Key Benefits:
| Chapter 1 | Scope of application |
| Chapter 2 | Definitions |
| Chapter 3 | Application, environmental approval, popenings and endorsements |
| Chapter 4 | Inline and Operations |
| Chapter 5 | Waste Receipt |
| Chapter 6 | Luter emissions |
| Chapter 7 | Residual products |
| Chapter 8 | Soil and ground water |
| Chapter 9 | Emissions of waste water from flue-gas treatment |
| Chapter 10 | Havari, technically unavoidable standings and so on. |
| Chapter 11 | Reporting and Public Announcement |
| Chapter 12 | Punishment |
| Chapter 13 | Entry into force and transitional provisions |
| Appendix 1 | Requirements for measurements of air emissions |
| Appendix 2 | Evaluation of compliance with emission limit values for air emissions |
| Appendix 3 | emission limit values for air from waste incineration plants |
| Appendix 4 | Luter emissions from co-incineration plants |
| Appendix 5 | Equivalence factors for dibenzo-p-dioxins and dibenzofurans |
| Appendix 6 | Wasted water from gas treatment |
Annuntation of plants burning waste 1)
In accordance with section 7 (2), 1, no. 1-3, and paragraph 1. 3, no. Paragraph 13, paragraph 13. One and two, section 29, section 35, section. 2, section 39, paragraph. 3 and 4, section 41 (a) (a), 3, section 41 (b) (b). 1, Section 79 b, section 79, c, paragraph 1. 1, no. Paragraph 1, section 80, paragraph. Rule 110 (1) and 110 (1). 3, in the law of environmental protection, cf. Law Order no. 879 of 26. June 2010, as amended by law no. 446 of 23. May 2012 and law no. 1149 of 11. December 2012 :
Chapter 1
Scope of application
§ 1. The notice lays down rules for the establishment and operation of waste incineration plants and waste incineration plants, which are incinerating or liquified waste.
Paragraph 2. The notice is in addition to the announcement of the approval of the list company.
§ 2. The commanders shall comprise all the incinerators or co-incineration lines, afloading and storage facilities, processing plants in the plant area, waste, fuel and air support systems, boilers, installations for the treatment of smoke gas, installations on the premises ; the place of treatment or storage of residues and waste water, chimneys, equipment and systems for the control of the incineration of the co-incineration and the monitoring and registration of the incineration or co-incineration conditions.
Paragraph 2. In the case of other processes other than oxidation, such as pyrolysis, gas flow or meltdown, the incinerator or waste incineration plant shall be the result of both the heat-handling process and the subsequent internal combustion process.
§ 3. The commuting does not include :
1) Facilities only dealing with radioactive waste.
2) Test facilities used for research, development and testing to improve the combustion process and which processes less than 50 tonnes of waste per year.
3) Installations authorised or registered only to dispose of the entire carcasses according to the rules applicable to animal by-products and derived products that are not intended for human consumption.
4) Facilities intended solely for biomass waste, as defined in section 4 (2), 6.
5) Gas or pyrolysis installations, the gases of which from this heat treatment of waste are cleansed in such a way that they no longer constitute waste prior to incineration, and they cannot cause any higher emissions than those caused by the loss of natural gas.
6) Offers for off-shore plants which burn waste resulting from prospecting and exploiting oil and gas resources.
Chapter 2
Definitions
§ 4. For the purposes of this notice :
1) Wastes : Any kind of flat-rate or liquid waste as defined in the notice of waste.
2) Waste incineration plants : Any stationary or mobile, technical unit and equipment used exclusively for heat treatment of waste regardless of whether the heat of the incinerator is recysable or not. This includes the incineration of waste at oxidation, and other heat treatment processes such as pyrolysis, gassing or meltdown, when the products of this treatment thereftain are then incinerated.
3) Waste incineration plants : Any stationary or mobile installation whose main purpose is to produce energy or produce material products and which uses waste as a normal fuel or subsidy. This includes the co-incineration of waste at oxidation and other heat treatment such as pyrolysis, gassing or meltdown, when the products of this treatment thereftain are then incinerated. If waste incineration takes place in such a way that the main purpose of the plant is not to produce energy or produce material products, but thermite thermite treatment of waste, the plant is considered to be a waste incineration plant.
4) AMS check : Automatic target system.
5) Standing waste incinerator :
a) Waste incineration plants operating and approved by the 28th. December 2002.
b) Waste incineration plants approved by the 28th. December 2002, provided that the plant was put into operation by the 28th. December 2003.
c) Waste incineration plants which, according to the opinion of the approval authority, submitted a complete application for approval by 28. in December 2002, provided that the installation is approved and operated by the 28th. December 2004.
6) BiomasseWaste :
a) Vegetabilly wastes from agriculture and forestry.
b) Vegetable waste from the food industry if the heat of the incinerator is used.
c) Fibre-containing vegetable waste from the production of virgin pulp and paper from pulp if it is co-incinerated at the place of production, and the heat of the incinerator.
d) Cork waste.
(e) Waste other than wood waste which may contain halogenated organic compounds or heavy metals as a result of treatment with wood preservatives or coating, in particular, of such wood waste from the construction and demolition of the construction of the products.
7) Mixed municipal waste : household waste and trade, industrial and institutional waste which, by its nature and composition, corresponds to household waste other than separately at the source of the collected fractions referred to in pos (heading No). 20 01 and other waste referred to under heading No s. 20 02 in the deposition on waste.
8) Dioxins and furans : the polychlorinated dibenzo-p-dioxins and dibenzofurans listed in Annex 5.
9) EBK : Afterburners of combustion.
10) Actual operational time : Any period during which waste is incinerated, except for the period during start-up and shutdown, where waste is not incinerated.
11) " Farligt waste " means any kind of solid or liquid waste defined as hazardous waste in the notice of waste.
12) Shutdown : decommissioning includes the time space from all waste in the kiln for the oven is completely cooled off.
13) Nominal capacity : the total combustion capacity of the ovens as a waste incineration plant or a waste incineration plant, as specified by the constructor and confirmed by the undertaking, taking account of the fallability of the waste ; the calorific value of the quantity of waste which may be incinerated in the hour.
14) Normal m 3 : m 3 air at a temperature of 273.15 K, pressure of 101,3 kPa dry gas.
15) New waste incineration plant : any waste incinerator not covered by the definition of existing waste incineration plants.
16) Start up : up to the time period up to the temperature of the afterburgings have reached 850 ° C and 1,100 ° C and the entry of waste into the kiln.
17) Residual products : any liquid or solid waste originating from a waste incineration plant or waste incineration plant.
18) Water-supply company : waste water supply company subject to section 2 (2). Paragraph 1, in the organisation and economic situation of the water sector.
Chapter 3
Application, environmental approval, popenings and endorsements
Requirements for the application
§ 5. An application for environmental approval in accordance with Article 33 (3) of the Environmental Protection Act. 1, in addition to the information required by the notification for the approval of the list undertaking, describe the measures to be taken by the establishment in order to ensure that :
1) The waste incineration or waste incineration plant shall be designed, equipped, maintained and operated in such a way as to satisfy the requirements of this notice, taking into account the categories of waste incinerated or co-incinerated.
2) The heat generated by combustion and co-incineration is used to the extent that it is practicable in the production of heat, steam or electricity.
3) Residual products are as much as possible in terms of quantity and harmlessness. The goods shall be re-used where appropriate.
§ 6. The application shall include a list of the types of waste which are intended to be processed, if possible on the basis of at least the types of waste in the notice of waste, and with information on the quantity of waste, where appropriate.
Paragraph 2. The application shall indicate whether the waste type is hazardous waste. For hazardous waste, the application must contain information about quantities distributed on EAK codes.
Outgoing public in the application for environmental approval
§ 7. In the case of waste incineration and waste incineration plants covered by this notice, which are not covered by Annex 1 in the notice of the approval of the list company, the rules on the prior disclosure of documents shall be laid down in Annex 1 to Annex 1 ; 1 undertakings in the notification of the use of the list undertaking by analogs.
Paragraph 2. The change or extension of a plant to incinerate or coincinerate non-hazardous waste, which means that the plant may, in future, be able to deal with hazardous waste, are considered to be a significant change or extension, cf. the announcement of the approval of the list company.
Approval, injunction and permit
§ 8. The approval authority or the supervisory authority shall, by approval after the Act of Title 33, or by injunction under Article 41 of the law, ensure that the requirements of this notice shall be at least complied with.
Paragraph 2. The Municipal Board shall be required to notify the local authorities of the section 28 (2) of the Environmental Protection Act on the granting of approval. 3, for waste incineration and waste incineration plants, ensure that the requirements of section 35-41, as a minimum are met.
§ 9. The approval authority shall determine, in addition to the conditions to be determined in accordance with the date of notification for the approval of the list undertaking, the terms of an authorization under the section 33 of the Act or in the light of the Act of Title 41, whether :
1) The types of waste which must be treated, if possible on the basis of at least the types of waste in the notice of waste and with information on the quantity of waste, where appropriate.
2) The nominal capacity of waste incineration or waste incineration plants.
3) Limits for air emissions.
4) The methods of sampling, measuring techniques and measuring frequencies to be used to comply with the terms of emission control.
5) The maximum allowable period in which emissions to the air must exceed the emission limit values set by technically unavoidable surgeements, disturbances or failure of purification facilities or measurement devices.
6) Direction and location of sampling points for sampling to control air emissions.
7) Where in the afterburgings of the EBK temperature are to be carried out.
8) Direction and operation of the installation, cf. § § 13-18.
9) The company must notify the supervisory authority immediately if the auditing measurements show that the emission limit values in the approval or the injunction have been exceeded.
10) Body of organic carbon in the ladle and the bundle.
11) Container capacity for polluted water caused by waste or fire extinguishing.
Paragraph 2. For installations incinerator or incinerator hazardous waste, the approval authority or the supervisory authority shall be determined in addition to the conditions laid down in paragraph 1. 1, terms of an approval or an opening statement of :
1) The quantity of hazardous waste distributed on waste type with corresponding EAC code in the notice of waste.
2) Minimum and maximum mass flow of hazardous waste, its lowest and highest combustible value and its maximum polychlorinated biphenyls, pentachlorophenol, chlorine, fluoride, sulphur and heavy metals and other pollutants.
Paragraph 3. For waste incineration and waste incineration plants, with wet smoke gas purification and direct discharge of waste water to the recipient, the approval authority or the supervisory authority shall be determined in addition to the conditions referred to in paragraph 1. 1, terms of an approval or an opening statement of :
1) Emission limit values for waste water.
2) The requirements for the pH, temperature and flow of the spilling water source.
3) The methods of sampling, measurement methods and frequency of measurement used to comply with the terms of emission control.
4) The maximum allowable period in which the emissions of waste water must exceed the set emission limit values due to technical unavoidable surgeons, disturbances or failure of purification facilities or measurement devices.
5) Where measurements and sampling for the control of waste water discharges shall be positioned.
Paragraph 4. In the case of waste incineration and waste incineration plants with wet smoke gas cleaning and discharges for waste-water utilities, the municipal management board shall lay down conditions in a permit for approval under the section 28 (3) of the law. 3, in accordance with paragraph 1. (3) (no) 1-5.
§ 10. The Supervisory Authority shall periodically review the approval conditions for plants covered by Annex 2 to the notice of the approval of the list company and shall amend them if necessary, cf. Act 41.
Chapter 4
Inline and Operations
General provisions
§ 11. The management and operation of waste incineration and waste incineration plants shall be carried out by a natural person who is competent to do so.
§ 12. Any heat generated from waste incineration or co-incineration plants must be used to the extent that it is practically possible.
§ 13. Waste incineration plants must be operated in such a way as to achieve a level of combustion where the total organic carbon content in the ladle and the batch is less than 3%, or the filament is less than 5% of the dry weight of the material. If necessary, waste is processed.
EBK temperature
§ 14. Waste incineration plants shall be designed, equipped, run and operated in such a way as to ensure that the gases generated by the incineration of waste after the last combustion air are heated in a controlled and uniform manner, even under the most unfavourable ; ratio to a temperature of at least 850 ° C. for at least two seconds.
Paragraph 2. However, on waste incineration plants that burn hazardous waste with a content of more than 1% halogenated organic substances, expressed as chlorine, the temperature must reach at least 1,100 ° C for at least 2 seconds.
§ 15. In the incineration plant, the temperature as referred to in section 14 must be measured near the internal wall of the combustion chamber, unless the approval authority is determined otherwise.
Paragraph 2. Measurements shall be carried out in accordance with Annex 1.
§ 16. Waste incineration plants shall be designed, equipped, run and operated in such a way as to ensure that the gases generated by the incineration of waste are heated in a controlled and uniform manner even in the most adverse conditions, to a temperature which for at least two seconds is required ; be kept at least 850 ° C.
Paragraph 2. However, on waste incineration plants that burn hazardous waste with a content of more than 1% halogenated organic substances, expressed as chlorine, the temperature must reach at least 1,100 ° C for at least 2 seconds.
Supporting fuels
§ 17. Each combustion chamber in a incinerator must be fitted with at least one aid burner.
Paragraph 2. The dust-burner shall be set in motion automatically when the temperature of the internal combustion gases is falling below the temperatures referred to in sections 14 and 16.
Paragraph 3. The dust burner shall also be used during start-up and shutdown so as to ensure that temperatures are maintained at any time during start-up and shutdown, and as long as there is still unburnt waste in the combustion chamber.
Paragraph 4. The fuel-burner must not be fuelled by fuel, which may result in more emissions than those caused by fuel oil, cf. the definition of the sulphur content of solid and liquid fuels, liquid gas and natural gas.
Automatic system preventing the insading of waste
§ 18. Waste incineration and waste incineration plants shall be operated with an automatic system which prevents waste disposal in the following situations :
1) During startup, until the temperature in section 14 or section 16 has been achieved.
2) If the temperature in section 14 or section 16 is not maintained during operation.
3) When the continuous measurements show that an emission limit value is exceeded due to disturbances or failures in the flue-gas purification plant, cf. § 43.
Fraviations from requirements for orientation and operation
§ 19. The approval authority or the supervisory authority may lay down conditions in waste incineration plants in accordance with the provisions of the section 33 of the law or in an open after section 41, which is different from the requirements of sections 13, 14 and 17 and a temperature in section 18, nr. 1 and 2, on condition that :
1) residues or residues are not caused by more organic pollutants than if the rules were not waived ; and
2) The other requirements of the notice may be complied with.
It must be specified in the conditions laid down for which particular types of waste or certain thermal processes are applied.
Paragraph 2. The approval authority or the supervisory authority may, on co-incineration plants, lay down conditions in an authorization under the section 33 of the law or in an open after section 41, which is different from the requirements of section 16, and the requirements for a temperature in section 18, no. 1 and 2, on condition that :
1) the emission limit values for TOC and CO in Annex 3 are complied with ; and
2) The other requirements of the notice may, by the way, be observed.
It must be specified in the conditions laid down for which particular types of waste or certain thermal processes are applied.
Chapter 5
Waste Receipt
20. The establishment must take all the necessary measures for the provision and reception of waste, in the widest possible, practicable extent to prevent or reduce pollution of air, soil, surface water and ground water, as well as water ; other environmental damage, odor and noise pollution, as well as to avoid direct risks to human health.
§ 21. In the case of the reception of waste, the establishment must ensure that :
1) that all necessary information on the waste is available in order to assess whether it is to be included in the planned internal combustion process, and
2) that the weight of each waste type is determined, if possible, in accordance with the EAC code, cf. the notice of waste.
§ 22. Before receiving hazardous waste in the waste incineration plant or the waste incineration plant, the undertaking shall collect all available information on the hazardous waste and check that the conditions of approval or on the conditions of waste are collected ; the quantity, mass flow, of the fuel and the content of contaminants, cf. Section 9 (1). Two, respected. The information must include :
1) All administrative information relating to the origin of the waste which is available in evidence, in accordance with any period applicable to waste, the transfer of waste and the carriage of dangerous goods by road.
2) The physical and as far as possible chemical composition as well as all other necessary information in order to assess whether it is suitable for the incineration intended for the intended combustion ;
3) The dangerous characteristics of the waste which is not to be mixed with and special precautions to be taken into handling the waste.
Paragraph 2. Before receiving hazardous waste in the waste incineration plant or the waste incineration plant, the undertaking shall at least complete the following procedures :
1) Verify the necessary documents, in accordance with the provisions applicable to waste, the transfer of waste and the transport of dangerous goods by means of any applicable waste.
2) As far as possible prior to reading, representative samples shall be taken to verify that the composition of the waste is in accordance with the information referred to in paragraph 1. 1, no. 1 3, in order to give the supervisory authority the opportunity to know the nature of the treated waste. The samples must be kept at the plant for at least one month after the incineration or co-incineration of the last part of that batch hazardous waste.
-23. The approval authority may relaxation the requirements of sections 21 and 22, for plants covered by Annex 1 in the notice of the approval of the list company, which are incinerating or incinerating its own waste.
§ 24. Clinical risk waste must be added to the furnace without direct handling and without being mixed with other waste.
Chapter 6
Luter emissions
Emission limits for air
§ 25. Waste incineration plants must at least comply with the emission limit values set out in Annex 3.
SECTION 26. Waste incineration plants shall at least comply with the emission limit values set out in Annex 4.
Paragraph 2. Where more than 40% of the heat-incineration plant is derived from hazardous waste, or the plant is incinerated untreated mixed municipal waste, the waste incineration plant must comply with the emission limit values set out in Annex 3.
Control of air traffic control
§ 27. Waste incineration and waste incineration plants must be fitted with measuring equipment that monitors emissions to the air according to the provisions of Annex 1.
Paragraph 2. The installation and operation of automatic systems for measuring and recording emissions for air shall be checked once a yearly basis as specified in Annex 1.
Paragraph 3. The performance measurements of atmospheric pollutants are carried out in accordance with Annex 1.
§ 28. The company must ensure that all monitor results are recorded, processed and presented in such a way as to ensure that the supervisory authority can verify that the operating conditions and emission limit values laid down in the permit or in the case of an injunction are observed.
Compliance with emission limit values for air
§ 29. The emission limit values for air in Annexes 3 and 4 shall be deemed to have been complied with when the requirements of Annex 2 are fulfilled.
Chapter 7
Residual products
-$30. Residual products must be limited to at least possible in terms of quantity and harmlessness. The goods shall be re-used where appropriate.
Paragraph 2. Exclusive residues which cannot be restricted or recysable must be disposed of in accordance with the rules in force.
§ 31. The carriage and temporary storage of dry residues in the form of dust shall be carried out in such a way that they are not released into the environment.
§ 32. Before disposal or recyctures are disposed of, appropriate tests must be carried out in order to determine the physical and chemical properties of residues and the potential for pollution. The tests must relate to the total content of soluble substances and the content of soluble heavy metals.
Chapter 8
Soil and ground water
§ 33. Areas of waste incineration and waste incineration plants, including associated storage places for waste, shall be designed and operated in such a way as to ensure that unapproved and unintended discharge of pollutants to soil, surface water and ground water must be established. Avoid.
§ 34. There shall be capacity for the storage of contaminated rainwater flow from the site of the waste incineration and waste incineration plants and of contaminated water, caused by waste or fire extinguishing. This storage capacity shall be sufficient to ensure that the water is to be cleansed before discharge is required.
Chapter 9
Emissions of waste water from flue-gas treatment
$35. Emissions to the aquatic environment of waste water from flue-gas treatment must be limited to the greatest possible extent.
Emission limits for waste water from gas treatment
§ 36. Waste incineration and waste incineration plants must at least comply with the emission limits set out in Annex 6 for waste water from the gas cleaning.
Paragraph 2. The waste water must not be diluted in order to comply with the emission limit values.
Property control with waste water from flue-gas treatment
§ 37. Waste incineration and waste incineration plants must be fitted with measuring equipment to monitor the emission of waste water from the flue-gas cleaning, in accordance with the provisions of Annex 6.
§ 38. The installation and operation of automatic systems for measuring and recording the wiring of waste water shall be reviewed annually, as specified in Annex 6.
§ 39. Measurements of water pollutants shall be carried out in accordance with Annex 6.
§ 40. The company must ensure that all monitor results are recorded, processed and presented in such a way as to ensure that the supervisory authority can verify that the operating conditions and emission limit values laid down in approval, injunction or approval shall be complied with.
Compliance with emission limit values for waste water from flue-gas treatment
§ 41. The emission limit values for waste water from the exhaust gas purification in Annex 6 shall be deemed to have been complied with when the criteria set out in Annex 6 are fulfilled.
Chapter 10
Havari, technically unavoidable standings and so on.
Havari
§ 42. In the event of an accident, the company must, as soon as practicable, restrict or discontinue operations until normal operation can be resumed.
Paragraph 2. During sea ari,
1) the emission of total dust from a waste incinerator does not exceed 150 mg/normal m 3 expressed as half-hour mean-value,
2) the emission of CO waste incinerators is not exceeded 100 mg/normal m 3 expressed as half-hour mean-value, and
3) the emission of TOC waste incineration plants shall not exceed 20 mg/normal m ; 3 expressed as half-hour mean.
Technical unavoidable surges, disturbances in the flue-gas purification plant, etc.
§ 43. Waste incineration and waste incineration plants must be operated with an automatic system preventing waste disposal when the continuous measurements show that an emission limit value in Annexes 3 or 4 is exceeded as a result of disturbances or disturbance ; failure of the flue-gas purification plant, cf. however, section 44 (3). 1, no. 2.
§ 44. Incineration of waste in oven lines associated with one and the same exhaust gas treatment plant shall not incinerate waste for an uninterrupted period of more than four hours if the emission limit values for half-times in column A in column A in the table in section 2 of Annex 3 are not to be used, x , BITCH. 2 , HCl, HF, and total dust have been exceeded because of :
1) technically unavoidable standings,
2) disturbation or failure of the flue-gas treatment plant ; or
3) disturbances or failures in measuring devices.
Paragraph 2. Operation under the conditions laid down in paragraph 1. 1 shall not exceed 60 hours in the course of a calendar year.
Paragraph 3. In situations referred to in paragraph 1, 1 may :
1) the emission of total dust from a waste incinerator does not exceed 150 mg/normal m 3 expressed as half-hour mean-value,
2) the emission of CO from a waste incineration plant does not exceed 100 mg/normal m 3 expressed as half-hour mean-value, and
3) the emission of TOC from a waste incineration plant shall not exceed 20 mg/normal m ; 3 expressed as half-hour mean.
Chapter 11
Reporting and Public Announcement
§ 45. The local authority shall forward to the Administrative Board, at the request of the EPA, to the facilities covered by the notice and on emissions, etc., which are necessary to enable Denmark to fulfil its obligation to report to the EU on implementation of : directives in the area.
§ 46. The Supervisory Authority shall publish at least once a year in the case of a list of waste incineration and waste incineration plants with a nominal capacity less than two tonnes per hour. The list shall be published before 1. April, first time before 1. April 2013. Announcement can be made entirely digitally on the supervisory authority's website.
Chapter 12
Punishment
§ 47. Unless higher penalties are inflited on other legislation, penalty shall be penalised by the penalty which :
1) fails to seek to make use of extra heat generated by waste incineration or co-incineration plants in violation of section 12,
2) refrain from taking all necessary measures after 20,
3) fail to ensure all necessary information and that the weight of each waste type is determined in accordance with section 21,
4) fails to collect information or check the terms of section 22,
5) handle clinical risk-waste in violation of section 24 ;
6) fails to register, process or submit any monitoring results according to section 28 ;
7) fails to seek to limit and revert residues in violation of section 30,
8) transporters and temporary storage of dry residues in violation of section 31,
9) fails to perform appropriate tests in accordance with section 32,
10) fails to design and operate sites for waste incineration and waste incineration plants after section 33,
11) exfodiers waste water from flue-gas purification in breach of section 35 ;
12) diluted waste water in violation of section 36 (3). 2,
13) fails to register, process or submit any monitoring results after Section 40,
14) omits to comply with the emission limits at sea-ari after Article 42 (3). 2,
15) fail to operate a waste incineration or waste incineration plant with an automatic system in breach of section 43.
Paragraph 2. The sentence may rise to prison for two years if the infringement has been committed intentionally or by gross negligence and if there is a breach of the infringement proceedings ;
1) damage to the environment or caused, or
2) obtained or intended for the economic benefit of the person concerned itself or others, including in the case of savings.
Paragraph 3. Companies can be imposed on companies, etc. (legal persons) punishable by the rules of the penal code 5. Chapter.
Chapter 13
Entry into force and transitional provisions
§ 48. The announcement will enter into force on the seventh. January 2013.
Paragraph 2. Publication no. 1356 of 21. December 2011 on installations incinerant.
§ 49. The pending cases in the first instance about the approval of waste incineration plants and waste incineration plants, including enhancements or amendments, where a full application has been submitted before the 7. In January 2013, the current rules on condition that the establishment is put into operation no later than 7 shall be completed under the current rules. January 2014.
$50. The Supervisory Authority shall take decisions on the approval of installations dealing with waste by gassing, pyrotic or meltdown, up to the review if the plant is covered by the notice, cf. Section 2 (2). 2, and § 3, nr. 5, and item 5.2 of Annex 1 concerning the approval of the list undertaking to ensure compliance with the requirements of the notice by the publication of the notice by 7. January 2014.
§ 51. The Supervisory Authority shall take decisions on the approval of cement kiln waste, up to re-evaluation, in order to ensure that the emission limit value for NO is ensured ; x in Annex 4, section 2.1, the following shall be observed :
1) In the case of LEPOL rotation and long rotherovenovens, no later than 1. January 2016.
2) For other cement kilns no later than 1. January 2014.
§ 52. The Supervisory Authority shall take decisions on approval which has been announced before 7. in January 2013, for combustion plants, subject to section 5.2 of Annex 1 to the announcement of the approval of the list company, if the plant is incinerated and has a nominal terminated thermal power of 100 MW and above, up to the reassessment, to the purpose of the establishment of a nominal thermal power of 100 MW and above for the purpose of the establishment of the Directive ensure that the installation complies with the emission limit values in Annex 4, section 3.1.1, not later than 7. January 2014.
§ 53. The Supervisory Authority shall take decisions on the approval of combustion plants which are incinerating waste, up to the reassessment with a view to ensuring that the installation complies with the emission limit values set out in section 3.1.2 of Annex 4, not later than 1. January 2016.
§ 54. The pending appeal proceedings are completed according to the applicable rules.
The Ministry of Environment, the 20th. December 2012
Ida Auken
/ Michel Schilling
Appendix 1
Requirements for measurements of air emissions
1. Measurement techniques
Periodic measurements of emissions into air shall be carried out in accordance with this Title.
Measurements for the determination of concentrations of air pollutants shall be carried out representative.
Sampling and analysis of all pollutants, including dioxins and furans, and quality assurance of the automatic measurement systems and reference measurement methods for calibration of these systems shall be carried out in accordance with CEN standards. If there is no CEN standards, ISO standards, national or other international standards shall apply, which shall ensure that information of equivalent scientific quality is obtained, use. Automatic measurement systems shall be subject to control by means of parallel measurements of reference methods at least once a year.
To the extent that the above standards do not impose more stringent requirements, the measurement programmes shall be carried out in accordance with the Environmental Management Board for the Environment, Chapter 5 and the Environmental Measurements for environmental measurements carried out by accredited laboratories, certificated persons, etc.
For the average values of the 95% confidens; the values of the 95% condenser range must not exceed the following percentages of the emission limit values :
|
2. Requirements for measures
The following measurements are carried out on atmospheric pollutants :
1. AMS control of the following substances : NO x , CO, total dust, TOC, HCl, HCl, HF, and SO 2
2. AMS control of the following operating parameters : Temperature (near the internal wall or other representative point of the combustion chamber as authorised by the approval authority), oxygen concentration, pressure, flue-gas temperature and water vapour content
3. However, at least twice a year of heavy metals and dioxins and furans shall be carried out at least one pre-station check every three months in the first 12 months of operation.
The control period for the AMS control is a calendar year.
The performance controls for heavy metals are carried out in accordance with the guidelines of the Environmental Management Board for the Environment. For dioxins and furans, the performance control consists of a single reading.
If the approval authority sets emission limit values for emissions other than those referred to in points 1 to 3, the approval or the tender shall include requirements for measurements of these substances.
The period of residence, minimum temperature and oxygen of oxygen shall be checked at least once when the incineration or waste incineration plant is being used and under the worst operating conditions.
3. Standardization of measure results for standard dilly concentration
The results of the measurements shall be standardised to the oxygen concentrations referred to in Annexes 3 or 4 or, in accordance with the procedure laid down in Annex 4, and in the case of the formula :
E S E M * (21-O S )/ (21-O M ()
E S : Calculated emission concentration by the standard percentage of oxygen concentration
E M : Measured emission concentration
O S : Standardite concentration
O M : Measured oxygen concentration
4. Fraviations from requirements for measurements and standardized oxygen content
4.1 Fraviations from the requirement for continuous measurements of water vapour content
The water vapour content of AMS is not necessary if the smoke gas test is dried before the emissions are analysed.
4.2 Fraviations from the requirement for AMS control of HF
AMS control of HF may be omitted if the treatment of HCl includes processing steps that ensure that the emission limit value for HCl is not exceeded. In this case, the HF test shall be carried out at least 2 times a year at least once every three months during the first 12 months of operation of the installation.
Performance checks shall be carried out in accordance with the guidelines laid down in the Environmental Management Board for the Environment.
4.3 Fraviations from the call for AMS-check by HCl, HF and SO 2
The Appointing Authority may derogate from the requirement for the AMS to check HCl, HF and SO 2 and instead require the performance review of HCl, HF and SO 2 at least twice a year, but at least one check every three months in the first 12 months of the installation, or drop the requirement for measurements. This presupvels that the company can prove that the emissions of these substances cannot, under any circumstances, be able to recover from the emission limit values laid down.
Performance checks shall be carried out in accordance with the guidelines laid down in the Environmental Management Board for the Environment.
4.4 Fraviations from the requirement for an AMS check by NO x
The approval authority may derogate from the requirement for an AMS check by NO x in the case of existing waste incineration or waste incineration plants, with a nominal capacity of less than 6 tonnes per hour, and instead require the stationary command of NO x at least twice a year, however, at least one control every three months in the first 12 months of operation of the installation. This requires that, on the basis of information on the characteristics of the waste concerned, the technology and the results of the emission control measures can prove that NO, x -emissions under no circumstances may be exceeded by the required emission limit value.
Performance checks shall be carried out in accordance with the guidelines laid down in the Environmental Management Board for the Environment.
4.5 Fraviation of the requirement for measurements for heavy metals and dioxins & furans
The approval authority may reduce the frequency of heavy metals and dioxins and furans to a measurement every two years of heavy metals and a measurement of dioxins and furans in the following cases :
1. Emissions from co-incineration or incineration of waste are below all proportion below 50% of the emission limit values,
2. the waste to be co-incinerated or incinerated shall consist of only certain sorted combustible fractions of non-hazardous waste which are not suitable for recycling and have specific characteristics and which are further specified on the basis of the waste, the assessment referred to in Point 3 and
3. on the basis of information on the characteristics of the waste and emission control, the company can be reimbursements that, in any case, the emission limit values for heavy metals and dioxins and furans shall be significantly below the emission limit values.
4.6 Fraviations from standardized oxygen content
If incineration or co-incineration of waste is carried out in an atmosphere of oxygen, the results of the measurements may be standardised to an oxygen content to be determined by the approval authority and which reflect the special circumstances of the said product in question ; case.
If the emission of pollutants is reduced by means of smoke-flushing in a waste incineration or waste incineration plant that treats hazardous waste, the calculation of standardized oxygen content is to be calculated only if the oxygen content that is measured under the control of the pollutant in question exceeds the appropriate standard content.
Appendix 2
Evaluation of compliance with emission limit values for air emissions
1. Determination of middle values
The half-hour average values and the 10-minute mean values are determined in the actual operating time (which do not include start-up and shutdown if waste is not incinerated) based on the values measured after the value of the value laid down in Annex 1, The context range is deduced. The values of the dead are determined from these validated middle values.
To obtain a valid 24-hour average values for a valid 24-hour average values, only five semi-timeaverage values should be discarded due to malfunctions or maintenance of the continuous measurement system. Only 10 24-hour average values per the measurement system must be discarded in the year due to malfunctions or maintenance of the continuous measurement system.
2. Compliance with emission limit values for waste incineration plants
The emission limit values for air are considered to be complied with if :
1) None of the average values exceed the emission limit values Annex 3, Section 1.
2) Either none of the half-hourly average values exceeds the emission limit values of Annex 3, section 2, column A, or where appropriate, at least 97% of the half-hourly average values in the course of the year does not exceed the emission limit values set out in Annex 3, Section 2, column B.
3) No pre-station checks on heavy metals, dioxins and furans during the sampling period exceed the emission limit values set out in section 3 and 4 of Annex 3.
4) At least 97% of the average CO values for CO during the calendar year do not exceed the emission limit value for the date of the death in Annex 3, section 5, point 5, 1.
5) At least 95% of all 10-minute average values for CO in any 24 hour period, or all semi-hourly mean values for CO during the same period do not exceed the half-hour emission limit value for half-hour in annex 3, paragraph 5, no. Two and three.
In the case of waste incineration plants where the gas from incineration for at least two seconds reaches a temperature of at least 1100 ° C, the oversight and approval authority may use an evaluation period of seven days for the ten-minute average values.
Mean values during the sampling period for the AMS control and performance controls shall be determined in accordance with the requirements of the environmental approval requirements for test methods, measuring techniques and frequencies, cf. Section 9 (1). 1, no. 4, requirements for the location of measuring techniques and sampling points, cf. Section 9 (1). 1, no. 6, and requirements for measuring techniques, cf. Annex 1, point. 1.
3. Compliance with emission limit values for waste incinerators
The emission limit values for air are considered to be complied with if :
1) None of the average values shall exceed the emission limit values set out in Annex 4 or, in accordance with the procedure laid down in Annex 4.
2) No performance controls for heavy metals, dioxins and furans during the sampling period exceed the emission limit values set out in Annex 4, or calculated in accordance with the procedure laid down in Annex 4 ;
3) The provisions of Annex 4 for CO are met.
Mean values during the sampling period for the AMS control and performance controls shall be determined in accordance with the requirements of the environmental approval requirements for test methods, measuring methods and frequencies, cf. Section 9 (1). 1, no. 4, requirements for the location of measurement points and sampling points, cf. Section 9 (1). 1, no. 6, and requirements for measuring techniques, cf. Annex 1.
Appendix 3
emission limit values for air from waste incineration plants
All emission limit values are calculated at a temperature of 273,15 K, a pressure of 101,3 kPa, and after correcting the water vapour content of the flue-gas.
They are standardised for an oxygen content of smoke gas of 11%, except where the waste oils are incinerated as defined in section 3, no. 42 in the notice of waste, in which case they are standardised to 3% oxygen content, and, except in cases where the approval authority has waived the requirement for standardised oxygen content, cf. Section 4.6 of Annex 1.
1. Emission limit values for the name of death
|
2. Emission limit values for semi-hourly mean values
|
3. Emission limit values for heavy metals
|
These average values include gaseous and vapour emissions of the relevant heavy metals, as well as the compounds thereof.
4. Emission limit values for dioxins & furans
Emission limit values for dioxins and furans during a test period of not less than six hours and not more than eight hours. The emission limit values refer to the total concentration of dioxins and furans calculated in accordance with Annex 5.
|
5. Emission limit values for carbon monoxide (CO)
1) 50 mg/normal m³ as the average value of the average
2) 100 mg/normal m³ as a semi-hourly mean value
3) 150 mg/normal m³ as a 10-minute average value.
The approval authority may authorise derogations from the emission limit values for CO provided for in this Title for waste incineration plants which use flu-bed technology if an emission limit value is set for carbon monoxide (CO) of not more than 100 mg/normal m 3 as the hour value.
Appendix 4
Luter emissions from co-incineration plants
Emission limits
The Annex shall apply to the co-incineration of waste, determined on the basis of the waste heat release. In the case of co-incineration of mixed municipal waste or by more than 40% of hazardous waste, Annex 3 must be applied to the whole of the incinerators.
1. Calculation of emission limit values
The following formula (mixing rule) is used when a specific total emission limit value of "C" has not been set out in a table in this Annex.
The emission limit value for each of the relevant pollutants and the co-incineration of the exhaust gas from co-incineration of waste shall be calculated as follows :
|
Special provisions for cement kilns which are burnin ' waste
2.1 Emission limit values for maximum total dust, HCl, HF, NO x , BITCH. 2 and TOC
The emission limit values (C) shall apply as 24-year-old values in order to ensure that the emission limit values are given by AMS. All values are standardized for an oxygen content of 10%.
Half-hourly average values are only necessary for the calculation of the average values.
|
||||||||||||||||||||||
2.2 Emission limit values for CO
The approval authority may lay down emission limit values for CO.
2.3 Emission limit values for heavy metals
Emission limit values (C) shall apply as a mean value for the sampling period, cf. Annex 1. All values are standardized for an oxygen content of 10%.
|
2.4 Emission limit values for dioxins and furans
The emission limit value (C) shall apply as a mean value for the sampling period, cf. Annex 1. All values are standardized for an oxygen content of 10%.
|
Special provisions for combustion plants, which are burnin ' waste
3.1 Eemission limit values for SO 2 , NO. x and dust for plants covered by section 3.1. 1 or 2
The emission limit values laid down in section 3.1 include the following combustion plants, which are burnin ' with waste :
1) A firing facility that's been approved by the environmental field before the 7th. January 2013.
2) Fire facility, where there before the 7th. In January 2013, a full application for environmental approval has been submitted and where the combustion plant has been put into operation by the 7. January 2014.
Section 3.2 sets emission limit values 2 , NO. x and dust for 'other' combustion plants, which are bursting waste, d.v.s installations not covered by paragraphs 1 or 2.
The emission limit values shall apply as 24-year-old mg/litre (mg/normal m³) determined at AMS Control. Half-hourly average values are only necessary for the calculation of the average values.
For the purpose of determining the total nominal of the combustion plants, the rules on the aggregation of large combustion plants shall be used by determining the total rated thermal output.
3.1.1 Emission limit values for Independent 2 , NO. x and dust until 31. December 2015
The emission limit values shall apply to combustion plants covered by Section 3.1.
C proc for solid fuel other than biomass (O 2 -content 6%)
|
C proc for biomass (O 2 -content 6%)
|
C proc for liquid fuel (O 2 -content 3%)
|
3.1.2 Emission limits for SO 2 , NO. x and dust from the 1. January 2016
The emission limit values shall apply to combustion plants covered by Section 3.1, except for gas turbines and gas engines.
C proc for solid fuel other than biomass (O 2 -content 6%)
|
C proc for biomass (O 2 -content 6%)
|
C proc for liquid fuel (O 2 -content 3%)
|
3.2 Emission limits for SO 2 , NO. x and dust for 'other' combustion plants ;
Emission limit values in section 3.2 shall comprise ' other ' combustion plants, which are co-incinerators, d.v.s combustion plants not covered by Section 3.1.
The emission limit values shall apply as 24-year-old mg/litre (mg/normal m³) determined at AMS Control. Half-hourly average values are only necessary for the calculation of the average values.
For the purpose of determining the total nominal of the combustion plants, the rules on the aggregation of large combustion plants shall be used by determining the total rated thermal output.
3.2.1 Emission limits for SO 2 , NO. x and dust until the 7th. January 2013
The emission limit values referred to in section 3.1.1 shall also apply to "other" combustion plants until the 7. January 2013.
3.2.2 Emission limits for SO 2 , NO. x and dust from the seventh. January 2013
Emission limit values (C proc ) apply to combustion plants covered by Section 3.2, except for gas turbines and gas engines.
C proc for solid fuel other than biomass (O 2 -content 6%)
|
C proc for biomass (O 2 -content 6%)
|
C proc for liquid fuel (O 2 -content 3%)
|
3.3 Emission limit values for heavy metals
The emission limit values shall apply as a mediocus value for the sampling period, cf. Annex 1. For solid fuels, a 6% oxygen content is standardised and for liquid fuel for a 3% oxygen content.
The emission limit values (C) shall apply to all combustion plants, which are burnin ' waste.
|
3.4 Emission limit values for dioxins and furans
The emission limit value (C) shall apply as a mean value for the sampling period, cf. Annex 1. For solid fuels, a 6% oxygen content is standardised and for liquid fuel for a 3% oxygen content.
The emission limit values shall apply to all combustion plants, which are burnin ' waste.
|
Specific provisions for waste co-incineration plants in industrial sectors
For waste incineration plants in industrial sectors not covered by Sections 2 or 3, the emission limit values for heavy metals and dioxins and furans shall be subject to the emission limit values.
The emission limit values (C) shall apply as a mean value for the sampling period, cf. Annex 1.
C-total emission limit value (ng/normal m 3 () for dioxins and furans, expressed as a mediocate value for a period of not less than six hours and not more than eight hours :
|
C-total emission limit values (mg/normal m 3 () for heavy metals expressed as middle values in a sampling period of not less than 30 minutes and not more than eight hours :
|
Appendix 5
Equivalence factors for dibenzo-p-dioxins and dibenzofurans
For the determination of the total concentrations of dioxins and furans multiply the mass concentrations of the following dibenzo-p-dioxins and dibenzofurans, with the following equivalence factors before they are aggregated :
|
Appendix 6
Wasted water from gas treatment
1. Emission limit values for the discharge of waste water from flue-gas treatment
|
||||||||||||||||||||||||||||||||||||||||||
2. Measurement techniques
Periodic measurement of emissions into water must be carried out in accordance with this section.
Measurements for the determination of concentrations of water pollutants shall be carried out representative.
Sampling and analysis of all pollutants, including dioxins and furans, and quality assurance of the automatic measurement systems and reference measurement methods for calibration of these systems shall be carried out in accordance with CEN standards. If there is no CEN standards, ISO standards, national or other international standards shall apply, which shall ensure that information of equivalent scientific quality is obtained, use. Automatic measurement systems shall be subject to control by means of parallel measurements of reference methods at least once a year.
3. Requirements for measures
The following measurements shall be taken at the water supply point :
a) AMS check for pH, temperature, and flow-through
b) daily measurements in random sampling of the total quantity of suspended substances or measurements of a current representative sample of the flow of the sample,
c) at least monthly measurements of one in relation to the mold representative sample of the derivation of Hg, Cd, TI, As, Pb, Cr, Cu, Cu, 9 and Zn
d) however, measurements shall be taken at least every six months of dioxins and furans ; a measurement must be carried out every three months during the first 12 months of operation of the installation.
Where waste water from flue-gas purification is cleaned in the waste water purification centre with waste water from other sources on the same waste incineration or waste incinerator, the operating manager must perform the measurements :
a) on the waste water from the flue-gas purification process before it is run into the joint waste-water purification centre ;
b) on the other waste water, before it is headed into the common waste water purification centre ;
c) at the point of the final waste water discharge after the purification.
4. Criteria to comply with emission limits
The emission limit values shall apply to the point where waste water from gas treatment is derived from the waste incineration or co-incineration plant.
Waste water processed outside the plant area of a waste water purification plant, which is solely responsible for the treatment of the waste water from gas treatment plants, must comply with the emission limit values where the waste water is derived from the waste water purification centre.
When waste water from flue-gas treatment is treated with waste water from other sources either on or outside the plant, the establishment shall make appropriate mass balance calculations based on the results of the measurements laid down in Section 3 to determine ; the emission levels in the final waste water discharge which can be attributable to waste water from gas treatment.
The emission limit values for waste water are considered to be complied with if :
1) 95% and 100% of measured values within a calendar year for the total amount of the suspended substances do not exceed the respective limit values set out in this Annex ;
2) A measurement of the year of heavy metals exceeds the limit values set out in this Annex, or, if the supervisory authority requires more than 20 samples per year, not more than 5% of these exceed the emission limit values), and
3) The half-yearly measurements for dioxins and furans do not exceed the limit value laid down in this Annex.
1) The announcement carries out parts of the European Parliament and Council Directive 2010 /75/EU of 24. Nov. 2010 on industrial emissions (integrated prevention and control of pollution) (recast), EU Official Journal 2010, nr. L 334, page 17 and Parliament and Council Directive 2000 /76/EC of 4. In December 2000, on the incineration of waste, the Official Journal of the European Communities, no. L 332, page 91.
