Division 1.5.2.2 Emissions of HCl, HF and SO2
United Kingdom
BAT 27. In order to reduce channelled emissions of HCl, HF and SO2 to air from the incineration of waste, BAT is to use one or a combination of the techniques given below.
| Technique | Description | Applicability | |
|---|---|---|---|
| (a) | Wet scrubber | See Section 2.2 | There may be applicability restrictions due to low water availability, e.g. in arid areas. |
| (b) | Semi-wet absorber | See Section 2.2 | Generally applicable. |
| (c) | Dry sorbent injection | See Section 2.2 | Generally applicable. |
| (d) | Direct desulphurisation | See Section 2.2. Used for partial abatement of acid gas emissions upstream of other techniques. | Only applicable to fluidised bed furnaces. |
| (e) | Boiler sorbent injection | See Section 2.2. Used for partial abatement of acid gas emissions upstream of other techniques. | Generally applicable. |
BAT 28. In order to reduce channelled peak emissions of HCl, HF and SO2 to air from the incineration of waste while limiting the consumption of reagents and the amount of residues generated from dry sorbent injection and semi-wet absorbers, BAT is to use technique (a) or both of the techniques given below.
| Technique | Description | Applicability | |
|---|---|---|---|
| (a) | Optimised and automated reagent dosage | The use of continuous HCl and/or SO2 measurements (and/or of other parameters that may prove useful for this purpose) upstream and/or downstream of the FGC system for the optimisation of the automated reagent dosage. | Generally applicable. |
| (b) | Recirculation of reagents | The recirculation of a proportion of the collected FGC solids to reduce the amount of unreacted reagent(s) in the residues. The technique is particularly relevant in the case of FGC techniques operating with a high stoichiometric excess. | Generally applicable to new plants. Applicable to existing plants within the constraints of the size of the bag filter. |
Table 5
BAT-associated emission levels (BAT-AELs) for channelled emissions to air of HCl, HF and SO2 from the incineration of waste
| The lower end of the BAT-AEL range can be achieved when using a wet scrubber; the higher end of the range may be associated with the use of dry sorbent injection. | |||
| (mg/Nm3) | |||
| Parameter | BAT-AEL | Averaging period | |
|---|---|---|---|
| New plant | Existing plant | ||
| HCl | < 2–6 f1 | < 2–8 | Daily average |
| HF | < 1 | < 1 | Daily average or average over the sampling period |
| SO2 | 5–30 | 5–40 | Daily average |
The associated monitoring is in BAT 4.
Annotations
Footnotes
- f1
-
The lower end of the BAT-AEL range can be achieved when using a wet scrubber; the higher end of the range may be associated with the use of dry sorbent injection.