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CO2 Sequestration through Deep Saline Injection and ...

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although contribution to capacity estimates from mineralization must be considered, in addition<br />

to hydrodynamic considerations that will govern the length of time <strong>CO2</strong> may be safely stored as<br />

the pure phase slowly diffuses into the system for solubility <strong>and</strong> mineral trapping.<br />

Table 2<br />

Average characteristics of Viking formation used in<br />

solubility estimations (e.g. [14, 56, 60])<br />

Parameter Assigned Value<br />

Depth, m 2000<br />

Temperature, deg C 55<br />

Pressure, MPa 20<br />

Salinity, g/l 70<br />

Plan view area, km 2<br />

400,000<br />

Thickness, m 30<br />

Porosity 0.2<br />

5.2.3. Mineral Trapping <strong>and</strong> Capacity<br />

Mineral trapping, as has been stated before, is a long term storage mechanism. The mechanism<br />

as described by Ortoleva et al. [61] is that <strong>CO2</strong> first dissolves in water to produce the weak<br />

carbonic acid,<br />

CO 2(g) + HO 2 � HCO 2 3<br />

. (11)<br />

This is followed by rapid dissolution of carbonic acid to for the bicarbonate ion which increases<br />

the acidity of the solution,<br />

HCO H + HCO −<br />

� . (12)<br />

+<br />

2 3 3<br />

This leads to the dissolution of many of the primary host rock minerals, which in turn causes<br />

complexing of dissolved cations with the bicarbonate ions such as<br />

Ca + HCO CaHCO<br />

+<br />

−<br />

2 3 �<br />

+<br />

3<br />

. (13)<br />

These dissolved bicarbonate species react with divalent cations to precipitate carbonate minerals<br />

<strong>and</strong> the formation of Ca, Mg, <strong>and</strong> Fe(II) carbonates are expected to be the primary means by<br />

which the <strong>CO2</strong> is immobilized [62] as is shown <strong>through</strong> the following equations:<br />

48

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