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

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Chapter 4<br />

Technical description<br />

A summary description is provided in Table 4.24. Operating temperatures <strong>for</strong> <strong>the</strong>rmal<br />

desorption typically range from 320 °C to more than 800 °C. Thermal desorption can be carried<br />

out with <strong>the</strong> help <strong>of</strong> vacuum or vibrating equipment [ 245, Euro <strong>Chlor</strong> 2009 ], [ 263, Khrapunov<br />

et al. 2007 ], [ 266, US EPA 2007 ].<br />

Achieved environmental benefits<br />

The achieved environmental benefit <strong>of</strong> this technique is <strong>the</strong> decontamination <strong>of</strong> soil.<br />

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

The temperature and <strong>the</strong> residence time are <strong>the</strong> most important factors <strong>for</strong> <strong>the</strong> efficiency <strong>of</strong><br />

<strong>the</strong>rmal desorption. In general, middle-range temperatures <strong>of</strong> 540 – 650 °C can decrease <strong>the</strong><br />

concentration <strong>of</strong> <strong>the</strong> residual mercury to levels below 2 mg/kg and <strong>the</strong> mercury can be reclaimed<br />

with a purity <strong>of</strong> 99 % despite its different structures and <strong>for</strong>ms [ 252, Chang and Hen 2006 ].<br />

At a mercury cell chlor-<strong>alkali</strong> site in Bohus (Sweden), approximately 25 kt <strong>of</strong> soil contaminated<br />

with mercury and PCDDs/PCDFs were planned to be treated in <strong>the</strong> period <strong>of</strong> 2000 – 2003.<br />

Thermal desorption was planned to take place in a rotary kiln using vacuum at a capacity <strong>of</strong><br />

2 t/h. The mercury contained in <strong>the</strong> exhaust gases (10 mg/m 3 ) was <strong>the</strong>n supposed to enter a wet<br />

scrubber containing hydrogen peroxide which oxidises elemental mercury <strong>for</strong> its precipitation as<br />

mercury sulphide [ 197, Götaverken Miljö 2000 ]. {Please TWG provide more in<strong>for</strong>mation.}<br />

At a mercury and diaphragm cell chlor-<strong>alkali</strong> site in Taipei (Taiwan), a full-scale test with a<br />

total <strong>of</strong> 4174 m 3 soil was carried out in 2001 – 2003. Two sets <strong>of</strong> <strong>the</strong>rmal desorption kilns were<br />

used with batch masses <strong>of</strong> 2 t per kiln and a capacity <strong>of</strong> 8 t/d per kiln. Optimised per<strong>for</strong>mance<br />

was obtained at a temperature <strong>of</strong> 750 °C and a residence time <strong>of</strong> 3 h. The post-treatment system<br />

mainly consisted <strong>of</strong> condenser, condensation water tank, buffer tank and sulphur-impregnated<br />

activated carbon tank (Figure 4.10) [ 252, Chang and Hen 2006 ].<br />

NB: 1: Thermal desorption kiln;<br />

2: Cooling water recycle system;<br />

3: Condensation water separate tank;<br />

4: Sulphur-impregnated activated carbon adsorption tank;<br />

5: Coagulation tank;<br />

6: Dewatering device;<br />

7: Buffer tank;<br />

8: Sulphur-impregnated activated carbon adsorption tank.<br />

Source: [ 252, Chang and Hen 2006 ]<br />

WORKING DRAFT IN PROGRESS<br />

Figure 4.10: Flow diagram <strong>of</strong> <strong>the</strong> on-site <strong>the</strong>rmal desorption system used at a chlor-<strong>alkali</strong> site in<br />

Taipei (Taiwan)<br />

262 December 2011 TB/EIPPCB/CAK_Draft_1

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