for the assessment of the measurement results.
(2) The emission limit values shall be deemed to be complied with if no result of a single measurement exceeds a mean value in accordance with Article 8 (1) or in Annex 3. Unofficial table of contents

Section 20 Special monitoring of emissions of heavy metals

(1) Where, due to the composition of the waste or substances referred to in Article 1 (1) or other findings, in particular on the basis of the assessment of individual measurements, emission concentrations of substances according to Appendix 1 (a) and (b) are to be expected. , which may exceed 60 per cent of the emission limit values, the operator shall identify and document the mass concentrations of these substances once a week. Section 18 (5) shall apply. (2) The determination of the mass concentrations referred to in paragraph 1 may be waived if, by means of other tests, for example by means of functional checks of the exhaust gas purification devices, with adequate safety it is possible to establish that the emission limits are not exceeded. Unofficial table of contents

§ 21 disturbances of the holding

(1) The operator shall inform the competent authority without delay from measurements that requirements relating to the operation of a waste incineration or co-incineration plant or for the limitation of emissions are not met. It shall immediately take the necessary measures for proper operation; § 4 (8) (2) and (3) shall remain unaffected. (2) The competent authority shall ensure, by means of appropriate monitoring measures, that the operator
1.
is subject to its legal obligations to ensure proper operation; or
2.
does not take up the plant.
In the case of waste incineration or co-incineration plants which consist of one or more waste incineration lines with common waste gas facilities, the Authority shall be responsible for technically unavoidable failures of the exhaust gas purification facilities in the Permit the period of time to be determined by the emission limit values in accordance with § 8 and Appendix 3 under certain conditions. The emission limit values for organic substances, expressed as total carbon, and carbon monoxide shall not be allowed to deviate from:
1.
Section 8 (1) (1) (b) and (h),
2.
Section 8 (1) (2) (b) and (h) and
3.
Appendix 3, points 2.1, 3.1, 3.2, 3.3, 3.5 and 4.1.
(4) In the cases referred to in paragraph 3, the installation shall no longer be allowed to continue to operate than:
1.
four consecutive hours and
2.
within a calendar year of 60 hours.
The emission limit for the total dust must be a mass concentration of 150 mg/m 3 Exhaust gas, measured as half-hourly average, does not exceed. § 4 (8) and (9), Article 8 (3) and Article 9 (4) shall apply accordingly. Unofficial table of contents

Section 22 Annual reports on emissions

(1) The operator of a large combustion plant which is co-incinerated shall, for the first time in 2016 and then annually, until 31 May of the following year, for each individual installation, shall be responsible for the first sentence of the competent authority in accordance with Article 9 (4) sentence 3. report:
1.
the installed combustion heat output of the combustion plant, in megawatt,
2.
the type of combustion plant: boiler firing, gas turbine, gas engine, diesel engine, other combustion plant with a precise indication of the type of combustion plant,
3.
the date of the holding and the last major change in the combustion plant, including the designation of the essential change;
4.
the total annual emissions, in megagrams per year, of sulphur oxides, expressed as sulphur dioxide, nitrogen oxides, expressed as nitrogen dioxide, and dust, expressed as a total of non-ferrous substances,
5.
the annual operating hours of the combustion plant;
6.
the annual total energy use, in terajoules per year, in relation to the lower calorific value, broken down into the following fuel categories:
a)
coal,
b)
Lignite,
c)
bioliquids,
d)
Torf,
e)
other solid fuels with a precise indication of the name of the solid fuel;
f)
liquid fuels,
g)
Natural gas,
h)
other gases with a precise indication of the name of the gas,
7.
for combustion plants, to be applied to point 3.1.2 of Appendix 3, the sulphur content of the domestic solid fuels used and the degree of sulphur separation achieved, averaged over each month and in the first year of application of point 3.1.2 Appendix 3 also provides the technical justification for why compliance with the rule emission limit values referred to in point 3.1 of Appendix 3 is not feasible,
8.
in the case of combustion plants which are in operation no more than 1 500 operating hours per year in the sliding average over a period of five years, the number of operating hours per year for the reference year and the preceding four calendar years,
9.
an indication as to whether the combustion plant is part of a refinery.
Up to and including the 2015 reference year, the operator of a large combustion plant with a waste co-incineration plant shall each year, by 31 May of the following year, to the competent authority for each installation as referred to in points 4, 6 and 9 of paragraph 1. (3) The supreme state authorities responsible under national law, or the authorities designated by them, shall examine the report in accordance with paragraphs 1 and 2 for plausibility and shall forward the report to the Federal Environment Agency until 31 December 2008. October of the year following the year under review by electronic means for forwarding to the European Commission. The Federal Environment Agency has compiled the reports on statements for each year and three-year periods, and the information on combustion plants in refineries is to be listed separately.

Section 4
Common rules

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Section 23 Publication requirements

The operator of a waste incineration or co-incineration plant shall, after the first calibration of the measuring equipment and thereafter publish once a year, the following:
1.
the results of the emission measurements,
2.
a comparison of the results of the emission measurements with the emission limit values and
3.
an assessment of the combustion conditions.
The provisions of the first sentence shall not apply to any information from which conclusions may be drawn on business or commercial secrets. The competent authority shall determine the nature and format of the publication. Unofficial table of contents

Section 24 Approval of exceptions

The competent authority may, at the request of the operator, grant derogations from the provisions of this Regulation where, taking into account the specific circumstances of the case,
1.
the individual requirements of the Regulation are not or can only be met with disproportionate effort,
2.
whereas, moreover, the emission limitation measures in accordance with the state of the art will be applied,
3.
the level of discharge in accordance with the technical instructions for the clean-keeping of the air is also designed for the emission limit value authorised as an exception, unless the conditions laid down in point 1 are met, and
4.
the requirements of the following directives are met:
a)
Directive 2008 /98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives (OJ L 327, 30.12.2008, p. OJ L 312, 22.11.2008, p. 3, L 127, 26.5.2009, p. 24) (Waste Framework Directive),
b)
Council Directive 96 /59/EC of 16 September 1996 on the disposal of polychlorinated biphenyls and polychlorinated terphenyls (PCB/PCT) (OJ L 206, 22.7.1996, p. 1). 31), as amended by Regulation (EC) No 596/2009 (OJ L 396, 30.12.2009, p. OJ L 188, 18.7.2009, p.
c)
Directive 2010 /75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) (recast) (OJ L 139, 30.4.2010, p. OJ L 334, 17.12.2010, p.17).
(2) By way of derogation from Article 4 (2), the competent authority may authorise waste incineration plants without waste bunkers or a partially open bunker construction method in connection with a targeted air extraction if, by means of structural or operational measures, or Due to the nature of the waste or substances referred to in Article 1 (1), the production of dust and odour emissions shall be kept as low as possible. (3) The competent authority shall document the reasons for the authorisation of exemptions in the Annex to the approval notices, including the justification of the conditions laid down. This information shall be made available to the public. Unofficial table of contents

Section 25 Further requirements and substantial changes

(1) The power of the competent authority to make other or more stringent requirements, in particular in order to avoid harmful environmental effects in accordance with Section 5 (1) (1) of the Federal Immission Protection Act, shall remain unaffected. (2) Has the In the case of an installation on a case-by-case basis, the competent authority has already submitted requirements to prevent adverse environmental effects from air pollution which go beyond the requirements of this Regulation, which shall continue to be relevant. Any further requirements arising out of other legislation or these specific administrative provisions shall remain unaffected. (3) The use of hazardous waste in an installation which is only for the use of non-hazardous waste , according to the first sentence of Article 16 (1) of the Federal Immission Protection Act, it is to be classified as a substantial change of the plant. (4) In accordance with Section 20 (3) of the Federal Immission Protection Act, the competent authority may: Prohibit the operation of a waste incineration or co-incineration plant if: it is not ensured that the person entrusted with the management of the installation is suitable for the management of the plant and that it provides a guarantee for the proper operation of the plant.

Section 5
Final provisions

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§ 26 Accessibility and equivalence of standards and worksheets

(1) The DIN standards referred to in § 2 (19) shall be related to Beuth Verlag GmbH, Berlin. The DVGW worksheets referred to in § 2 (14) are to be obtained from the economic and publishing company Gas und Wasser mbH, Bonn. The above-mentioned DIN standards are listed in the German National Library, the mentioned worksheets are protected by the German Patent and Trademark Office in Munich. (2) The DIN Standards and DVGW Worksheets referred to in § 2 are available. such relevant CEN standards and, in so far as no such CEN standards are available, ISO standards or any other international standards which, in the case of national standards, are subject to equivalent equivalent requirements. Unofficial table of contents

§ 27 Administrative Offences

(1) In the sense of Section 62 (1) (2) of the Federal Immission Control Act, who intentionally or negligently acts in accordance with the provisions of the Federal Immission Control Act
1.
Contrary to § 3 (6) sentence 3, § 4 (2) sentence 1, § 4 (3) sentence 1, § 4 (7) sentence 1, § 4 (8) or § 16 (1) sentence 2, a transfer point or an installation referred to therein shall not be equipted either correctly or not in good time,
2.
contrary to § 4 (1) sentence 1, § 5 (1), § 5 (4), § 6 (1), 2, 3, 8 or 9 sentence 1, § 7 (1), (2) or (3), § 8 (1), § 9 (1) sentence 1, § 13 sentence 1 or sentence 2, § 24 (4) sentence 1 or sentence 2 or § 28 (2), one sentence Waste incineration or co-incineration plant is not properly constructed or is not properly operated,
3.
Contrary to Article 12 (2), first sentence, it does not ensure that the waste referred to therein is not collected separately,
4.
Contrary to Article 12 (4), third sentence, it does not ensure that the waste is transported or intermediately stored in closed containers,
5.
contrary to § 13 sentence 2 of the heat referred to therein, does not generate electricity,
6.
Contrary to § 14, a measuring station is not or is not correctly set up,
7.
Contrary to Article 15 (1), first sentence, it does not ensure that a measurement procedure is used or a measuring device referred to therein is used,
8.
does not ensure that sampling or analysis or quality assurance is carried out in accordance with the standards referred to in Article 15 (2) sentence 1,
9.
, contrary to § 15 (3), the proof referred to there is not presented or presented in good time,
10.
Contrary to Article 15 (4), a measuring instrument shall not be calibrated in time or shall not be calibrated in time, or cannot be checked in due time for its functioning,
11.
Contrary to § 15 (6), § 17 (2) sentence 1, § 19 (1) sentence 1 or § 22 (1) or (2), a report is not presented, not correct, not complete or not in good time,
12.
contrary to the first sentence of Article 16 (1), Article 16 (5) or the first sentence of Article 20 (1), the mass concentration of the emissions referred to therein, the volume of oxygen mentioned therein, the temperature or the operating quantity referred to in that sentence, shall not be Correct or non-timely identification, not registered, not correct or not registered in time, not evaluated correctly or not in time, or not documented in good time, not correct or not documented in time,
13.
, contrary to the second sentence of Article 16 (3), second sentence, third sentence, no proof, not correct or complete, shall not be presented, whether or not presented in good time or not, or kept for at least five years,
14.
an enforceable arrangement in accordance with § 16 (7) sentence 2,
15.
Contrary to the second sentence of Article 17 (1), a reading of a measured value for periods other than the periods mentioned therein,
16.
shall not, contrary to the second sentence of Article 17 (2), keep a report or a record referred to therein for at least five years,
17.
, contrary to Article 18 (1), a combustion condition referred to in paragraph 18 (1) cannot be verified or
18.
does not allow a measurement referred to in paragraph 18 (2) to be carried out in the prescribed manner or not in a timely manner,
19.
Contrary to the first sentence of Article 21 (1), a communication does not make, not correct or not, in time,
20.
Contrary to § 23 sentence 1, a publication does not make a publication, not correct, not complete or not in time.
(2) In the sense of Section 62 (1) (7) of the Federal Immission Control Act, who intentionally or negligently acts in the sense of the law
1.
, contrary to Article 10 (1) or (2), an installation is not established correctly or is not properly operated, or
2.
Contrary to § 17 (4) sentence 2 or sentence 3, proof not, not correct or complete, is not, not correct, not complete or not stored in time or not stored in time or not stored for at least five years.
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Section 28 Transitional arrangements

(1) For existing installations,
1.
the requirements of this Regulation, with the exception of § 10, as from 1 January 2016,
2.
the requirements of § 10 as from 1 January 2019.
(2) In the case of existing installations in which the residence time specified in § 6 (3) cannot be achieved due to particular technical difficulties, this requirement shall not be met at the latest in the case of a new direction of the combustion line or of the (3) A waste incineration or co-incineration plant shall be expanded by the addition of one or more waste incineration or co-incineration lines in such a way as to ensure that the existing lines and the new lines to be re-incinerated are: together, the requirements for the new installation shall be determined Lines according to the requirements of the second and third sections, for the existing lines, the requirements according to this provision are to be determined. (4) By way of derogation from paragraph 1, existing waste incineration plants must meet the requirements of § 8 (1) Point 1 (f) and Article 8 (1) (2) (f) for nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, only from 1 January 2019. (5) By way of derogation from paragraph 1, existing plants for the production of Cement clinker and cements as well as plants for firing lime the requirements of Appendix 3 Point 2.1 (d) at the latest from 1 January 2019; up to this date the requirements of the Regulation on the incineration and co-incineration of waste are in the version of the Notice of 14 August 2003 (BGBl. 1633), as defined by Article 2 of the Regulation of 27 January 2009 (BGBl). (6) By way of derogation from paragraph 1 (2), existing waste incineration plants shall not be subject to the requirements of Article 10 (1) (1). (7) By way of derogation from Paragraph 1 (2) shall not apply to existing large combustion plants which are co-incinerated with waste, the requirements of Annex 3 (3.7) (a). Unofficial table of contents

Appendix 1 (to § 8 (1), § 18 (5) and § 20 (1))
Emission limit values for carcinogenic substances

(Fundstelle: BGBl. I 2013, 1057)

The following emission limit values shall apply to the carcinogenic substances referred to in points (a) to (d):
a)
Cadmium and its compounds, expressed as cadmium,
Thallium and its compounds, expressed as thallium,
a total of 0.05 mg/m 3 ,
b)
Antimony and its compounds, expressed as antimony,
Arsenic and its compounds, expressed as arsenic,
lead and its compounds, as lead,
chromium and its compounds, expressed as chromium,
Cobalt and its compounds, expressed as cobalt,
copper and its compounds, expressed as copper,
Manganese and its compounds, indicated as manganese,
nickel and its compounds, expressed as nickel,
Vanadium and its compounds, expressed as vanadium,
Tin and its compounds, expressed as tin,
a total of 0.5 mg/m 3 ,
c)
Arsenic and its compounds (except arsenic hydrogen),
specified as arsenic,
benzo (a) pyrene,
Cadmium and its compounds, expressed as cadmium,
water-soluble cobalt compounds, expressed as cobalt,
Chromium (VI) compounds (other than barium chromate and
lead chromate), indicated as chromium
a total of 0.05 mg/m 3
or
Arsenic and its compounds, expressed as arsenic,
benzo (a) pyrene,
Cadmium and its compounds, expressed as cadmium,
Cobalt and its compounds, expressed as cobalt,
chromium and its compounds, expressed as chromium,
a total of 0.05 mg/m 3
and
d)
Dioxins and furans according to Appendix 2
a total of 0.1 ng/m 3 .
Unofficial table of contents

Appendix 2 (to Appendix 1 (d))
Equivalence factors

(Fundstelle: BGBl. I 2013, 1058)
For the total value for polychlorinated dibenzodioxins, dibenzofurans and diPCBs to be formed in accordance with Appendix 1, the concentrations of the following dioxins, furans and di-PCBs, determined in the exhaust gas, are to be found with the indicated equivalence factors. multiply and summate.

Substance equivalence factor
Polychlorinated dibenzodioxins (PCDD) WHO-TEF 2005
2,3,7,8 -Tetrachlorodibenzodioxin (TCDD) 1
1,2,3,7,8 -pentachlorodibenzodioxin (PeCDD) 1
1,2,3,4,7,8 -Hexachlordibenzodioxin (HxCDD) 0.1
1,2,3,7,8,9 -Hexachlordibenzodioxin (HxCDD) 0.1
1,2,3,6,7,8 -Hexachlordibenzodioxin (HxCDD) 0.1
1,2,3,4,6,7,8 -heptachlorodibenzodioxin (HpCDD) 0.01
Octachlorodibenzodioxin (OCDD)

0.0003
Polychlorinated dibenzofurans (PCDF) WHO-TEF 2005
2,3,7,8 -Tetrachlorodibenzofuran (TCDF) 0.1
2,3,4,7,8 -pentachlorodibenzofuran (PeCDF) 0.3
1,2,3,7,8 -pentachlorodibenzofuran (PeCDF) 0.03
1,2,3,4,7,8 -Hexachlordibenzofuran (HxCDF) 0.1
1,2,3,7,8,9 -Hexachlordibenzofuran (HxCDF) 0.1
1,2,3,6,7,8 -Hexachlordibenzofuran (HxCDF) 0.1
2,3,4,6,7,8 -Hexachlordibenzofuran (HxCDF) 0.1
1,2,3,4,6,7,8 -heptachlorodibenzofuran (HpCDF) 0.01
1,2,3,4,7,8,9 -heptachlorodibenzofuran (HpCDF) 0.01
Octachlorodibenzofuran (OCDF)

0.0003
Polychlorinated biphenyls WHO-TEF 2005
Non ortho PCB
PCB 77 0.0001
PCB 81 0.0003
PCB 126 0.1
PCB 169 0.03
Mono ortho PCB
PCB 105 0.00003
PCB 114 0.00003
PCB 118 0.00003
PCB 123 0.00003
PCB 156 0.00003
PCB 157 0.00003
PCB 167 0.00003
PCB 189 0.00003
Unofficial table of contents

Appendix 3 (to § 9, § 10 (2), § 16 (1) and (4), § 17 (1) and (5)), § 18 (2), § 19 (2), § 21 (3), § 22 (1) and § 28 (5) and (6))
Emission limit values for co-incineration of waste

(Fundstelle: BGBl. I 2013, 1059-1065)

Appendix 3 is used to establish emission limit values for waste co-incineration plants. If a fixed emission limit value or a fixed reference oxygen content is already specified in this installation for certain emission parameters, the emission limit value or the reference oxygen content shall replace the calculation of the emission limit value or the reference oxygen content. Emission limit value or the reference oxygen content for this emission parameter. The fixed emission limit values laid down in this Annex shall apply to the waste co-incineration plants concerned, taking into account the exceptions mentioned therein.
1.
Calculation of the emission limit values for co-incineration of waste Insofar as no fixed emission limit values or fixed reference oxygen contents are specified in this Appendix, the following formula (mixing rule) shall be applied. The mixing rule shall be used for the calculation of the emission limit values for each emission parameter regulated under Article 5 (1) and for the calculation of the reference oxygen content. Emission parameters within the meaning of this Appendix are the pollutants listed in § 5 (1), for which daily average values, half-hourly average values or mean values are determined over the respective sampling time.
VWaste:
Exhaust gas flow resulting from the incineration of the maximum permissible fraction of the waste or substances referred to in Article 1 (1), including the additional fuel required for the incineration of these substances. Where the permitted proportion of waste or substances in accordance with Article 1 (1) is less than 10% of the total heating performance of a co-incineration plant, the associated exhaust gas flow shall be based on an assumed quantity: of 10 per cent of these wastes or substances in accordance with Article 1 (1).
VProcess:
Remaining part of the normalized exhaust gas stream.
CWaste:
Emission limit value for the emission parameters or reference oxygen content listed in Article 8 (1) for the reference oxygen content specified in Article 8 (2).
CProcess:
The emission value and the reference oxygen content in accordance with the tables in this Annex. For all other emission parameters, for which no fixed emission limit values or fixed reference oxygen levels are specified in this Annex, the relevant provisions shall apply, as in the case of the relevant provisions, such as 13. BImSchV or TA Luft-in the course of the combustion of the emission values, which are normally permitted, or Reference oxygen content. In the event that such guidelines do not exist, the emission limits laid down in the permit shall be: Use the reference oxygen content. In the absence of such provisions, actual emissions or oxygen content shall be based on the operation of the plant without the use of waste or substances in accordance with Article 1 (1).
C:
Calculated emission limit value or calculated reference oxygen content for co-incineration plants resulting from the application of the formula listed above.
2.
Installations for the production of cement clinker or cements, as well as plants for burning lime, in which waste or substances are co-incinerated in accordance with Article 1 (1). Emissions shall be subject to compliance with the emission limit values, to a the fixed reference oxygen content of 10 per cent. The emission limit values laid down in Article 8 (1) (3) for the categories of pollutants to be grouped (heavy metals, benzo (a) pyrene, polychlorinated dibenzodioxins and dibenzofurans) shall apply, taking into account the provisions of the first sentence of the Reference oxygen content.
2.1
Fixed emission limit values (daily average values in mg/m 3 ) Emission Parameter C
a) Total dust 10
b) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 10
c) gaseous inorganic fluorine compounds, indicated as hydrogen fluoride 1
d) Nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide in
(aa) installations for the production of cement clinker and cement 200
(bb) installations for the burning of lime 350
e) Sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide 50
f) organic substances, expressed as total carbon 10
g) Mercury and its compounds, indicated as mercury 0.03
h) Ammonia, provided that a process for the selective catalytic or non-catalytic reduction is used to reduce the emissions of nitrogen oxides 30
2.1.1
In the event of substantial changes to these installations by 31 December 2018, it is necessary to consider whether the requirements for limiting nitrogen monoxide and nitrogen dioxide for new plants can be complied with at a proportionate cost. The possibilities of further reducing the emissions of nitrogen monoxide and nitrogen dioxide from the exhaust gas in plants by fire engineering or other measures corresponding to the state of the art are to be exploited.
2.1.2
The competent authority may, at the request of the operator, authorise exemptions for sulphur dioxide and total carbon dioxide, provided that these exceptions are necessary on the basis of the composition of the natural raw materials and can be excluded that: additional emissions of total carbon and sulphur dioxide due to the use of waste or substances in accordance with Article 1 (1).
2.1.3
The competent authority may, at the request of the operator, authorise exemptions for mercury and its compounds, provided that these exceptions are necessary on the basis of the composition of the natural raw materials and may be excluded by: the use of waste and substances in accordance with § 1 (1) additional emissions of mercury are produced and a daily average of up to 0.05 mg/m 3 is not exceeded. The possibilities to further reduce emissions of mercury and its compounds, indicated as mercury, from the exhaust gas by means of fire engineering or other measures corresponding to the state of the art, must be exploited.
2.1.4
The competent authority may, at the request of the operator, authorise exemptions for ammonia, provided that these exceptions are necessary on the basis of the composition of the natural raw materials and can be excluded from the use of waste. or substances in accordance with Article 1 (1), additional emissions of ammonia are produced. In this case, the ammonia limit value shall be added to the raw material-related ammonia emissions to be determined by comparison measurements; the emissions resulting from waste are not taken into account.
2.2
Fixed emission limit values (half-hourly average values in mg/m 3 ) Emission Parameter C
a) Total dust 30
b) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 60
c) gaseous inorganic fluorine compounds, indicated as hydrogen fluoride 4
d) Sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide 200
e) Mercury and its compounds, indicated as mercury 0.05
2.2.1
The competent authority may, at the request of the operator, authorise exemptions for sulphur dioxide and total carbon dioxide, provided that these exceptions are necessary on the basis of the composition of the natural raw materials and can be excluded that: additional emissions of total carbon and sulphur dioxide are produced by the incineration of waste or substances in accordance with Article 1 (1).
2.2.2
The competent authority may, at the request of the operator, authorise exemptions for mercury and its compounds, provided that these exceptions are necessary on the basis of the composition of the natural raw materials and may be excluded by: the use of waste and substances in accordance with § 1 (1) additional emissions of mercury are produced and a half-hourly average value of up to 0.1 mg/m 3 is not exceeded. The possibilities to further reduce emissions of mercury and its compounds, indicated as mercury, from the exhaust gas by means of fire engineering or other measures corresponding to the state of the art, must be exploited.
2.3
Fixed emission limit values (annual mean values in mg/m 3 )
Emission Parameters C
Nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide 200

By way of derogation from the emission limit value for nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, an emission limit value of 350 mg/m shall apply to installations for the burning of lime in rotary kilns with rust preheaters 3 .
2.4
Emission limit value for carbon monoxide
2.4.1
The competent authority shall set an emission limit value for carbon monoxide, taking into account the requirements laid down in Article 8 (1).
2.4.2
The competent authority may, at the request of the operator, derogate from the emission limit value set out in paragraph 8 (1) for carbon monoxide, provided that such exceptions are necessary and excluded on the basis of the composition of the natural raw materials , the use of waste or other substances in accordance with Article 1 (1) may result in additional emissions of carbon monoxide.
3.
Combustion plants in which waste or substances are co-incinerated in accordance with Article 1 (1). Emissions shall be used to check whether the emission limit values are complied with, to the following reference oxygen contents:
a)
on the use of solid fossil fuels or biofuels to a fixed reference oxygen content of 6%
b)
in the case of the use of liquid or gaseous fuels, to a fixed reference oxygen content of 3% or
c)
for emission values as set out in Annex 3, points 3.1, 3.2 and 3.3, to the reference oxygen content to be calculated in accordance with Annex 3, point 1.
The emission limit values laid down in Article 8 (1) (3) for the categories of pollutants to be grouped (heavy metals, benzo (a) pyrene, polychlorinated dibenzodioxins and dibenzofurans) shall apply, taking into account the values set out in sentence 1 for each of the groups concerned. Fuel specified in terms of reference oxygen content.
3.1
Emission values (Cmethods) in the use of solid fossil fuels (daily average values in mg/m 3 ) in the case of different combustion heat outputs (in MW):








Emis sions- para- meter 1 MW to < 10 MW10 MW up to < 50 MW50 MW up to 100 MW> 100 MW up to 300 MW> 300 MW
SO2 and SO3 Coal 1 300 400 200 and
Sulphur-
Scheidegrad
≥ 85%
150 and
Sulphur
minde-
rungs-
degree
≥ 85%
Lignite 1 000
Fluidized bed 350 or
Desulphurisation
≥ 75 percent
350 and sulphur-
Scheidegrad
≥ 75 percent
200 and
Sulphur-
Scheidegrad
≥ 85%
NOX 500,
for vertebrae
stratified fire-
300
400,
for vertebrae
stratified fire-
300
300 200 150,
at Braun-
kohlestaub-
humidification 200
CO 150 * 150 150 200
*
In the case of individual furnaces with a thermal output of less than 2.5 MW, the emission value shall only be valid in operation at nominal load.
3.1.1
In the case of installations with a thermal output of 100 MW or more, the requirement for sulphur separation to emissions of less than 50 mg/m 3 for the daily average, at least one degree of sulphur separation shall be observed, which shall be subject to emissions of not more than 50 mg/m 3 for the daily average.
3.1.2
Where, on the basis of the increased sulphur content of the fuels used, the emission values for coal, lignite and fluidised bed listed in the table cannot be complied with at a proportionate cost, the competent authority may: On a case-by-case basis, the Authority shall use higher emission values as the basis for calculation, provided that the thermal input of the combustion is
a)
50 MW to 100 MW, alternatively, a sulphur separation of 93 per cent will not be exceeded;
b)
More than 100 MW to 300 MW an emission limit value of 300 mg/m 3 is not exceeded and, in addition, a sulphur separation rate of at least 93 per cent is not exceeded;
c)
More than 300 MW has an emission limit value of 400 mg/m 3 is not exceeded and, in addition, a sulphur separation rate of at least 97 per cent is not exceeded.
By way of derogation from the first sentence, the competent authority may, on a case-by-case basis, use, on a case-by-case basis, higher emission levels as the basis for calculation in the case of large combustion plants which are co-incineration with waste, provided that the
a)
50 MW to 100 MW as an alternative, a sulphur separation rate of 92 per cent will not be exceeded;
b)
More than 100 MW to 300 MW an emission limit value of 300 mg/m 3 is not exceeded and, in addition, a sulphur separation of at least 92 per cent shall not be exceeded;
c)
More than 300 MW has an emission limit value of 400 mg/m 3 is not exceeded and, in addition, a sulphur separation rate of at least 96 per cent is not exceeded.
In the case of the application of sentence 1 or 2, Cwaste shall be 0 mg/m 3 .
3.1.3
By way of derogation from the emission levels set out in the table, sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide, shall apply to large combustion plants with a thermal output of 300 MW or more in the case of existing waste co-incineration plants. an emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average. The requirements for the degree of sulfur separation remain unaffected.
3.1.4
By way of derogation from the emission levels set out in the table, nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, shall apply to large combustion plants with a thermal output of 300 MW or more, in the case of existing waste co-incineration plants; or an emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average.
3.2
Emission values (Cmethods) in the use of biofuels (daily average values in mg/m 3 ) in the case of different combustion heat outputs (in MW):






Emis sions- para- meter < 50 MW50 MW up to 100 MW> 100 MW up to 300 MW> 300 MW
SO2 and SO3 Natural wood 200 200 200 150
other
Biofuel
350
NOX Natural wood 250 250 200 150
other
Biofuel
400
CO Natural
wood and
Wood waste
150 * 150 200 200
other
Biofuel
250 * 250 250 250
*
In the case of individual furnaces with a thermal output of less than 2.5 MW, the emission value shall only be valid in operation at nominal load.
3.2.1
By way of derogation from the emission levels set out in the table, sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide, shall apply to large combustion plants with a thermal output of 300 MW or more in the case of existing waste co-incineration plants. Emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average.
3.2.2
By way of derogation from the emission levels set out in the table, nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, shall apply to existing waste co-incineration large combustion plants with a firing heat output of
a)
50 MW to 100 MW an emission limit value of 300 mg/m 3 for daily mean value and 600 mg/m 3 for the half-hour average;
b)
More than 100 MW up to 300 MW an emission limit value of 250 mg/m 3 for daily mean value and 500 mg/m 3 for the half-hour average;
c)
More than 300 MW has an emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average.
3.3
Emission values (Cmethods) in the use of liquid fuels (daily average values in mg/m 3 ) in the case of different combustion heat outputs (in MW):






Emis sions- para- meter < 50 MW50 MW up to 100 MW> 100 MW up to 300 MW> 300 MW
SO2 and SO3 Heating oil EL 10. BImSchV
other
Fuel
850 350 200 and
Sulphur
Degree of reduction
≥ 85%
150 and
Sulphur
Degree of reduction
≥ 85%
NOX Heating oil EL 250 200 150 100
other
Fuel
350 300
CO 80 80 80 80
3.3.1
In the case of the use of light heating oil, the emission value (Cmethod) for sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide, shall be the emission value, as measured in each case for the operation without the use of waste or substances in accordance with Article 1 (1). In the case of installations with a thermal output of more than 300 MW, sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide, shall be the emission value (Cmethod) of 150 mg/m. 3 ,
3.3.2
In the case of installations with a thermal output of 100 MW or more, the requirement for sulphur separation to emissions of less than 50 mg/m 3 for the daily average, at least one degree of sulphur separation shall be observed, which shall be subject to emissions of not more than 50 mg/m 3 for the daily average.
3.3.3
By way of derogation from the emission levels set out in the table, sulphur dioxide and sulphur trioxide, expressed as sulphur dioxide, shall apply to existing large combustion plants incinerating waste, with the exception of the use of light heating oil, with a Combustion heat output of
a)
More than 100 MW to 300 MW an emission limit value of 250 mg/m 3 for daily mean value and 500 mg/m 3 for the half-hour average;
b)
more than 300 MW an emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average.
3.3.4
By way of derogation from the emission levels set out in the table, nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, shall apply to existing waste co-incineration large combustion plants with a firing heat output of
a)
50 MW to 100 MW and the use of other liquid fuels as a light heating oil, an emission limit value of 350 mg/m 3 for daily mean value and 700 mg/m 3 for the half-hour average;
b)
More than 100 MW up to 300 MW an emission limit value of 200 mg/m 3 for daily mean value and 400 mg/m 3 for the half-hour average;
c)
More than 300 MW has an emission limit value of 150 mg/m 3 for daily mean value and 300 mg/m 3 for the half-hour average.
3.4
Combustion plants for gaseous fuels When gaseous substances from the pyrolysis or gasification of solid or liquid waste are used in combustion plants for gaseous fuels, the competent authority shall have a continuous supply of gaseous fuels. the emission limit value (daily mean value and half-hourly average value) for SO2 and SO3 and for NOX, taking into account the specific fuels referred to in the Regulation on large-scale fire, gas turbine and combustion engine installations, and the corresponding reference oxygen content in the permit. For all other emission parameters, paragraphs 3.5 to 3.7 and as Cprocedures shall be an emission value for carbon monoxide as the daily mean value of 80 mg/m 3 or in the case of natural gas of 50 mg/m 3 in each case with a reference oxygen content of 3 percent.
3.5
Fixed emission limit values for all fuels (daily average in mg/m 3 ) Emission Parameter C
a) Total dust 10
b) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 20
c) gaseous inorganic fluorine compounds, indicated as hydrogen fluoride 1
d) organic substances, expressed as total carbon 10
e) Mercury and its compounds, indicated as mercury 0.03
3.5.1
By way of derogation from the specific emission limit values, in the case of fluidised bed furnaces, a mean daily value for gaseous inorganic chlorine compounds, expressed as hydrogen chloride, of 100 mg/m shall be considered. 3 .
3.5.2
By way of derogation from the specific emission limit values for gaseous inorganic fluorine compounds, expressed as hydrogen fluoride, existing waste-co-incineration large combustion plants shall be subject to the operation of the waste-gas desulphurisation system is required to withdraw heat from the exhaust gas stream upstream of the exhaust gas desulphurisation system by means of rotating or fixed storage masses as a heat transfer medium, which heat transfer medium to reheat the exhaust gas stream after the exhaust gas desulphurisation system is used, a daily average for gaseous inorganic Fluorine compounds, expressed as hydrogen fluoride, of 10 mg/m 3 .
3.6
Fixed emission limit values for all fuels (half-hourly average values in mg/m 3 ) Emission Parameter C
a) Total dust 20
b) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 60
c) gaseous inorganic fluorine compounds, indicated as hydrogen fluoride 4
d) Mercury and its compounds, indicated as mercury 0.05

By way of derogation from the specific emission limit values, a half-hourly average value for gaseous inorganic chlorine compounds, expressed as hydrogen chloride, of 200 mg/m, shall apply in the case of fluidised bed furnaces. 3 . By way of derogation from the specific emission limit values for gaseous inorganic fluorine compounds, expressed as hydrogen fluoride, existing waste-co-incineration large combustion plants shall be subject to the operation of the waste-gas desulphurisation system is required to withdraw heat from the exhaust gas stream upstream of the exhaust gas desulphurisation system by means of rotating or fixed storage masses as a heat transfer medium, which heat transfer medium to reheat the exhaust gas stream after the exhaust gas desulphurisation system is used, a half-hourly average value for gaseous inorganic Fluorine compounds, expressed as hydrogen fluoride of 15 mg/m 3 .
3.7
Fixed emission limit values for the use of solid fuels, biofuels and liquid fuels in plants with a heating capacity of 50 MW or more (annual mean values in mg/m 3 ) Emission Parameter C
a) Nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, in the case of a thermal heat output of
aa) 50 MW to 100 MW 250
bb) more than 100 MW 100
b) Mercury and its compounds, indicated as mercury 0.01

The monitoring of the prescribed limits of emissions of mercury and its compounds, indicated as mercury, shall begin six months after the notification of a suitable measuring device, but no later than 1 January 2019.
4.
Other installations, d. h. Installations not listed in point 2 or 3 where waste or substances are co-incinerated in accordance with Article 1 (1). Emissions shall be subject to compliance with the emission limit values for the purpose of the respective procedure the relevant reference oxygen content, which may, however, be at most 11 per cent. In the case of installations which are operated with a predominant share of operational secondary air and in the case of combustion with pure oxygen or significantly oxygen-enriched air, the Authority shall, at the request of the operator, provide the Emission limit values refer to a reference oxygen content adapted to the process conditions of the plant, or to dispense with the establishment of a reference oxygen content. The emission limit values laid down in Article 8 (1) (3) for the categories of pollutants to be grouped (heavy metals, benzo (a) pyrene, polychlorinated dibenzodioxins and dibenzofurans) shall apply, taking into account the provisions of the first sentence or the second sentence of paragraph 2. the reference oxygen content.
4.1
Fixed emission limit values (daily average in mg/m 3 ) Emission Parameter C
a) Total dust 10
b) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 10
c) organic substances, expressed as total carbon 10
d) Mercury and its compounds, indicated as mercury 0.03
4.2
Fixed emission limit values (half-hourly average values in mg/m 3 ) Emission Parameter C
a) Gaseous inorganic chlorine compounds, indicated as hydrogen chloride 60
b) Mercury and its compounds, indicated as mercury 0.05
4.3
Fixed emission limit values for fixed (except for the exclusive use of biofuels) and liquid fuels for installations with a thermal output of more than 50 MW (annual mean values in mg/m 3 ) Emission Parameter C
Nitrogen monoxide and nitrogen dioxide, expressed as nitrogen dioxide, in the case of a thermal heat output of
a) 50 MW to 100 MW 250
b) more than 100 MW 100

Footnote

Appendix 3, point 3.1.3. Italics: Should "sulfur trioxide" should be correct Unofficial table of contents

Appendix 4 (to § 15 (1), § 16 (1) and Article 17 (5))
Requirements for the continuous measuring equipment and the validation of the measurement results

(Fundstelle: BGBl. I 2013, 1066)


1.
The value of the confidence interval of 95 percent of a single measurement result shall not exceed the following percentages of the emission limit set for the daily mean value:
a)
Carbon monoxide 10 percent,
b)
Sulphur dioxide 20 percent,
c)
Nitrogen oxide 20 percent,
d)
Total dust 30 percent,
e)
Organically bound total carbon 30 percent,
f)
Hydrogen chloride 40 percent,
g)
Hydrogen fluoride 40 percent,
h)
Mercury 40 percent.
2.
For total dust, by way of derogation from point 1, the percentage referred to in paragraph 1 shall refer to the emission limit set for the half-hourly average value, provided that the emission limit is a daily average of 10 mg/m. 3 is less than.
3.
The validated half-hour and daily average values shall be determined on the basis of the measured half-hourly average values and after deduction of the confidence interval determined in the calibration.
4.
The half-hourly average values before deduction of the measurement uncertainty (normalized values) determined in the calibration must be available for the purposes of the annual emission rates to be determined in accordance with § 22.
Unofficial table of contents

Appendix 5 (to § 2 (10))
Conversion formula

(Fundstelle: BGBl. I 2013, 1067)
Where emission limit values are related to reference oxygen content in the exhaust gas, the mass concentrations measured in the exhaust gas shall be converted according to the following equation:

EB =
Mass concentration, based on the reference oxygen content
EM =
measured mass concentration
OB =
Reference oxygen content
OM =
measured oxygen content