Environmental Engineering Reference
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adsorption quantities of LFA1 with 17.51% carbon and LFA2 with 39.87% carbon
were similar, and these values were larger than that of FA with 6.13% carbon. The
adsorption ability of fly ash was not proportional to its carbon content. Other ele-
ments in fly ash and the composition of flue gas might have great effects on mercury
adsorption by fly ash.
5.3.1.2 Hg 0 Adsorption Ability of Calcium-Based Sorbent
Three different sorbents, namely hydrated lime (Ca(OH) 2 of 97.6%), lime (CaO of
87.6%) and MFC (mixture of fly ash and lime), were chosen in the study of the Hg 0
adsorption ability of calcium-based sorbents.
Hg 0 adsorption ability of hydrated lime
Adsorption experiments were conducted on two kinds of simulated flue gas: 1) BL
and 2) BL added with 800 ppm SO 2 . Other conditions were the same (Hg 0 concen-
tration: 19.9 g/m 3 ; temperature: 125 °C; flow: 1 L/min). The adsorption kinetic
and adsorption efficiency curves of Hg 0 by hydrated lime on the two kinds of
simulated flue gas are shown in Fig. 5.3. The existence of SO 2 was favorable for
hydrated lime adsorbing Hg 0 because SO 2 reacted with the hydrated lime, promot-
ing the adsorption of Hg 0 . Reaction equations are as follows:
, (5-1)
Ca(OH) +SO +O
CaSO +H O+O
2
2
2
4
2
2Hg +O
0
Hg O
, (5-2)
2
0
, (5-3)
Ca(OH)+SO+O+2Hg
CaSO+HO+HgO
2
2
2
4
2
2
. (5-4)
Ca(OH) +SO
CaSO +H O
2
2
3
2
0.6
no SO 2
800 ppm SO 2
100
0.5
0.4
90
Inlet Hg 0 20.5383 g/m 3
0.3
80
0.2
BL
800 ppm SO 2
Inlet Hg 0 19.8728 g/m 3
70
0.1
0.0
60
0
5
10
15
20
25
30
35
0
5
10
15
20
25
30
35
Time (min)
Time (min)
(a) (b)
Fig. 5.3 Hg 0 adsorption by hydrated lime on two kinds of simulated flue gas
Hg 0 adsorption ability of lime
Adsorption experiments were conducted on two kinds of simulated flue gas: 1) BL
and 2) BL added with 800 ppm SO 2 . Other conditions were the same (Hg 0 concen-
tration: 18.4 g/m 3 ; temperature: 125 °C; flow: 1 L/min). The adsorption kinetic and
 
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