Commission Implementing Decision of 28 February 2012 establishing the best available techniques (BAT) conclusions under Directive 2010/75/EU of the European Parliament and of the Council on industrial emissions for the manufacture of glass (notified under document C(2012) 865) (Text with EEA relevance) (2012/134/EU)
EU Decision 2012/134 · Adopted 28 February 2012 · Extends to United Kingdom
Commission Implementing Decision
of 28 February 2012
establishing the best available techniques (BAT) conclusions under Directive 2010/75/EU of the European Parliament and of the Council on industrial emissions for the manufacture of glass
(notified under document C(2012) 865)
(Text with EEA relevance)
(2012/134/EU)
THE EUROPEAN COMMISSION,
Having regard to the Treaty on the Functioning of the European Union,
Having regard to Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control)f1 and in particular Article 13(5) thereof,
Whereas:
(1)
Article 13(1) of Directive 2010/75/EU requires the Commission to organise an exchange of information on industrial emissions between it and Member States, the industries concerned and non-governmental organisations promoting environmental protection in order to facilitate the drawing up of best available techniques (BAT) reference documents as defined in Article 3(11) of that Directive.
(2)
In accordance with Article 13(2) of Directive 2010/75/EU, the exchange of information is to address the performance of installations and techniques in terms of emissions, expressed as short- and long-term averages, where appropriate, and the associated reference conditions, consumption and nature of raw materials, water consumption, use of energy and generation of waste and the techniques used, associated monitoring, cross-media effects, economic and technical viability and developments therein and best available techniques and emerging techniques identified after considering the issues mentioned in points (a) and (b) of Article 13(2) of that Directive.
(3)
‘BAT conclusions’ as defined in Article 3(12) of Directive 2010/75/EU are the key element of BAT reference documents and lay down the conclusions on best available techniques, their description, information to assess their applicability, the emission levels associated with the best available techniques, associated monitoring, associated consumption levels and, where appropriate, relevant site remediation measures.
(4)
In accordance with Article 14(3) of Directive 2010/75/EU, BAT conclusions are to be the reference for setting permit conditions for installations covered by Chapter 2 of that Directive.
(5)
Article 15(3) of Directive 2010/75/EU requires the competent authority to set emission limit values that ensure that, under normal operating conditions, emissions do not exceed the emission levels associated with the best available techniques as laid down in the decisions on BAT conclusions referred to in Article 13(5) of Directive 2010/75/EU.
(6)
Article 15(4) of Directive 2010/75/EU provides for derogations from the requirement laid down in Article 15(3) only where the costs associated with the achievement of emissions levels disproportionately outweigh the environmental benefits due to the geographical location, the local environmental conditions or the technical characteristics of the installation concerned.
(7)
Article 16(1) of Directive 2010/75/EU provides that the monitoring requirements in the permit referred to in point (c) of Article 14(1) of the Directive are to be based on the conclusions on monitoring as described in the BAT conclusions.
(8)
In accordance with Article 21(3) of Directive 2010/75/EU, within 4 years of publication of decisions on BAT conclusions, the competent authority is to reconsider and, if necessary, update all the permit conditions and ensure that the installation complies with those permit conditions.
(9)
Commission Decision of 16 May 2011 establishing a forum for the exchange of information pursuant to Article 13 of Directive 2010/75/EU on industrial emissionsf2 established a forum composed of representatives of Member States, the industries concerned and non-governmental organisations promoting environmental protection.
(10)
In accordance with Article 13(4) of Directive 2010/75/EU, the Commission obtained the opinionf3 of that forum on the proposed content of the BAT reference document for the manufacture of glass on 13 September 2011 and made it publicly available.
(11)
The measures provided for in this Decision are in accordance with the opinion of the Committee established by Article 75(1) of Directive 2010/75/EU,
HAS ADOPTED THIS DECISION:
Annotations to the whole text
Footnotes
- f1
- f2
- f3
-
http://circa.europa.eu/Public/irc/env/ied/library?l=/ied_art_13_forum/opinions_article
Contents
- 1Article 1
- 2Application and Interpretation
- Signature
- Annex: BAT CONCLUSIONS FOR THE MANUFACTURE OF GLASS
- SCOPE
- DEFINITIONS
- GENERAL CONSIDERATIONS
- Averaging periods and reference conditions for air emissions
- Conversion to reference oxygen concentration
- Conversion from concentrations to specific mass emissions
- DEFINITIONS FOR CERTAIN AIR POLLUTANTS
- AVERAGING PERIODS FOR WASTE WATER DISCHARGES
- 1.1General BAT conclusions for the manufacture of glass
- Environmental management systems
- 1Division 1
- Applicability
- Energy efficiency
- 2Division 2
- Materials storage and handling
- 3Division 3
- 4Division 4
- General primary techniques
- 5Division 5
- 6Division 6
- 7Division 7
- 8Division 8
- Applicability
- 9Division 9
- 10Division 10
- 11Division 11
- Monitoring
- Emissions to water from glass manufacturing processes
- 12Division 12
- 13Division 13
- Waste from the glass manufacturing processes
- 14Division 14
- Noise from the glass manufacturing processes
- 15Division 15
- 1.2BAT conclusions for container glass manufacturing
- Dust emissions from melting furnaces
- 16Division 16
- Nitrogen oxides (NOX) from melting furnaces
- 17Division 17
- 18Division 18
- Sulphur oxides (SOX) from melting furnaces
- 19Division 19
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 20Division 20
- Metals from melting furnaces
- 21Division 21
- Emissions from downstream processes
- 22Division 22
- 23Division 23
- 1.3BAT conclusions for flat glass manufacturing
- Dust emissions from melting furnaces
- 24Division 24
- Nitrogen oxides (NOX) from melting furnaces
- 25Division 25
- 26Division 26
- Sulphur oxides (SOX) from melting furnaces
- 27Division 27
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 28Division 28
- Metals from melting furnaces
- 29Division 29
- 30Division 30
- Emissions from downstream processes
- 31Division 31
- 1.4BAT conclusions for continuous filament glass fibre manufacturing
- 1.4.1Dust emissions from melting furnaces
- 32Division 32
- Nitrogen oxides (NOX) from melting furnaces
- 33Division 33
- Sulphur oxides (SOX) from melting furnaces
- 34Division 34
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 35Division 35
- Metals from melting furnaces
- 36Division 36
- Emissions from downstream processes
- 37Division 37
- 1.5BAT conclusions for domestic glass manufacturing
- Dust emissions from melting furnaces
- 38Division 38
- Nitrogen oxides (NOX) from melting furnaces
- 39Division 39
- 40Division 40
- Sulphur oxides (SOX) from melting furnaces
- 41Division 41
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 42Division 42
- Metals from melting furnaces
- 43Division 43
- 44Division 44
- 45Division 45
- Emissions from downstream processes
- 46Division 46
- 47Division 47
- 1.6BAT conclusions for special glass manufacturing
- Dust emissions from melting furnaces
- 48Division 48
- Nitrogen oxides (NOX) from melting furnaces
- 49Division 49
- 50Division 50
- Sulphur oxides (SOX) from melting furnaces
- 51Division 51
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 52Division 52
- Metals from melting furnaces
- 53Division 53
- Emissions from downstream processes
- 54Division 54
- 55Division 55
- 1.7BAT conclusions for mineral wool manufacturing
- Dust emissions from melting furnaces
- 56Division 56
- Nitrogen oxides (NOX) from melting furnaces
- 57Division 57
- 58Division 58
- Sulphur oxides (SOX) from melting furnaces
- 59Division 59
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 60Division 60
- Hydrogen sulphide (H2S) from stone wool melting furnaces
- 61Division 61
- Metals from melting furnaces
- 62Division 62
- Emissions from downstream processes
- 63Division 63
- 1.8BAT conclusions for high temperature insulation wools (HTIW) manufacturing
- Dust emissions from melting and downstream processes
- 64Division 64
- 65Division 65
- Nitrogen oxides (NOX) from melting and downstream processes
- 66Division 66
- Sulphur oxides (SOX) from melting and downstream processes
- 67Division 67
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 68Division 68
- Metals from melting furnaces and downstream processes
- 69Division 69
- Volatile organic compounds from downstream processes
- 70Division 70
- 1.9BAT conclusions for frits manufacturing
- Dust emissions from melting furnaces
- 71Division 71
- Nitrogen oxides (NOX) from melting furnaces
- 72Division 72
- Sulphur oxides (SOX) from melting furnaces
- 73Division 73
- Hydrogen chloride (HCl) and hydrogen fluoride (HF) from melting furnaces
- 74Division 74
- Metals from melting furnaces
- 75Division 75
- Emissions from downstream processes
- 76Division 76
- Glossary
- Description of techniques
- 1.10.1Dust emissions
- 1.10.2NOX emissions
- 1.10.3SOX emissions
- 1.10.4HCl, HF emissions
- 1.10.5Metal emissions
- 1.10.6Combined gaseous emissions (e.g. SOX, HCl, HF, boron compounds)
- 1.10.7Combined emissions (solid + gaseous)
- 1.10.8Emissions from cutting, grinding, polishing operations
- 1.10.9H2S, VOC emissions