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Waste Combustion Regulation (Avv-Novelle 2010)

Original Language Title: Änderung der Abfallverbrennungsverordnung (AVV-Novelle 2010)

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476. Ordinance of the Federal Minister for Agriculture, Forestry, Environment and Water Management and the Federal Minister for Economic Affairs, Family and Youth, with which the Waste Incineration Ordinance is amended (AVV-Novelle 2010)

Because of

1.

Section 82 (1) of the 1994 Commercial Code-GewO 1994, BGBl. N ° 194, as last amended by the Federal Law BGBl. I No 66/2010, and

2.

§ § 4 para. 3 and 4, 9 para. 7, 13 para. 2, 14 para. 8, 15 para. 6 and 17 para. 2 of the Emissions Protection Act for boiler plants-EC-K, BGBl. I n ° 150/2004, as last amended by the Federal Law BGBl. I No 65/2010,

is based on the agreement of the Federal Minister for Economic Affairs, Family and Youth in agreement with the Federal Minister for Agriculture, Forestry, Environment and Water Management.

3.

§ § 23 and 65 of the Waste Management Act 2002 (AWG 2002), BGBl. I n ° 102, as last amended by the Federal Law BGBl. I No 115/2009, and

4.

§ 59a of the Water Rights Act 1959-WRG 1959, BGBl. No. 215, as last amended by the Federal Law BGBl. I n ° 123/2006 and the Federal Ministries of the Federal Ministries of Law 2009, BGBl. I No 3,

is agreed by the Federal Minister for Agriculture, Forestry, Environment and Water Management in agreement with the Federal Minister for Economic Affairs, Family and Youth, and on the basis of

5.

§ 5 of the Waste Management Act 2002 (AWG 2002), BGBl. I n ° 102, as last amended by the Federal Law BGBl. I No 115/2009,

is assigned by the Federal Minister for Agriculture, Forestry, Environment and Water Management:

The Waste Incineration Ordinance (AVV), BGBl. II No 389/2002, as amended by the BGBl Regulation. II No 296/2007, is amended as follows:

1. The title of the Regulation shall be followed by the following: "Federal Minister for Economic Affairs and Labour" through the phrase "Federal Minister for Economic Affairs, Family and Youth" replaced.

2. The promulgation clause is:

" On Reason

1.

§ § 23 and 65 of the Waste Management Act 2002 (AWG 2002), BGBl. I n ° 102, as last amended by the Federal Law BGBl. I n ° 115/2009, concerning treatment facilities pursuant to § 2 (1) (1) (1) of this Regulation, by the Federal Minister for Agriculture, Forestry, the Environment and Water Management in agreement with the Federal Minister for Economic Affairs, Family and Youth,

2.

Section 82 (1) of the 1994 Commercial Code-GewO 1994, BGBl. N ° 194, as last amended by the Federal Law BGBl. I n ° 66/2010, the Federal Minister for Economic Affairs, the Family and Youth, in agreement with the Federal Minister for Agriculture, Forestry, the Environment, and the Federal Minister for Economic Affairs and the Environment, water management,

3.

§ § 3 (4), 4 (3) and 4 (4), 9 (7), 13 (2), 14 (8), 15 (6), 16 (8) and 17 (2) of the Emissions Protection Act for boiler plants-EC-K, BGBl. I n ° 150/2004, as last amended by the Federal Law BGBl. 1 and 2 of this Regulation, by the Federal Minister for Economic Affairs, Family and Youth in agreement with the Federal Minister for Agriculture, Forestry, the Environment and Water Management,

4.

§ 59a of the Water Rights Act 1959-WRG 1959, BGBl. No. 215, as last amended by the Federal Law BGBl. I n ° 123/2006, as regards Articles 13 and 13a of this Regulation and Annex 6 to this Regulation concerning discharges of waste water from the gas scrubbing, which are subject to a regulation in accordance with § § 33b (3), (4), (5) and (7) and 33c (1) WRG 1959, by means of the Federal Minister for Agriculture, Forestry, Environment and Water Management in agreement with the Federal Minister for Economic Affairs, Family and Youth and

5.

§ 5 of the Waste Management Act 2002 (AWG 2002), BGBl. I n ° 102, as last amended by the Federal Law BGBl. I n ° 115/2009, concerning the waste disposal of substitute fuels by the Federal Minister for Agriculture, Forestry, the Environment and Water Management

orders: "

3. In the subsection of § 2 paragraph 2, after the word "applies" the phrase "-subject to paragraph 3-" inserted.

4. The following paragraphs 3 and 4 are added to § 2:

§ 6 (2), (6a), 11a, 15 (1), last sentence, 19b and Annex 8 shall apply to co-incineration plants which exclusively burn waste according to § 2 (2) (1) (1) (1).

(4) This Regulation shall apply to:

1.

Waste producers as regards § § 5a, 11a, 18a, Annex 8, Chapter 2, and Annex 9,

2.

Waste collectors with regard to § § 11a, 18a, Annex 8, Chapter 2 and Annex 9, and

3.

Qualified specialists and specialist institutions with regard to § § 11a, 15, 18a, Annex 8, Chapter 2 and Annex 9. "

5. § 3 reads:

" § 3. For the purposes of this Regulation, are

1.

Waste stream: a certain waste which, from a defined process (the same process, the same process conditions, and the same ingredients), is regularly produced by a waste producer in the same quality; this shall be assessed with regard to the limit value levity and the criteria for use in a specific co-incineration plant;

2.

wastes: wastes according to AWG 2002;

3.

Exhaust gas: a gas mixture consisting of the gaseous combustion products produced in the combustion or co-incineration plant during the combustion of solid, liquid or gaseous fuels and waste, and the gaseous combustion products from the combustion air, the excess air, the exhaust gas treatment plant, and the gas components from the production process, including the solid or liquid substances contained therein;

4.

Preparation: the treatment of waste prior to use in co-incineration plants, such as classification, sorting, iron (Fe) and non-ferrous metal deposition. The preparation may also consist of a single assembly, provided that the limit values laid down in Annex 8, Chapter 1, are complied with;

5.

Qualified specialists or specialist institutions: pursuant to § 2 paragraph 6 Z 6 AWG 2002;

6.

Existing incineration or co-incineration plant: an incineration plant or co-incineration plant, which shall be carried out before 28 December 2002

a)

approved and operated in a legally binding manner, or

b)

approved in the first instance and the plant was put into operation no later than 28 December 2003;

As existing incineration plants or co-incineration plants, the following shall also apply:

Installations for which, before 28 December 2002, an experimental plant according to § § 354 GewO 1994, 29 para. 8 of the Waste Management Act-AWG (hereinafter: AWG 1990), BGBl. No 325/1990, 44 of the Waste Management Act 2002-AWG 2002, BGBl. No 102, or 4 (10) of the Air Pollution Control Act for boiler systems-LRG-K, BGBl. No 380/1988, or trial operation in accordance with § § 29 (8) of the AWG 1990 and 44 AWG 2002 or 4 para. 10 LRG-K, and the trial or trial operation was started no later than 28 December 2003;

7.

Assessment Value: Value to check compliance with the limit values. In the case of emissions into the air, the assessment value is the measurement result taking into account the error limit of the measurement method (error bandwidth). In the case of continuous measurements, the error bandwidths must be determined by calibration, and in the case of discontinuous measurements, the error bandwidths shall apply in accordance with Appendix 4. The calculation of the assessment value for waste incinerated in co-incineration plants shall be carried out in accordance with Annex 8, Chapter 1.8;

8.

Biomass: products of agricultural or forestry origin made of vegetable material or parts thereof, which can be used for energy recovery purposes, as well as those in § 2 para. 2 (2) (1) (lit). (a) to (e) waste; wood wastes from construction and demolition waste are not biomass within the meaning of this Regulation;

9.

Fuel heat output from the incineration of waste: the average hourly amount of heat actually supplied with the waste in one month;

10.

Fuel heat output from the combustion of fuels: the average hourly amount of heat, which is actually supplied in one month, with fuels that are not waste;

11.

Declaration: the assignment of a substitute fuel to a intended use as a product on the basis of a valid proof of assessment, which is documented in the records, which is the responsibility of the Federal Minister for Agriculture, Forestry, the Environment, and water management;

12.

Dioxins and furans: polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/F), specified as 2,3,7,8-TCDD-equivalent (I-TEF) in accordance with Appendix 3;

13.

single waste: waste which is not a waste stream;

14.

Individual measurement value: the result of a single measurement;

15.

Emission: the direct or indirect release of substances, shocks, heat or noise from point sources or diffuse sources within the installation into the air, water or soil;

16.

Declaration of emission: a message from a registration of the master data in the master data register in the context of the registration, a waste input-output message, one or more reports of emissions into the air (declaration of air emissions) and, if: Waste water from the purification of combustion gas is produced, one or more reports of emissions into the water (water-emission declaration) are present;

17.

Emission limit values: maximum permissible values determined in accordance with the state of the art, which are linked to certain measuring and operating conditions and which may not be exceeded in one or more periods; emission limit values shall be considered to be the the mass of air pollutants, which may enter the free atmosphere at the emission source per unit volume of the exhaust gas (mass concentration). The volume unit of the exhaust gas is related to 0 ° C and 1013 mbar and to the oxygen content specified for the respective combustion or co-incineration plant, after deduction of the moisture content. The mass concentration shall be expressed in the unit mg/m³ (in the case of dioxins and furans in ng/m³);

18.

Substitute fuels: wastes which are used in their entirety or in a relevant extent for the purpose of energy production and which meet the requirements set out in Appendix 8. A relevant extent for the purpose of energy production is to be found if self-established combustion is possible without additional firing. For the purposes of this Regulation, sewage sludges and paper fibre residues which are incinerated and which meet the requirements of Appendix 8 shall be considered as solid substitute fuels;

19.

Replacement fuel products: replacement fuels which meet the requirements of Appendix 9 and for which the end of the waste property on the basis of the transmission of a valid assessment certificate to the Federal Minister for Agriculture, Forestry, Environment and water management;

20.

Substitute raw materials: waste which meets the requirements for recycling in accordance with Article 2 (5) (2) Z 2 of the AWG 2002;

21.

Field sample: a sample from which the laboratory sample is prepared for the subsequent investigation;

22.

Combustion plant within the meaning of Appendix 2, point 3: any co-incineration plant in which fuels are oxidised with a view to the use of the heat produced, including any subsidiary equipment relevant to emissions and, if appropriate, Connected or downstream exhaust gas purification systems. Appendix 2, point 3 shall not apply to combustion plants in which the combustion gases are used directly for heating or heating or drying or for the other treatment of objects or materials;

23.

liquid waste: all wastes in liquid form (at standard conditions: 25 ° C, 1 013 mbar), but excluding sludges;

24.

hazardous waste: waste according to a regulation according to § 4 AWG 2002. For the following hazardous waste, the provisions on hazardous waste contained in this Regulation are not applicable, with the exception of § § 6 (4) and (7) (9).

a)

combustible liquid waste, including waste oil, having a specific calorific value of at least 30 MJ/kg, the mass content of which is based on polychlorinated aromatic hydrocarbons, such as polychlorinated biphenyls (PCBs) or pentachlorophenol, (PCP), do not reach more than 50 ppm, and which do not have, due to other components, a gefahrenrelevant property in accordance with a regulation pursuant to § 4 AWG 2002;

b)

combustible liquid waste, including waste oil, if the exhaust gases immediately produced during combustion cannot cause any other emissions and no higher emission concentrations than those which are extra light in the combustion of heating oil waste gases produced;

25.

Total fuel heat output: the sum of fuel heat output from the incineration of waste and fuel;

26.

Half-hourly average value (HMW): the arithmetic mean of the individual measured values over the period of half an hour;

27.

Packaging: the treatment of waste to improve the physical properties required for use in a co-incineration plant or the improvement of the combustion behaviour of the substitute fuel. Examples of compounding are comminution, drying, pelletizing or mixing to achieve a certain calorific value. A preparation according to Z 4 may consist of a single assembly, provided that the limit values are complied with in accordance with Annex 8, Chapter 1.

28.

Continuous emission measurements: measurements, which reflect the concentration of the parameters to be measured continuously. The evaluation of the individual data is carried out in half-hour or daily average values;

29.

laboratory sample: a sample obtained from the field sample after preparation, rejuvenation and, if necessary, preservation, and used for laboratory testing;

30.

Los: the quantity of waste which is determined in accordance with Annex 8 (2) (2) or (9) (2), the properties of which must be determined (a subset of the waste assessment);

31.

Measurement result: the arithmetic mean of the measured values;

32.

Measured value: the result of a measuring process. The measured value is obtained

a)

as the arithmetic mean of the individual measured values,

b)

from the time-place integral at a measurement level, or

c)

as a single value at a measuring point representative of the channel cross-section;

33.

Co-incineration plant: any fixed or mobile technical plant, the main purpose of which is the production of energy or of the production of material products; and

a)

in which waste is used as a rule or additive fuel, or

b)

in which waste is thermally treated with a view to disposal.

If co-incineration takes place in such a way that the main purpose of the plant is not in the production of energy or in the production of material products, but in the thermal treatment of waste, the plant shall be considered as an incineration plant.

This definition covers the location of the plant and the entire plant, including all co-incineration lines, the acceptance and storage of the waste, the pre-treatment facilities located on the site, the waste fuel, fuel and the waste, and air supply system, the boiler, the exhaust gas treatment facilities, the facilities located on the site for the treatment and storage of residues and waste water, the chimney, the devices and systems for the control of the combustion operations, to Recording and monitoring of combustion conditions;

34.

Nominal capacity of an incineration plant: the sum of the combustion capacities of all lines of an incineration plant specified by the manufacturer and confirmed by the plant owner, taking account of the calorific value of the waste, expressed in the the amount of waste burnt per hour (t/h);

35.

Rated heat output: the highest heat output intended for the operation of the co-incineration plant (nominal load);

36.

Test quantity: the mass or the volume of material used in the material, the material or the material either the laboratory sample or the test sample has been taken and is necessary for the determination of the composition or other properties of interest;

37.

Test sample: a laboratory sample after a suitable pre-treatment carried out by the laboratory (e.g. grinding to achieve sufficient homogeneity and fineness, drying);

38.

qualified sample: a sample consisting of several samples, which can be assigned to a lot;

39.

Residue: any liquid or solid waste arising from combustion, waste gas or waste water treatment or any other process within the incineration or co-incineration plant;

40.

Rehearsals: an aliquot of the field sample, which shall be retained for any check-ups;

41.

Sample: a sample that is drawn at a given location at a particular point in time. A sample is not individually examined, but is combined with other samples into a qualified sample;

42.

Daily average value (TMW): the arithmetic mean of the half-hourly average values over a calendar day;

43.

(unprocessed) mixed municipal waste: waste from private households and other waste which, due to its nature or composition, is similar to waste from private households. Excluded from this are separately collected fractions, as well as garden and parking waste. Mixed municipal waste is of inhomogeneous composition or has high or highly fluctuating pollutant contents. Simple individual processing steps, such as drying, pressing or only partial separation and sorting, do not lead to any substantial change in these properties, so that unprocessed mixed municipal waste is still available;

44.

Incineration within the meaning of Article 6a (1): the reaction of a waste with gaseous oxygen, with the emission of heat with or without visible light. The reaction of a waste which has an ash content of at least 80% in relation to the dry mass (for example, fly ash, foundry sand) is not covered by the concept of combustion. The ash content must be determined in accordance with ÖNORM CEN/TS 15403 "Solid secondary fuels-Procedures for the determination of the ash content", issued on 1 December 2006. Likewise, the use of metal-containing waste in installations for the production of non-ferrous metals, iron and steel within the scope of recovery procedures R 4, R 5 or R 8 in accordance with Annex 2 to the AWG 2002 shall not be covered by the concept of incineration;

45.

Incineration plant: any fixed or mobile technical plant which is used for the thermal treatment of waste with or without the use of the generated heat of combustion and which does not apply as a co-incineration plant. This includes the incineration by oxidation of waste and other thermal treatment processes, such as pyrolysis, gasification and plasma processes, to the extent that the substances formed during the treatment are subsequently incinerated. This definition shall cover the location of the incineration plant and the entire incineration plant, including all incineration lines, the acceptance and storage of the waste, the pre-treatment facilities located on the site, the Waste, fuel and air supply system, boiler, exhaust gas treatment plants, facilities located on the site for the treatment and storage of residues and waste water, the chimney, the devices and systems for controlling the Combustion processes, recording and monitoring of the Combustion conditions;

46.

Pre-treatment: process steps at the site for the preparation of the waste for incineration, such as shredders, mixing or other chemical-physical treatment;

47.

intended customers:

a)

Persons who are likely to have a substitute fuel product on the basis of a legal relationship in the coming calendar year from the person who wishes to leave the waste property or who has declared the end of the waste property including a self-application.

b)

Persons who, by the person who declared the end of the waste property, took over a substitute fuel product, including a self-application, in the previous calendar year. It is also possible to mention overtakers who have taken over replacement fuel products in the calendar year before. "

6. § 4 (1) Z 9 reads:

" 9. Information from which the intended measurement techniques for emissions into the air in accordance with Appendix 5 and for emissions into the water in accordance with Annex G of the Regulation of the Federal Minister for Agriculture, Forestry, the Environment and Water Management are to be provided on the basis of Limitation of waste water emissions from the purification of combustion gas (AEV combustion gas), BGBl. 271/2003 idgF.,

7. § 5 (1) Z 7 reads:

" 7. Requirements for measurements to monitor the combustion process of significant operational data, parameters and emissions, measurement techniques for emissions into the air according to Appendix 5, and for emissions into the water in accordance with Annex G of the Regulation of the Federal Minister for Agriculture, Forestry, Environment and Water Management on the limitation of waste water emissions from the purification of combustion gas (AEV incineration gas), BGBl. N ° 271/2003 idgF.; "

8. In accordance with § 5, the following § 5a together with the heading is inserted:

" Obligations of the producer of waste subject to § 6a (1)

§ 5a. A mixture of waste which is subject to § 6a (1) and which is to be incinerated in co-incineration plants shall be permitted if:

1.

a valid proof of assessment is already available for each individual waste; or

2.

the waste has been shown to be treated as a source of pollutant decontamination with regard to the parameters in respect of which the input limit values have been exceeded or where the reason for the justification is that There is a suspicion of such an exceedation, so that the limit values are not complied with solely by mixing.

A mere comminution, drying or pelletizing (packaging) does not result in any pollutant deframing in the sense of the Z 2. "

9. § 6 para. 2 reads:

" (2) The owner of the plant shall ensure, through the entry control, that only the types of waste covered by the authorisation for the incineration or co-incineration plant are incinerated. The owner of the plant has to determine the mass of the particular type of waste when the waste is accepted. The entry control for waste, which is subject to § 6a (1), consists of

1.

a visual check in which the conformity of the delivered waste with the waste information or, where available, must be determined with the assessment certificate;

2.

a review of the relevant documents (in particular the waste information or, if available, the assessment certificate); and

3.

an identity check to be carried out in accordance with Chapter 2.13 of Annex 8, provided that the proof of assessment is not drawn up by the owner of the co-incineration plant. If the identity of the waste is not given, the plant owner must reject the waste delivery and transmit the results of the identity check to the waste owner. "

10. The following sentence is added to Article 6 (3):

"The waste information in accordance with Section 11a (2) or the proof of assessment pursuant to § 11a (1) replace this waste description."

Article 6 (5) reads as follows:

" (5) In the context of the entry control of hazardous waste, representative samples must be taken according to the state of the art and examined for the parameters set out in Annex 8, Chapter 1, unless they are based on the origin or the nature of the waste. dangerous waste can be reliably assumed that these parameters are present in insignificant quantities; unconsidered parameters must be documented. The scope of the chemical analysis needs to be expanded if it is to be assumed that other emission-related pollutants are contained in the hazardous waste. Excluded from this

1.

wastes which may present a hazard in accordance with ÖNORM S 2104 "medical waste", issued on 1 July 2008, inside and outside the medical sector,

2.

wastes according to § 6a (1) and

3.

hazardous waste where, due to the inhomogeneity, representative sampling according to the state of the art is not possible, provided that the incineration takes place in an installation which at least complies with the limit values of Appendix 1. "

12. § 6 (6) deleted.

13. In accordance with § 6, the following § 6a and title is inserted:

" specifications for waste to be incinerated in co-incineration plants

§ 6a. (1) Waste to be incinerated in co-incineration plants shall comply with the requirements laid down in Annex 8.

(2) Paragraph 1 shall not apply to:

1.

wastes to be incinerated in co-incineration plants which have been shown to comply with at least the emission limit values for incinerators in accordance with Appendix 1, provided that the solid residues are disposed of in a proper landfill, at the latest after a Pre-treatment, or a permitted use as a substitute raw material, where, in the case of use as a substitute raw material, a quality assurance system according to the state of the art must ensure that the quality of the raw material remains constant is given,

2.

wastes (separated by origin and type of waste) up to 25 tonnes/year, or

3.

wastes to be incinerated in co-incineration plants with a rated thermal power of less than 500 kW.

The Authority may, upon request, allow derogations from the requirements set out in Annex 8, Chapters 1.1 to 1.6 (limit values), if the applicant is required to take appropriate measures, such as equipment and operation, control and surveillance during the Operation and aftercare, ensure that the same protection is achieved, as it would be expected to comply with Annex 8, Chapter 1.1 to 1.6 (limit values). Where necessary, the Authority shall, in order to ensure the same level of protection, prescribe appropriate conditions, conditions or deadlines.

(4) The Authority may, upon request, allow derogations from the requirements set out in Annex 8 if the incineration of waste is to be carried out in order to ensure that the interests of public supply and disposal are to be ensured;

1.

which are unexpected (e.g. caused by a contamination caused by an accident, by accident or by natural disasters) and

2.

in respect of which there is a public interest in environmentally sound thermal treatment,

provided that the legal and technical requirements for incineration are met. The Federal Minister for Agriculture, Forestry, the Environment and Water Management is to be informed of a modest nature. "

14. In § 7 (7), the following sentence shall be inserted before the phrase "The height of the chimneys ...":

"Incineration and co-incineration plants shall be designed, equipped, exported and operated in such a way as to prevent emissions from being emitted into the air leading to significant air pollution on the ground."

15. The following paragraph 11 is added to § 7:

"(11) Any heat generated during the incineration or co-incineration process must be used, as far as practicable."

16. In accordance with § 11, the following § 11a including the heading is inserted:

" Recording and reporting requirements in the co-incineration of waste subject to § 6a (1)

§ 11a. (1) The owner of a co-incineration plant shall only be allowed to burn waste if there is a valid proof of assessment in accordance with Annex 8; Chapter 2.6 of Appendix 8 shall remain unaffected. The waste producer, the waste collector or the owner of the co-incineration plant shall be able to draw up a certificate of assessment. These persons can serve an authorized subject or specialist institution. The prerequisite for the preparation of the assessment certificate is compliance with a quality assurance system according to the state of the art. A certificate of assessment must comply with the requirements of Annex 8, Chapter 2.12. Any change in the origin of the waste, including input materials or the process, which has an impact on the quality of the waste, must be accompanied by a new proof of assessment. The assessment must be based on 1. January 2015 will be transmitted electronically by the register in accordance with § 22 AWG 2002.

(2) Where no evidence of assessment has been drawn up by the producer or collector of waste to be incinerated in co-incineration plants, in accordance with Annex 8, Chapter 2.12, the owner of the co-incineration plant shall have a waste owner Waste information is transmitted. Waste information can be produced by the waste producer or by the waste collector. These persons may be used to create a waste information of an authorized subject or specialist institution. The waste information must be from 1. January 2015 will be transmitted electronically by the register in accordance with § 22 AWG 2002. The owner of the co-incineration plant must verify this information. Waste information shall contain the following information:

1.

the unique identifier;

2.

the undertaking which produces the waste information;

3.

the owner of the waste, if he is not ident with the company;

4.

Date of delivery;

5.

basic information about the waste:

a)

Waste type according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended and in the case of shipments, in addition to Annex 2 of the Waste Regulation; the type of waste must be determined in accordance with the allocation criteria of the Waste Waste Collection Regulation;

b)

Origin according to the Waste Balance Ordinance, BGBl. II No 497/2008, in the current version;

c)

description of the waste (in particular odour, colour, consistency);

d)

in the case of hazardous waste: hazard-relevant properties; physical parameters-as far as the target is concerned-in accordance with Table 1, point 13 of the ÖNORM S 2110 "Investigation of waste for chemical-physical or thermal treatment", issued on 1 January 2008. September 2001; chemical composition and other information to the extent that this is necessary to assess the suitability for the intended combustion process; substances with which the waste may in any case not be mixed, and precautions for use in dealing with the waste;

6.

in the case of a one-off waste, the total quantity of waste in tonnes, in the case of a waste stream, the estimated annual quantity of waste in tonnes, and

7.

the description of the origin of the waste and any treatment steps; the description of the input materials of the process in which the waste is produced and the output materials of the treatment; and an indication of any contamination and any contamination; and whose cause.

In addition, the waste information can be used to indicate the location of the waste, as well as photos of the waste which is to be incinerated in co-incineration plants, and file attachments, if this is appropriate to the feasibility of the assessment of the waste. . Waste information shall be valid for a maximum of five years from the date of the first transmission date. Any change in the origin of the waste, including input materials or the process, which may have an impact on the quality of the waste, shall be accompanied by a new waste information.

(3) If the waste information is not produced by the owner who passes the waste to the owner of the co-incineration plant, but from a waste owner in the chain, this waste owner must have the waste information to the in each case of the waste. The same shall also apply to the assessment of the assessment if it is not drawn up by the owner of the co-incineration plant. As soon as a proof of assessment is available, it is only necessary to provide more information.

(4) Weiters shall record the owner of a co-incineration plant:

1.

the basic procedure for the entry control,

2.

the results of the entry control, in particular the results of the identity checks referred to in Annex 8, Chapter 2.13;

3.

Failure declarations indicating the waste information or where available the assessment certificate, the waste concerned and the waste shipments, and

4.

the results of the checks carried out in the context of external surveillance in accordance with Annex 8, Chapter 2.14.

(5) On request, the authorities must be granted access to the records and the records must be submitted on request. The records must be recorded as of 1. January 2015 is electronically conducted and stored electronically as well as electronically transmitted on request by means of the register according to § 22 AWG 2002. Evidence of assessment and waste information which has not yet been transmitted electronically by the register pursuant to Article 22 of the AWG 2002 must be kept at least seven years after the expiry of the validity period. At the request of the Authority, they shall be submitted.

(6) Interfaces must be established in the electronic recording system so that defined excerpts can be drawn from the current data and from the data to be stored which are related to the content, the data structure and the data. Identifications comply with the requirements of § § 11a and 18a. The basis of the defined excerpts and the data structure for § § 11a and 18a is the ON-rule 192150 "Data structures for the electronic data exchange in waste management", issued on 1 November 2007. The resulting XML data format structures for waste information, assessment certificates, excerpts and reports, booking types and test rules will be published on the EDM-Portal, edm.gv.at.

(7) Waste information and evidence of assessment can also be drawn up for waste which is not subject to § 6a (1) and must be accepted by the contractor of this waste. Paragraph 3 must be applied mutasensitily. "

17. The following paragraph 4 is added to § 12:

"(4) If no daily average value for CO is exceeded, CO para. 2 Z 2 can be used."

18. The following sentence shall be added to section 15 (1):

" Where waste is incinerated which is subject to § 6a (1), the test must also contain the points referred to in Annex 8, Chapter 2.14, provided that the studies referred to in Annex 8, Chapters 2.1 to 2.10 and 2.13, are not fully carried out by a qualified person or "Fachanstalt shall be carried out."

19. In accordance with § 18, the following § 18a and title shall be inserted:

" Waste end for substitute fuels

§ 18a. (1) Spare fuel products shall comply with the requirements of Appendix 9. You lose with the declaration on the basis of the transmission of a valid proof of assessment to the Federal Minister for Agriculture, Forestry, Environment and Water Management their waste property for the intended use (Annex 9 Chapter 1.5). In the records according to the Waste Balance Ordinance, BGBl. II No 497/2008, as amended, is to document the end of the waste property in the form of a reservation in a product warehouse. For replacement fuel products made from wood waste and other replacement fuel products, a separate product warehouse must be recorded as a relevant part of the plant in the master data. The waste producer or the waste collector may draw up a certificate of assessment. These persons may be used to prepare the assessment certificate of an authorized subject or specialist institution. The prerequisite for the preparation of the assessment certificate is compliance with a quality assurance system according to the state of the art. A certificate of assessment must comply with the requirements of Annex 9, Chapter 2.8. Any change in the origin of the substitute fuel product, including input materials or the process, which has an impact on the quality of the substitute fuel product, must be accompanied by a new assessment. The assessment must be based on 1. January 2015 will be transmitted electronically by the register in accordance with § 22 AWG 2002.

(2) Paragraph 1 shall not apply to:

1.

hazardous waste and

2.

wastes which may present a risk in accordance with ÖNORM S 2104 "medical waste", issued on 1 July 2008, only within the medical sector.

(3) The waste owner who declares the end of the waste must submit the following information on the previous calendar year to the Federal Minister for Agriculture, Forestry, Environment and Water Management by 10 April of each year at the latest:

1.

the nature and quantity of the substitute fuels whose waste property has ended,

2.

changes to the intended customers and

3.

the results of the checks carried out in the context of external surveillance in accordance with Annex 9, Chapter 2.9.

This information must be available from 1 January 2008. January 2015 will be transmitted electronically by the register in accordance with § 22 AWG 2002.

(4) The waste owner who declares the end of the waste must, together with the replacement fuel product, have to transmit the following information to the customer:

1.

the valid proof of assessment, including the unique identifier and

2.

Data for the intended use according to Appendix 9, Chapter 1.5.

(5) On request, the Federal Minister for Agriculture, Forestry, Environment and Water Management must be granted access to the records and the records must be submitted on request. The records must be recorded as of 1. January 2015 is electronically conducted and stored electronically as well as electronically transmitted on request by means of the register according to § 22 AWG 2002. Evidence of assessment which has not yet been transmitted electronically by the register in accordance with § 22 AWG 2002 must be kept for at least seven years after the expiry of the validity period. At the request of the Federal Minister for Agriculture, Forestry, Environment and Water Management, they must be presented.

(6) In the case of electronic records and notifications, Section 11a (6) shall apply.

(7) The waste owner who declares the end of the waste must keep records of the customers of the replacement fuel products delivered (name, address, quantity, date) and keep them for seven years.

(8) In the production of substitute fuels, in which the waste owner wishes to declare the waste end, the ÖNORM CEN/TS 15358 " Solid secondary fuels-quality management systems-Special requirements for use in the case of the waste management system must be Manufacture of solid secondary fuels ", issued on 1 July 2006, including a quality management system with external quality assurance."

20. According to § 19a, the following § § 19b and 19c shall be inserted together with the headings:

" Transitional provisions for waste subject to § 6a (1)

§ 19b. (1) Insofar as 1. Jänner 2011 for waste subject to § 6a (1) are contained in existing authorisations deviating provisions, these 12 months after the entry into force pursuant to § 20 para. 4 are no longer to be applied and from this date the requirements shall apply. of this Regulation.

(2) Where existing authorisations for waste are contained in accordance with Article 6a (1), which contain a higher level of protection than this Regulation, the owner of the co-incineration plant shall, within six months of the entry into force, of this Regulation, in accordance with Article 37 (4) (1) of the AWG 2002, to the Authority, setting out the limit values (Median and 80-er percentile) with regard to sampling, sampling and implementation of the provisions of this Regulation. Studies for the parameter or parameters concerned shall be subject to the same level of protection as in the existing authorisation is reached. In this case, the changeover to the new rules for sampling, sampling and carrying out the studies with regard to the parameters concerned must be taken from the final date of knowledge of the adjustment, but at the earliest from 1. Jänner 2012, take place.

Transitional provisions for replacement fuel products

§ 19c. From the 1st January 2012, this Regulation shall apply to replacement fuels which are before 1. Jänner 2011 as products have been used and will continue to be used. "

21. In § 20, the following paragraph 4 is added:

" (4) The promulgation clause, § 2 (2), (3), (4) and (5), § 3, § 4 (1) (9), § 5 (1) Z 7, § 5a and the title, § 6 (2), (3), (5) and (6), § 6a including the title, § 7 (7) and (11), § 11a including the title, § 12 (4), § 15 (1), § 18a and the heading, § 19b together with the title, § 19c and title, Appendix 1, Chapter 1, Appendix 2, Chapter 2.1, Appendix 4, Chapter 1, Appendix 5, Appendix 6, point B, Z 13, Appendix 8, and Appendix 9 in the version of the BGBl Regulation. II No 476/2010 are due to 1. Jänner 2011 in force.

22. Annex 1, Chapter 1. Half-hourly averages (f) are:

" f)

Nitrogen oxides (NO and NO 2 ), specified as NO 2

at a nominal capacity of up to 2 tonnes Waste /h

-for new installations

200

mg/m³

-for existing installations

300

mg/m³

at a nominal capacity of more than 2 to 6 tonnes Waste /h

200

mg/m³

at a nominal capacity of more than 6 tonnes Waste /h

100

mg/m³ "

Appendix 2, Chapter 2.1, point (g) reads:

" (g)

If ammonia or ammonium compounds are used to reduce the emissions of nitrogen oxides, the approval authority shall require a limit value for the ammonia emissions from the denitrification. "

24. In Appendix 4, Chapter 1, the table shall be supplemented by the following line:

NH 3

25

"

25. Appendix 5 is:

" Appendix 5

(to § 4 (1) Z 9, § 7 (1), § 9 (1), § 10 (3) and § 11 (1))

Sampling and analysis methods for emission measurements 1 )

Parameters

Rule Set

Organic substances

(C org )

ÖNORM EN 12619

Edition 1999 09 01

Emissions from stationary sources-Determination of the mass concentration of the entire gaseous organically bound carbon in low concentrations in exhaust gases-Continuous process using a flame ionization detector

Carbon monoxide (CO)

ÖNORM EN 15058

Issue 2006 08 01

Emissions from stationary sources-Determination of the mass concentration of carbon monoxide (CO)-Reference method: Non-dispersive infrared spectrometry

Hydrogen chloride

(HCl)

ÖNORM EN 1911

Edition 1998 07 01

Emissions from stationary sources-Manual method for the determination of HCl

Part 1

Intake of the progas

Part 2

Absorption of gaseous compounds

Part 3

Analysis of absorption solutions and calculation of results

Hydrogen fluoride

(HF)

VDI 2470 sheet 1

Measurement of gaseous emissions; measurement of gaseous fluorine compounds; absorption processes

(Note: The analytical determination by means of ion chromatography is also permissible-ÖNORM EN ISO 10304-1 " Water condition-Determination of dissolved anions by means of liquid ion chromatography-Part 1: Determination of bromide, chloride, Fluoride, Nitrate, nitrite, phosphate and sulphate ", issued on 1 August 2009

)

Sulphur dioxide

(SO 2 )

ÖNORM EN 14791

Issue 2006 04 01

Emissions from stationary sources-Determination of the mass concentration of sulphur dioxide-Reference methods

Nitrogen oxides

(NO + NO 2 )

ÖNORM EN 14792

Issue 2006 04 01

Emissions from stationary sources-Determination of the mass concentration of nitrogen oxides (NO X ) -Reference method: chemiluminescence

dustlike emissions

ÖNORM EN 13284-1

Issue 2002 03 01

Emissions from stationary sources-Determination of the dust mass concentration at low dust concentrations-Part 1: Manual gravimetric procedure

ÖNORM EN 13284-2

Edition 2004 12 01

Emissions from stationary sources-Determination of the dust mass concentration at low dust concentrations-Part 2: Automatic measuring devices

ÖNORM M 5861-1

Edition 1993 04 01

Manual determination of dust concentrations in flowing gases-Gravimetric procedure-General requirements

ÖNORM M 5861-2

Edition 1994 04 01

Manual determination of dust concentrations in flowing gases-Gravimetric process-Special measurement requirements

VDI 2066 sheet 1

Measurement of particles-dust measurements in flowing gases-Gravimetric determination of dust loading

Heavy metals:

Antimony (Sb)

Arsenic (As)

Lead (Pb)

Cadmium (Cd)

Chromium (Cr)

Cobalt (Co)

Copper (Cu)

Manganese (Mn)

Nickel (Ni)

Mercury (Hg)

Thallium (Tl)

Vanadium (V)

Tin (Sn)

ÖNORM EN 13211

Edition 2005 05 01

Air quality-Emissions from stationary sources-Manual procedure for the determination of total mercury concentration (consolidated version)

ÖNORM EN 14884

Issue 2006 03 01

Air quality-Emissions from stationary sources-Determination of total mercury concentration: Automatic measuring devices

ÖNORM EN 14385

Edition 2004 05 01

Emissions from stationary sources-Determination of the total emission of As, Cd, Cr, Co, Cu, Mn, Ni, Pb, Tl and V

Polychlorinated dibenzo-p-dioxins and dibenzofurans

(PCDD/F)

ÖNORM EN 1948

Edition 2006 05 01

Emissions from stationary sources-Determination of the mass concentration of PCDD/PCDF and dioxin-like PCBs

Part 1

Sampling of PCDD/PCDF

Part 2

Extraction and purification of PCDD/PCDF

Part 3

Identification and quantification of PCDD/ PCDF

Ammonia
(NH) 3 )

VDI 3496 sheet 1

Measurement of gaseous emissions; Determination of the basic nitrogen compounds detectable by absorption in sulphuric acid

Oxygen
(O 2 )

ÖNORM EN 14789

Issue 2006 04 01

Emissions from stationary sources-Determination of the volume concentration of oxygen (O 2 ) -Reference procedure: paramagnetism

Water vapour content

ÖNORM EN 14790

Issue 2006 04 01

Emissions from stationary sources-Determination of water vapour in lines

Equivalence of reference methods

ÖNORM CEN/TS 14793

Edition 2005 07 01

Emissions from stationary sources-Laboratory internal validation of alternative methods by comparison with a reference method

Emission measuring instruments and systems

ÖNORM M 9410

Edition 1991 01 01

Air pollution control; measurement technology; definitions and characteristics of continuously operating concentration measuring instruments for emissions and immissions

ÖNORM M 9411

Edition 1999 11 01

Continuously working concentration measurement systems for emissions of air pollutants-requirements, installation and maintenance

ÖNORM M 9412

Edition 2008 12 01

Requirements for evaluation devices for continuous emission measurements of air pollutants

Part 1

Data collection and output

Part 2

Aptitude Check

ÖNORM EN 15259

Edition 2007 12 01

Air quality-Measurement of emissions from stationary sources-Measurement strategy, measurement planning, measurement reports and design of measuring stations

Quality assurance for automatic measuring devices, measurement uncertainty

ÖNORM EN 14181

Edition 2004 09 01

Emissions from stationary sources-quality assurance for automatic measuring devices

VDI 3950

Emissions from stationary sources-quality assurance for automatic measuring and electronic evaluation devices

Analytical methods for residues

Parameters

Rule Set

Total organic carbon (TOC)

ÖNORM EN 13137

Edition 2001 12 01

Characterization of waste-determination of the total organic carbon (TOC) in waste, sludge and sediments

Loss of glow

ÖNORM EN 15169

Edition 2007 05 01

Characterization of waste-determination of the loss of ignition in waste, sludge and sediments "

26. Appendix 6 point B Z 13 reads:

" 13.

Waste used:

Label * 2 , annual quantity * 2 , where appropriate the identifier (s) of the assessment certificate (s), GLN of the BE_ABIL * 1 , breakdown of the quantity used according to origin * 2 "

The following Annexes 8 and 9 shall be added to Annex 7:

" Annex 8

(to § 6a (1))

Requirements for waste incineration in co-incineration plants

1.

Limit values for waste incineration in co-incineration plants

1.1

Limit values for substitute fuels when used in equipment for cement production

1.2

Limit values for substitute fuels when used in power plant installations

1.3

Limit values for substitute fuels for use in other co-incineration plants

1.4

Limit values for waste, which are not substitute fuels and which are incinerated

1.5

Additional requirements for waste oils and solvents

1.6

Cd and Hg limit values for sewage sludges and paper fibre residues

1.7

Compliance with limit values

1.8

Calculation of the medians and the 80-er percentile

2.

Requirements for sampling, sampling and carrying out of studies

2.1

Sampling planning

2.2

Sampling rules for waste streams > 40 000 t/a

2.2.1

Investigation of the first lot (in the first year)

2.2.2

Investigations from the second lot (in the first year)

2.2.3

Pre-information

2.2.4

Investigations from the second year

2.2.5

Limitation of the investigation framework

2.3

Sampling rules for waste, excluding waste streams > 40 000 t/a

2.3.1

Investigation of the first Loses

2.3.2

Investigations from the second lot

2.4

Sampling requirements for liquid waste

2.4.1

Investigation of the first Loses

2.4.2

Investigations from the second lot

2.5

Resamples

2.6

Exceptions to the test

2.7

Heating value

2.8

PCB

2.9

Sample preparation

2.10

Determination procedure

2.11

X-ray fluorescence analysis

2.12

Evidence of assessment

2.13

Identity Control

2.14

External monitoring

1.

Limit values for waste incineration in co-incineration plants

1.1

Limit values for substitute fuels when used in equipment for cement production

The limit values apply to the plant parts of cementing plants in which cement clinker is fired (furnace plant according to § 2 Z 1 lit. c Cement V 2007, BGBl. II No 60/2007, consisting of the rotary kiln, the cyclone or rust preheater and the calcination agent).

Parameters

Limit values [mg/MJ]

Median

80-he Perzentil

Sb

7

10

S

2

3

Pb

20

36

Cd

0.23 1 )

0.46 1 )

Cr

25

37

CO

1.5

2.7

Ni

10

18

Hg

0.075

0.15

1 ) For quality-assured substitute fuels (key number 91108 according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended), a limit value of 0.45 mg/MJ applies to the median, and a limit value of 0.7 mg/MJ for the 80-th percentile.

1.2

Limit values for substitute fuels when used in power plant installations

The limit values shall apply to boilers which use mainly hard coal or lignite and which are used for the production of electricity and district heating. The proportion of the fuel heat output from the combustion of waste at the total fuel heat output is limited to a maximum of 15%.

Parameters

Limit values [mg/MJ]

Share of BWL 1 ) ≤ 10%

Share of BWL 1 ) ≤ 15%

Median

80-he Perzentil

Median

80-he Perzentil

Sb

7

10

7

10

S

2

3

2

3

Pb

23

41

15

27

Cd

0.27

0.54

0.17

0.34

Cr

31

46

19

28

CO

1.4

2.5

0.9

1.6

Ni

11

19

7

12

Hg

0.075

0.15

0.075

0.15

1 ) The percentage of the fuel heat output from the combustion of waste in the total fuel heat output.

1.3

Limit values for substitute fuels for use in other co-incineration plants

The limit values apply to co-incineration plants with the exception of systems for the production of cement and power plants.

Parameters

Limit [mg/MJ]

Median

80-he Perzentil

Sb

7

10

S

1

1.5

Pb

15

27

Cd

0.17

0.34

Cr

19

28

CO

0.9

1.6

Ni

7

12

Hg

0.075

0.15

For recurrent production-specific waste incinerated at the site of origin or other nearby sites, the limit values laid down in Chapter 1.2 (columns for a proportion of fuel heat output ≤ 10%) shall apply.

1.4

Limit values for waste, which are not substitute fuels and which are incinerated

The limit values shall apply to all co-incineration plants.

Parameters

Limit [mg/kg TM]

Median

80-he Perzentil

Sb

35

50

S

5

7.5

Pb

75

135

Cd

0.85

1.7

Cr

95

140

CO

4.5

8

Ni

35

60

Hg

0.375

0.75

For recurrent production-specific waste incinerated at the site of production or other nearby sites, the following limit values shall apply:

Parameters

Limit [mg/kg TM]

Median

80-he Perzentil

Sb

35

50

S

10

15

Pb

115

205

Cd

1.35

2.7

Cr

155

230

CO

7

12.5

Ni

55

95

Hg

0.375

0.75

1.5

Additional requirements for waste oils and solvents

For waste oils and solvents, a limit value for the sum of PCBs is set at a level of 10 mg/kg. For the purpose of determining the sum of PCBs, the sum of the following seven compounds shall be determined: PCB 28, PCB 52, PCB 101, PCB 118, PCB 138, PCB 153 and PCB 180. The thermal treatment of waste oils and solvents with a PCB content of greater than 10 mg/kg shall be allowed, provided that a verifiable evidence shows that the co-incineration plant will ensure a secure destruction of the PCBs, where an exception to the operating conditions with regard to temperature and residence time is not permitted in accordance with Article 7 (6).

1.6

Cd and Hg limit values for sewage sludges and paper fibre residues

By way of derogation from the provisions of Chapters 1.1, 1.2 and 1.3, sewage sludge and paper fibre residues (waste of the key number groups 943, 945 and 948 in accordance with the Waste Directory Regulation, BGBl. II No 570/2003, as amended), for the parameters Cd and Hg, the following limit values.

Parameters

Limit [mg/MJ]

Median

80-he Perzentil

Cd

0.8

0.95

Hg

0.15

0.25

1.7

Compliance with limit values

Compliance with limit values shall be assessed separately for each waste, other than waste as defined in Chapter 2.6, by origin and by waste type.

For the determination of the median and the 80-er percentile, the 10 most recent test results are used. In the case of less than 10 analytical results, any pre-information may have to be taken into account up to a maximum of 10 test results. At the beginning of investigations 5 to 9 analytical results (incl. if any pre-information may be available), the median and the 80-er percentile must also be determined. The median and 80% percentile values calculated in accordance with Chapter 1.8, expressed in unit mg/kg TM, in the case of liquid waste in unit mg/kg, shall be determined by the calorific value (the arithmetic mean of the results of the examination of the last two years). 12 months) in relation to the dry matter and divided into liquid waste in relation to the original substance. By way of derogation, the test results of all the lots investigated are used for the determination of the median, the 80-er percentile and the mean value for the calorific value in the case of one-off waste. The values thus obtained represent the assessment values. The limit value shall be deemed to be complied with if the assessment value does not exceed the limit value.

By way of derogation, in the case of waste which is not a substitute fuel and which are incinerated, the calculated values in the unit mg/kg TM are the assessment values (ie. there is no division by the calorific value).

If fewer than five analysis results are present (at the beginning of the investigations), the arithmetic mean (assessment value) is calculated from the analysis results in deviation from the above explanations. In this case, the limit value shall be deemed to be complied with if the assessment value does not exceed the limit value for the median and if no individual measurement result exceeds the limit value for the 80-er percentile.

In the case of waste oils and solvents, each analytical result must comply with the PCB limit value.

Compliance with the limit values must be checked after each examination of a lot (in the course of the examination of the first lot after each partial quantity examined) and the documentation must be made in the assessment certificate (see Chapter 2.12). The current proof of assessment is valid from the date of transmission until the next assessment proof, but at the latest one year and for waste streams > 40 000 t/a three months.

Elimination of outliers is not permitted in principle.

If an assessment value exceeds the limit value for the median or the 80 percentile, the waste must not be incinerated and the studies of the first lot in accordance with Chapter 2.2.1, 2.3.1 or 2.4.1 must be reinitiated. The overrun must be communicated to the Authority without delay.

If substantial changes occur in the process of the waste, so that a waste stream no longer falls within the same quality, an investigation shall be carried out in accordance with the first batch in accordance with Chapter 2.2.1, 2.3.1 or 2.4.1 will be reinitiated.

1.8

Calculation of the medians and the 80-er percentile

The median is the value which decomposes the value series ordered according to their size into two parts of equal size. Ie. the data is ordered by size, and you look at the value in the middle of the list.

In the case of an even number of data, the arithmetic mean of the two average values is formed. The figure thus obtained has the property that half of the values below it is half above.

The 80-er percentile is the value that decomposes the value series ordered according to their size into two parts, so that 80% of all values are less than or equal to and 20% of all values are greater than or equal to the values.

To do this, the number of values is multiplied by 0.8.

If this product does not produce a whole number, then the whole number following the product must be determined. The value of the value series associated with this number represents the 80-er percentile.

If this product yields an integer, the value of the value row corresponding to this number must be added to the next value of the value series and the sum must be divided by two.

2.

Requirements for sampling, sampling and carrying out of studies

Sampling and sample preparation, as well as analytical studies, may be carried out by the waste producer, waste collector, co-incineration plant owner or by a qualified person or specialist institution.

Each waste must be tested separately according to the origin and type of waste in the state of use in which it is incinerated, in order to be able to carry out the assessment of the waste for incineration in co-incineration plants.

2.1

Sampling planning

A sampling plan for each waste must be separated according to origin and type of waste in accordance with ÖNORM CEN/TS 15442 "Solid secondary fuels-methods for sampling", issued on 1 January 2008. Jänner 2007. In the case of liquid waste, according to ÖNORM S 2123-4, " sampling plans for waste-part 4: sampling liquid or of pasty waste ", issued on 1 November 2003.

In order to assess the existence of a waste stream > 40 000 t/a, the water content of the waste must be taken into account, in which the actual test takes place.

2.2

Sampling rules for waste streams > 40 000 t/a

The amount of lobe, ie. that amount of a waste whose properties are to be determined is the amount of waste produced in the period of one month. The subsets for the investigations correspond in each case to an average daily production quantity. The number and mass of samples must be calculated in accordance with ÖNORM CEN/TS 15442, using at least 6 to 10 samples for the preparation of the qualified samples (daily mixing samples). The minimum sample quantity for the qualified sample must be calculated according to ÖNORM CEN/TS 15442.

2.2.1

Investigation of the first lot (in the first year)

From the first batch, at least 10 qualified samples must be evenly distributed (e.g. at least two to three daily mixing samples per week), separately prepared and separately supplied to the analysis.

2.2.2

Investigations from the second lot (in the first year)

From the second lot of the first year, at least six qualified samples per lot shall be evenly distributed (one or two daily mixing samples per week), three of which shall be sampled from the sample. If the last assessment value (median or 80-er percentile) is for one or more parameters in the area close to the limit, all six qualified samples must be examined separately at least for those parameters. The area close to the limit value is the range ≥ 80% of the limit value.

2.2.3

Pre-information

If the number of analytical results within the framework of the pre-information is ≥ 20, the studies referred to in Chapter 2.2.4 may be initiated directly. However, these pre-existing test results must be carried out with comparable procedures (taking into account the size of the subsets examined, the minimum quantities for samples and qualified samples, the sample preparation and the ). If pre-information has not been obtained on the basis of a full conclusion, it may be determined by the provision or Derivation of factors for the respective waste (separate by type of waste) is a conversion of the values obtained on the basis of the preliminary information. The assessment of the presence of this comparability must be shown in the assessment certificate.

2.2.4

Investigations from the second year

At least four qualified samples must be evenly distributed per lot (daily mixing samples), two of which shall be sent to the examination. If the last assessment value (median or 80-er percentile) is for one or more parameters in the area close to the limit value, all four qualified samples must be examined for these parameters. The area close to the limit value is the range ≥ 80% of the limit value.

2.2.5

Limitation of the investigation framework

If the last assessment values for one or more parameters for the ratio of 80-er percentile to median are given a value of ≤ 1.5, the number of qualified samples to be examined can be halved for these parameters (note: Unless a whole number is obtained, the next integer must be rounded up. This restriction of the investigation framework shall be admissible for investigations starting from the second lot of the first year.

If either the last assessment value (Median and 80-er percentile) is for one or more parameters in the range ≤ 20% of the limit value (not earlier than the second lot of the first year) or the assessment values of the past 12 months (median and 80-he percentile) for one or more parameters in the range ≤ 50% of the limit value, the number of qualified samples to be examined can be halved for these parameters (note: if there is not a whole number, the next step must be taken to the next the whole number are rounded up).

In the case of recurring production-specific waste of comparable composition, which is the same type of waste according to the Waste Directory Regulation, BGBl. II No 570/2003, as amended, and which are produced at different production sites of a company, the qualified samples may be sampled at the respective production sites at the earliest starting from the second lot of the the first year.

In the case of recurring production-specific waste, the rounding-up rule referred to in the preceding paragraphs shall not apply.

2.3

Sampling rules for waste, excluding waste streams > 40 000 t/a

In the case of waste, other than waste streams > 40 000 tonnes/a, the amount of the lot is 1 500 tonnes.

2.3.1

Investigation of the first Loses

The first lot (ie. the first 1 500 tonnes) must be divided into subsets of 150 tonnes each, with the subsets 1, 3, 5, 7 and 9 having to be used for the studies.

For each subset to be examined, two qualified samples must be produced, one of which must be examined.

The number and mass of samples must be calculated in accordance with ÖNORM CEN/TS 15442, using at least 6-10 samples for the production of the qualified samples. The minimum sample quantity for the qualified sample must be calculated according to ÖNORM CEN/TS 15442.

If the assessment value (Median or 80-er percentile or in the case of less than five test results arithmetic mean or individual measurement result) for one or more parameters in the area close to the limit value, the second qualified sample shall also have to be separated at least to those parameters shall be examined. The area close to the limit value is the range ≥ 80% of the limit value.

Due to the already existing test results, the necessary examinations can be restricted in the first batch in the case of waste streams. However, these pre-existing test results must be carried out with comparable procedures (taking into account the size of the subsets examined, the minimum quantities for samples and qualified samples, the sample preparation and the ). If pre-information has not been obtained on the basis of a full conclusion, it may be determined by the provision or Derivation of factors for the respective waste (separate by type of waste) is a conversion of the values obtained on the basis of the preliminary information. The assessment of the presence of this comparability must be shown in the assessment certificate. If the number of analytical results within the framework of the preliminary information is ≥ 5, the first lot shall be examined in accordance with the requirements for the second lot.

In the case of waste streams, at least two qualified samples must be produced per calendar year, one of which must be examined for each parameter. If the last assessment value (median or 80-er percentile) is for one or more parameters in the area close to the limit value, the second qualified sample must also be examined separately at least on these parameters. The area close to the limit value is the range ≥ 80% of the limit value.

When using an automatic sampling device, the production of a qualified sample is sufficient for each quantity to be examined. From each qualified sample, two field samples (instead of two parallel-produced qualified samples) are produced for the subsequent studies.

2.3.2

Investigations from the second lot

From the second batch, two qualified samples shall be produced per 1 500 tonnes, one of which shall be sent to the examination.

The number and mass of the samples must be calculated in accordance with ÖNORM CEN/TS 15442, using a total of at least 24 samples for the production of the qualified samples. The minimum sample quantity for the qualified sample must be calculated according to ÖNORM CEN/TS 15442.

In the case of waste streams < 1 500 t/a, at least two qualified samples must be produced per calendar year, one of which must be examined for each parameter. The test must be carried out on a randomly selected subset of a maximum of 150 tonnes, with at least 6-10 samples having to be used for the preparation of the qualified samples.

When using an automatic sampling device, the production of a qualified sample is sufficient for each quantity to be examined. From this qualified sample, two field samples (instead of two parallel-produced qualified samples) are produced for the subsequent studies.

If the assessment value (median or 80-er percentile) is for one or more parameters in the area close to the limit value, the second qualified sample must also be examined separately at least for those parameters, unless these parameters are: Parameters the ratio of 80-er percentile to median gives a value of ≤ 1.5. The area close to the limit value is the range ≥ 80% of the limit value.

After the investigation of 12 lots of 1 500 tonnes, two qualified samples can be produced on waste streams-instead of every 1 500 t-per month (from any lot), one being sent to the test. If the number of analytical results within the framework of the pre-information is ≥ 16, it is possible to start directly with a monthly examination in the case of waste streams. However, these pre-existing test results must be carried out with comparable procedures (taking into account the minimum quantities for samples and qualified samples, the size of the subsets examined, the sample preparation and the ). If pre-information has not been obtained on the basis of a full conclusion, it may be determined by the provision or Derivation of factors for the respective waste (separate by type of waste) is a conversion of the values obtained on the basis of the preliminary information. The assessment of the presence of this comparability must be shown in the assessment certificate.

If, in the case of a recurrent production-specific waste (waste stream), either the last assessment value (Median and 80-er percentile) is in the range ≤ 20% of the limit value for one or more parameters, or the last 10 assessment values (Median and 80-er percentile) for one or more parameters in the range ≤ 50% of the limit value, the number of qualified samples to be examined for these parameters can be halved.

In the case of recurring production-specific waste of comparable composition, which is the same type of waste according to the Waste Directory Regulation, BGBl. II No 570/2003, which are in force in the current version, and which are produced at different production sites of a company, the qualified samples may be examined alternately at the respective production sites.

This means that it is not possible to examine each lot in the case of recurring production-specific waste.

2.4

Sampling requirements for liquid waste

In the case of liquid waste, the amount of lobe amounts to 1 500 tonnes.

2.4.1

Investigation of the first Loses

The first lot (ie. the first 1 500 tonnes) must be divided into subsets of 150 tonnes each, with the subsets 1, 3, 5, 7 and 9 having to be used for the studies. The production of the qualified samples is carried out in accordance with ÖNORM S 2123-4. From the qualified samples, a field sample (bulk sample from the qualified samples) is produced for the subsequent investigation for each selected subset.

Due to existing examination results, a limitation of the necessary examinations can be carried out in the first batch. However, these pre-existing test results must have been obtained using comparable methods (sampling, determination procedures). The assessment of the presence of this comparability must be shown in the assessment certificate. If the number of analytical results within the framework of the preliminary information is ≥ 5, the first lot shall be examined in accordance with the requirements for the second lot.

In the case of waste streams, at least one field sample must be examined for each calendar year on each parameter.

2.4.2

Investigations from the second lot

In the case of liquid waste, the production of the qualified samples is carried out in accordance with ÖNORM S 2123-4. From the second batch, a field sample (sample of the qualified samples) per lot for the subsequent examination will be produced from the qualified samples. After the investigation of 12 lots of 1 500 tonnes, a field sample (sample of the qualified samples) per month for the subsequent examination can be produced for waste streams-instead of all 1 500 t-from the qualified samples. .

In the case of waste streams, at least one field sample must be examined for each calendar year on each parameter.

2.5

Resamples

Recovery samples shall be produced from all laboratory samples and kept for inspection in the context of external surveillance in accordance with Chapter 2.14, but at least 6 months. A drying of the recovery samples at a maximum of 40 ° C is permitted. By way of derogation, in the case of waste which is biological agents (§ 40 para. 4 ASchG), drying can be carried out at 105 ° C, provided that there is evidence that no difference in the determination of the Hg content of the waste in the analytical results is determined. between drying at 40 ° C and 105 ° C, or the Hg content of the waste is less than or equal to 0.02 mg/MJ (median) and less than or equal to 0.03 mg/MJ (80-er percentile).

The minimum requirements for laboratory testing in accordance with the ÖNORM CEN/TS 15442 must be met.

2.6

Exceptions to the test

No analytical studies are required in the incineration of the following waste:

a)

Old tires (key number 57502 according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended),

b)

wastes which may pose a risk in accordance with ÖNORM S 2104 "medical waste", issued on 1 July 2008, only inside and inside and outside the medical sector; and

c)

wastes according to Appendix 9, Chapter 2.4.

The proof of compliance with the limit values referred to in Chapter 1 shall be deleted.

2.7

Heating value

In the parameter calorific value, a limitation of the frequency of examination is possible. However, the determination of the calorific value must be carried out in at least every tenth laboratory sample.

2.8

PCB

Polychlorinated biphenyls (PCBs) are only part of the parameter range in the case of waste oils and solvents. The investigation of PCBs in waste oils and solvents must be carried out on a field sample of the first batch and from the second batch in each field sample, but at least once a year.

2.9

Sample preparation

The laboratory sample must be manufactured in accordance with the ÖNORM CEN/TS 15443 "Solid secondary fuels-Process for the production of laboratory samples", issued on 1 January 2008. Jänner 2007. The preparation of the test sample from the laboratory sample must be carried out in accordance with the ÖNORM CEN/TS 15413 "Solid secondary fuel processes for the preparation of the test sample from the laboratory sample", issued on 1 December 2006.

By way of derogation, in the case of waste which is biological agents (§ 40 para. 4 ASchG), drying can be carried out at 105 ° C, provided that there is evidence that no difference in the determination of the Hg content of the waste in the analytical results is determined. between drying at 40 ° C and 105 ° C, or the Hg content of the waste is less than or equal to 0.02 mg/MJ (median) and less than or equal to 0.03 mg/MJ (80-er percentile).

In order to obtain the test sample, a reduction of the particle size to < 0.5 mm must be carried out.

The requirements for the minimum sample quantities in accordance with Annex D of the ÖNORM CEN/TS 15442 must be complied with for each step and each examination procedure.

The foreign parts sorted out during the sample preparation process must be documented.

In the case of liquid waste, according to ÖNORM EN 15002, "Characterization of waste-preparation of test quantities from the laboratory sample", issued on 1 April 2006, must be handled.

2.10

Determination procedure

The following methods of determination must be applied:

a)

The determination of the trace elements must be carried out in accordance with process A of the ÖNORM CEN/TS 15411 "Solid secondary fuel processes for determining the content of trace elements (As, Ba, Be, Cd, Co, Cr, Cu, Hg, Mo, Mn, Ni, Pb, Sb, Se, Tl, V and Zn)", issued on 1 December 2006, with a full conclusion regarding the parameters to be determined (for example, with the aid of a adapted temperature control). For certain cases, alternative methods of exclusion may be authorised, specifying the justification for the selection of the specific inference procedure and, in any event, achieving a full breakdown of the elements of interest must be. The direct analysis of Hg in accordance with the method cited in EPA Method 7473 "Mercury in Solids and Solutions by Thermal Decomposition, Amalgamation and Atomic Absorption Spectrophotometry" is permitted.

b)

The determination of the calorific value must be carried out in accordance with ÖNORM CEN/TS 15400 "Solid secondary fuels-Method for determining the calorific value", issued on 1 December 2006. The required weight can be reduced to at least 0.2 g (without combustion aids).

c)

The determination of the water content must be carried out according to

-

ÖNORM CEN/TS 15414-1 "Solid secondary fuels-Determination of the water content using the furnace drying method-Part 1: Determination of the content of total water by means of reference methods", issued on 1 December 2006, or

-

ÖNORM CEN/TS 15414-3 "Solid secondary fuels-Determination of the water content using the furnace drying method-Part 3: Water content in ordinary analysis samples", issued on 1 December 2006,

,

d)

The determination of the content of C, H and N must be carried out according to ÖNORM CEN/TS 15407 "Solid secondary fuel processes for the determination of the content of carbon (C), hydrogen (H) and nitrogen (N)", issued on 1 December 2006.

e)

The determination of PCBs in liquid substitute fuels must be carried out in accordance with ÖNORM EN 12766-1 " Mineral oil products and used oils-Determination of PCBs and related products-Part 1: Separation and determination of selected PCB Congeners by means of Gas chromatography (GC) using an electron capture detector (ECD) ", issued on 1 September 2000.

Certified reference materials must preferably be used to collect the quality of the information and analysis. Alternatively, it is possible to use suitable own control samples, the composition of which has been determined by suitable methods.

The limits of detection and determination must be determined in accordance with DIN 32645 "Chemical analysis-detection, detection and determination limit under repeatable conditions-terms, procedures, evaluation". If an examination result is below the limit of determination, the value of the half-determination limit must be used for the calculation of the assessment values. If an examination result is below the detection limit, the value of zero must be used for the calculation of the assessment values.

2.11

X-ray fluorescence analysis

The X-ray fluorescence analysis (RFA) is approved as an alternative method for the determination of Sb, As, Pb, Cd, Cr, Co and Ni. The determination must be carried out in accordance with the ÖNORM EN 15309 "Characterization of wastes and soils-Determination of the elemental composition by x-ray fluorescence analysis", issued on 1 July 2007. In the case of liquid waste, the procedure must be at least according to standardised internal operating instructions.

For each waste (separate by type of waste, but no distinction according to origin), a separate calibration must be carried out using the determination procedures set out in Chapter 2.10. For calibration, preferably certified reference materials must be used. [0050] Alternatively, suitable own control samples can be used.

2.12

Evidence of assessment

The proof of assessment shall include, on the one hand, the documentation of all the information relevant to the relevant waste and the results of the investigation resulting from the preliminary information and the investigations, and those for the feasibility of the assessment. and plausibility check of the assessment is required. On the other hand, all assessments, conclusions and justifications for the possibility of incineration of waste in co-incineration plants must be included.

The respective current assessment of a waste stream must include all the contents of the previous assessment documents.

A proof of assessment shall include:

a)

the handle

b)

the reference to previous assessments;

c)

the creator;

d)

the owner of the waste, unless he or she is the owner of the waste;

e)

the date of first transmission and the period of validity of the proof of assessment;

f)

the waste information referred to in Article 11a (2), where the waste information must be checked and, if necessary, modified;

g)

If there is no waste information, the following:

i)

Waste type according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended and in the case of movement, in addition to Annex 2 of the Waste Directory Regulation, BGBl. II No 570/2003, as amended; the type of waste must be in accordance with the allocation criteria of the Waste Directory Regulation, BGBl. II No 570/2003, as amended;

ii)

Origin according to the Waste Balance Ordinance, BGBl. II No 497/2008, in the current version;

iii)

description of the waste (in particular odour, colour, consistency);

iv)

in the case of hazardous waste: hazard-relevant properties; physical parameters-as far as the target is concerned-in accordance with Table 1, point 13 of the ÖNORM S 2110 "Investigation of waste for chemical-physical or thermal treatment", issued on 1 January 2008. September 2001; chemical composition and other information to the extent that this is necessary to assess the suitability for the intended combustion process; substances with which the waste may in any case not be mixed, and precautions for use in dealing with the waste;

v)

in the case of a one-off waste, the total quantity of waste in t, in the case of a waste stream, the estimated annual amount of waste in t;

vi)

the description of the origin of the waste and any treatment steps; the description of the input materials of the process in which the waste is obtained and the output materials of the treatment; and an indication of any contamination and any contamination; and whose cause;

vii)

In addition, the site of the case may be indicated, as well as photos of the waste to be incinerated in co-incineration plants, and file attachments, provided that this is conducive to the assessment of the waste being assessed.

h)

Presentation of the included pre-information, ie. existing studies and their results; the use of different methods to assess comparability;

i)

indication of the sample preparation and method of determination used; in particular, the use of alternative digestion methods;

j)

all the results of the analysis and their reference to the associated lot by means of test, laboratory, field and qualified sample;

k)

information on the restriction of the number of qualified samples to be examined, on the basis of the statement of reasons;

l)

the calculation of the assessment values;

m)

Assessment of the waste for incineration in co-incineration plants;

n)

in the case of waste streams, specifications for the investigations of the next lot (e.g. number and timing of the tests, limitation of the qualified samples to be examined and parameters).

The assessment certificate shall be accompanied by the sampling plan with calculations and bases, such as preliminary surveys or other documents used for the assessment, any updates in the course of the investigations and the sampling protocols. can be connected.

2.13

Identity Control

In the context of the entry control, sample-like analytical tests must be carried out to verify the identity of the waste delivered. These identity checks must be carried out at least once a year. If, in the case of visual control of the waste, contamination or incorrect assignment to a type of waste is suspected, a punctual test must be carried out.

In the case of waste streams > 40 000 t/a, the analytical examination must be carried out at an average daily production quantity, and for all other waste at a subset of 150 tonnes.

The determination of the number and mass of samples as well as the minimum sample quantity for the qualified sample, the production of the field sample in the case of liquid waste, the sample preparation and the determination procedures must be carried out in accordance with Chapter 2. are carried out.

Recovery samples shall be produced from all laboratory samples and kept for inspection in the context of external surveillance in accordance with Chapter 2.14, but at least 6 months. A drying of the recovery samples at a maximum of 40 ° C is permitted. The minimum requirements for laboratory testing in accordance with the ÖNORM CEN/TS 15442 must be met.

By way of derogation, in the case of waste which is biological agents (§ 40 para. 4 ASchG), drying can be carried out at 105 ° C, provided that there is evidence that no difference in the determination of the Hg content of the waste in the analytical results is determined. between drying at 40 ° C and 105 ° C, or the Hg content of the waste is less than or equal to 0.02 mg/MJ (median) and less than or equal to 0.03 mg/MJ (80-er percentile).

If no individual measurement result exceeds the limit value for the 80-er percentile for all parameters, the identity check is considered to be positive. If the individual measurement result for one or more parameters exceeds the limit value for the 80-er percentile, then the identity check must be repeated at least for these parameters. If the individual measurement result for one of these parameters exceeds the limit value for the 80-er percentile for one of these parameters, the identity of the waste is no longer given and it is necessary for this waste to be carried out in accordance with the the first batch shall be started in accordance with Chapter 2.2.1, 2.3.1 or 2.4.1 and a new proof of assessment shall be drawn up.

A report must be drawn up on the basis of the assessment of the assessment of the identity of the person in question.

If no analytical studies are required in accordance with Chapter 2.6, no identity check shall be carried out.

If the identity check is carried out by an authorised subject or institution, the results of the examination may also be credited for external surveillance in accordance with Chapter 2.14.

2.14

External monitoring

The owner of a co-incineration plant must have at least once a year verified compliance with the requirements of this installation by a qualified specialist or technical institute.

The external surveillance shall include in particular:

a)

the verification of the evidence of completeness and accuracy;

b)

the sampling and analysis of waste (with the exception of the waste referred to in Chapter 2.6): any type of waste from which at least 1 500 t/a shall be incinerated shall at least once be sampled and analysed (an average of Daily production quantity for waste streams > 40 000 tonnes; for all other waste, a subset (150 tonnes) must be selected randomly and a qualified sample is produced from it); a report must be drawn up on the basis of each individual investigation the assessment certificate shall be drawn up;

c)

the analysis of return samples; at least one randomly selected reset sample must be analysed for each waste type. In the case of recurring production-specific waste, an analysis of the rehearsals may be carried out; a report must be drawn up on the basis of the evidence of assessment of each individual investigation;

d)

the verification of the calibration of the RFA equipment by means of control analyses, in so far as investigations are carried out in accordance with Chapter 2.11;

e)

the verification of the results of identity checks.

The determination of the number and mass of samples as well as the minimum sample quantity for the qualified sample, the production of the field sample in the case of liquid waste, the sample preparation and the determination procedures must be carried out in accordance with Chapter 2. are carried out.

From all laboratory samples, rehearsals must be produced and kept for at least one year. A drying of the recovery samples at a maximum of 40 ° C is permitted. The minimum requirements for laboratory testing in accordance with the ÖNORM CEN/TS 15442 must be met.

By way of derogation, in the case of waste which is biological agents (§ 40 para. 4 ASchG), drying can be carried out at 105 ° C, provided that there is evidence that no difference in the determination of the Hg content of the waste in the analytical results is determined. between drying at 40 ° C and 105 ° C, or the Hg content of the waste is less than or equal to 0.02 mg/MJ (median) and less than or equal to 0.03 mg/MJ (80-er percentile).

Compliance with the limit values must be assessed in accordance with Chapter 1.7.

The RFA is not approved as a determination procedure for the investigations carried out by the authorized subject or specialist institution in the context of external supervision.

If, in the course of the inspections, deviations from the consenient state of the co-incineration plant arise in the sense of this Annex, the holder of the co-incineration plant must notify the Authority without delay.

If the studies referred to in Chapters 2.1 to 2.10 and 2.13 are carried out by one for the vast majority of the test methods according to ÖVE/ÖNORM EN ISO/IEC 17025 "General requirements for the competence of testing and calibration laboratories", issued on 1 July 2008. The additional sampling and analysis of waste as well as the analysis of return samples in accordance with Chapter 2.14 (b) and (c) are not required.

If the studies referred to in Chapters 2.1 to 2.10 and 2.13 are carried out by an authorised subject or institution, no external surveillance under Chapter 2.14 is required.

Appendix 9

(to § 18a (1))

Quality requirements for replacement fuel products

1.

Limit values for the presence of waste in the case of replacement fuels and intended use

1.1

Limit values for replacement fuel products from wood waste

1.2

Limit values for other replacement fuel products

1.3

Compliance with limit values

1.4

Calculation of the medians and the 80-er percentile

1.5

Intended use

2.

Requirements for sampling, sampling and carrying out of studies

2.1

Sampling planning

2.2

Sampling rules

2.2.1

Investigation of the first Loses

2.2.2

Investigations from the second lot

2.3

Resamples

2.4

Exceptions to the test

2.5

Heating value

2.6

Sample preparation

2.7

Determination procedure

2.8

Evidence of assessment

2.9

External monitoring

1.

Limit values for the presence of waste in the case of replacement fuels and intended use

1.1

Limit values for replacement fuel products from wood waste

Wood waste is the waste of the key number group 17 according to the Waste Directory Ordinance BGBl. II No 570/2003, in the current version. Replacement fuels from wood waste must comply with the following limit values for the presence of the waste.

Parameters

Limit values [mg/kg TM]

Median

80-he Perzentil

S

1.2

1.8

Pb

10

15

Cd

0.8

1.2

Cr

10

15

Hg

0.05

0.075

Zn

140

210

Cl

250

300

F

15

20

Total PAK (EPA)

2

3

1.2

Limit values for other replacement fuel products

Other substitute fuels shall comply with the following limit values for the presence of the waste.

Parameters

Limit [mg/MJ]

Median

80-he Perzentil

Sb

0.5

0.75

S

0.8

1.2

Pb

4

6

Cd

0.05

0.075

Cr

1.4

2.1

CO

0.7

1.05

Ni

1.6

2.4

Hg

0.02

0.03

S

200

300

Cl

100

150

1.3

Compliance with limit values

For the determination of the median and the 80-er percentile, the 10 most recent test results are used. The verification of compliance with limit values is only possible after the existence of 10 test results.

The median values calculated in accordance with Chapter 1.4 and the 80% percentile specified in the Unit mg/kg TM-represent the assessment values for substitute fuel products from wood waste.

In the case of other substitute fuel products, the median and the 80% percentile values calculated in accordance with Chapter 1.4 shall be expressed in the unit mg/kg TM-by the calorific value (arithmetic mean of the results of the last 12 tests) months) in relation to the dry matter. By way of derogation, the test results of all the lots investigated are used for the determination of the median, the 80-er percentile and the mean value for the calorific value in the case of one-off waste. The values thus obtained represent the assessment values.

The limit value shall be deemed to be complied with if the assessment value does not exceed the limit value.

Elimination of outliers is not permitted in principle.

Compliance with the limit values must be checked after each examination of a lot, and documentation must be made in the proof of assessment (see Chapter 2.8). The current proof of assessment is valid from the date of transmission to the Federal Minister for Agriculture, Forestry, Environment and Water Management until the availability of the next assessment certificate, but at the most valid one year.

If an assessment value exceeds the limit value for the median or the 80-er percentile, the waste must not be placed on the market as a substitute fuel product and the studies of the first lot in accordance with Chapter 2.2.1 have to be reopened . The German Federal Minister for Agriculture, Forestry, the Environment and Water Management must be informed immediately of the overrun.

1.4

Calculation of the medians and the 80-er percentile

The median is the value which decomposes the value series ordered according to their size into two parts of equal size. The data are sorted according to size, and the arithmetic mean of the fifth and sixth values corresponds to the median.

The 80-er percentile is the value that decomposes the value series ordered according to their size into two parts, so that 80% of all values are less than or equal to and 20% of all values are greater than or equal to the values. The data are sorted according to size and the arithmetic mean of the 8. and 9. Value corresponds to the 80-er percentile.

1.5

Intended use

Replacement fuel products may only be used in installations with a rated thermal power of ≥ 50 kW, which shall have a dust limit of 20 mg/m 3 (as a half-hour average), or in installations subject to the scope of section 2 (1), are burnt.

As O 2 -reference shall be made to the oxygen content specified for emission limit values in the existing permit. If no emission limit values are laid down in the existing permit, the actual oxygen content in the exhaust gas shall be used. In the case of the incineration of replacement fuel products from animal meal or animal fat, the requirements laid down in Article 12 of Regulation (EC) No 1774/2002 laying down health rules for animal by-products not intended for human consumption, OJ L 327, 31.12.2002, p. No. OJ L 273, 10.10.2002 p. 1.

The reference to purchasers of replacement fuel products that they are demonstrably meeting the objective criteria for the end of the waste in accordance with this Regulation and that the above-mentioned provisions must be complied with in the incineration of these products, is, as information within the meaning of Article 32 (1) (d) of Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), OJ L 327, 30.12.2006, p. No. OJ L 396, 30.12.2006, p.

2.

Requirements for sampling, sampling and carrying out of studies

The sampling and sample preparation as well as the analytical examinations can be carried out by the waste producer, waste collector or by an authorized subject or specialist institution.

2.1

Sampling planning

There must be a sampling plan for each substitute fuel product according to ÖNORM CEN/TS 15442 "Solid secondary fuels-Procedures for sampling", issued on 1 January 2008. Jänner 2007.

2.2

Sampling rules

The amount of lobe amounts to 1 500 t.

2.2.1

Investigation of the first Loses

The first lot (ie. the first 1 500 tonnes) must be divided into subsets of 150 tonnes each, with the subsets 1, 3, 5, 7 and 9 having to be used for the studies.

At least two qualified samples must be produced and examined for each subset to be examined.

The number and mass of the samples shall be calculated in accordance with ÖNORM CEN/TS 15442, using at least 6 to 10 samples for the preparation of the qualified samples. The minimum sample quantity for the qualified sample must be calculated according to ÖNORM CEN/TS 15442.

At least two qualified samples must be produced per calendar year (with the exception of one-off waste) and shall be examined.

When using an automatic sampling device, at least one qualified sample must be produced for each subset to be examined. From this qualified sample, two field samples (instead of two parallel-produced qualified samples) are produced for the subsequent studies.

2.2.2

Investigations from the second lot

From the second batch, four qualified samples shall be produced per 1 500 tonnes, two of which shall be sent to the examination.

The number and mass of the samples must be calculated in accordance with ÖNORM CEN/TS 15442, using a total of at least 24 samples for the production of the qualified samples. The minimum sample quantity for the qualified sample must be calculated according to ÖNORM CEN/TS 15442.

In the case of substitute fuels < 1 500 t/a (except in the case of replacement fuels produced once), at least four qualified samples must be produced per calendar year, two of which must be examined for each parameter. The investigation must be carried out on a randomly selected subset of 150 tonnes, using at least 6 to 10 samples for the preparation of the qualified samples.

When using an automatic sampling device, at least one qualified sample must be produced for each subset to be examined. From this qualified sample, four field samples (instead of four parallel-produced qualified samples) will be produced for the subsequent studies.

If the assessment value (median or 80-er percentile) is for one or more parameters in the area close to the limit value, the third and fourth qualified samples must also be examined separately at least for these parameters. The area close to the limit value is the range ≥ 80% of the limit value.

2.3

Resamples

From all laboratory samples, rehearsals must be produced and kept for at least 12 months. A drying of the recovery samples at a maximum of 40 ° C is permitted.

The minimum requirements for laboratory testing in accordance with the ÖNORM CEN/TS 15442 must be met.

2.4

Exceptions to the test

No analytical studies shall be carried out for the following wastes:

a)

Untreated and untreated wood waste, which is treated separately at the site of the waste, and which comply with the allocation criteria of the Waste Directory Ordinance BGBl. II No 570/2003, as amended, must be assigned to the following types of waste (specification must be used):

i)

SN 17101 Rinde,

ii)

SN 17102 Swaiting, splint made of natural, clean, uncoated wood,

iii)

SN 17103 sawdust and sawdust from natural, clean, uncoated wood,

iv)

SN 17104 02 Wood grinding dust and sludge; (from) verifiably exclusively mechanically treated (m) wood

v)

SN 17201 02 Wood embales and wood waste, not contaminated; (from) demonstrably only mechanically treated (m) wood,

vi)

SN 17201 03 Wood embales and wood waste, not contaminated; treated (m) wood, pollutant-free; zB treated with heavy metal-free linseed oil,

vii)

SN 17203 Holzwolle, not polluted.

b)

Animal meal (key numbers 11701, 11702, 97101 and 97102 according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended),

c)

Animal fat (key number 12302 according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended),

d)

Edible oil (key number 12102 and 12302 according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended), and

e)

vegetable waste from agriculture, food, consumption and feed production.

Proof of compliance with the limits laid down in Chapter 1 shall be deleted.

2.5

Heating value

In the parameter calorific value, a limitation of the frequency of examination is possible. However, the determination of the calorific value must be carried out in at least every tenth laboratory sample.

2.6

Sample preparation

The laboratory sample must be manufactured in accordance with the ÖNORM CEN/TS 15443 "Solid secondary fuels-Process for the production of laboratory samples", issued on 1 January 2008. Jänner 2007. The preparation of the test sample from the laboratory sample must be carried out in accordance with the ÖNORM CEN/TS 15413 "Solid secondary fuel processes for the preparation of the test sample from the laboratory sample", issued on 1 December 2006.

In order to obtain the test sample, a reduction of the particle size to < 0.5 mm must be carried out.

The requirements for the minimum sample quantities in accordance with Annex D of the ÖNORM CEN/TS 15442 must be complied with for each step and each examination procedure.

The foreign parts sorted out during the sample preparation process must be documented.

2.7

Determination procedure

The following methods of determination must be applied:

a)

The determination of the trace elements must be carried out in accordance with process A of the ÖNORM CEN/TS 15411 "Solid secondary fuel processes for determining the content of trace elements (As, Ba, Be, Cd, Co, Cr, Cu, Hg, Mo, Mn, Ni, Pb, Sb, Se, Tl, V and Zn)", issued on 1 December 2006, with a full conclusion regarding the parameters to be determined (for example, with the aid of a adapted temperature control). For certain cases, alternative methods of ingestion may be authorised, specifying the justification for the selection of the specific inference procedure and, in any event, achieving a full breakdown of the elements of interest must. The direct analysis of Hg in accordance with the method cited in EPA Method 7473 "Mercury in Solids and Solutions by Thermal Decomposition, Amalgamation and Atomic Absorption Spectrophotometry" is permitted.

b)

The determination of the calorific value must be carried out in accordance with ÖNORM CEN/TS 15400 "Solid secondary fuels-Method for determining the calorific value", issued on 1 December 2006. The required weight can be reduced to at least 0.2g (without combustion aids).

c)

The determination of the water content must be carried out according to

-

ÖNORM CEN/TS 15414-1 "Solid secondary fuels-Determination of the water content using the furnace drying method-Part 1: Determination of the content of total water by means of reference methods", issued on 1 December 2006, or

-

ÖNORM CEN/TS 15414-3 "Solid secondary fuels-Determination of the water content using the furnace drying method-Part 3: Water content in ordinary analysis samples", issued on 1 December 2006,

,

d)

The determination of the content of C, H and N must be carried out according to ÖNORM CEN/TS 15407 "Solid secondary fuel processes for the determination of the content of carbon (C), hydrogen (H) and nitrogen (N)", issued on 1 December 2006.

Certified reference materials must preferably be used to collect the quality of the information and analysis. Alternatively, it is possible to use suitable own control samples, the composition of which has been determined by suitable methods.

The limits of detection and determination must be determined in accordance with DIN 32645 "Chemical analysis-detection, detection and determination limit under repeatable conditions-terms, procedures, evaluation". If an examination result is below the limit of determination, the value of the half-determination limit must be used for the calculation of the assessment values. If an examination result is below the detection limit, the value of zero must be used for the calculation of the assessment values.

2.8

Evidence of assessment

The assessment must include, on the one hand, the documentation of all the information relevant to the respective substitute fuel and the results of the examination, which are necessary for the feasibility and plausibility check of the assessment. On the other hand, all assessments, conclusions and justifications for the presence of the end of the waste property must be included.

The respective current assessment of a waste stream must include all the contents of the previous assessment documents.

A proof of assessment shall include:

a)

the identifier;

b)

the reference to previous assessments;

c)

the creator;

d)

the owner of the waste, unless he or she is the owner of the waste;

e)

Date of submission to the Federal Minister for Agriculture, Forestry, the Environment and Water Management and the period of validity of the assessment certificate;

f)

basic information on the replacement fuel product:

i)

Waste type according to the Waste Directory Ordinance, BGBl. II No 570/2003, as amended; the type of waste must be in accordance with the allocation criteria of the Waste Directory Regulation, BGBl. II No 570/2003, as amended;

ii)

Location: the waste producer, its location and the plant, where appropriate the plant part;

iii)

Waste producer and its location, unless ident is sublit. (ii)

iv)

Origin according to the Waste Balance Ordinance, BGBl. II No 497/2008, as amended, provided that it is not in the position of the person concerned;

v)

description of the substitute fuel (in particular odour, colour, consistency);

vi)

Photo (s) of the replacement fuel product;

vii)

in the case of a one-off substitute fuel, the total quantity of substitute fuel in t, in the case of a waste stream, the estimated annual quantity in t;

viii)

the description of the origin of the substitute fuel product and any treatment steps; the description of the input materials of the process in which the substitute fuel product is produced and the output materials of the treatment; and any contamination and the cause thereof;

g)

Indication of the sample preparation and method of determination used, in particular with regard to the use of alternative digestion methods (excluding wood waste in accordance with Chapter 2.4);

h)

all the results of the analysis and their reference to the associated lot by means of a sample, laboratory, field and qualified sample (other than wood waste referred to in Chapter 2.4);

i)

the calculation of the assessment values (excluding wood waste referred to in Chapter 2.4);

j)

Assessment of the replacement fuel with regard to the quality requirements for replacement fuel products;

k)

in the case of waste streams, specifications for the studies of the next lot (other than wood waste in accordance with Chapter 2.4);

l)

a declaration that the prohibition of mixing is complied with in accordance with Section 15 (2) of the AWG 2002;

m)

in the case of replacement fuel products made from wood waste and meat and bone meal, a confirmation that it is other natural substances in accordance with Annex V, point 8. Regulation (EC) No 987/2008 amending Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), as regards Annexes IV and V, OJ L 327, 30.12.2006, p. No. 14., as referred to in Section 7, unless they have been chemically modified, unless they meet the criteria for classification as dangerous under Directive 67 /548/EEC or are not persistent, bioaccumulative and toxic or not very persistent and very bio-accumulative in accordance with the criteria of Annex XIII or they have not been identified in accordance with Article 59 (1) for at least two years as substances which are as worrying as those in Article 57, point (f);

n)

in the case of replacement fuel products from edible oils and animal fat, a confirmation that the substances obtained from natural raw materials are in accordance with Annex V, point 9. Regulation (EC) No 987/2008 amending Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), as regards Annexes IV and V, OJ L 327, 30.12.2006, p. No. 14., unless they have been chemically modified, unless they fulfil the criteria for classification as dangerous in accordance with Directive 67 /548/EEC, with the exception of those substances which are only flammable [R 10], Skin irritation [R 38] or eye irritant [R 36], or they are not persistent, bioaccumulative and toxic or they are not very persistent and very bioaccumulative according to the criteria in Annex XIII or they are not in accordance with Article 59 (1) has been identified for at least two years as substances which are just as worrying as those in Article 57 (f).

The assessment certificate, except in the case of wood waste as defined in Chapter 2.4, shall be subject to the sampling plan with calculations and bases, such as preliminary surveys or other documents used for the assessment, and any updates in the course of the Investigations and the sampling protocols shall be connected.

2.9

External monitoring

The waste owner, who makes the waste property of a substitute fuel, has to have the requirements of this installation checked at least once a year by a qualified specialist or specialist institution.

The external surveillance shall include in particular:

a)

the verification of the evidence of completeness and accuracy;

b)

the sampling and analysis of the replacement fuel products (with the exception of substitute fuel products in accordance with Chapter 2.4): a subset (150 tonnes) per substitute fuel product must be selected randomly and a qualified sample , a report must be drawn up on the basis of the proof of assessment of each individual investigation;

c)

the analysis of rehearsals; at least one randomly selected rehearsals must be analysed for each substitute fuel product; a report must be drawn up on the basis of the proof of assessment of each individual examination.

The determination of the number and mass of samples, as well as of the minimum sample quantity for the qualified sample, sample preparation and the determination procedures, shall be carried out in accordance with Chapter 2.

From all laboratory samples, rehearsals must be produced and kept for at least one year. A drying of the recovery samples at a maximum of 40 ° C is permitted. The minimum requirements for laboratory testing in accordance with the ÖNORM CEN/TS 15442 must be met.

If the individual measurement result for one or more parameters exceeds the limit value for the 80-er percentile, then a further qualified sample must be produced and at least to be examined for these parameters. If the individual measurement result of this re-examination for one of these parameters exceeds the limit value for the 80-er percentile, then the Federal Minister for Agriculture, Forestry, the Environment and Water Management must immediately be informed of this. shall be informed.

Where the inspections result in deviations from the requirements of this installation, the waste owner who leaves the waste property of a substitute fuel shall immediately notify the Federal Minister for Agriculture, Forestry, the Environment and the Environment, Report on water management.

Berlakovich Mitterlehner