Commission Implementing Decision (EU) 2016/1032Show full title

Commission Implementing Decision (EU) 2016/1032 of 13 June 2016 establishing best available techniques (BAT) conclusions, under Directive 2010/75/EU of the European Parliament and of the Council, for the non-ferrous metals industries (notified under document C(2016) 3563) (Text with EEA relevance)

1.9.1.2. Dust and PAH emissions U.K.
BAT 178.In order to reduce dust emissions to air from the storage, handling and transportation of coke and pitch, and mechanical processes (such as grinding) and graphitising and machining, BAT is to use a bag filter.U.K.

BAT-associated emission levels: See Table 51.

Table 51

BAT-associated emission levels for dust and BaP (as an indicator of PAH) emissions to air from the storage, handling and transportation of coke and pitch, and mechanical processes (such as grinding) and graphitising and machining

a

As an average over the sampling period.

b

BaP particles are only expected if processing solid pitch.

ParameterBAT-AEL (mg/Nm3)a
Dust2-5
BaP≤ 0,01b

The associated monitoring is in BAT 10.

BAT 179.In order to reduce dust and PAH emissions to air from the production of green paste and green shapes, BAT is to use one or a combination of the techniques given below.U.K.
a

Descriptions of the techniques are given in Section 1.10.

Techniquea
aDry scrubber using coke as the adsorbent agent and with or without precooling, followed by a bag filter
bCoke filter
cRegenerative thermal oxidiser
dThermal oxidiser

BAT-associated emission levels: See Table 52.

Table 52

BAT-associated emission levels for dust and BaP (as an indicator of PAH) emissions to air from the production of green paste and green shapes

a

As an average over the sampling period.

b

The lower end of the range is associated with the use of a dry scrubber using coke as the adsorbent agent followed by a bag filter. The upper end of the range is associated with the use of a thermal oxidiser.

ParameterBAT-AEL (mg/Nm3)a
Dust2-10b
BaP0,001-0,01

The associated monitoring is in BAT 10.

BAT 180.In order to reduce dust and PAH emissions to air from baking, BAT is to use one or a combination of the techniques given below.U.K.
a

Descriptions of the techniques are given in Section 1.10.

TechniqueaApplicability
aESP, in combination with a thermal oxidation step (e.g. regenerative thermal oxidiser) when highly volatile compounds are expectedGenerally applicable
bRegenerative thermal oxidiser, in combination with a pretreatment (e.g. ESP) in cases of a high dust content in the exhaust gasGenerally applicable
cThermal oxidiserNot applicable to continuous ring furnaces

BAT-associated emission levels: See Table 53.

Table 53

BAT-associated emission levels for dust and BaP (as an indicator of PAH) emissions to air from baking and rebaking

a

As an average over the sampling period.

b

The lower end of the range is associated with the use of a combination of an ESP and a regenerative thermal oxidiser. The higher end of the range is associated with the use of a thermal oxidiser.

c

The lower end of the range is associated with the use of a thermal oxidiser. The upper end of the range is associated with the use of a combination of an ESP and a regenerative thermal oxidiser.

d

For cathode production, the upper end of the range is 0,05 mg/Nm3.

ParameterBAT-AEL (mg/Nm3)a
Dust2-10b
BaP0,005-0,015c d

The associated monitoring is in BAT 10.

BAT 181.In order to reduce dust and PAH emissions to air from impregnation, BAT is to use one or a combination of the techniques given below.U.K.
a

Descriptions of the techniques are given in Section 1.10.

Techniquea
aDry scrubber followed by a bag filter
bCoke filter
cThermal oxidiser

BAT-associated emission levels: See Table 54.

Table 54

BAT-associated emission levels for dust and BaP (as an indicator of PAH) emissions to air from impregnation

a

As an average over the sampling period.

ParameterBAT-AEL (mg/Nm3)a
Dust2-10
BaP0,001-0,01

The associated monitoring is in BAT 10.