• 검색 결과가 없습니다.

The Effect of Residual Water on the Adsorption Process of Carbon Tetrachloride by Activated Carbon Pellet

N/A
N/A
Protected

Academic year: 2021

Share "The Effect of Residual Water on the Adsorption Process of Carbon Tetrachloride by Activated Carbon Pellet"

Copied!
9
0
0

로드 중.... (전체 텍스트 보기)

전체 글

(1)HWAHAK KONGHAK Vol. 40, No. 6, December, 2002, pp. 694-702.    

(2)     

(3) *   †.   , *  4

(4) 20 , 2002 9

(5) 11 ). (2002. The Effect of Residual Water on the Adsorption Process of Carbon Tetrachloride by Activated Carbon Pellet Sung Jun Jeong, Dae Lo Lee, Tae Young Kim, Jin Hwan Kim*, Seung Jai Kim† and Sung Young Cho Department of Environmental Engineering, *Department of Chemical Engineering, Chonnam National University, Gwangju 500-757, Korea (Received 20 April 2002; accepted 11 September 2002).    

(6)    ,  ,       !. " # $ % &' CTC(Cabon Tetrachloride, CCl )( )*+ ,- ./( 012 #$34. 56 )*7. CTC( &$8, 9:;< ,- =>?@> )*A( ;< B ( ./ C*D EF #$34.  ( ./A 0 20%(w/w)GH !IJK, LM NO 298.15 K P34JK  Q R<S( )*TUNOV>% LangmuirWXJ Y ZI. ( ./ A[ \E ,] CCl ( )*A ^S34 JK R<S( )* ,- ./( C* _`J ^SI, LDF(linear driving force)La2 [3b => ?@2 Y Lc  !I. 4. 4. Abstract − Activated carbons have been used as adsorbents in various industrial application, such as solvent recovery, gas separation, deodorization, and catalysts. In this study, the effects of residual water on the activated carbon adsorbent surface on the adsorption capacity of CCl4 were investigated. Adsorption behavior in a fixed bed was studied in terms of feed concentration, flow rate, breakthrough curve and adsorption capacity for CCl4. Desorption characteristics of residual water on activated carbon were also studied. The water contents of the activated carbon were varied in the range of 0-20%(w/w) and all experiments were performed at 298.15 K. The adsorption equilibrium data CCl4 on the activated carbon were well expressed by Langmuir isotherm. The adsorption capacity of CCl4 decreased with increasing residual water content. Desorption of residual water in activated carbon decreased expotentially with CCl 4 adsorption. The obtained breakthrough curves using LDF(linear driving force) model represented our experimental data. Key words: Adsorption, Desorption, CCl4, Activated Carbon. 1..  . 7 N O

(7) 1JP, QRS, T

(8)

(9) )U  N, VB, 

(10) W 1./. 12 6X7

(11) Y< JK L P(Fourth Annual Report on Carcinogens, NTP 85-002, 1985)[2] 3 Z, 0[\: ]^, _`, abc, de, f1, gh, \]]^, i jZkl ! m/. n oW p", =q]^ l -rG Is  n/. 12 1997? tu 26,919v wx< 1998? 22,871vn yJK 1Jz/[CV{|}]. :~

(12)  M o ( €E yJK 1< L Bn‚

(13) (%

(14) & Wƒ 98? y+: 1,287„'[CV{|}])n l  † K  ‡ ˆ‰g- "Š= ‹is Œn 1}./. VOCs( K  ‡

(15)  Ž, O, ‘7 ’“, ”S•–, ’, —O#, ˜ ~ ™x- 1JKr š/. ›B ‡ œ= žŸ  N7 $ ¡W, *.  H7(¢6s, •–7, . VOCs(Volatile Organic Compounds) 

(16) ,   

(17) , VOC       (paraffin, olefind)  !"   , # $ %

(18) & '( )* +,(aldehyde, keton )- )*./[1]. VOCs0 12 34 567  8 $ 

(19) (9:;<= 1998-77>) 1998? 2@ 21! AB. 9:CD8 E FG2 $ HBF I

(20) 8BJK L/. 2 567 M dry cleaning, N,  † To. whom correspondence should be addressed. E-mail: [email protected] 694.

(21)    

(22)   . I7, ’“7 ), SW, £q, ¤W l <¥¦ 8D8( §E W +n -] ”¨s ‡l œBs/. w 0 ’“DM /© s l ™x%  L< Kª gNW «¬ ~%  L P ­M )®¯°l -< LK ¦±²³ media(‘7, silica )( n , +l ´µ< ¯°l Z-=¶  L/[3]. ·¸ A6. ’“ ‡M ™x¹ VOC ¡W- 20 ppm;º ·”¢6s(LEL) 1/4 ¡ W» ™x%  LW¼ 6¹½ P n n

(23)  ™x- K¾< + :~n/. VOC ¡W- ’“=f ™xksœl ˆ¿ :À  =fnÁ ÂÃx † •–=fl 1 Œn :~!  L/. w±Á ’“=fM  Ä- -ÅP 41n -Å Á Æ+Ç VOC Ä= ™x+l kÈÉ Ê!  L/ Ë ]Ìn L /. †s ’“=f VOC( ¡–=m Í =f  Á ÂÃx † •–=fl n¦ :~

(24) Ä% W L/[4].  ›B £qÎ9’“›B(Pressure Swing Adsorption Process) $ ŽÎ9’“›B(Thermal Swing Adsorption Process)l n 1< L/. ŽÎ9a ’-ϓ›BM ’“, ϓ wx< 4˜¿B

(25) g7J K L P n( ns ¦± - 567 l ’“Ä Fs M ‰g- ÐJK š/[5-11]. Nelson [12]n 1976? respirator cartridge ¯°7 FI ‰g s nÍ

(26) ‘7 ’“›B ‘7 s VOC ’“=, ›0  Ãn VOC ’“›B ÑÒ Ó Cs ‰g( н/ [13-20]. w±Á ’“¿Bn ÔÕ /Ö Z

(27) ‘7l 4˜=¶ : À ×N- 

(28) ’“Øl ×N=m ÍW ‘7u ÃM ÙÚ ¬ JÛ n±s ÙÚ Ã Ó FI Biron¿ Evans[21] ‘7u ÙÚ ÿ ›ÜÝ0 ¤W s Z  7 ¯¿( ‰g½/. n ‰g 7Z 7Þn( e ¦ ‘7ßE ’“3kl à fcIá< L P, Delage [20] M ‘7u 9.8%(w/w) ÙÚÿ 0-60% ›0 kF¤W 1 n VOC ’“ Fs Ól ‰g½ Á âãM ‘6É ‰gÐJ< L ä/. n±s åæn Ú4 ›B A6l çI ’“Ãx›B è1 f( çI ‹is ’“ é $ œW( › êë [22] ’“ 쒓 1n ’“í² $ îH7 Fs ‰gœïJKð s/. ñ ‰g 7²‘7 Fs 12 ’“í² Ûnº( òK n( hF

(29) 12 ’“îH7l ‰g½/. ‘7u ÙÚ Ã*é óô 12 ’“í², ’“W, ’“õ¿ öœ å, ÙÚà óô ’“é å, ϓJK ÁG Ãé  å l <¥¦  ‘7 ’“›B ~ %  L ˆ |}( ò<| ½/. 2..  . 2-1.  . ~ è÷

(30) ø <Bù î~ú S’“õ¿¿BM , k¿ ‘71n ¹û, ’“í²C, :N׿ ˆ< L ‚

(31) nü CÌ ’“í²¿ ›B îq ©k èý fcJ Kð s/. ¦ 1. è÷M Langmuir, Freundlich, Sips Sal 1þ P ¹ûM LDF è÷ I ß3½/. ‘7

(32) ÿ. <Bù 12 ’“ Fs î~è÷ l VÀ çI /Ö¿ M 1l -B½/. (1) = M S¿BnP, ’“ g²n/. (2) ’“ u V›gN ,!s Ã)

(33) nKr L/. (3) ": £qgž, ¡Wgž $ M =%  L P, ’ “ SœM Langmuir è÷a

(34) Á  L/.. (4). L/.. 695. ƒ x~ 7æM !BP, – # ±w î

(35) . (5) ¹û ”M ’“ u #”¿ o; ƒk¿ ’“  ßE1n  ¹û ”

(36) g7JK L/. (6) ’“W y|u #n ° nP, ó V›u  Ì t; í²n 7

(37) ./. (7) ¹ûW LDFA model

(38) ß3%  L/. (8) ’“Ø u ƒ M !B/. (9) ’“Ø u £q  =%  L/. ç -B –Ã#l <¥s <Bù !;ÃFs  aM /Ö¿ /. ∂ Ci ∂Ci ∂C i 1 – εb ∂qi – DL ---------+ v -------- + -------- + ------------ ρ p ------- = 0 2 ∂Z ∂t ∂t εb ∂Z. (1). C i ( z, t = 0 ) = 0. (2). 2. ∂C D L --------i = –v ( C i – Ci ) Z=0 Z=0 ∂Z Z = 0. (3). ∂Ci =0 -------∂Z Z = L. (4). –. +. a (3)¿ (4) Wehner and Wilhelm(1956)- s Ã#. plug flow  Fs  U :N×n/. 2-2.

(39)   . !"~

(40) /›7 ’“ Fs ’“W V›u nî I ž( /. , ‘7- ÿÃÉ < n ’“ site( n%  L/E, u; V›l ó ’“. n nî%  L/[23]. y|u; ¹ûl fc çI ñ ‰g LDF è ÷l 1½/. LDF è÷M y|u; ’“¡W Ã)( parabolic $ quadratic ²

(41) -BE /Ö¿ /. 3kf ∂-----q- ----------( C – C s ) = ks ( q s – q ) = ∂t R p ρp. (5). ¦ k  ßE#

(42)  Ûnº è1Ò( +*

(43) ø w Æn ïB./. 2-3.    <Bù’“ Fs :¹û /Ö al 1¦ ïBþ /[24]. s. Dm - ( 2.0 + 1.1Re 0.6 Sc0.33 ) k f = -------2R p. (6). Micoro pore”M =J<, LDF ¹û  biporous g² ’ “ Fs ¹û”¿ CJP /Ö¿ /. 2 q*ρ Rp 1 R q*ρ ---- = ------p- ⋅ -----------p- + ---------------- ⋅ -----------pks 3kf Co 15τp De Co. (7).  /Ö Ca

(44) ;º g%  L/[25].. Kunudsen diffusivity T D k = 9700r po ----M. (8). ¯#(D ) Ã|#(D ), Kundsen diffusivity(D ), $ ß E#(D ) CJP /Ö¿ /[26]. e. m. k. s. HWAHAK KONGHAK Vol. 40, No. 6, December, 2002.

(45)  !". 696. τ 1 1 ------ = ------p- + -----------------------------------------------D e D m D K 1 – εp  q*ρp Ds ------- + ------------ ------------ -----εp  C o  τs τp. (9). Surface diffusivity(D ) pore tortuosity(τ )¿ surface tortuosity(τ )/< -B‚

(46) ø a (9)

(47) ;º g%  L/[27]. ¦ 1. tortuosity ÆM 4( 1½/. –Ã#(D ) /Ö a

(48) ;º g½/[28]. s. p. s. L. DL 1- -------------= P e 2vR p. (10). r1 ε 1 1 ----- = ------------ + ----------------------------------P e ReSc βr 1ε  Pe∞  1 + ----------- ReSc. (11). ¦ r1=0.73, β=13, Pe=2.0, Pe=Peclet number. 3..  .    ’“ ’“

(49)  Norit(B4)1 pellet type 7² ‘7l 1½/. ’“ 1 ¹ ›×N 24= î 393.15 K SW

(50) ×N=m /Ö Ã Ól <¥¦ xn  Û= nº YC¦ 1½/. V›~, V› $ +ßE~ BM  ’“Dl n¦ g½ P, BJ Á ›. ‘7 Norit (B4) x~ú H7l Table 1 Áuz/. 3-1-2. ’“ ’“

(51) 1. 12 99.5%, Showa(Japan)l ¹™x n 1½ P 12 x~ 7M Table 2 Áuz/. 298.15 K, 308.15 K, 318.15 K ’“ )Z£(Ps)¿ ) 3-1. 3-1-1.. Table 1. Physical properties of activated carbon used Physical properties Supplier Equivalent diameter(cm) Pellet length(cm) BET surface area(m2/g)* Pore distribution** Micropore distribution(<1 nm) Transition pores(1-100 nm) Macropores(>100 nm) Porosity. ¡W(Cs) Antoine a[29]l nI g½ P ¦ n. ’“  ;ì(Vs) Rackett a[30]

(52) g½/. ›ÜÝ

(53)  air (99.9%)( 1½/. 3-2.  3-2-1. ’“í² ÙÚÃn  :À Cahn electronic balance- fÒ. 0éa ’“  ]Ò

(54) ’“í²l н P n  ]Ò g7W Fig. 1 Áuz/. ñ ]Ò  î Sl  ç I S u fÒJK L/. Cahn electronic balance o è! ] Ò Pyrex x

(55) "Jz P #$ ;al Â ç¦ ˆ|Ý( 1½/. Pellet type ‘7 ~Èél B¦ Cahn electro balance ]“n JK L pan ç Ãî¿ *% &M Í › 'Q

(56) Ͻ/. = } ¬- !BI  Í, SN( n¦ ' SW (298.15 K, 308.15 K, 318.15 K)( E /= ÿÃs =î( 5= nk) Ͻ/. Ï- ÔÕ Í valve 4( (w< valve 1l Ž K =})

(57) ;º 12 =}( Z6=* ]Ò u y JW ¼ ½/. £qn ' Æ WûE valve 4( +< ’“é å ( B½/. ÙÚà Fs ’“í²M column dynamic method

(58) l н/. 3-2-2. <Bù ’“ !7à <Bù ’“ ‘7u ÙÚ Ã Ó l B çs ]Ò Fig. 2 /. ]Ò è! CM ã:n 1/4"  ,úx  Cl 1½ P ’“Ø ã:M 1/2" n< # $ C ;æM Swagelock Co. l 1½/. Pressure bottle l !Bs SW

(59)  ç¦ Î9a SN( n½ P 50 bar( -.  L H 4

(60) /0n . ( 1½/. Z6 u 6 mm xg1l ÿ¹=* )¯°l ZF=2/. Steel tube u ƒ •–l  çI SN SWY/ ­¬ %  LW ¼ heating band( 1½/. ’“›B0 ’“ columnu; thermo couplel fÒ¦ SW å( B½/. †s ¹

(61) ( fÒ¦ column o; SW( 25 C

(62) =*áz/. ‘7 ÙÚÃM Z Ý( Z¦ ‘7 ’“=* mass balance( e¦ g½ /. bÎn  . 34s › ýA flow meter

(63) 5±-Û, o. Activated carbon pellet Norit(B4) 0.326 0.670 826 45.16% 9.68% 45.16% 0.68. *from manufacturer **from nitrogen adsorption at 77 K Table 2. Physical properties of solvent used Items Manufactured Molecular weight Purity grade[%] Boiling point temp.[K]* Critical point pressure [atm]* Vapor pressure[mmHg]**. CCl4 Showa(Japan) 153.82 99.5 349.85 45.0 114.38. *Properties are obtained from data book **Vapor pressures were calculated from Antoine equation at 298.15 K.  40 6 2002 12. Fig. 1. Schematic diagram of the vapor sorption apparatus. 1. Constant temperature bath 5. Cahn electro balance 2. Gas storage vessel 6. Data analysis computer 3. Liquid vessel 7. Vacuum pump 4. Manometer 8. Constant unit.

(64)    

(65)   . Fig. 2. Flow diagram of adsorption system. 1. Air compressor 2. Silica gel 3. Constant temperature bath 4. Water bath. 5. Pressure bottle 6. Flow meter 7. Thermocouple Thermometer 8. Humidity set. Á 12- æKL Z6

(66) YuK 12 6. /. /ô Á 12 7ú ›Ý( !B¡W, !B

(67) !/. ý - kM chamber

(68) æK- 8J<, ‘7n ÿJ K L ’“Ø

(69) YuK /. ’“ columnl e¿s 12  Silica DC-120n ÿ. Ãx 9:¿ b;nS <Ÿ(FID)- = [K - 

(70) >hw?ì(GC-14B, Shimadzu, Japan)

(71) Ã ½ P N"N×l Table 3 Áuz/. 12 ¡W Z6 SWå

(72) N´½/. †s, ›ÜÝ0 ¤W bÎl    çI Silca gel ÿØl ›Bˆ Wy¦ ¤W $ bÎ

(73) ú Table 3. Operating conditions of gas chromatography Items. Contents. Packing material Column length Carrier gas Carrier gas flow rate Column temperature Injector temperature Detector temperature Detector type. Silica DC-120 5m He 50 ml/min 150 oC 180 oC 180 oC FID. 697. 9. Digital controller 10. Furnace 11. Chamber 12. Adsorption column. 13. P. C. 14. G. C. 15. Thermometer. s ï¿ errorÆl ·½/. Table 4 N×l Áu z/. 4.. 

(74). 4-1.  SWå9 ›Bl è1 çI SW óô ’“í²é å ( @âð s/. ñ ‰g 298.15 K, 308.15 K, 318.15 K ’“ í²l н P w ï¿( Fig. 3 Áuz/. ’“í² Ûnº( ¦± - í² è÷a

(75) è1I ñ ï¿ Langmuir isotherm n 12 í²l à è1I Al @  Lz/. wB YC n SW- Z-* ó ’“én µ½< †s  SW 12 ¡W Z- óô ’“é Z-°n í²¡W- 2 mol/m nk D¬ kE*l @  Lz/. ‘7 ’“ Fs 12  ’“ SœM Brunauer ÃÝ[31] óô F²n< ’“éM £qn Z- Á SW- Gl¼ Z- !"~ú ’“H7l Á u< LÖl @  Lz/. SW óô Langmuir, Freundlich wx< Sips Sa parameter( #¦ Table 5 Áuz/. Fig. 4 298.15 K <Bù õ¿

(76) ;º òM ï¿

(77) ø ‘7 ÙÚà ó ô ’“ í²é Æ¿ Langmuir a

(78) è1s Æl ÁH Œn/. 3. Table 4. Experimental conditions for fixed bed adsorption Bed length(m). 0.2. Velocity(m/sec). Conc.(mol/m3). Water contents %(w/w). Bath temp.(K). Experimental temp.(K). 0.48. 0.120 0.335 0.058 0.166. 0, 5, 10, 20. 298.15-308.15. 298.15. 1.01. Bed porosity(εb): 0.448 Packing density(ρp): 370.88 kg/m3 HWAHAK KONGHAK Vol. 40, No. 6, December, 2002.

(79)  !". 698. Fig. 4. Adsorption equilibrium data and Langmuir equation of CCl4 at different residual water contents of activated carbon(298.15 K). Table 6. Langmiur parameters for adsorption equilibrium isotherms with respect to residual water of activated carbon Residual water contents of activated carbon(w/w) Isotherm Parameters type 5% 10% 20% Langmuir. qm b Error(%). 4.44 16.13 13.75. 14.26 13.77 14.26. 3.41 15.561 7.01.  #. parameterÆl Table 6 Áuz/. data

(80) ;º @  LCn ‘7 u ÙÚà ©n Z-%¼ ’“éM µ : l Y½/. ErrorÆM í²an I ’“é¿ Ò ´FGÞ( Ò

(81) ÁJ í,kFGÞ

(82) Áuz/. w aM /Ö¿ /. qj. ( exp t ) – q j.( pred) 100 Average Relative Deviation(ARD)= --------- ∑ ------------------------------------------------(13) Nd j = 0 qj. ( exp t ) Nd. Fig. 3. Adsorption equilibrium data and Langmuir, Freundlich, Sips equation of CCl4 at different temperatures.. Table 5. Parameters for adsorption equilibrium isotherms Isotherm type. Parameters. Langmuir. qm b Error(%) k n Error(%) qm b n Error(%). Freundlich. Sips. Temperature 318.15 K. 308.15 K. 298.15 K. 3.58 20.48 4.58 3.22 9.88 5.86 3.58 27.76 0.94 3.66. 4.00 23.26 4.06 3.62 12.11 3.93 4.01 25.19 1.09 1.53. 4.82 22.92 2.31 4.32 10.75 3.93 4.82 25.14 1.05 3.56. 4-2.   kK~

(83) nJ< L ’“ Ãx FA <Bù ]Ò( n< L/. nŒM ÃxJKð % ¿ ’“ LW Þn  ¦ +~ ÜMs õ¿öœl òl  L êën/. <Bù u ’ “ îl <N çI  7Ãæ õ¿öœl ~

(84) g*M O è1~ú ‰gW ‹i¬ JÛ, nŒM ’“  c $ 4˜= ïB ’“]Ò f 0is |}- J êë n/. ’“ õ¿öœM ’“í², nî $ ]Òu ƒP ~ H7 ó å¬ JÛ !"~

(85) ’“ù Qn- Q Á n OÀ RS :À ’“í²n õ¿öœl ž Œ

(86) @ ¥r L<, ’“ù u n Tô :À nî Ón kF ~

(87) ¬ ÁÕ/. ó ’“ Ãx( çs õ¿öœl è1 :À ’“í²C $ nî 3kl *% <¥ Œn UVã /[32, 33]. Fig. 5 6M î!s  CCl  ¡W( ûx¦ s ï¿ 4.  40 6 2002 12.

(88)    

(89)   . Fig. 5. Effect of initial concentration of CCl4 on behavior of adsorption breakthrough curves(298.15 K, vo: 0.48 m/s, Dry carbon).. Fig. 6. Effect of initial concentration on behavior of adsorption breakthrough curves of CCl4(298.15 K, vo: 1.01 m/s, Dry carbon).. n/. wB YCn õ¿öœ ²³ yg¡W Ón Ë Œ

(90) ÁW P,  Ûnº LDF nO

(91) è1s ï¿ à !Ò* l @  Lz/. Fig. 7M ›Ø W- 0.48 m/s! ê ‘7 Fs ÙÚÃé Ó l <N çI 0.12 mol/m ¡W l Ðs ï¿

(92) , ‘ 7 ÙÚ Ãén Z-%¼ õ¿- Xx !KÁ Œl.  Lz/. Fig. 8W  LCn, n±s :M ›ØW- 1.01 m/s

(93) YZ ­l êW Á[l @  L/. n ‘7 ’“ site à n ’“JK 12 ’“él Ên Œ

(94) \ JP Ã| (: 3], 12: 6])( +I ê, ’“ ÑV V› ’“ JKL Ãn ϓJ ^¦ kF~

(95) 12 ’“ › 3. 699. Fig. 7. Effect of water content in activated carbon on behavior of adsorption breakthrough curves of CCl4(298.15 K, vo: 0.48 m/s, Co: 0.120 mol/m3).. Fig. 8. Effect of water content in activated carbon on behavior of adsorption breakthrough curves of CCl4(298.15 K, vo: 1.01 m/s, Co: 0.058 mol/m3). l Ên ᅪ<  L/. †s 12 Ã|-  Ã|Y/ ’“ ßE Fs Lqn  êë 12 Ã|  Ã| 1n :_’“l e¦  Ã|( ϓ =` Œ

(96) 1}./. † s Fig. 9 ÙÚÃ*én 5%(w/w)!ê à ϓ öœ¿ 12  õ¿öœl î= ÁH wBnP, 10%(w/w) 20%(w/w)! ê W 5%(w/w) 1s ï¿( Y¦áz/. Fig. 7¿ Fig. 10  LCn ‘7 à *én Z-%¼ à ϓ =n Q K< à *én 5%(w/w) 10%(w/w) "•ˆ Ã Ï “n ÜMÉ JE 12 ’“n Ta¬ ÐJz/. "E HWAHAK KONGHAK Vol. 40, No. 6, December, 2002.

(97) 700.  !". Fig. 9. Comparison of adsorption characteristics of CCl4 and desorption characteristics of water from 5%(w/w) water contented activated carbon(298.15 K, vo: 0.48 m/s, Co: 0.120 mol/m3).. Fig. 11. Effect of residual water in activated carbon on 1% breakthrough time for different CCl4 concentration(298.15 K, vo: 1.01 m/s).. Fig. 10. Water desorption characteristics from pre-humidified activated carbons(298.15 K, vo: 0.48 m/s, Co: 0.120 mol/m3)..  à ϓn âã ÐJ ¿B ’“n bïJ  Œ

(98) Y⠒“n  >xJ Ì 12  8ƒ- Ú4¦ ¡W õ¿ öœ tailing ¦*l @  Lz /. Fig. 11M ‘7 ÙÚÃé óô 1% õ¿= å( Á H wBn/. î!s  ÙÚÃén Z-%¼ õ¿=n ! c Wû½ P, î!s N× 12 ¡W- Gl¼ ‘7  ÙÚà Z- óô õ¿= d- ÜMÉ µ½/. Fig. 12 ÁÕ Œ¿ n ÙÚÃén Z-%¼ 12 )’ “éM ÊKŠ :l Y½/. w±Á kF~

(99) ’“ ¡W­l ê Jonas [14] ‰g n Ã*én õ¿=nÁ ’“é Ë Ól ÑÒ ä Œ

(100) 1}./. 20%(w/w).  40 6 2002 12. Fig. 12. Effect of residual water in activated carbon on adsorption capacities(298.15 K, vo: 1.01 m/s).. 4-3. !"# $! %& <Bù ’“Ø 12 !7à õ¿öœ BM ›Ø W- 0.48 $ 1.01 m/s ! ê 12 yg¡W( å=`E õ ¿öœl B<, a (6)¿ a (10)

(101) gs : ¹û (k ), – Ã#(D )( Table 7 Áuz/. è÷ simulation

(102) g s y|u ¹û(LDF k, k ) ßE#(D ) Æ eç ( Table 8 Áuz/. y|u ¹û 10 -10 s eç Lz P n( Fig. 13 W=I ñ ï¿ ‘7 ÙÚÃén Z f. L. s. −3. s −4. −1.

(103)    

(104)   . 701. Table 7. Adsorption dynamic constants for fixed-bed model simulation Superficial velocity(m/s). kf ×10(m/s). DL×103(m2/s). 0.48 1.01. 1.02 1.59. 0.76 1.69. Table 8. Values of mass transfer coefficients and surface diffusivities obtained by fixed-bed model simulation with respect to residual water contents of activated carbon at different superficial velocities Superficial velocity(m/s). ks×103(s−1). Ds×1010(m2/s). 0.48 1.01. 0.80-1.30 0.90-1.70. 3.16-10.00 1.74-5.660. Fig. 14. Effect of residual water in activated carbon on surface diffusivities (298.15 K, vo: 0.48 m/s)..  ñ ‰g ‡f4 ‰g+(KRF-YOO-316) I ÐJz P n µ1Š

(105) g/..  Fig. 13. Effect of residual water in activated carbon on mass transfer coefficients(298.15 K, vo: 0.48 m/s).. -%¼ k Æn Z- :l Y½/. Fig. 14 D ( W=s Œ

(106) D ÆM 10 -10 m /seç Lz P ÙÚÃén Z-E % ¼ D Æn Z- :l Y½/. s. s. −8. −10. s. 2. s. 5..  . ‘7 12 ’“í²M Langmuir isotherm

(107) à è1 %  Lz P, SW- Z-* ó )’“én µ <,  SW 12 ãZ- ó ’“én Z- ½/. (2) ›ØW yg¡W- !B% ê ‘7 s 12 ’ “éM <¡WY/ ”¡W ‘7u ÙÚÃén Z-%¼ µ½/. (3) Ãn Ñx ’“. ‘7 :À Ã|æM = FI  ~

(108) ϓJz P, à *én Z-%¼ 12 õ¿= M X< ’“éM µ½/. (4) y| u ¹û ßE# ÙÚÃén Z-% ¼ œ²~

(109) Z- :l Y½/. (5) Ãn Ñx ’“. ‘7 ’“›B 12 < Bù ’“ îM LDF model

(110) fc%  Lz/. (1). b C Co Cs Ce d De. : adsorption parameter : concentration in the fluid phase [mol/m3] : initial concentration of bulk fluid [mol/m3] : saturation concentration of the sorbate in the liquid phase [mol/m3] : equilibrium concentration [mol/m3] : column diameter [m] : effective diffusivity [m2/sec]. Dk DL Dm Ds L k kf ks M q q* qm. : knuden diffusivity [m2/sec] : axial dispersion coefficient [m2/sec] : molecular diffusion coefficient [m2/sec] : effective surface diffusion coefficient [m2/sec] : distance through bed [m] : adsorption parameter : film mass transfer coefficient [m/sec] : solid mass transfer coefficient [s−1] : weight of sorbent particle [kg/mol] : equilibrium amount adsorbed on the adsorbent [mol/kg] : moles of adsorbate adsorbed per unit mass of adsorbent [mol/kg] : maximum adsorption capacity of adsorbent [mol/kg]. qs r rpo Rp T t. : concnetration adsorbed on the surface of adsorbent [mol/kg] : radial distance [m] : mean pore radius [m] : particle radius [m] : temperature [K] : time [sec, hr] HWAHAK KONGHAK Vol. 40, No. 6, December, 2002.

(111)  !". 702. tb v. : time at break point [sec] : interstitial velocity [m/sec]. vo V W Z. : superficial velocity [m/sec] : volume of solution [m3] : weight of sorbents [kg] : axial distance [m]. '()* +. ε εb εp ρb ρf ρp. : void fraction : bed porosity : particle porosity : bed density [kg/m3] : fluid density [kg/m3] : particle density [kg/m3]. τs,p. : tortuosity, surface, pore. , Pe Re Sc. : peclet number : reynolds number : schmidt number.   1. Mukhopadhyay, N. and Moreti, E. C.: “Current & Potential Future Industrial Practices for Reducing and Controlling Volatile Organic Compounds,” American Institute of Chemical Engineers, New York(1993). 2. Susan Budavari.: “The Merck Index,” 11th, Merck & Co. Inc., New Jersey(1989). 3. Rudy, E. N. and Carroll, L. A.: Chem. Eng. Progress., 89, 28(1994). 4. Hwang, K. S., Choi, D. K. and Kong, S. Y.: HWAHAK KONGHAK, 36, 159(1998). 5. Parmele, C. S., O’Connell, W. L. and Basdekis, H. S.: Chem. Eng., 86, 58(1979). 6. Barnebey, H. L.: Chem. Eng. Prog., 67, 49(1971). 7. Lovett, W. D. and Cunniff, F. T.: Chem. Eng. Prog., 70, 43(1974). 8. Yang, R. T.: “Gas Separation by Adsorption Process,” Butterworths, Boston(1987)..  40 6 2002 12. 9. Ruthven, D. M.: “Principles of Adsorption and Adsorption Processes,” Wiley, New York(1984) 10. Cicerone, R. J., Stolarski, R. S. and Walters, S.: Science, 185, 1165 (1974). 11. Wolf, K., Yezdani, A. and Yates, P.: J. Air Wastedmanage Assoc., 41, 1055(1991). 12. Nelson, G. O., Correia, A. N. and Harder, C. A.: Am. Ind. Hyg. Assoc. J., 37, 280(1976). 13. Okazaki, M., Tamon, H. and Toei, R.: Japan. J. Chem. Eng., 11, 209 (1978). 14. Jonas, L. A., Sansone, E. B. and Farris, T. S.: Am. Ind. Hyg. Assoc. J., 46, 20(1985). 15. Werner, M. D.: Am. Ind. Hyg. Assoc. J., 46, 585(1985). 16. Spirey, J.: J. Env. Progress., 7, 31(1988). 17. Jang, B. H., Lee, S. S., Yeon, T. H. and Tie, T. E.: Korean J. Chem. Eng., 15, 516(1998). 18. Gong, R. and Keener, T. C.: J. Air Waste Mgmt. Assoc., 43, 864(1993). 19. Chou, M. S. and Chiou, J. H.: J. Env. Eng., 5, 437(1997). 20. Delage, F., Pre, P. and Cloirec, D. L.: J. Env. Eng., 12, 1160(1999). 21. Biron, E. and Evans. M. J. B.: Carbon, 36, 1191(1998). 22. Lee, C. H.: HWAHAK KONGHAK, 35, 69(1997). 23. McKay, G., Blair, H. S. and Hindon, A.: Indian J. Chem., 28A, 356 (1989). 24. Wakao, N. and Funazkri, T.: J. Chem. Eng. Sci., 33, 1375(1978). 25. Karger, J. and Ruthven, D. M.: “Diffusion in Zeolites and Other Microporous Solids,” Wiley, New York(1992). 26. Malek, A. and Faroog, S.: AlChE. J., 43, 761(1997). 27. Huang, C. C. and Fair, J. R.: AlChE. J., 34, 1861(1988). 28. Edwards, M. F. and Richardson, J. F.: J. Chem. Eng. Sci., 23, 109(1968). 29. Dean, J. A.: “Lange’s Handbook of Chemistry,” Mcgraw-Hill, New York (1999). 30. Rackett, H. G.: J. Chem. Eng. Data, 15, 514(1970). 31. McCabe, W. L., Smith, J. C. and Harriott., P.: “Unit operations of Chemical Engineering,” McGraw Hill, New York(1993). 32. Moon, H. and Lee, W. K.: J. Chem. Eng. Sci., 41, 1995(1986). 33. Moon, H. and Lee, W. K.: J. Chem. Eng. Sci., 43, 1269(1988)..

(112)

참조

관련 문서

v i 는 측정하려는 단자간 전압이고, Probe는 RC 병렬 회로이고 오실로스코프에서는 내부에 RC 병렬회로가 우선적

Currents in the Cheju Strait have the eastward barotrophic component of about 5cm/sec through the year and become stronger in summer by the addition

The value relevance of accounting information is measured by the earnings response coefficient(ERC) and the explanatory power(R 2 ) of

Second, the SAQ training program meaningfully affects isokinetic leg strength (60°/sec)of recreational futsal members, which means it is confirmed as an

An efficient algorithm for mining association rules in large databases. An effective hash-based algorithm for

 Kernel 1, which has an arithmetic intensity of 0.5 FLOPs/byte, is limited by memory bandwidth to no more than 8 GFLOPS/sec.  Kernel 2, which has an arithmetic intensity of

→ The dispersion coefficient in a real stream (1D model) should be obtained by neglecting the vertical profile entirely and applying Taylor's analysis to the

Effect of pain control and improve function of knee joint applied to osteoarthritis by carbon surface-heating... Diagram of