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

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{Please TWG provide more in<strong>for</strong>mation.}<br />

Achieved environmental benefits<br />

The achieved environmental benefits <strong>of</strong> this technique include:<br />

prevention <strong>of</strong> emissions <strong>of</strong> ozone-depleting substances;<br />

prevention <strong>of</strong> emissions <strong>of</strong> substances with high global warming potential.<br />

Chapter 4<br />

Environmental per<strong>for</strong>mance and operational data<br />

At <strong>the</strong> Dow plant in Stade (Germany) chlorine is used as refrigerant [ 199, Bezirksregierung<br />

Lüneburg 1997 ].<br />

At <strong>the</strong> Orica plants in Melbourne and Sydney (Australia), <strong>the</strong> chlorine gas is liquefied by carbon<br />

dioxide evaporating at -45 °C and <strong>the</strong> carbon dioxide is in turn recondensed by an ammonia<br />

refrigeration unit operating at -52.6 °C saturated suction temperature and 40 °C condensing<br />

temperature. Because ammonia and chlorine are so reactive, <strong>the</strong>y are physically separated from<br />

each o<strong>the</strong>r in <strong>the</strong> plant and in <strong>the</strong> refrigeration system. The ammonia refrigeration system is<br />

designed to provide cooling to a carbon dioxide <strong>the</strong>rmosiphon loop which <strong>the</strong>n provides cooling<br />

to <strong>the</strong> chlorine liquefaction process. The advantage <strong>of</strong> <strong>the</strong> <strong>the</strong>rmosiphon system is that <strong>the</strong>re are<br />

no moving parts or additional energy inputs. The brake horsepower <strong>of</strong> <strong>the</strong> refrigeration system<br />

ranges from 4.4 – 4.5 per tonne <strong>of</strong> refrigeration. The liquefied chlorine is stored at -41 °C and<br />

atmospheric pressure [ 270, Orica 2011 ].<br />

Cross-media effects<br />

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Technical considerations relevant to applicability<br />

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Economics<br />

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Driving <strong>for</strong>ce <strong>for</strong> implementation<br />

The driving <strong>for</strong>ce <strong>for</strong> implementation <strong>of</strong> this technique is environmental legislation.<br />

Example plants<br />

Dow in Stade (Germany), chlorine capacity 1585 kt/yr, use <strong>of</strong> chlorine as refrigerant<br />

[ 199, Bezirksregierung Lüneburg 1997 ];<br />

Orica in Melbourne (Australia), chlorine capacity 31 kt/yr, use <strong>of</strong> carbon dioxide and<br />

ammonia as refrigerants [ 238, Clews 2001 ];<br />

Orica in Sydney (Australia), chlorine capacity 31 kt/yr, use <strong>of</strong> carbon dioxide and<br />

ammonia as refrigerants [ 238, Clews 2001 ].<br />

<strong>Reference</strong> literature<br />

[ 78, Regulation EC/1005/2009 2009 ], [ 198, WMO 2006 ], [ 199, Bezirksregierung Lüneburg<br />

1997 ], [ 200, UBA 2011 ], [ 238, Clews 2001 ], [ 270, Orica 2011 ]<br />

WORKING DRAFT IN PROGRESS<br />

4.3.6 Techniques to reduce emissions to water<br />

4.3.6.1 Techniques to reduce emissions <strong>of</strong> sulphate<br />

4.3.6.1.1 Overview<br />

In addition to <strong>the</strong> technique described in <strong>the</strong> following Section 4.3.6.2.2, <strong>the</strong> recycling or reuse<br />

<strong>of</strong> spent sulphuric acid from chlorine drying (see Section 4.3.7) and <strong>the</strong> use <strong>of</strong><br />

non-sulphur-containing reducing agents to reduce emissions <strong>of</strong> free oxidants (see<br />

Sections 4.3.6.3.3 to 4.3.6.3.6) also reduce sulphate emissions.<br />

TB/EIPPCB/CAK_Draft_1 December 2011 231

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