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Novel Design of an Integrated Pulp Mill Biorefinery for the ...

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3.3 Dimethyl E<strong>the</strong>r Syn<strong>the</strong>sis<br />

3.3.1 Syngas Cle<strong>an</strong>-up<br />

The major components <strong>of</strong> <strong>the</strong> syngas at <strong>the</strong> outlet <strong>of</strong> <strong>an</strong> entrained flow slagging gasifier<br />

are CO, H2, <strong>an</strong>d CO2. Some N2, CH4 <strong>an</strong>d small amounts <strong>of</strong> H2S are present. Some amount <strong>of</strong><br />

char (unconverted carbon) <strong>an</strong>d ash are also contained in <strong>the</strong> exit flow <strong>of</strong> <strong>the</strong> gasifier. Table 26<br />

provides <strong>the</strong> composition <strong>of</strong> <strong>the</strong> raw syngas.<br />

Table 26: The composition <strong>an</strong>d components <strong>of</strong> <strong>the</strong> raw syngas.<br />

Components Mole percentage Mass percentage<br />

CO 45.7 0.62683<br />

H2 37.0 0.03659<br />

CH4 1.2 0.00916<br />

CO2 13.5 0.29094<br />

N2 1.9 0.02560<br />

H2S 0.7 0.01084<br />

Syngas quenching<br />

The quench ensures that <strong>the</strong> char <strong>an</strong>d ash particles will be non-sticky to prevent fouling<br />

issues. After capture in a filter, <strong>the</strong>se particles will be recycled to <strong>the</strong> gasifier to increase <strong>the</strong><br />

carbon conversion efficiency. Among <strong>the</strong> four main alternatives <strong>for</strong> quenching, a water quench<br />

will be used in <strong>the</strong> gas cle<strong>an</strong>ing system which uses sensible heat from <strong>the</strong> syngas to vaporize<br />

water. The hot syngas will be totally quenched with water to about 300 o C.<br />

Particle removal<br />

Wet solids removal systems use water scrubbers operating at a temperature lower th<strong>an</strong><br />

<strong>the</strong> dewpoint <strong>of</strong> <strong>the</strong> gas so that <strong>the</strong> smallest solid particles c<strong>an</strong> act as nuclei <strong>for</strong> condensation <strong>an</strong>d<br />

ensure efficient operation. Dry solids removal systems use c<strong>an</strong>dle filters that c<strong>an</strong> remove all<br />

solids from <strong>the</strong> gas at temperatures between 300 <strong>an</strong>d 500 o C. Above 500 o C, alkali compounds<br />

may pass <strong>the</strong> filters in signific<strong>an</strong>t amounts. Below 300 o C, <strong>the</strong> filters may be blinded <strong>of</strong> deposits<br />

<strong>of</strong> ammonium chloride (NH4Cl) [10] (C. Higm<strong>an</strong> <strong>an</strong>d M. v<strong>an</strong> der Burgt, “Gasification”, Elsevier,<br />

2003).<br />

Sulfur compounds<br />

The major part (>90 %) <strong>of</strong> <strong>the</strong> sulfur components in <strong>the</strong> feed are hydrogen sulfide (H2S).<br />

Up to 99.8 % <strong>of</strong> <strong>the</strong> coal sulfur c<strong>an</strong> be removed in <strong>the</strong> acid gas removal process. Since <strong>the</strong> syngas<br />

will be used to produce DME, deep sulfur removal will be required to protect <strong>the</strong> catalyst<br />

downstream. Usually, Rectisol physical solvent (meth<strong>an</strong>ol as solvent) AGR (acid gas removal)<br />

process will be applied. But <strong>the</strong> relatively low temperature (40 o C) in <strong>the</strong> AGE process will result<br />

in great heat loss in <strong>the</strong> gas cle<strong>an</strong>ing process. Herein, zinc oxide will be used as sorbent <strong>for</strong> H2S<br />

removal. In this case, remarkably higher desulfurization temperatures <strong>of</strong> ca. 400 o C will be<br />

obtained[101].<br />

52

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