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(BAT) Reference Document for the Production of Chlor-alkali ...

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Chapter 3<br />

Table 3.31: Yearly waste Waste generation and final treatment at <strong>the</strong> Hydro Polymers AB<br />

chlor-<strong>alkali</strong> plant in Stenungsund (Sweden) (chlorine capacity 120 kt/yr;<br />

production based on vacuum salt)<br />

Waste type<br />

Waste<br />

amount in<br />

t/yr<br />

[tonnes/year]<br />

Brine sludge 20 – 25<br />

Waste water<br />

treatment sludge<br />

Hg Mercury<br />

content be<strong>for</strong>e<br />

treatment in<br />

g/kg<br />

0.050 – 0.100<br />

50 – 100<br />

mg/k<br />

g<br />

5 – 15 5 – 10 g/kg<br />

Carbon sludge 2 – 3.5 150 – 450 g/kg<br />

Decomposer carbon 0.5 – 1 150 – 300 g/kg<br />

Rubberlining 0.5<br />

Steel/iron<br />

construction parts<br />

Concrete and o<strong>the</strong>r<br />

construction waste<br />

Source: [ 75, COM 2001 ]<br />

10 – 15<br />

1 – 3<br />

0.010 – 0.400<br />

10 – 400 mg/kg<br />

Landfilled<br />

Treatment<br />

Distilled<br />

Landfilled after<br />

stabilisation<br />

Distilled<br />

Landfilled after<br />

stabilisation<br />

Distilled<br />

Landfilled after<br />

stabilisation<br />

Acid bath<br />

Incineration<br />

Acid bath<br />

Sold as scrap<br />

Landfilled after<br />

stabilisation<br />

Annual plant capacity: 120000 tonnes <strong>of</strong> chlorine. <strong>Production</strong> based on vacuum salt.<br />

3.1.2.1.4 Mercury contained in products<br />

Final<br />

mercury<br />

content in<br />

[mg/kg]<br />

WORKING DRAFT IN PROGRESS<br />

TB/EIPPCB/CAK_Draft_1 December 2011 127<br />

< 10<br />

20 – 200<br />

20 – 200<br />

Hydrogen and caustic soda from amalgam chlor-<strong>alkali</strong> plants contain a certain amount <strong>of</strong><br />

mercury. The mercury level in chlorine is negligible, i.e. less than 0.001 g/tonne. No mercury<br />

removal processes are used <strong>for</strong> this product. Traces <strong>of</strong> mercury in chlorine may be due to <strong>the</strong><br />

presence <strong>of</strong> mercury in <strong>the</strong> sulphuric acid used to dry chlorine. As regards sodium and<br />

potassium hydroxides and hydrogen, purification techniques are needed be<strong>for</strong>e <strong>the</strong> products are<br />

sold. Mercury content in sodium and potassium hydroxides remains <strong>the</strong> most important<br />

compared to o<strong>the</strong>r products.<br />

Mercury losses to products in 1996, as reported by OSPARCOM, varied from 0.01 to 0.93 g per<br />

tonne chlorine capacity, corresponding to 612 kg emitted. These figures correspond to <strong>the</strong> sum<br />

<strong>of</strong> mercury in chlorine gas, in <strong>alkali</strong>s and in hydrogen which is sold <strong>for</strong> fur<strong>the</strong>r processing or<br />

use, but which is not sold as a fuel. {This in<strong>for</strong>mation is contained in Section 3.5.8 on emissions<br />

via products.}<br />

3.5.10 Mass balance calculation<br />

{The following paragraph was moved to Section 3.5.3. For a better understanding, it should be<br />

described at <strong>the</strong> beginning <strong>of</strong> <strong>the</strong> section why figures are expressed per capacity and not per<br />

actual production.}<br />

Reported figures<br />

As regards mercury outputs, figures are expressed and reported by <strong>the</strong> industry in terms <strong>of</strong><br />

chlorine capacity ra<strong>the</strong>r than real production. This is quite specific to <strong>the</strong> mercury chlor-<strong>alkali</strong><br />

300<br />

< 15

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