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

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4.3.6.3.4 Catalytic decomposition reduction<br />

Chapter 4<br />

Description<br />

This technique consists in converting free oxidants to chloride and oxygen by using<br />

nickel-, iron- or cobalt-based catalysts. Catalytic decomposition can be carried out in fixed-bed<br />

reactors or with a catalyst slurry.<br />

Technical description<br />

The catalytic decomposition occurs The decomposition <strong>of</strong> free oxidants to chloride and oxygen<br />

can be catalysed by a nickel, iron or cobalt based catalyst, according to <strong>the</strong> following overall<br />

reaction:<br />

[M] n+<br />

2 NaOCl V 2 NaCl + O2w<br />

This decomposition reaction generally occurs in hypochlorite solutions, albeit too slow to<br />

remove free oxidants in technical systems. The reaction is accelerated by metal catalysts, lower<br />

pH values and higher temperatures (see Section 2.6.12.2). Depending on <strong>the</strong> conditions,<br />

hypochlorite may instead decompose to chloride and chlorate (see Section 4.3.6.3.5).<br />

Some systems operate with a catalyst slurry which uses solutions <strong>of</strong> nickel, iron or cobalt<br />

compounds added to <strong>the</strong> waste water in stirred or agitated tanks [ 208, Johnson Mat<strong>the</strong>y 2009 ].<br />

Metal concentrations are typically 20 mg/l [ 2, Le <strong>Chlor</strong>e 2002 ]. The high pH value <strong>of</strong> <strong>the</strong><br />

solution causes <strong>the</strong> metal ions to precipitate as <strong>the</strong>ir hydroxides, which are <strong>the</strong>n removed and<br />

regenerated. Alternatively, a fine dispersion <strong>of</strong> an insoluble metal compound can be used which<br />

removes <strong>the</strong> need <strong>for</strong> <strong>the</strong> catalyst regeneration stage. is blended with <strong>the</strong> waste water stream to<br />

promote <strong>the</strong> reaction, in a batch process. To avoid emissions <strong>of</strong> metals In both cases, <strong>the</strong> catalyst<br />

must be allowed to settle be<strong>for</strong>e <strong>the</strong> supernatant water can be discharged, to avoid emissions <strong>of</strong><br />

heavy metals. The reaction time combined with <strong>the</strong> settling <strong>of</strong> <strong>the</strong> catalyst takes several days<br />

[ 208, Johnson Mat<strong>the</strong>y 2009 ]. The catalyst activity decreases from batch to batch, although it<br />

is unclear whe<strong>the</strong>r this is due to deactivation <strong>of</strong> <strong>the</strong> catalyst or loss <strong>of</strong> metal [ 75, COM 2001 ].<br />

O<strong>the</strong>r systems operate with <strong>the</strong> catalyst on a fixed-bed reactor (Figure 4.7). The catalyst used is<br />

a nickel oxide promoted with iron on an alumina support. The design <strong>of</strong> <strong>the</strong> reactor is modular.<br />

The gravity-fed hypochlorite solution flows countercurrently with respect to <strong>the</strong> evolving<br />

oxygen [ 206, Denye et al. 1995 ], [ 207, Stitt et al. 2001 ], [ 208, Johnson Mat<strong>the</strong>y 2009 ]. , see<br />

Figure 4.7, reducing <strong>the</strong> loss <strong>of</strong> metals and increasing <strong>the</strong> capacity (no settling required)<br />

compared to slurry type catalytic systems. Also, <strong>the</strong> necessary concentration <strong>of</strong> catalyst is low<br />

(20 ppm), [Le <strong>Chlor</strong>e, 1996].<br />

WORKING DRAFT IN PROGRESS<br />

TB/EIPPCB/CAK_Draft_1 December 2011 239

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