Environmental Engineering Reference
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present solution conditions, two equilibrium reactions occur, as shown in Eqs. (4.8)
and (4.9). An increase in the pH value means a decrease developing in the
hydrogen ion concentration. Accordingly, the two equilibrium reactions move to a
positive direction, which dissociate SO 2 ⋅H 2 O into HSO 3 , and then HSO 3 into
SO 3 2 . Again, the reaction rate between NO 2 and SO 3 2 (Eq. (4.10)) is 40 times [24]
of that between NO 2 and HSO 3 (Eq. (4.11)). Consequently, the increasing factor
of absorption reactions (i.e., in Eq. (4.1)) increases, resulting a higher NO 2
removal efficiency. The pH influence on the NO 2 removal, in essence, is attributed
to the concentration changes of the tetravalent-S components such as SO 2 ⋅H 2 O,
SO 3 2 , and HSO 3 with respect to pH.
HSO 3 +H + (4.8)
SO 2
H 2 O
=
HSO 3
= SO 3 2 +H + (4.9)
2NO 2 +H 2 O+SO 3 2
= 2NO 2 +2H + +SO 4 2 (4.10)
2NO 2 +H 2 O+HSO 3
= 2NO 2 +3H + +SO 4 2 (4.11)
Fig. 4.8 Influence of the pH value on NO 2 removal with 0.01 mol/L S(IV) existence
Fig. 4.9 shows ion concentrations in the absorption solution. Concentrations of
NO 2 and NO 3 gradually increases and decreases, respectively, as the pH value
increases. This implies that SO 3 2 , which is prone to react with NO 2 , develops an
increase in its concentration, whereas the hydrolysis reaction (generating a low
NO 3 concentration) weakens to some extent. Consequently, reactions of NO 2 with
the tetravalent-S components strengthen, leading to an increasing contribution of
the redox reactions in the total NO 2 removal.
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