# 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), Division 39

Extent: E+W+S+N.I.

BAT is to reduce NOX emissions from the melting furnace by using one or a combination of the following techniques:
A description of the techniques is given in Section 1.10.2.
Technique
Applicability
(i) Combustion modifications
(a)
Reduction of air/fuel ratio
Applicable to air/fuel conventional furnaces.
Full benefits are achieved at normal or complete furnace rebuild, when combined with optimum furnace design and geometry
(b)
Reduced combustion air temperature
Applicable only under installation-specific circumstances due to a lower furnace efficiency and higher fuel demand (i.e. use of recuperative furnaces in place of regenerative furnaces)
(c)
Staged combustion:
(f) Air staging
(g) Fuel staging
Fuel staging is applicable to most conventional air/fuel furnaces.
Air staging has very limited applicability due to its technical complexity
(d)
Flue-gas recirculation
The applicability of this technique is limited to the use of special burners with automatic recirculation of the waste gas
(e)
Low-NOX burners
The technique is generally applicable.
The achieved environmental benefits are generally lower for applications to cross-fired, gas-fired furnaces due to technical constraints and a lower degree of flexibility of the furnace.
Full benefits are achieved at normal or complete furnace rebuild, when combined with optimum furnace design and geometry
(f)
Fuel choice
The applicability is limited by the constraints associated with the availability of different types of fuel, which may be impacted by the energy policy of the Member State
(ii)
Special furnace design
The applicability is limited to batch formulations that contain high levels of external cullet (> 70 %).
The application requires a complete rebuild of the melting furnace.
The shape of the furnace (long and narrow) may pose space restrictions
(iii)
Electric melting
Not applicable for large volume glass productions (> 300 tonnes/day).
Not applicable for productions requiring large pull variations.
The implementation requires a complete furnace rebuild
(iv)
Oxy-fuel melting
The maximum environmental benefits are achieved for applications at the time of a complete furnace rebuild
Table 29
BAT-AELs for NOX emissions from the melting furnace in the domestic glass sector
A conversion factor of 2,5 × 10–3 has been applied for combustion modifications and special furnace designs and a conversion factor of 3 × 10–3 has been applied for electric melting (see Table 2). However, a case-by-case conversion factor may have to be applied for specific productions.
The achievable levels depend on the quality of the natural gas and oxygen available (nitrogen content).
Parameter
BAT
BAT-AEL
mg/Nm3
kg/tonne melted glass
NOx expressed as NO2
Combustion modifications,
special furnace designs
< 500 – 1 000
< 1,25 – 2,5
Electric melting
< 100
< 0,3
Oxy-fuel melting
Not applicable
< 0,5 – 1,5

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Source: https://www.legislation.gov.uk/eudn/2012/134/annex/division/5/division/1.5/division/1.5.2/division/39 (the official version)
Page: https://openlegislation.uk/eu-decision-2012-134/annex/division-5/division-1.5/division-1.5.2/division-39
Contains public sector information licensed under the Open Government Licence v3.0. Source: legislation.gov.uk, The National Archives.