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

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Chapter 3<br />

3.5 Emissions Emission and consumption levels and waste<br />

generation from <strong>the</strong> mercury cell technique process<br />

3.5.1 Overview<br />

Emissions and consumption <strong>of</strong> mercury as well as <strong>the</strong> generation <strong>of</strong> mercury-contaminated<br />

waste are specific to <strong>the</strong> mercury cell technique. At present some 12000 tonnes <strong>of</strong> mercury are<br />

contained in mercury cells used <strong>for</strong> chlorine production in <strong>the</strong> EU. This is based on an average<br />

<strong>of</strong> 1.8 kg <strong>of</strong> mercury per tonne <strong>of</strong> annual chlorine capacity and an EU mercury cell chlorine<br />

capacity <strong>of</strong> 6.9 millions tonnes <strong>of</strong> chlorine per year [Lindley, 1997]. This mercury Mercury is<br />

contained and recycled within <strong>the</strong> chemical process. Never<strong>the</strong>less, due to <strong>the</strong> process<br />

characteristics, mercury emissions to air and water occur and some mercury leaves <strong>the</strong> process<br />

via waste into air, water and also in wastes are generated. Products, mainly caustic soda, and to<br />

a lesser extent hydrogen, contain certain amounts <strong>of</strong> mercury and are treated be<strong>for</strong>e being used<br />

or sold. As regards <strong>the</strong> mercury level in chlorine, it is virtually zero and no mercury removal<br />

processes are used <strong>for</strong> this product. Some emissions occur during <strong>the</strong> decommissioning <strong>of</strong> an<br />

installation or its conversion to <strong>the</strong> membrane cell technique.<br />

Any attempt to draw a balance generally results in a difference between inputs and outputs <strong>of</strong><br />

mercury, ei<strong>the</strong>r positive or negative. This item issue is specifically addressed in Section 3.5.10.<br />

3.5.2 Mercury in cells<br />

At <strong>the</strong> end <strong>of</strong> 2010, <strong>the</strong> total chlorine production capacity in EU-27 and EFTA countries based<br />

on <strong>the</strong> mercury cell technique amounted to 3.97 Mt/yr [ 55, Euro <strong>Chlor</strong> 2011 ]. A total <strong>of</strong> 6870 t<br />

<strong>of</strong> metallic mercury were contained in cells and ano<strong>the</strong>r 630 t were stored in facilities on site,<br />

ei<strong>the</strong>r as stock <strong>for</strong> fur<strong>the</strong>r use or as waste after <strong>the</strong> respective mercury cell unit had ceased to<br />

operate [ 82, Euro <strong>Chlor</strong> 2011 ]. Table 3.22 summarises <strong>the</strong> amount <strong>of</strong> mercury in cells.<br />

Table 3.22: Amount <strong>of</strong> mercury in cells per annual chlorine production capacity in mercury<br />

cell chlor-<strong>alkali</strong> plants in EU-27 countries in 2010<br />

Amount <strong>of</strong> mercury in cells in kg per tonne <strong>of</strong> annual chlorine capacity ( 1 )<br />

Min. 10th percentile 25th percentile Median 75th percentile 90th percentile Max.<br />

0.795 1.20 1.39 1.54 2.04 2.54 4.36<br />

( 1 ) 33 data from 33 plants.<br />

Source: [ 55, Euro <strong>Chlor</strong> 2011 ], [ 82, Euro <strong>Chlor</strong> 2011 ]<br />

3.5.3 Reporting <strong>of</strong> figures per chlorine capacity<br />

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

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

WORKING DRAFT IN PROGRESS<br />

<strong>alkali</strong> sector. Because <strong>of</strong> <strong>the</strong> electrolytic process in itself, mercury emissions are not linked to<br />

production in a linear way. The majority <strong>of</strong> <strong>the</strong> emissions are from <strong>the</strong> cell room where <strong>the</strong><br />

absolute amount mainly depends on small leaks or accidental losses and on historical<br />

contamination <strong>of</strong> <strong>the</strong> building which are mostly independent from <strong>the</strong> production rate. The<br />

emissions are is far more related to dependent on <strong>the</strong> equipment, plant design, maintenance<br />

requirements, pressure and temperature <strong>of</strong> <strong>the</strong> cell and decomposer denuder [ 83, Euro <strong>Chlor</strong><br />

2010 ].<br />

However, it could be assumed that if half <strong>of</strong> <strong>the</strong> cells are switched <strong>of</strong>f, <strong>the</strong> reporting <strong>of</strong> figures<br />

per chlorine capacity may be inappropriate this reasoning may be wrong. The industry gives two<br />

main reasons to argue that this is usually not <strong>the</strong> case <strong>for</strong> reporting mercury emissions in terms<br />

104 December 2011 TB/EIPPCB/CAK_Draft_1

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