Division 39
United Kingdom
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. | |
| Techniquef1 | 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:
| 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 glassf2 | ||
| NOx expressed as NO2 | Combustion modifications, special furnace designs | < 500 – 1 000 | < 1,25 – 2,5 |
| Electric melting | < 100 | < 0,3 | |
| Oxy-fuel meltingf3 | Not applicable | < 0,5 – 1,5 | |
Annotations
Footnotes
- f1
-
A description of the techniques is given in Section 1.10.2.
- f2
-
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.
- f3
-
The achievable levels depend on the quality of the natural gas and oxygen available (nitrogen content).