Commission Decision (EU) 2020/1803 of 27 November 2020 establishing the EU Ecolabel criteria for printed paper, stationery paper, and paper carrier bag products (notified under document C(2020) 8155) (Text with EEA relevance)
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The specific amount of Cr and Cu at the point of discharge must not exceed, respectively, 20 mg per m2 and 200 mg per m2 of printing cylinder surface area used in the press.
Assessment and verification: discharges of Cr and Cu shall be checked at rotogravure printing plants after treatment and immediately prior to discharge. A representative composite sample of Cr and Cu discharges shall be collected at least every 3 months. At least one annual analytical test shall be carried out by an accredited laboratory to determine the content of Cr and Cu from the composite sample according to EN ISO 11885 or equivalent standard methods that are accepted by the competent body as providing data of equivalent scientific quality.
Compliance with this criterion shall be assessed by dividing the content of Cr and Cu, as determined by the annual analytical test, by the cylinder surface used in the press during the printing. The cylinder surface used in the press during printing is calculated by multiplying the cylinder surface (= 2πrL, where r is the radius and L the length of the cylinder) by the number of printing productions during a year (= number of different printing jobs).
The following requirements shall apply to printing processes covered by Annex I and VII to Directive 2010/75/EU or to equivalent printing processes outside the EU that meet specifications of Annex I and VII to Directive 2010/75/EU.
Fugitive VOC emissions, as calculated by the solvent mass balance, should be lower or equal to 2,0 % of the solvent input, and TVOC(2) in waste gases shall be lower or equal to 16,0 mg C/Nm3.
Emissions of Cr(VI) to air shall not exceed 15,0 mg/tonne paper. Abatement equipment for reduction of emission to air shall be installed
Total VOC emissions as calculated by the solvent mass balance should be lower or equal to 0,03 kg VOCs per kg of ink input; alternatively fugitive VOC emissions as calculated by the solvent mass balance should be lower or equal to 8 % of the solvent input and TVOC emissions in waste gases should be lower or equal to 12,0 mg C/Nm3.
Total VOC emissions as calculated by the solvent mass balance should be lower or equal to 0,24 kg VOCs per kg of ink input; alternatively fugitive VOC emissions as calculated by the solvent mass balance should be lower or equal to 9,6 % of the solvent input and TVOC emissions in waste gases should be lower or equal to 16,0 mg C/Nm3.
Assessment and verification: the applicant shall provide detailed calculations and test data showing compliance with this criterion, together with related supporting documentation.
For total or fugitive VOC emissions, as applicable, solvent mass balance calculation shall be based on the production during 12 months of operation. The solvent mass balance shall be in line with the definition laid down in Part 7(2) of Annex VII to Directive 2010/75/EU. In case of a new or a rebuilt production plant, the calculations shall be based on at least three months of representative running of the plant.
A declaration of the VOC content in, inks, washing agents, damping solutions or other corresponding chemical products shall be provided by the applicant or a chemical supplier.
The solvent mass balance shall be performed on yearly basis. A written evaluation shall be done by a responsible staff member. Upon request, the evaluation shall be provided to the competent body.
For the monitoring of total TVOC emissions to air in waste gases, any stack with a TVOC load less than 10 kg C/h should be monitored at least once a year according to EN 12619, or equivalent. In the case of a TVOC load less than 0,1 kg C/h (as an annual average), or in the case of an unabated and stable TVOC load of less than 0,3 kg C/h, the monitoring frequency may be reduced to once every three years or the monitoring may be replaced by calculation provided that it ensures the provision of data of an equivalent scientific quality.
For any stack with a TVOC load higher or equal to 10 kg C/h the monitoring shall be continuous according to EN 15267-1, EN 15267-2, EN 15267-3 and EN 14181. For continuous measurement, the data shall represent daily average over the period of one day based on valid hourly or half-hourly averages.
The VOC destruction in the abatement system (e.g. thermal oxidation, adsorption to activated carbon) shall be determined, with a frequency of at least every three years, by combined measurements of VOC concentration in raw gas and clean gas.
The measurement data of waste gas shall be registered and available upon request for the competent body.
The applicant shall provide a description of the system in place, together with a documentation related to the control and the monitoring of Cr(VI) emissions. The documentation shall include the test results related to the reduction of Cr(VI) emissions to the air.
The following requirements shall apply to printing processes not covered by Annex I or by Annex VII Part 2 to Directive 2010/75/EU or to equivalent printing processes outside the EU that do not meet specification of Annex I and VII to Directive 2010/75/EU.
Total VOC emissions as calculated by the solvent mass balance shall be lower or equal to:
4,5 kg VOC/tonne of paper for sheet fed offset printing;
1,0 kg VOC/tonne of paper for digital printing;
2,0 kg VOC/tonne of paper for heat set web offset printing;
2,5 kg VOC/tonne of paper for cold set web offset printing;
3,0 kg VOC/tonne of paper for other rotogravure, flexography, rotary screen printing, laminating or varnishing units.
Alternatively, where off-gas treatment is applied fugitive VOC emissions as calculated by the solvent mass balance should be lower or equal to 10 % of the solvent input and TVOC emission in waste gases should be lower or equal to 20 mg C/Nm3.
Volatile solvents from the drying process of heat-set offset, rotogravure and flexography printing shall be managed by means of solvent recovery or thermal treatment or any equivalent system, i.e. substitution by the use of water-based inks.
Assessment and verification: the applicant shall provide a description of the system in place together with documentation and test results related to the control and the monitoring of emissions to air.
For total or fugitive VOC emissions, as applicable, solvent mass balance shall be calculated on the production during 12 months of operation. The solvent mass balance shall be in line with the definition laid down in Part 7(2) of Annex VII to Directive 2010/75/EU. For the allocation of VOCs emission into mass of paper, all printed surfaces shall be calculated. In case of a new or a rebuilt production plant, the calculations shall be based on at least three months of representative running of the plant.
For the monitoring of total TVOC emissions to air in waste gases, any stack with a TVOC load less than 10 kg C/h should be monitored at least once a year according to EN 12619, or equivalent. In the case of a TVOC load less than 0,1 kg C/h (as an annual average), or in the case of an unabated and stable TVOC load of less than 0,3 kg C/h, the monitoring frequency may be reduced to once every three years or the monitoring may be replaced by calculation provided that it ensures the provision of data of an equivalent scientific quality.
A declaration of the VOC content in inks, washing agents, damping solutions or other corresponding chemical products shall be provided by the applicant or a chemical supplier.
Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) (OJ L 334, 17.12.2010, p. 17).
Total volatile organic carbon, expressed as C (in air).
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