CuO/γγγγ -Al
2O
3†* **
*
**
(2001 7 25 , 2001 11 14 )
Effects of Heat Treatment Condition on Sulfur Removal Capacity of CuO/γγγγ-Al
2O
3Sorbent
Kyung Seun Yoo†, Sang Done Kim* and Soon Kook Kang**
Department of Environmental Engineering, Kwangwoon University, Seoul 139-701, Korea
*Department of Chemical Engineering, Korea Advanced Institute of Science and Technology, Daejeon 305-701, Korea
**Department of Environmental Engineering, Sunmoon University, Asan 336-840, Korea (Received 25 July 2001; accepted 14 November 2001)
CuO/γ-Al2O3 (300oC, 500oC)
! "# $%&'(. )! 500oC(bulk sulfation), CuO/γ-Al2O3 800oC*
+ ,-&'. / 0 12&'(. /34 300oC 56 700oC*+
7%&8 9+: ; < 12&'(. => ?@ )! > CuSO4A &B CDE SO3-F &B GHE +I JK )! > L+: CuO MNOP &B SO2 JKQ &B GHE RS (. 800oC
$\ ]^_ L+: Cu JK`) +ab . / ; octahedral cdef tetrahedral c g
T CuAl2O4 CD ,-Z[ ,-& RS (. CuAl2O4 ?@ )! > h)-F CuO/
γ-Al2O3 iT$jkd Y&B 7l4+ mkn CuAl2O4 o`p DRS XRDp P&B qY&'(.
Abstract−Effects of heat treatment temperature and time on sulfur removal capacity of CuO/γ-Al2O3 sorbent were deter- mined in a thermogravimetric analyzer with a variation of sulfation temperature (300oC, 500oC). At sulfation temperature of 500oC (bulk sulfation), sulfur removal capacity of CuO/γ-Al2O3 sorbent increases with increasing heat treatment temperature up to 800oC and then decreases. At sulfation temperature of 300oC (surface sulfation), however, sulfur removal capacity of the sorbent remains constant up to 700oC and then slightly decreases. This is because bulk sulfation advances by SO3 gas decom- posed from the CuSO4, whereas surface sulfation goes on by surface transfer of SO2 via catalytic function of CuO. Sulfur removal capacity of sorbent heated at 800oC shows a maximum value at the heat treatment time of 12 hr and then decreases with increasing heat treatment time. This is because redispersion of Cu ions is dominant at initial step and then formation of CuAl2O4 increases with increasing heat treatment time by the movement of impregnated copper ions from octahedral (Oh) to tetrahedral (Td) site. Bulk sulfation does not occur in CuAl2O4 due to the strong bonding of SO2 with CuO/γ-Al2O3 and the existence of CuAl2O4 has been confirmed using diffuse reflectance spectra (DRS) and x-ray diffractometer (XRD).
Key words: Sorbent, Calcination, SO2, Desulfurization, DRS
1.
SOx NOx ! "#! $%&' ()*[1-5], CuO/γ-Al2O3
+,-/./ 01 234 '! 5,! 236 789 :"[6-9].
; CuO/γ-Al2O3+,-/./ '1! <=>? @ ABC 7DE F >? G H I"* F% JK)". 90LM &
NO Centi P[10-12]4 Q@R ./Q STU SO3F 7DE VWX 'Y ABVW' >? G !" 0Z[ \ C]* Yoo P[13]4 Q@R AH^_ >?`a bc de 7D
†To whom correspondence should be addressed.
E-mail: yooks@daisy.kwangwoon.ac.kr
E AB >?%aF surface sulfation, deep sulfation, bulk sulfation
f FH @gh[ ijkXl 7DE AB >?mT[
" @B ]". 'n <=>?' JKU +,- oS>? mT[
*pkXl 7DE qrg' Al2(SO4)3 sU t5a 1'
u oSN HvwC <=-oS x'y' zHh[ \C]"[6]. 'n Jeong_ Kim[8]4 CuO/γ-Al2O3+,- 7{R |[ }F -b kXl SO2-Al2O3>?[ ~4 `aOa JK , :[ *
]".
CuO/γ-Al2O3+,-O 7DE AB _wC <=>? G AHU Q@R % AH Q@R R `a
de 7DE %@bF u U". deO
@O CuO/γ-Al2O3 <=[ M R _ `ab c[ a* CuO/γ-Al2O3+,- -bbc' <= E
M *p* !".
2.
2-1.
@ 01 +,- 3 mm pellet γ-Al2O3(Strem Chemical)
'1 -b]". Cu(NO3) · 3H2O %a AH
^' a Q , C n, J$ e
γ-Al2O3 k ". 70oCO e ,1 ' ¡
¢ W £¤O 24 Y¥ cb!". cbU +,-
$ g O R `a 500-1,000oC, R 2-170X
T¦". TU CuO/γ-Al2O3+,- ball mill
g§! n sieving 1-1.41 mm ¨]X EDX '1 Q
@R ©! AH \C]* -bU +,- |Q 1
@Rªa A.A.(Atomic Absorption Spectrophotometer) «%
AHU Q@R#[ «%]". BET 01 -bU +,-
VWw_ $ «%]".
2-2.
@ 01U TGA(TGDTA92 Setaram, France) Fig. 1 a
]". 10−6g %\T[ ¬ ®[ 01, ¯TBF
>?° ± ²&N F ³[ ´ µ 15 mm ¶t[ FJ quartz ·[ '1]". >?B ,%zR· q¸X ¹º
¸X >? /»¼ ½¾ basket ¿ÀU +,-
>?u U". 4 ±F 2X Á graphite Â&NJ FÃF furnace 6Ä `a PID -N Ås Æ
ÇÈU".
TGAO =Q >?[ JK ½¾ basket 30 mg
+,- ¿À* 900 cc/min $ ²R >?`aÉ H `a FÊ". >?`aO 6^ gF ¥%
W SO2ªaF 15,000 ppm' a SO2 ¹º =Q>?[ , K!". ® Ëu PC ¿ +,- <=s Ì[ Q]".
3.
<=>? `a de ,KU 8 wt% CuO/γ-Al2O3 +,- S/Cu Í ¸ Wwr -ÎU Ï=QF Í, >? de Fig. 2
a]". S/Cu Í ÏÐ (1) Q)".
(1)
O W +,- >? dÑ Ëu Ò, Wo +,- ;Ëu, Co +,- Q@R Ó^gÌ, Mi iTg
g^[ ÒÔ". +,- S/Cu Í >?' Fk
deO Ï=QF CuO/γ-Al2O3+,- >? Fk[
Õ , :". Fig. 2 ÒÖ × Ø' ¡Ù >?`aO S/Cu Í S
Cu--- (W W– o)⁄MSO3 WoCo⁄MCuO ---
=
Fig. 1. Schematic diagram of thermal gravimetric analyzer
1. N2 7. Blower
2. Air 8. Sample basket
3. SO2 9. Balance
4. H2 10. Controller
5. Gas chromatograph 11. Buffering line
6. SO2 trap 12. Thermocouple
Fig. 2. Captured amount of SO2 and S/Cu mole ratio of CuO/γγγγ-Al2O3 sorbent as a function of reaction time with a variation of sulfa- tion temperature.
40 1 2002 2
1.0[ ;_* :X >?`aF FÚ, S/Cu ÍF Fk[ \CÚ , :". '! _ Table 1 a! × Ø' Centi P[10]' -! >?(9-11)_ Yoo P[13]' -! >?
(14) ! 7DE >?G C!".
>?`a 400oC 'O ÛÜO Õ , :Ý' CuO/γ-Al2O3 + ,- Ï=QF -Î^' ÞwX %! ß[ ' Þ*
:". '³4 Q@R +ÀU Ï=QF surface transfer[10]
! 7DE VW =Q >?' JK" 7DE >?VW Ï
=QF -Î1^' àáW â 'q >?' HvH ã* Þ
äå'". <=>? `a 500oCO >? 180g' t_!
na %! ® ¬X HvwX Ï=QF +,- >
?' JK* :[ \CÚ , :".
8 wt% Q@RF AHU 7DE +,- t5 7DE V Ww[ æ! Q@R AH^4 5µmol/m2' * Nam_ Gavalas [14] *U Å,! 7DE Â Ï=QF -Î 2µmol/
m2[ æW M -Î^4 7µmol/m2' HÂ Fig. 2 a! 500oC
<=>?_ Ï=QF -Î^ 15µmol/m2 'ç* :X è!
HvwC >?' éqU". Koballa Dudukovic[17]4 CuSO4 t5
>? (6) SO3F STê , :[ -! × :X Kocaefe P[18]4 SO3 ¾vQÆ Ï=QF -Î' u q ê , :[ *! × :". Yoo P[13]4 >?`a 500oC O >?
(16) SO3 FF ST* 7DE AB >?' >?
(17) JKN ë=Q >?' JKU"* *]*
'! ìíîïX 7DE ABF HvwX =Q >? G
³[ ë=Q(bulk sulfation) >?X %]"[13].
Fig. 3A 3B R `a ð T! CuO/γ-Al2O3+, - >?`a 500oC(A) 300oC(B)O =Q >?[ JKð
dÑ S/Cu Í a]". Fig. 3AO Õ , : × Ø'
R `a F, +,- <=4 R `a 800oCÉ H F]* 900oCO ñòó ]". Û =Q>? ` a 300oCO R `a 800oCÉH ô õ' 'H IöX
900oCO <= F Ò÷". R `a 800oCÉH
w ST CuO islandO ë =Q >? ¹ U øTù°Ú[ CuSO4 ST' 1'u JKN ë =Q
>?T' F ³X 0U". Û R `a 900oC t 5 AHU Q@R 7DE >? ú ûü
ýþQÆC CuAl2O4 T' JK ³X 0U". Friedman_
Freeman[15] W 7DE VW AHU Q@R R `
aF FÚ, distorted octahedral siteO tetrahedral site 'Y ' F* R`a 900oCO CuAl2O4 T' ÿçu JK
³X *U × :". deO R `a 800oCO M ë
=Q >?' JK ³X 0U".
=Q>? 300oC _ W, R `a dÑ F u Ò H I* :X R `a 800oCÉH <=
F Ò * 900oCO <= F " Fk[ \CÚ , :". ' R `aF Fk de w ! Q@R . /øT VWw F Y>) äåX 0U". VW=
Q >? :NO ./øT Q@R øTùO JK
VW =Q >?va Ò * VWw STU SO3
-Î1^ Ò äå'".
R `a dÑ CuO/γ-Al2O3 +,- X-ray g
_ Fig. 4 a]". AHU Q@R t5 7DE AB
VWw 100 m2/g[ æX @Rk^ 4 wt%'qO XRD ' 2θ ß[ æX 35.6, 36.7, 38.8O Ò u U". Fig. 4 a!
× Ø' R `a 700oC _" R `a 800oCO AH U Q@R w 35.6_ 38.8 Q@R ' F
³[ \CÚ , :". è! R `a 900oCO CuAl2O4 mT ' 36.9O íu F ³X \C)".
R `a dÑ CuO/γ-Al2O3+,- diffuse reflectance spectra
_ Fig. 5 a]". Q þ! ¾v'` t5 ¾v'`
[ Q @b deO '°' O "çu Ò u U
". ¾v'`[ Q'`' 4(C tetrahedral R t5 ' Table 1. Sulfation reaction mechanism of CuO/γγγγ-Al2O3 sorbent
Reaction mechanism Reference
MeO+SO2(g)↔MeSO3*(ads) O2(g)↔2O*(ads)
MeSO3*(ads)+O*(ads) ↔MeSO4(s) MeSO3*(ads)↔MeSO3(s) MeSO3*(ads)↔Me*(s)+SO3(s) MeSO4(s)↔MeO(s)+SO3(g) 2Me*(s)+O2(g)↔2MeO(s)
(1) (2) (3) (4) (5) (6) (7)
Koballa and Dudukovic [17]
SO2(g)↔A+SO2(ads) CuO+SO2(ads)↔CuO-SO2(ads) CuO+CuO-SO2(ads)↔CuSO4(s)+Cu Al2O3+CuO-SO2(ads)↔Al2O3-SO3(s)+Cu Cu+O2→CuO
(8) (8) (10) (11) (12)
Centi et al. [10]
CuO+SO2+1/2O2→CuSO4 Al2O3+CuO-SO2→Al2O3-SO3+Cu Cu+O2→CuO
CuSO4→CuO+SO3 Al2O3+SO3→Al2O3-SO3
(13) (14) (15) (16) (17)
Yoo et al. [13]
Fig. 3. S/Cu mole ratio of CuO/γγγγ-Al2O3 sorbent as a function of reac- tion time with a variation of heat treatment temperature: (A) bulk sulfation(Ts=500oC), (B) surface sulfation(Ts=300oC).
°4 1,300-1,600 nm' Q'`' 6(C octahedral R t5 600-800 nmO Ò u U"[16]. γ-Al2O3 AHU Q@R t5 tetralhedral R 1,415 nmO \C, octahedral site 740 nm
O \CU". Fig. 5 a! _ Ø' AHU Q@R R
`a F, 1,415 nmO a F* 740 nm
O a k[ \CÚ , :". R `a 1,000oC_
W tetrahedral R 4 ¡¢ 0eH* octahedral R shoulder Â' u ' CuO CuAlO2þÆ _ /5 z0!
_ ¹* :". '! _ R `aF Fk de R
`a 900oCÉH Q@R F octahedral RO tetrahedral
R 'Y CuAl2O4 @bF ST 1,000oCO * q>? CuAlO2 þÆ' STh[ E!".
R `a 800oCO R dÑ CuO/γ-Al2O3 +,-
Ï=QF -Î[ <=>?`a 300oC 500oC M Fig. 6
a]". <=>?`a 500oC t5 W R 12[
æX +,- <=4 Mß[ C n Û 'qO R
de Âu ]". Û <=>?`a 300oC t5
R de /5 Efu _ Ò)". <
=>? `a 500oC t5 R 12O M <=[
C 'z AHU Q@R w_ Q@R octahedral RO tetrahedral R R'Y' k N äåC ³X
0U". w ! CuO island T4 ë=Q >?
" zRHÂ octahedral RO tetrahedral R 'Y
CuAl2O4F ST ³4 CuSO4 Al2(SO4)3 ST ¡¢ 2µu Ru 1u U". deO 800oC _O Õ , : ×
Ø' +,- w R 4 12C ³X 0U".
Fig. 74 CuO/γ-Al2O3 +,- R dÑ ¸ Wwr Ï=
QF -Î[ VW =Q>?_ ë =Q>?X @g R `a de a! _'". ë =Q >?' JK
Fig. 4. XRD spectra of heat treated CuO/γγγγ-Al2O3 sorbent.
Fig. 5. Diffuse reflectance spectra of heat treated CuO/γγγγ-Al2O3 sorbent.
Fig. 5. Diffuse reflectance spectra of heat treated CuO/γγγγ-Al2O3 sorbent.
Fig. 6. Sulfur removal capacity of CuO/γγγγ-Al2O3 sorbent heat treated at 800oC as a fuction of heat treatment time with a variation of sulfation temperature.
40 1 2002 2
<=>? `a 500oC _ R `a F, +,- Ï
=QF -Î' q)X 700oCÉH R ' F
a +,- <=' Î %u zH)". Û R `a 800oCO R' Fk de AHU Q@R ocathedral
RO tetrahedral R R'Y ! CuAl2O4 ST' J KN +,- <=4 OOó ]". VW =Q >?' J K <=>? `a 300oC _ R `a 700oCÉH +,-
<=' Î 'H IöX R `a 800oCO <
= FF Ò÷". Fig. 7O Õ , :Ý' VW =Q >?
:NO ¸ Wwr Ï=QF -Î^4 Å,! 7DE Â -Î^
2µmol/m2[ H I* :X è! 800oC R STU CuAl2O4 ! +,- <= F Ò H I* :[ Õ , :". '! _ VW =Q >?_ ë =Q >? ìíîï õ' C ³X ë =Q >?O CuAl2O4ST
ë =Q >?[ za CuSO4 ST' 2µN HvwC A B >?' -!HÂ VW =Q >?O Ï=QF >?' CuO, CuAl2O4@' JK äå'"[9].
4.
CuO/γ-Al2O3+,- R `a dÑ Ï=QF -Î
E [ 6^g '1 *p]". +,- R `a FW AHU Q@R ogQ_ k >?' JK ë =Q >?T' F]". R `a 800oCO
M ë =Q >?T' Ò÷X 900oC'q *`O Q
@R 7DE *q>? ST CuAlO2 ë
=Q >?T' ñòu ]". w R `a 800oC O R [ FW R 12ÉH w
! >?T FF Ò * Û 'q O OOó ST
CuAl2O4 >?T' u U". VW =Q >?4 R [ Î H IöX ' SO2 >?' CuO, CuAl2O4
@' JK äåX 0U". R `a 800oC 'O
CuAl2O4 STvaF `a de ñòu äå R [ Fða ë =Q >?_ VW =Q >? ¡¢ >
?T F Ò H Iö".
' å4 2000La üM @ @) X ' 0î".
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Fig. 7. Sulfur removal capacity and sulfate on alumina as a function of heat treatment time with a variation of heating temperature(,: 600oC, ,: 700oC, ,: 800oC.