Division BAT 25 In order to prevent or reduce SOX, HCl and HF emissions to air from the combustion of solid biomass and/or peat, BAT is to use one or a combination of the techniques given below.
United Kingdom
| Technique | Description | Applicability | |
|---|---|---|---|
| a. | Boiler sorbent injection (in-furnace or in-bed) | See descriptions in Section 8.4 | Generally applicable |
| b. | Duct sorbent injection (DSI) | ||
| c. | Spray dry absorber (SDA) | ||
| d. | Circulating fluidised bed (CFB) dry scrubber | ||
| e. | Wet scrubbing | ||
| f. | Flue-gas condenser | ||
| g. | Wet flue-gas desulphurisation (wet FGD) | Not applicable to combustion plants operated < 500 h/yr. There may be technical and economic restrictions for retrofitting existing combustion plants operated between 500 h/yr and 1 500 h/yr | |
| h. | Fuel choice | Applicable within the constraints associated with the availability of different types of fuel, which may be impacted by the energy policy of the Member State | |
Table 10
BAT-associated emission levels (BAT-AELs) for SO2 emissions to air from the combustion of solid biomass and/or peat
| These BAT-AELs do not apply to plants operated < 1 500 h/yr. | ||||
| For plants operated < 500 h/yr, these levels are indicative. | ||||
| For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 100 mg/Nm3. | ||||
| For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 215 mg/Nm3. | ||||
| For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 165 mg/Nm3, or 215 mg/Nm3 if those plants have been put into operation no later than 7 January 2014 and/or are FBC boilers combusting peat. | ||||
| Combustion plant total rated thermal input(MWth) | BAT-AELs for SO2 (mg/Nm3) | |||
|---|---|---|---|---|
| Yearly average | Daily average or average over the sampling period | |||
| New plant | Existing plantf1 | New plant | Existing plantf2 | |
| < 100 | 15–70 | 15–100 | 30–175 | 30–215 |
| 100–300 | < 10–50 | < 10–70f3 | < 20–85 | < 20–175f4 |
| ≥ 300 | < 10–35 | < 10–50 | < 20–70 | < 20–85f5 |
Table 11
BAT-associated emission levels (BAT-AELs) for HCl and HF emissions to air from the combustion of solid biomass and/or peat
| For plants burning fuels where the average chlorine content is ≥ 0,1 wt-% (dry), or for existing plants co-combusting biomass with sulphur-rich fuel (e.g. peat) or using alkali chloride-converting additives (e.g. elemental sulphur), the higher end of the BAT-AEL range for the yearly average for new plants is 15 mg/Nm3, the higher end of the BAT-AEL range for the yearly average for existing plants is 25 mg/Nm3. The daily average BAT-AEL range does not apply to these plants. | ||||||
| The daily average BAT-AEL range does not apply to plants operated < 1 500 h/yr. The higher end of the BAT-AEL range for the yearly average for new plants operated < 1 500 h/yr is 15 mg/Nm3. | ||||||
| These BAT-AELs do not apply to plants operated < 1 500 h/yr. | ||||||
| The lower end of these BAT-AEL ranges may be difficult to achieve in the case of plants fitted with wet FGD and a downstream gas-gas heater. | ||||||
| For plants operated < 500 h/yr, these levels are indicative. | ||||||
| Combustion plant total rated thermal input(MWth) | BAT-AELs for HCl (mg/Nm3)f6 f7 | BAT-AELs for HF (mg/Nm3) | ||||
|---|---|---|---|---|---|---|
| Yearly average or average of samples obtained during one year | Daily average or average over the sampling period | Average over the sampling period | ||||
| New plant | Existing plantf8 f9 | New plant | Existing plantf10 | New plant | Existing plant | |
| < 100 | 1–7 | 1–15 | 1–12 | 1–35 | < 1 | < 1,5 |
| 100–300 | 1–5 | 1–9 | 1–12 | 1–12 | < 1 | < 1 |
| ≥ 300 | 1–5 | 1–5 | 1–12 | 1–12 | < 1 | < 1 |
Annotations
Footnotes
- f1
-
These BAT-AELs do not apply to plants operated < 1 500 h/yr.
- f2
-
For plants operated < 500 h/yr, these levels are indicative.
- f3
-
For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 100 mg/Nm3.
- f4
-
For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 215 mg/Nm3.
- f5
-
For existing plants burning fuels where the average sulphur content is 0,1 wt-% (dry) or higher, the higher end of the BAT-AEL range is 165 mg/Nm3, or 215 mg/Nm3 if those plants have been put into operation no later than 7 January 2014 and/or are FBC boilers combusting peat.
- f6
-
For plants burning fuels where the average chlorine content is ≥ 0,1 wt-% (dry), or for existing plants co-combusting biomass with sulphur-rich fuel (e.g. peat) or using alkali chloride-converting additives (e.g. elemental sulphur), the higher end of the BAT-AEL range for the yearly average for new plants is 15 mg/Nm3, the higher end of the BAT-AEL range for the yearly average for existing plants is 25 mg/Nm3. The daily average BAT-AEL range does not apply to these plants.
- f7
-
The daily average BAT-AEL range does not apply to plants operated < 1 500 h/yr. The higher end of the BAT-AEL range for the yearly average for new plants operated < 1 500 h/yr is 15 mg/Nm3.
- f8
-
These BAT-AELs do not apply to plants operated < 1 500 h/yr.
- f9
-
The lower end of these BAT-AEL ranges may be difficult to achieve in the case of plants fitted with wet FGD and a downstream gas-gas heater.
- f10
-
For plants operated < 500 h/yr, these levels are indicative.