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Kinetics and Reaction Engineering Aspects of Syngas Production by the Heterogeneously Catalysed Reverse Water Gas Shift Reaction

Unde, Rajabhau Bajirao

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1 Kine ics and Reac ion Enginee ing Aspec s o Syngas P oduc ion by he He e ogeneously Ca alysed Re e se Wa e Gas Shi Reac ion 1 Von de Fakul ä ü Angewand e Na u wissenscha en de Uni e si ä Bay eu h zu E langung de Wü de eines Dok o -Ingenieu s (D .-Ing.) genehmig e Disse a ion 1 o geleg e on M.Tech. Unde Rajabhau Baji ao aus Undewadi (Indien) E s gu ach e : P o . D .-Ing. And eas Jess Zwei gu ach e : P o . D . e . na . Pe e Wasse scheid Tag de mündlichen P ü ung 11. June 2012 Leh s uhl ü Chemische Ve ah ens echnik Uni e si ä Bay eu h 2012 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Acknowledgemen s Fi s o all I would like o exp ess my since ely hank o P o . D . And eas Jess o gi ing me he oppo uni y o wo k in his g oup, o making my wish become ealis ic, o his excellen guidance and suppo , o he en husiasm in supe ision and i edless co ec ion o my disse a ion. His ad ice and insigh in o hings h oughou my doc o al p ojec ha e been in aluable. My hanks go o P o . D . Pe e Wasse scheid o ag eeing co- e e ee o my hesis, and also o P o . D . Ru h F ei ag and P o . D . Ral Moos o accep ing o be in my examina ion commi ee. I hank o D . Ch is oph Ke n o his suppo in he modelling, o p o iding aluable sugges ions, and o he co ec ion o my disse a ion and also o D . Wol gang Ko h o co ec ion o my disse a ion and help ul commen s as well as many use ul discussions. I also hanks o D . Leonid Da se ich o his ui ul discussions, M . Jö g Ge chau o much help o expe imen al se -up and he ope a ion o ins umen s, and o he help o sol ing compu e p oblems, M s. Bi gi B unne o he help and suppo du ing my esea ch wo k. I hank Sec e a y M s. Ri a Pannek o he adminis a i e assis ances. I hank my colleagues om Chai o Chemical Enginee ing Johannes Thiessen and Lisa Schilde o a good ime o sha ing he o ice wi h hem and o hei help, Flo ian Heym, Amadeus Rose, Anne Piegsa, S e an F i z, S ephan Aschaue , Philipp Kaise , Pe e F eme ey and Susanne F i schi o hei help, suppo and p o iding pleasan and iendly esea ch a mosphe e o e he yea s. I hank o all my iends and my coun y-ma es in Bay eu h o hei lo e, suppo s and encou agemen . I am o e e indeb ed o my pa en s, pa en s in law, amily membe s and iends o hei lo e, p aye s, suppo s and encou agemen . Finally, I hank o my lo ely wi e, Sudha, o he suppo , unde s anding, encou agemen and endless pa ience. 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 Pa s o his wo k we e al eady published: 1 1. A. Jess, P. Kaise , C. Ke n, R. B. Unde and C. on Olshausen, Conside a ions conce ning he Ene gy Demand and Ene gy Mix o Global Wel a e and S able Ecosys ems. Chemie Ingenieu Technik 83, 1777–1791 (2011). 2. R. B. Unde, C. Ke n and A. Jess, High empe a u e CO 2 hyd ogena ion o e Ni Ca alys . 8 h Eu opean Cong ess o Chemical Enginee ing, P ocessNe , Be lin, Sep embe 25–29 (2011). 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 i Table o Con en s Lis o symbols ....................................................................................................................... 1 1. 1 In oduc ion ................................................................................................................. 1 1 2. 1 Basic heo y and backg ound o he wo k ................................................................ 3 1 2.1 He e ogeneous ca alysis ............................................................................................... 3 1 Di usion p ocesses in he e ogeneous ca alysis ...................................................... 3 1 2.1.1 In luence o in e nal and ex e nal mass anspo on he e ogeneously ca alysed 2.1.2 eac ions ................................................................................................................. 5 1 Ca alys deac i a ion phenomena .......................................................................... 13 1 2.1.3 2.2 U iliza ion o CO 2 o p oduc ion o chemicals and uels .......................................... 16 1 2.3 Concep o p oduc ion o liquid uels om CO 2 ia e e se wa e gas shi (RWGS) and Fische T opsch syn hesis (FTS) ........................................................................ 20 1 2.4 The modynamics o CO 2 con e sion ( e e se wa e gas shi and me hana ion) ...... 27 1 2.5 Kine ics o e e se wa e gas shi eac ion and me hana ion .................................... 32 1 3. 1 Objec i e and scope o he wo k .............................................................................. 39 1 4. 1 Expe imen al me hod and da a analysis ................................................................. 41 1 4.1 Expe imen al se up ..................................................................................................... 41 1 4.2 Expe imen al p ocedu e ............................................................................................. 43 1 4.3 Ca alys cha ac e isa ion ............................................................................................ 45 1 4.4 E alua ion o he expe imen al da a ........................................................................... 47 1 CO 2 hyd ogena ion eac ion .................................................................................. 47 1 4.4.1 4.4.1.1 Con e sion o CO 2 and yield o CO and CH 4 .............................................. 47 1 4.4.1.2 De e mina ion o he in insic kine ic pa ame e s ........................................ 48 1 4.4.1.3 In e nal mass anspo calcula ions ............................................................. 49 1 4.4.1.4 Calcula ion o ex e nal mass anspo limi a ions ...................................... 51 1 CO hyd ogena ion (me hana ion) eac ion ............................................................ 52 1 4.4.2 4.4.2.1 Con e sion o CO and yield o CO 2 and CH 4 .............................................. 52 1 4.4.2.2 Kine ic analysis and mass anspo calcula ions ......................................... 52 1 Wa e gas shi (WGS) eac ion ............................................................................ 53 1 4.4.3 4.4.3.1 Con e sion o CO and yield o CO 2 and CH 4 .............................................. 53 1 4.4.3.2 Kine ic analysis and mass anspo calcula ions ......................................... 53 1 5. 1 Resul s and discussion ............................................................................................... 55 1 iii Dimensionless numbe s Nu Nussel numbe P P and l numbe 9A Reynolds numbe 3B Schmid numbe 3 C She wood numbe Abb e ia ions CCC ca bon cap u e and con e sion FTS Fische T opsch syn hesis HTE high empe a u e elec olysis o wa e MFC mass low con olle NTP no mal empe a u e and p essu e (20 °C and 1 a m) RWGS e e se wa e gas shi oe onnes o oil equi alen , 1 oe = 42 GJ TPR empe a u e p og ammed educ ion TPS echnical pho osyn hesis WGS wa e gas shi XRD x- ay di ac ion In oduc ion 1 1. In oduc ion Ca bon dioxide is he mos impo an g eenhouse gas being emi ed in o he a mosphe e om ossil uel combus ion and o he an h opogenic ac i i ies. Acco ding o he Na ional Oceanic and A mosphe ic Adminis a ion (NOAA), he CO 2 concen a ion in he a mosphe e was 392 ppm in Feb ua y 2011 [1] which is e y high compa ed o 379 ppm in 2005 and a om he na u al ange o he las 650,000 yea s [2]. The annual emissions o CO 2 ha e g own be ween 1970 and 2004 by abou 80% om 21 o 39 giga onnes [2]. The g owing concen a ion o ca bon dioxide in he a mosphe e inc eased he impac on he en i onmen such as global wa ming and o cing a clima e change. The main g eenhouse gases a e wa e apou (H 2 O), ca bon dioxide (CO 2 ), me hane (CH 4 ), ni ous oxide (N 2 O), hyd o luo oca bons (HFCs), pe luo oca bons (PFCs), and sulphu hexa luo ide (SF 6 ), bu CO 2 con ibu es abou 77% o he wo ld’s g eenhouse gas emissions (excluding wa e apou ) in o he a mosphe e in 2004 [2]. Al e na i e ene gy sou ces a e no only impo an wi h ega d o global wa ming bu also o main ain he ising cos o c ude oil. Bo h aspec s ha e mo i a ed esea che s o look o solu ions o educe he g eenhouse gas emission and/o i s u iliza ion. The mi iga ion o g eenhouse gas emissions is also an in e es ing challenge in explo ing new concep s and new oppo uni ies o ca alysis and indus ial chemis y. Recen ly a ious ca bon cap u e and s o age echnologies (CCS) a e de eloped o a signi ican educ ion o CO 2 emissions in o he a mosphe e [3]. These echnologies a e mainly sui able o cap u e CO 2 om la ge indus ial sou ces such as ossil uel i ed powe plan s. Bu only wi h hese e o s i is no possible o educe and con ol CO 2 emissions [4], and he a ailabili y o su icien s o age capaci y o cap u e ca bon dioxide is also s ill an open ques ion. Howe e , e y li le a en ion has been paid by indus y and academia in u iliza ion o CO 2 because o i s high he modynamic s abili y. Fo he educ ion o g eenhouse gas emission a ious s a egies ha e been sugges ed ha includes p omo ing ene gy end-use e iciency, suppo ing he use o enewable ene gy esou ces as well as sus ainable anspo a ion and was e managemen [5]. One e ec i e app oach o a oid CO 2 accumula ion in o he a mosphe e is he eco e y o ca bon dioxide om lue gases and i s ecycle by con e ing o use ul chemicals [6, 7]. The In oduc ion 2 con e sion o CO 2 o CO by ca aly ic hyd ogena ion has been ecognized as a e y p omising p ocess. In indus y, syn hesis gas con aining H 2 and CO can be used o p oduce me hanol as well as long chain hyd oca bons ia he Fische -T opsch syn hesis. The e o e, he e e se wa e gas shi (RWGS) eac ion (CO 2 + H 2 5 CO + H 2 O) is an impo an op ion o CO p oduc ion. The ans o ma ion o CO 2 and H 2 in o CO and H 2 O depends upon se e al ac o s such as ca alys selec ion, a io o CO 2 /H 2 , and eac ion empe a u e and p essu e. The e o e, he main ocus o his s udy was o selec a sui able ca alys and eac ion condi ions o CO 2 hyd ogena ion in a ixed bed eac o . The expe imen s we e designed such ha he RWGS eac ion could be examined in he o wa d and e e se di ec ion, i.e. he “no mal” wa e gas shi eac ion (CO + H 2 O 5 CO 2 + H 2 ) was also s udied. The consecu i e CO hyd ogena ion, i.e. me hana ion eac ion (CO + 3H 2 5 CH 4 + H 2 O) also had o be conside ed. In he e ogeneous ca alysis, anspo p ocesses (ex e nal bounda y laye di usion, po e di usion) may ha e an in luence on he e ec i e eac ion a e, and we e also s udied in his wo k in de ail. Basic heo y and backg ound o he wo k 3 2. Basic heo y and backg ound o he wo k In he ollowing, some basic aspec s o he e ogeneous ca alysis and phenomena o mass ans e in he e ogeneous ca alysis (gas-solid di usion in a ixed bed eac o ), deac i a ion phenomena o ca alys s a e b ie ly ou lined. Some CO 2 u iliza ion p ocesses including e e se wa e gas shi , and he he modynamics o CO 2 con e sion a e also discussed. 2.1 He e ogeneous ca alysis The s udy o he e ogeneous ca alysis da es back o he ea ly 1800s whe e Fa aday was one o he i s scien is s who pe o med he abili y o pla inum o acili a e oxida ion eac ions [8]. A e ha , he ield o he e ogeneous ca alysis has been g own con inuously and a ac ed se e al Nobel p izes ( o example, in 2007, Ge ha d E l, a Ge man physical chemis was awa ded he Nobel P ize in chemis y o his con ibu ion in he a ea o su ace science). The p oduc ion o low cos and high quali y aw ma e ials, p oduc ion o anspo a ion uels, and pollu ion con ol a e he majo a eas in which he e ogeneous ca alysis has shown a ema kable impac . I is well known ha he ca alys e iciency is di ec ly p opo ional o i s su ace a ea. Many o he he e ogeneous ca alys s used in oday’s indus y consis o one o mo e ca aly ically ac i e componen s deposi ed on he su ace o a suppo ma e ial ha ing a high su ace a ea, high po osi y, and a sui able he mal and mechanical s eng h. He e ogeneous eac ions occu in a sys em in which wo o mo e phases a e p esen (e.g. he solid ca alys and liquids o gases as eac an s) and he eac ions occu a he in e ace be ween hese phases. Di usion p ocesses in he e ogeneous ca alysis 2.1.1 The chemical eac ions o he e ogeneous ca alysis occu be ween he adso bed eac an s and he su ace o he solid ca alys pa icle. The di usion o eac an s o he ca alys su ace (mos ly o he inne su ace o po es) and he di usion o p oduc s om his su ace a e pu ely physical phenomena. In case o ca aly ic gas-solid eac ions, he a e o eac ion wi hin a po ous ca alys s ongly depends upon he accessibili y o eac an s o he ac i e si es dispe sed h oughou he po ous s uc u e o he ca alys (Fig. 2-1). Basic heo y and backg ound o he wo k 4 Fig. 2-1: Sequen ial s eps in ol ed in he e ogeneous ca aly ic gas phase eac ion. Conside a simple gaseous eac ion (A → B) occu ing inside a eac o con aining po ous ca alys pa icles. In o de o con e he eac an A in o p oduc B, he ollowing physical and chemical p ocesses a e impo an : 1. Di usion o eac an A om he bulk gas phase h ough he bounda y laye o s agnan gas ilm su ounding he ca alys pa icle o he ex e nal su ace o he ca alys ( ilm di usion). 2. Di usion o eac an A in o he po ous s uc u e o he ca alys pa icle o he poin whe e adso p ion/ eac ion akes place (po e o in apa icle di usion). 3. Adso p ion o eac an s on he inne su ace o he ca alys . 4. Su ace eac ion o adso bed eac an A o adso bed p oduc B a he ca alys su ace. 5. Deso p ion o p oduc B om he inne su ace o he ca alys in o he po es. 6. Di usion o o med p oduc s h ough he po ous ne wo k s uc u e o he ex e nal su ace o he ca alys (in apa icle di usion). Basic heo y and backg ound o he wo k 5 7. Di usion o p oduc B om he ex e nal su ace o he ca alys h ough he bounda y laye in o he bulk gas phase. As a esul o hese s eps, a concen a ion p o ile may exis in he ca alys pelle and ou side in he ilm laye . The s eps 3, 4, and 5 a e chemical p ocesses, which s ongly depend on empe a u e ypically wi h e ec i e ac i a ion ene gies o 20 o 200 kJ/mol. The s eps 1, 2, 6, and 7 a e di usional p ocesses o mass ans e wi h ela i e low empe a u e dependence compa ed o he chemical p ocesses. I hese s eps a e e y as , hen he e is no esis ance o mass ans e om he bulk phase o he ex e nal su ace a ea o he pa icles and o he ac i e si es inside he po e. So he concen a ion a he in e nal ca alys su ace is he same as ha o he bulk phase, and he mass ans e does no a ec he eac ion a e. Bu in case ha mass ans e is slow ela i e o he chemical eac ions, he e may be an in luence o con ol o he o e all eac ion a e by he mass ans e . The ne kine ics ob ained om all eac ion s eps (1 o 7) is hus called e ec i e kine ics o mac o-kine ics. In luence o in e nal and ex e nal mass anspo on he e ogeneously ca alysed 2.1.2 eac ions In he e ogeneous ca aly ic eac ions, he conside a ion o in e nal and ex e nal mass ans e limi a ions is e y impo an when expe imen s a e pe o med o de e mine in insic kine ic pa ame e s. Acco ding o A henius law, he in insic chemical a e is nea ly an exponen ial unc ion o empe a u e and he mass ans e a e is less s ongly in luenced by he empe a u e, e.g. o gas di usion he a e is p opo ional o abou T 1.5 . Fig. 2-2 shows an A henius plo o he empe a u e dependence o he e ec i e a e cons an o a ca aly ic eac ion o he h ee eac ion a e con olling egimes. Regime o in insic kine ic: A low empe a u es, he a e o he chemical eac ion is slow compa ed o mass anspo p ocesses. The e o e only a negligible concen a ion g adien will be es ablished in he ex e io and in e io o he ca alys pa icle. The eac ion empe a u e also emains cons an o e he en i e c oss-sec ion o he ca alys pelle and also in he bounda y laye . This is called as an in insic egion whe e he ue in insic kine ics o eac ions is measu ed. Fo his egion, he slope o he cu e ln k m s 1/T is p opo ional o he chemical ac i a ion Basic heo y and backg ound o he wo k 6 ene gy (E A ). The eac ion a e o gas-solid eac ions is o en desc ibed wi h accu acy by a powe law equa ion: D E F  4 5    F  E     1  (2.1) The eac ion a e usually depends upon he a e cons an (k m ) ela ed o he mass o ca alys (m ca ), concen a ion o eac an (   ), and he in insic o de o eac ion (n). The empe a u e dependence o he eac ion a e cons an is gi en by he A henius equa ion:  E F  E    A   !" 1  (2.2) In he A henius equa ion, k m,0 is he equency ac o and E A is he in insic ac i a ion ene gy o he chemical eac ion. Regime o po e di usion: A in e media e empe a u es, he chemical eac ion a e is as e han he inne mass anspo (po e di usion). Be ween his egime and he egime o in insic kine ic, a ansi ion egime is loca ed whe e he slope o he cu e changes wi h empe a u e. In he po e di usion egion, he concen a ion o eac an s a he po e mou h is much highe han ha inside he po e and d ops dis inc ly. He e he en i e ca aly ic su ace is no accessible o he same concen a ion. The e o e he e ec i e eac ion a e will be less as compa ed o he a e wi hou mass ans e limi a ions. Fo his egion, he e ec i e ac i a ion ene gy is oughly one hal o he ue ac i a ion ene gy (E A /2). In gene al, he e is no only he change in e ec i e ac i a ion ene gy bu he e ec i e o de o he eac ion also changes when he ansi ion om kine ic o di usion con ol occu s. Fo an n h o de eac ion, he e ec i e eac ion o de app oaches he alue o (n + 1)/2 in case o s ong limi a ion by po e di usion. Basic heo y and backg ound o he wo k 7 Fig. 2-2: Typical A henius plo o empe a u e dependence o he e ec i e a e cons an o ca aly ic eac ion; h ee egimes o eac ion a e con ol o low, in e media e and high eac ion empe a u e. Fo a i s o de eac ion he e ec i e a e o chemical eac ion is gi en as D E  #$$ F %   E     & 1  (2.3) whe e  & ' he concen a ion a he ca alys su ace and 6 is he e ec i eness ac o which is a unc ion o he Thiele modulus. The e ec i eness ac o 2 is de ined as he a io o he obse ed a e o eac ion o he a e in he absence o any di usional esis ance, i.e. % F (B)*(+  DA(B),-4  D()A ,4)D,4.,B  D()A  -/  B C A,B(+  DA(B),-4 F D E  #$$ D E 1  (2.4) The e a e se e al ac o s which in luences he e ec i eness ac o , such as po e shape and po e s uc u e (mic o-mac o), pa icle size dis ibu ion, and change in olume upon eac ion [9]. The magni ude o he e ec i eness ac o anges be ween 0 and 1 which indica e he ela i e impo ance o di usion and eac ion limi a ions [10]. The in e nal e ec i eness ac o a ies o di e en ca alys geome ies (see Fig. 2-3) and o di e en eac ion o de s (see Fig. 2-4). Basic heo y and backg ound o he wo k 8 Fig. 2-3: Rela ionship o he e ec i eness ac o e sus gene alized Thiele modulus (Eq. (2.7)) o di e en shapes o ca alys . Fig. 2-4: Rela ionship o he e ec i eness ac o e sus gene alized Thiele modulus (Eq. (2.8)) o simple-o de eac ions [11]. The e ec i eness ac o as a unc ion o he Thiele modulus o a la pla e and an iso he mal, i e e sible i s -o de eac ion is gi en as: 2324 234 4 2324 234 4 42 422 E ec i eness ac o [1] Thiele modulus [2] 567819678A B9CADA EF6AD Basic heo y and backg ound o he wo k 9 % F )(4 C 8 8 1  (2.5) Fo he sphe ical pa icle, an e ec i eness ac o is gi en as: % F 0 8 1 0 )(4 C 2 3 8 4 5 0 2 3 8 4 6 1  (2.6) The ela ion be ween Thiele modulus and e ec i eness ac o o a la pla e in Eq. (2.5) gi es he app oxima ion ha 2 equals 1/8 o la ge alues o he Thiele modulus (8 8 2). The equa ion o an e ec i eness ac o o a la pla e can be used in a good app oxima ion o any pa icle geome y wi h cha ac e is ic leng h (L p ), which is gi en by Eq. (2.9). The dimensionless Thiele modulus (8) plays a key ole in de e mining po e di usion limi a ions. Fo gene al shape, i s o de and i e e sible eac ion, he Thiele modulus is gi en as [9]: 8 F 7 8 9  E  : 8 ;   #$$ 1  (2.7) Fo a i e e sible eac ion and o de n 7 1, he Thiele modulus is gi en as: 8 F 7 8 9 1 4 < 0 = 6  E  : 8  > ?  @ ;   #$$ 1  (2.8) whe e 6 p is he densi y o pa icle, D i,e is he e ec i e di usi i y o species i, and L p is he cha ac e is ic leng h o a ious shapes which is gi en as: 7 8 F A-+*A  -/  . C (BA AC)AD4(+  (DA(  -/  . C (BA 1  (2.9) The cha ac e is ic leng h o cylinde s is L p = d p /4, o sphe es L p = d p /6 and o la pla e L p (whe e d p is he pa icle diame e and 2L p is he pla e hickness). The poin a which a pelle o op imal dimension shows he ansi ion om chemical o di usion con ol egion is p ac ically impo an . Small pa icles ha e a low cha ac e is ic leng h, which dec eases he alue o he Thiele modulus (see Eq. (2.7) and Eq. (2.8)) and hus inc ease he e ec i eness ac o , and lowe s he po e di usion esis ance. On he o he hand, a small pa icle size c ea es a high p essu e d op in a ixed bed eac o . The e o e om Basic heo y and backg ound o he wo k 16 Alloying: In alloying, a combina ion o wo o mo e me als akes place a high empe a u e (pa icula ly unde educ ion condi ions). Alloying may change he ac i i y and s abili y o ca alys . The Cu-Zn alloy o ma ion du ing he educ ion o he ca alys in he empe a u e ange o 230 o 500 °C wi h a mix u e o H 2 and N 2 deac i a es he ca alys and educes i s ac i i y o he wa e gas shi [27]. O he example a e o ma ion o RhAl 2 O 4 in P -Rh/Al 2 O 3 ca alys s in ca aly ic con e e s o educ ion o ca engine emissions, o ma ion o Ni 2 Al 2 O 4 du ing s eam e o ming o e Ni/Al 2 O 3 , and o ma ion o KAlO 2 in FTS. 2.2 U iliza ion o CO 2 o p oduc ion o chemicals and uels The ene gy ela ed CO 2 emissions ha e inc eased wi h an a e age annual g ow h a e o 1.9% om 1990 o 2007 and he emissions a e expec ed o ise wi h an annual a e o 1.3% un il 2035 [8]. The global CO 2 emissions om ossil uels combus ion inc ease om nea by ze o in 1870 o 29.7 billion me ic ons in 2007 and a e p ojec ed o inc ease up o 42 billion me ic ons in 2035 [8]. The analysis o wo ld ene gy- ela ed ca bon dioxide emissions by he consump ion o ossil uels (Fig. 2-6) shows ha coal is he la ges sou ce o ca bon dioxide (12.5 billion me ic ons), ollowed by liquid uels (11.3 billion me ic ons), and na u al gas (5.9 billion me ic ons). Fig. 2-6: The wo ld ene gy- ela ed ca bon dioxide emissions by uel ype [8]. Basic heo y and backg ound o he wo k 17 To a oid CO 2 emissions, a ious measu es such as eco e y, emo al, and s o age disposal ha e been p oposed. Ca bon cap u e and s o age needs la ge amoun s o ene gy o i s cap u e, anspo a ion, and seques a ion. The e o e he u iliza ion o CO 2 in chemical con e sion p ocesses may become an impo an op ion o sus ainable de elopmen , mi iga ion o ca bon emissions, and o a oid global wa ming. The a ious di ec and indi ec uses o CO 2 a e shown in Fig. 2-7. The po en ial o CO 2 in he di ec use is e y low compa ed o indi ec use. The indi ec u iliza ion o CO 2 has ad an ages such as p oduc ion o alue added chemicals, en i onmen iendly p ocessing, and non-haza ds p ocess u iliza ion o CO 2 . Fig. 2-7: Va ious di ec and indi ec pa hways o CO 2 u iliza ion (modi ied a e [5]). Un il oday, CO 2 is no used in i s ulles po en ial e en in he indi ec way o u iliza ion because o i s high he modynamic and kine ic s abili y. The use o e icien ca alys s and selec i e eac ion pa hways a e needed o p omo e he eac ion a e. Undoub edly, he chemical indus y can only make li le di ec con ibu ion owa ds he educ ion o o e all CO 2 emission. Acco ding o cu en es ima es, he chemical indus y could con ibu e o con e a ound 1% o global CO 2 emissions in o chemical p oduc s [3]. Table 2-2 shows he u iliza ion o CO 2 in a ious chemical con e sion p ocesses in 2006. Basic heo y and backg ound o he wo k 18 The ixa ion o CO 2 in o hese o ganic compounds e e s o eac ions ha use he en i e molecule. The de ail desc ip ion o he syn hesis o hese o ganic compounds using CO 2 is gi en in appendix A. All hese p ocesses use CO 2 o p oduce alue added p oduc s in an en i onmen ally iendly way whe e u iliza ion po en ial assis ed in e ms o less ene gy use and lowe was e p oduc ion. Table 2-2: Indus ial p ocess u iliza ion o CO 2 as a aw ma e ial o syn hesis o o ganic compounds [28]. Indus ial p ocesses ha u ilize CO 2 as aw ma e ial Wo ld capaci y pe yea [million onnes] Amoun o ixed CO 2 [million onnes] Chemical syn hesis: Salicylic acid 0.07 0.025 U ea 143 105 Cyclic ca bona es 0.080 0.04 Poly (p opylene ca bona e) 0.070 0.03 Fuel syn hesis: Me hanol 20 2 Syn he ic na u al gas - - O he uels - - Table 2-2 clea ly indica es ha he amoun o CO 2 u ilized oday o he p oduc ion o o ganic chemicals and uels (me hanol) is e y small (a ound 100 million onnes) compa ed o oday’s global CO 2 emissions o a ound 30 billion onnes. I should also be no ed ha only a ound 10% o he global c ude oil consump ion is used oday in he chemical indus y. The majo ly is used as liquid uels such as gasoline, diesel and hea y oil. Hence, an e ec i e use o CO 2 wi h ega d o a no iceable educ ion o he global ne emissions o CO 2 can only be eached, i he CO 2 (e.g. sepa a ed om lue gases o in he e y a u u e om ai ) is u ilized o uels, e.g. by e e se wa e gas shi and subsequen Fische T opsch syn hesis. Basic heo y and backg ound o he wo k 19 The e e se wa e gas shi eac ion echnology is a simple and e ec i e way o u ilize ca bon dioxide in many indus ies [29, 30]. This eac ion occu s a high empe a u es whe e CO 2 is con e ed wi h H 2 in o CO and wa e . i P   <   j P    k   i   <    j P i       1 ! j l Pmn  o  F  p0 [ =  q O -+ 1  (2.21) Se e al mos ly unwan ed pa allel and side eac ions may also ake place: The Saba ie eac ion: i P   <   p j P   k   j   <   = j P i       1 ! j l Pmn  o  F  5 0Y`  q O -+ 1  (2.22) The Bosch eac ion: i P   <   = j P   k       <    = j P i       1 ! j l Pmn  o  F  5 Z [ =  q O -+ 1  (2.23) Boudoua d eac ion: =s   k       <    i P       1 ! j l Pmn  o  F  5 0 = [ Y  q O -+ 1  (2.24) Me hana ion eac ion: s   <   3 j P   k    j   <    j P i       1 ! j l Pmn  o  F  5 =ZY  q O -+ 1  (2.25) The e e se wa e gas shi eac ion has been known o chemis y since he mid 1800's bu no expe imen al wo k was done o e eal i s iabili y [31]. Since he las wo decades, s udies ha e been ocused on ca aly ic con e sion o CO 2 o indus ially impo an chemicals such as ligh ole ins and liquid hyd oca bons. Depending on he eac ion ou e and ca alys used, i is di ided in o wo g oups. One is he hyd ogena ion o CO 2 o hyd oca bons ia me hanol syn hesis [32, 33] which combines wo eac ion s eps: me hanol syn hesis om CO 2 and subsequen con e sion o me hanol o gasoline by he MTG p ocess: i P   <   3 j P   k    j u ij   <    j P i       1 ! j l Pmn  o  F  5 p [ `  q O -+ 1  (2.26) = j u ij   k    j u i j u   <    j P i        (D-(),B. w [      (2.27) Al e na i ely, me hanol can also be used di ec ly a liquid uel, bu he in as uc u e is no ye es ablished. The second ou e o con e CO 2 in o liquid hyd oca bons is Fische T opsch syn hesis [34-36], which also combines wo s eps: hyd ogena ion o ca bon dioxide Basic heo y and backg ound o he wo k 20 by e e se wa e gas shi eac ion (Eq. (2.21)) and, hen, u he hyd ogena ion o CO o hyd oca bons: i  <  = j P   2 5 j P 5 4   <   j P i       1 ! j l Pmn  o  F  5 0`=  q O -+   (2.28) The e m (-CH 2 -) ep esen s a me hylene g oup o a pa a in. This ou e is discussed in some de ails in he subsequen chap e . 2.3 Concep o p oduc ion o liquid uels om CO 2 ia e e se wa e gas shi (RWGS) and Fische T opsch syn hesis (FTS) The concep o p oduc ion o liquid uels om CO 2 ia RWGS and FTS was ecen ly desc ibed and discussed [37], whe e some mo e de ails can be ound. He e only some main aspec s should be ou lined. Elec ici y p oduced by sola ene gy (o o he enewables) can be used o p oduce liquid uels like diesel oil wi h no o li le ne CO 2 p oduc ion by he ollowing s eps [38-42]: a) Sepa a ion o CO 2 om lue gases (o in he long un e en om he a mosphe e). b) H 2 p oduc ion by high empe a u e wa e (s eam) elec olysis and non- ossil elec ici y: 3 j P s       3 j P   <   0 [ ` i P       1 ! j l Pmn  o  F  3=  q O -+ 1  (2.29) c) CO p oduc ion by e e se wa e gas shi (Eq. (2.21)). d) Fische T opsch syn hesis o hyd oca bons (p e e ably o diesel oil) (Eq. (2.28)). In summa y we ge : i P   <   j P s      2 5 j P 5 4   <    0 [ ` i P       1 ! j l Pmn  o  F  p  q O -+ 1  (2.30) I we compa e Eq. (2.30) wi h na u al pho osyn hesis i P   <   j P s      0 Y  x j @P i x   <    i P     1  (2.31) we may ega d his p ocess as a echnical pho osyn hesis (TPS, Fig. 2-8). This ou e is also called ca bon cap u e and con e sion (CCC) [42]. Compa ed o he p oduc s o na u al pho osyn hesis (e.g. wood), hose o he echnical pho osyn hesis ha e a much highe ene gy densi y ela ed o mass ( ac o 3) and e en mo e ela ed o olume ( ac o 6). Basic heo y and backg ound o he wo k 21 Fig. 2-8: The simpli ied lowshee o a plan o p oduc ion o liquid uels om CO 2 by Fische T opsch syn hesis and sola ene gy. The echnical pho osyn hesis may also be help ul o ene gy s o age and anspo . Liquid uels ha e excellen s o age, loading and anspo capabili ies, and app op ia e la ge-scale s o age echnologies will be needed in u u e o he e icien use o enewable ene gies: (1) Many enewable ene gy sou ces (mos no ably sola and wind) a e subjec o na u al luc ua ions. These ha e o be compensa ed o by s o ing excess supply peaks, which inc eases he e iciency and economic alue o enewable ene gy, and keeps ins an aneous elec ical gene a ion and consump ion in a be e balance. (2) The economically mos p ac ical me hod o de eloping al e na i e ene gy sou ces is o make use o he ea h's sunbel and high-wind zones, bu hese egions a e mos ly a away om consume s. Hence, he e is a need o a sui able ca ie o ene gy in o de o anspo he ene gy om he sou ce o sui able ma ke s. One could also hink o using he hyd ogen gene a ed by elec olysis di ec ly o s o age and anspo o sola -elec ical ene gy. Bu he ene gy densi y o liquid hyd ogen is only 0.2 oe/m 3 (and e en only 0.1 oe/m 3 o comp essed H 2 a 700 ba and 25 °C) compa ed o diesel oil wi h 0.8 oe/m 3 ( oe: onnes o oil equi alen , 1 oe = 42 GJ). The lique ac ion and Basic heo y and backg ound o he wo k 22 anspo o H 2 is no easy: High sa e y equi emen s and a new in as uc u e a e needed, e.g. 20% o 30% o he ene gy con en is consumed o lique ac ion [43] and 8% o anspo as comp essed gas ia pipelines (pe 1000 km) [44]. Fo a p elimina y basic layou o a TPS plan o he p oduc ion o liquid uels om CO 2 by sola ene gy and Fische T opsch syn hesis (FTS) he ollowing assump ions we e made: Hyd ogen p oduc ion H 2 is gene a ed by high empe a u e solid oxide elec olysis (HTE) a 830 °C. Acco ding o S oo s e al. 124 MJ elec ical ene gy a e consumed pe kg H 2 (= 13.8 MJ pe kg con e ed H 2 O) [45]. I we use he ene gy eleased by he exo he mic Fische T opsch syn hesis o he p oduc ion o sa u a ed s eam (22 ba , 215 °C) (see below), he ene gy needed o o e hea he s eam (215 5 830 °C) is 1.4 MJ/kg. Hence in o al, 137 MJ elec ical ene gy is needed pe kg H 2 (= 15.2 MJ pe kg con e ed H 2 O). Desalina ion o seawa e I eshwa e is no a ailable, seawa e has o be desalina ed o p oduce he eed o he elec olysis. 7 kJ elec ical ene gy is su icien pe kg wa e , i e e se osmosis is used [46]. This equi emen is only 0.04 % o he ene gy o he subsequen elec olysis. Fo compa ison: 170 kJ/kg is needed, i mul i-s age lash dis illa ion is used [44], which is s ill only 0.9% compa ed o wha he elec olysis consumes. CO 2 p oduc ion CO 2 has o be sepa a ed om lue gases (o on he long un e en om ai ). The inescapable ene gy equi emen (in J/mol CO 2 ) o concen a ing CO 2 om a gas mix u e is gi en by he laws o he modynamics, as we ha e a leas o o e come he di e ence o he en opy o he mix u e and o he pu e compounds (see Fig. 2-9): y E F  L  z 3 F 5 { | } ~ 9  L  +4 U { | } ~ W 5 U 0 5 { | } ~ W  9  L  +4 U 0 5 { | } ~ W { | } ~  1  (2.32) Basic heo y and backg ound o he wo k 23 Fig. 2-9: Inescapable ene gy equi emen o concen a ing CO 2 om lue gases (11 ol.-% CO 2 ) and ai (300 ppm CO 2 ) a 25 °C (Eq. (2.32)). Fo sepa a ion o CO 2 om lue gases wi h ypically 11 ol-% CO 2 , he minimum ene gy equi emen is 7.8 kJ/mol (177 kJ/kg) and o ai 22.4 kJ/mol CO 2 (509 kJ/kg). In he ideal case, each mol o CO 2 is inally con e ed by FTS in o one mol o CH 2 -g oups (hyd oca - bons) wi h a hea ing alue o 595 kJ/mol = 42500 kJ/kg. Hence, he ene gy equi emen o CO 2 sepa a ion is 3.8% (ai ) and 1.3% ( lue gases) o he ene gy con en o he liquid uels p oduced by FTS. O cou se in eali y, much mo e ene gy is consumed a he cu en s a us o echnology. He e we use a alue o 1.2 MJ/kg CO 2 as gi en by Gö liche and P uschek [47] o CO 2 sepa a ion om lue gases by chemical abso p ion. This alue is 7 imes highe han he inescapable ene gy equi emen . Fo CO 2 sepa a ion om ai , a alue o 3.6 MJ/kg CO 2 (= 7 E min ) may be aken as a i s es ima ion. In he ideal case o a echnical pho osyn- hesis, 3 mol wa e a e con e ed by elec olysis pe mol o CO 2 (Eq. (2.21) and (2.29)), i.e. 1.23 kg H 2 O/kg CO 2 . Hence, o he con e sion o 1 kg o CO 2 24.5 MJ a e needed o elec olysis o wa e compa ed o 1.2 MJ o CO 2 sepa a ion om lue gases and 3.6 MJ om ai . Re e se wa e gas shi H 2 and CO 2 a e con e ed o H 2 O and CO by RWGS a a empe a u e o abou 800 °C. A he eac o ou le , he he modynamic equilib ium is eached as p o en by espec i e expe imen s wi h a Ni-ca alys (see sec ion 5.1). The eac o is hea ed (e.g. elec ically). I Basic heo y and backg ound o he wo k 24 hea losses a e neglec ed, he equi ed ene gy is 41 kJ/mol CO 2 (Eq. (2.21)) o 932 kJ/kg CO 2 . Fische T opsch syn hesis P oduc ion o syn he ic uels ia FTS has he po en ial o p oduce uels like gasoline and diesel oil as well as pe ochemicals om ossil and enewable sou ces. In ecen yea s, he a ailabili y o cheap na u al gas, coal, and biomass has gi en momen um o FT echnology. The wo ldwide FT plan capaci ies will inc ease in u u e, oday wi h na u al gas a ou ed as eeds ock. In 2015, he wo ldwide annual p oduc ion o liquid uels ia FT will be a ound 30 million onnes, mainly p oduced in coun ies like Sou h A ica, Malaysia, and Qa a . Beside o he main eac ion o he FT syn hesis (Eq. (2.28)), me hana ion (Eq. (2.25)) is o en conside ed as a sepa a e eac ion. The hi d eac ion ha plays an impo an ole (a leas i i on based ca alys s a e used) p oduces unwan ed CO 2 by he WGS eac ion:   i   <    j P i   k   i P   <   j P       1 ! j l Pmn  o  F  5 p0 [ =  q O -+ 1  (2.33) Two eac o ypes a e cu en ly a ou ed o FTS, he mul i- ubula ixed bed and he slu y bubble column. FT eac o s a e usually cooled by boiling wa e . Sa u a ed s eam is p oduced and may be used a e u he hea ing as eed o he HTE. A ypical FT cooling empe a u e is 215 °C [48]. The equi ed he mal ene gy is hen 2.7 MJ pe kg sa u a ed s eam = 48.6 kJ/mol. Hence, 3.1 mol o s eam can be gene a ed pe mol CO con e ed by FTS (1jl Pmno = - 152 kJ/mol CO), which is he amoun needed o elec olysis. Typical selec i i ies (in C-%) o he FTS wi h Fe-ca alys s (30% CO con e sion pe pass, i.e. ecycle o uncon e ed syngas has o be ins alled) a e: 18% CO 2 , 5% me hane, 11% C 2 o C 4 , 10% gasoline, 17% diesel and 39% waxes [48-50]. The waxes a e u he con e ed (mainly) o diesel oil by mild hyd oc acking a 70 ba and 350 °C [51]. All ligh hyd oca bons (me hane o C 4 ) and also he CO 2 o med by he wa e gas shi eac ion in he FTS (Eq. (2.33)) may be ecycled o he RWGS uni o be inally con e ed by s eam e o ming ( e e se o Eq. (2.25)) o by he RWGS (Eq. (2.21)) o CO and H 2 , espec i ely. In summa y we ge he ollowing mass balance: Fo each mol o esh CO 2 , we ha e o ecycle app oxima ely 0.18 mol CO 2 and 0.18 mol ca bon (as C 1 o C 4 ) in o he RWGS eac o . Hence, abou 2 imes mo e ene gy is needed o un he RWGS eac o Basic heo y and backg ound o he wo k 25 (1.18 x 41 kJ/mol CO 2 and 0.16 x 206 kJ/mol C as C 1 o C 4 compa ed o 41 kJ/mol wi hou ecycle). Based on he abo e lis ed assump ions and ac s, an es ima ion o he ene gy equi emen s o he p oduc ion o liquid uels om CO 2 by FTS and sola ene gy is possible (Table 2-3). The ene gy equi ed o he con e sion o CO 2 o CO is calcula ed by including he con e sion o ecycled CO 2 and C 1 o C 4 hyd oca bons (coun ed as CH 4 ), bo h unwan ed by- p oduc s o FTS, and RWGS and s eam e o ming ( e e se o Eq. (2.25)), espec i ely. Table 2-3: Es ima ion o ene gy equi emen s o he p oduc ion o liquid uels om CO 2 by FTS and sola ene gy (con e sion o 1 kg CO 2 o 0.32 kg liquid uels). P ocess/ene gy ou pu Ene gy [kJ] Commen /assump ion Sepa a ion o 1 kg CO 2 om lue gas (ai ) 1200 (3600) Value om [47],which is 7 imes he he modynamic minimum (Fig. 2-9) Con e sion o CO 2 o CO (RWGS) 2144 Only coun ing en halpy o eac ion Desalina ion o 1.23 kg seawa e 9 Re e se osmosis plan HT-elec olysis o 1.23 kg wa e 18700 13.8 MJ/kg H 2 O elec ical ene gy o elec olysis [45] and 1.4 MJ/kg o o e hea sa u a ed s eam gene a ed in he FTS (215 5 830 °C) FT syn hesis - Hea o eac ion is used o gene a e sa u a ed s eam (215 °C, 22 ba ) To al equi ed ene gy 21773 (24173) P oduc ion o 0.32 kg liquid uels 13600 Hea ing alue o uel = 42500 kJ/kg P ocess e iciency 62% (= 13600/21773) CO 2 om lue gases 56% (= 13600/24173) CO 2 om ai Basic heo y and backg ound o he wo k 32 he p oduc ion o uels ia Fische T opsch syn hesis. Exempla ily, he equilib ium composi ion o syngas is shown in Fig. 2-16. Fo empe a u e abo e 750 °C, a mosphe ic p essu e, and H 2 /CO 2 inle a io o 2, he CO 2 hyd ogena ion can gi e he equi ed a io o syngas o he p oduc ion o uel. Fo example, a 800 °C and a mosphe ic p essu e, he equilib ium composi ion a he eac o ou le is 57% CO, 28% H 2 , and 15 ol.-% CO 2 . Hence, he CO/H 2 a io is abou 2. Fig. 2-16: Equilib ium composi ion o syngas a e emo al o wa e o e empe a u e in CO 2 hyd ogena ion eac ion wi h me hana ion (p = 1 a m, H 2 /CO 2 = 2). 2.5 Kine ics o e e se wa e gas shi eac ion and me hana ion Two gene al mechanisms ha e been p oposed o me hana ion o CO 2 o e Ni con aining ca alys s [33, 57-59]. In he i s mechanism o me hane o ma ion, ini ially CO 2 unde goes apid dissocia e adso p ion wi h he o ma ion o CO and a omic oxygen on he ca alys su ace and, hen, u he s eps coincide wi h CO hyd ogena ion s eps, whe e u he dissocia ion o CO occu s in o in e media e ca bon and oxygen. The in e media e ca bon species is hen hyd ogena ed in a chain mechanism o o m me hane. In his case, CO 2 hyd ogena ion p inciple would ha e o become simila as ha o CO hyd ogena ion. The mechanism p oposed o bo h CO 2 and CO me hana ion [58] a e shown in Table 2-4. Basic heo y and backg ound o he wo k 33 Table 2-4: Mechanism o me hane o ma ion om CO 2 and CO [58]. E  1A8C7781A C7!"1 s P  k  s  < s    1#4$ 1  P  k  =    1#$ 1 s  k  s 1#$ 1 s  k    < s  1#$ 1   <   k   1#$ 1   <   k  P  1#$ 1  P  <   k  u  1#$ 1  u  <   k   1#$ 1   k  1#$ 1 i  < j  k ij  1#42$ ij  < j  k j P i  1#44$ j P i  k j P i 1#4$ The second mechanism in ol es he pa hway ha does no equi e ini ial ans o ma ion o CO 2 o CO. Ins ead, he hyd ogena ion o CO 2 o me hane occu s di ec ly h ough he o ma ion o in e media es (Table 2-5). This explana ion was gi en on he basis o he di e ence in speci ic ac i i y and selec i i y wi h espec o me hane o ma ion in CO and CO 2 hyd ogena ion eac ion [59]. Acco ding o [59], he s eps 13 and 14 a e as and s ep 15 is slow, and he subsequen s eps 16 o 23 a e as and i e e sible. Basic heo y and backg ound o he wo k 34 Table 2-5: Mechanism o me hane o ma ion wi hou CO o ma ion [59]. E  1A8C7781A C7!"1 s P  k  s P  1 2034  P  k  =    1 20p4 s P  <   k  ss  1 20`4 ss  <   k  s  < s  1 20Y4 s  <   k   < s  1 20 4   <   k  P  1 20K4  P  <   k  u  1 20 4  u  <   k   1 2=Z4   k  1 2=04 ij  < j  k j P i  1 2==4 j P i  k j P i 1 2=34 The di ec hyd ogena ion o CO 2 o hyd oca bons (Eq. (2.39)) using lase gene a ed i on ca bide ca alys s has been ecen ly in es iga ed by Fia o e al. [60]. This eac ion is p oposed o p oceed ia dissocia i e adso p ion o ca bon dioxide in o CO and oxygen ollowed by u he hyd ogena ion o he adso bed species on he ca alys su ace ia chain eac ion mechanism. i P  <  3 j P   2 5 j P 5 4 <  = j P i       1 j l Pmn  o  F  5 00Z [ K  q O -+   (2.39) The ans o ma ion o CO 2 and H 2 depends upon many ac o s. Se e al a emp s ha e been made by se e al in es iga o s o o e come he limi a ions o RWGS eac ion. Se e al noble me als (e.g. P , Ru, Pd) and ansi ion me als (e.g. Cu, Ni, Fe, Co) suppo ed on di e en me al oxides (e.g. 8-Al 2 O 3 , CeO 2 , SiO 2 ) ha e been explo ed o ca y ou RWGS eac ion [30]. The a ious ca alys s in es iga ed as: Basic heo y and backg ound o he wo k 35 Coppe ca alys : A ca alys wi h 12 w .-% Cu loaded on alumina has shown a good ac i i y and excellen selec i i y o CO in CO 2 hyd ogena ion [61], whe e 28% con e sion o CO 2 wi h 100% CO selec i i y a 350 °C and a mosphe ic p essu e was es ablished. The eac ion was ca ied ou wi h H 2 /CO 2 eed a io o 4 and a a space eloci y o 100 ml/g ca /min. The exclusi e selec i i y o CO was ob ained on Cu compa e o o he ca alys such as Ni, Ru, Rh and P on alumina. These ca alys s p oduce only CH 4 while Pd ca alys s gi e bo h CH 4 and CO unde he same eac ion condi ion. A ca alys wi h 5 w .-% Cu suppo ed on alumina (H 2 /CO 2 eed a io o 3, space eloci y o 100 ml/g ca /min, 220 °C, 3 MPa) p oduces CO and CH 3 OH wi h he selec i i y o abou 87% and 7.5%, espec i ely [62]. Some imes, he ca alys suppo may al e he selec i i y o p oduc . Wi h he same amoun o Cu on SiO 2 he selec i i ies a e abou 87% and 13% o CO and CH 3 OH, espec i ely while on TiO 2 he alues a e 92.5% and 4.3% o CO and CH 3 OH, espec i ely and 2.9% o CH 4 . Simila ly, when 5 w .-% Cu/SiO 2 ca alys ope a ed a 350 °C (p essu e o 0.2 ba , gas ecycle loop ha ing a H 2 /CO 2 a io o 4), he selec i i y o CO was abou 97% wi h small amoun o CH 4 (<1.5%), C 2 H 4 (<0.5%) and C 2 H 6 (<0.4% ) [63]. The addi ion o a small amoun o Ni o a Cu ca alys enhances he ca aly ic ac i i y bu also s a s CH 4 o ma ion. When he 5 w .-% Cu/SiO 2 ope a ed a 280 °C (6 MPa, H 2 /CO 2 a io o 3, space eloci y o 50 ml/g ca /min), he selec i i y o CO dec eases and he me hanol selec i i y inc eases o 76% and 24%, espec i ely [64]. I on ca alys : The CO 2 hyd ogena ion on Fe ca alys s has been s udied by Lee and cowo ke s [35, 65-70] and Cubei o e al. [71]. A 400 °C (2 MPa, space eloci y o 31.67 ml/g ca /min), he Fe/Al 2 O 3 ca alys gi es abou 49% con e sion o CO 2 and 12.4% and 87.6% o selec i i y owa ds CO and hyd oca bons, espec i ely [35]. The addi ion o po assium o Fe ema kably inc eases he ca alys ac i i y and selec i i y owa ds C 2+ –hyd oca bons. Unde he same eac ion condi ion wi h K/Fe mola a io o 0.5, CO 2 hyd ogena ion ac i i y inc eased o abou 70% while selec i i y changes o abou 4% and 96% o CO and hyd oca bons, espec i ely. Fu he inc ease in mola a io o K/Fe o 1 showed a small dec ease in ac i i y and hyd oca bon selec i i y while he selec i i y o CO sligh ly inc eased. The addi ion o alumina i sel ac s as a p omo e when he Fe-Cu-K/Al 2 O 3 Basic heo y and backg ound o he wo k 36 ca alys was p epa ed by he co-p ecipi a ion me hod [65]. The long e m s abili y es on Fe-K/Al 2 O 3 ca alys showed a signi ican dec ease in CO 2 con e sion and selec i i y o hyd oca bons [66], whe e he deac i a ion was a ibu ed mainly due o he ca bonaceous deposi ion on he ca alys su ace. A simila beha iou was ob ained wi h a Fe-Cu-K/Al 2 O 3 ca alys , whe e he ca alys deac i a ion was caused by he g ow h o c ys alli es and he esul ing dec ease in dispe sion o ca alys componen s (p omo e s) [67]. To imp o e he s eng h o ca alys s, binde s a e some imes added. A high empe a u es, binde s a e no chemically ine . The addi ion o an alumina binde o a Fe-K/Al 2 O 3 ca alys showed excellen ac i i y and selec i i y owa ds highe hyd oca bons (C 5+ ) while ac i i y and selec i i y d ama ically dec eased wi h silica binde . The eason o his in luence on he ac i i y and selec i i y was he change in acidi y o ca alys , s uc u e and me al-suppo in e ac ion [68]. The s ong me al-suppo in e ac ion be ween Fe-K/9-Al 2 O 3 makes he ca alys mo e ac i e and selec i e owa ds long chain hyd oca bons and ligh ole ins [69]. A s udy on Fe/Al 2 O 3 ca alys p epa a ion me hods such as imp egna ion, p ecipi a ion, and physical mixing and ca alys cha ac e iza ion was pe o med by Cubei o e al. [71]. The e ec o K p omo e in bo h CO 2 and CO hyd ogena ion was also in es iga ed. Gold ca alys : Gold ca alys s suppo ed on a ious me al oxides such as ZnO, Fe 2 O 3 , CeO 2 , TiO 2 , Z O 2 La(OH) 3 NiO, and Co 3 O 4 we e used by Saku ai e al. [72] o CO 2 hyd ogena ion. All he ca alys s es ed o CO 2 hyd ogena ion we e ea ed a 150 o 400 °C (8 MPa, H 2 /CO 2 a io o 3, space eloci y o 50 ml/g ca /min). Among all he ca alys s, Au suppo ed on TiO 2 , Fe 2 O 3 , and ZnO we e he mos ac i e ca alys s o he e e se wa e gas shi eac ion, whe e he equilib ium con e sion o CO 2 was ob ained a 400 °C. Bu e en a lowe empe a u es be ween 150 and 200 °C, Au/TiO 2 gi es equilib ium yield o CO. Howe e , in he empe a u e ange o 150 o 200 °C, Au/Fe 2 O 3 and Au/ZnO ca alys s p oduce much me hanol. The ac i i y o he ca alys and he selec i i y g ea ly di e depending upon he eac ion p essu e and na u e o oxide suppo [73], i.e. when he p essu e was dec eased om 5 o 0.1 MPa, he CO selec i i y inc eased om 86% o 99% on Au/TiO 2 ca alys (250 °C). Basic heo y and backg ound o he wo k 37 Cobal ca alys : The CO 2 hyd ogena ion was also s udied o e Co Fische T opsch ca alys [74, 75]. The Co/SiO 2 ca alys a 210 °C (2.4 MPa, H 2 /CO 2 a io o 4, space eloci y o 83.3 ml/g ca /min) showed deac i a ion o e ime and also p oduces mo e han 70% o me hane [74]. The compa a i e CO 2 hyd ogena ion on Fe, Co, and Ni ca alys using Al 2 O 3 as s uc u al suppo showed highes ac i i y o e Co/Al 2 O 3 ca alys . The selec i i y o de o CO was Fe/Al 2 O 3 > Co/Al 2 O 3 > Ni/Al 2 O 3 [76]. Nickel ca alys : Cu en ly, Ni is one o he mos s udied ca alys s o CO 2 hyd ogena ion eac ion because o i s high ac i i y and compa a i ely low cos . A low empe a u es, he CO 2 hyd ogena ion o e Ni ca alys p incipally p oduces CH 4 as a main p oduc [58, 77-80]. A kine ic s udy o CO 2 hyd ogena ion o e Ni/SiO 2 ca alys showed ha he ac i a ion ene gy shi s om 89 o 39 kJ/mol as empe a u e is inc eased om 227 o 327 °C [58]. The p epa a ion me hod is also impo an . The speci ic ac i i y o Ni/Al 2 O 3 cop ecipi a ed ca alys dec eases as he me al loading inc eases whe eas he ac i i y inc eases wi h me al loading o an imp egna ed ca alys [77]. The speci ic ac i i y ( ela ed o Ni only) inc eases wi h me al loading up o 30% and hen i dec eases o Ni/Z O 2 ca alys p epa ed by an ul asound assis ed me hod [78]. Du ing he eac ion, ans o ma ion o zi conium o zi conium dioxide and he c ys alliza ion o me allic Ni pa icles occu s [80]. A a high Ni con en , nickel exis s as a bulk NiO and co espondingly p oduces mo e me hane [81]. The Ni ca alys p epa ed by cop ecipi a ion me hod wi h a loading om 0 o 20% on CeO 2 showed ha he 2 w .-% Ni- CeO 2 exhibi s excellen ca aly ic ac i i y, selec i i y, and s abili y o he e e se wa e gas shi eac ion [81]. A 600 °C and a mosphe ic p essu e wi h H 2 /CO 2 a io o 1 and a qui e high space eloci y o 2 l/g ca /min, CO 2 con e sion ob ained o e 2 w .-% Ni/CeO 2 ca alys was abou 35% wi h 100% CO selec i i y. The o he RWGS eac ion ca alys (10 w .-% NiO/ZnO) showed an e en highe ac i i y (CO 2 con e sion o 38%, which is e y nea o equilib ium con e sion o 40%) and a selec i i y owa ds CO o abou 98% [82]. 38 Objec i e and scope o he wo k 39 3. Objec i e and scope o he wo k As men ioned in he p e ious chap e , he consump ion o ossil uels and he elease o CO 2 in o he a mosphe e is con inuously g owing. E e y yea billion ons o an h opogenic ca bon dioxide a e eleased in o he a mosphe e. The abili y o sepa a e CO 2 om lue gases and o s o e a se e al billion ons o CO 2 emi ed pe yea is ques ionable as a e he en i onmen al consequences. The e o e he con e sion o CO 2 o use ul chemicals and uels is an a ac i e op ion o CO 2 mi iga ion. A possible a enue o sus ainable de elopmen is he ca aly ic con e sion o CO 2 o liquid uels by Fische T opsch syn hesis and sola o wind ene gy. The e e se wa e gas shi eac ion (RWGS) is he i s s ep, and he p oduced CO u he con e ed o liquid uels by Fische T opsch syn hesis. The ans o ma ion o CO 2 and H 2 depends upon se e al ac o s such as ca alys selec ion, a io o CO 2 /H 2 , and eac ion empe a u e and p essu e. The e o e, he main ocus o his wo k was o use a sui able ca alys and o de e mine he op imal eac ion condi ions o CO 2 hyd ogena ion in a ixed bed eac o . The expe imen s we e designed such ha he RWGS eac ion could be examined in bo h he o wa d and e e se di ec ion. In addi ion o hese expe imen s, he consecu i e eac ion o CO o me hane was also conside ed. The s udies o all h ee eac ions we e pe o med using a comme cial Ni ca alys in a lab scale ixed bed eac o . Since anspo p ocesses (ex e nal bounda y laye di usion and po e di usion) may ha e s ong in luence, his aspec was also conside ed. The mos a ailable s udies o ca aly ic hyd ogena ion o CO 2 we e pe o med a low empe a u es whe e me hane is he main p oduc . The e o e, in his wo k CO 2 hyd ogena ion is s udied a high empe a u es whe e he e e se wa e gas shi eac ion is a ou ed he modynamically and p oduces CO and H 2 O as main p oduc s. Fo he basic in es iga ion o ca aly ic ac i i y, pu e alumina and some alumina suppo ed C , Zn-Cu, and Ni ca alys s we e used. A e compa ing he ac i i y o all hese ca alys s, he comme cial Ni ca alys supplied by Süd-Chemie (sphe ical pelle , d p = 5 o 7 mm) was chosen o a de ailed kine ic s udy. Objec i e and scope o he wo k 40 The pa ame e s ha in luence he eac ion a e such as empe a u e, eac an concen a ion, esidence ime, and pa icle size o he ca alys we e s udied in a lab scale ixed bed qua z eac o . To de e mine he kine ic, he expe imen s we e conduc ed a condi ions su icien ly a away om equilib ium. No only he RWGS eac ion, bu also CO hyd ogena ion (me hana ion) (CO + 3H 2 5 CH 4 + H 2 O) and WGS eac ion (CO + H 2 O 5 CO 2 + H 2 ) we e s udied in de ail. Finally, a one dimensional adiaba ic and iso he mal ixed bed eac o model was de eloped a echnical condi ions (high empe a u e) o e Ni/Al 12 O 19 as well as Al 2 O 3 ca alys sys em o simula e he pe o mance o hyd ogena ion o CO 2 o CO o he p oduc ion o liquid uels ia Fische T opsch syn hesis. The axial p o iles o eac o pe o mance ( empe a u e and con e sion) we e simula ed along he ca aly ic ixed bed. Expe imen al me hod and da a analysis 41 4. Expe imen al me hod and da a analysis In he ollowing, he expe imen al se up and he p ocedu e used in CO 2 hyd ogena ion, CO hyd ogena ion o me hane as well as wa e gas shi eac ion, and i s co esponding calcula ion me hods a e in oduced. 4.1 Expe imen al se up The expe imen al se -up wi h eac o appa a us cons uc ed o his s udy is shown in Fig. 4-1. I mainly consis s o a qua z eac o , mass low con olle s, a hea ing u nace and a empe a u e con ol sys em, a wa e sa u a o , a cooling sys em, and an online gas analyse . Fig. 4-1: Expe imen al se -up used o CO 2 hyd ogena ion, CO hyd ogena ion and wa e gas shi eac ion. A pho og aph and a schema ic diag am o he bench-scale ixed bed eac o (2 cm inne diame e and 45 cm leng h) used o he expe imen al s udies is shown in Fig. 4-2. In he Expe imen al me hod and da a analysis 48 me hane a e he only de ec able p oduc s o CO 2 hyd ogena ion eac ion, CO 2 con e sion is calcula ed as: i P  B-4AAD.,-4  2  |} ~ 4  F 2 i 4 FJ < 2 j 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.3) Simila ly, he yield o CO and CH 4 can be calcula ed (no CO and CH 4 in he eed) as: i  {,A+  2  |} 4  F 2 i 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.4) j  {,A+  2  |   4  F 2 j 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.5) 4.4.1.2 De e mina ion o he in insic kine ic pa ame e s The in insic kine ic expe imen s we e ca ied ou in a qua z glass ixed bed eac o wi h an inne diame e o 2 cm, illed wi h 1.2 g ca alys o 5 o 7 mm diame e . The iso he mal expe imen s we e ca ied ou a a mosphe ic p essu e. The inle eed passed h ough he eac o (H 2 /CO 2 = 6) was dilu ed wi h 23 ol.-% o ni ogen. The expe imen s we e pe o med un il cons an con e sion o CO 2 was ob ained. Fo he bimolecula CO 2 hyd ogena ion eac ion (CO 2 + H 2 5 CO + H 2 O), he in insic eac ion a e o e solid ca alys is calcula ed as: D E  | } ~ F  E  | } ~   |} ~     ~ E 1 (4.6) Fo he eac ion o de n 7 1, he eac ion a e cons an  E|}~ is gi en as:  E  | } ~  F 2 0 5   ~ 4 @  ? 5 0 2  5 0 4   E   |} ~   @    ~ E 1 (4.7) This calcula ed  E|}~ in Eq. (4.7) may no be he in insic a e cons an , which can be con i med by calcula ing he e ec i eness ac o . The modi ied esidence ime E as a unc ion o mass o ca alys and olume low a e a eac ion empe a u e and o al p essu e o gas is gi en as:  E F   6 5  2 L   FQ 4 1 (4.8) Expe imen al me hod and da a analysis 49 The ac i a ion ene gy E A and equency ac o k m,0 can be calcula ed om he A henius equa ion:  E  | } ~  F  E  F  A   !" 1 (4.9) 4.4.1.3 In e nal mass anspo calcula ions As men ioned in chap e 2, he po e di usion limi a ions may occu , and he measu ed kine ics may no be he in insic bu he e ec i e one. The e ec i e a e o chemical eac ion is calcula ed wi h he help o he e ec i eness ac o 2 is gi en as: D E  #$$ F %  D E 1 (4.10) The e ec i eness ac o 2 o n h o de i e e sible eac ion is gi en by: % F D E  #$$ D E F )(4 C 8 8 1 (4.11) The Thiele modulus o he ca alys wi h homogeneous dis ibu ion and o n h o de , i e e sible, bi-molecula CO 2 hyd ogena ion eac ion is gi en as 8 F 7 8  9 1 4 < 0 = 6  E  : 8   |}~   @   ~ E ; |} ~  #$$ 1 (4.12) whe e he cha ac e is ic leng h L p is he a io o he olume o he pa icle o he ex e nal su ace o he pa icle ( o sphe ical pa icle L p = D 8 O3). Fo a shell ca alys he modi ied Thiele modulus (8  4 is gi en as [83] 8  F 7 8  9 1 4 < 0 = 6  E   : 8  |}~   @   ~ E ; |} ~  #$$ 1 (4.13) whe eas he cha ac e is ic leng h (L p ) o a shell ca alys is gi en as 7 8 F  0 5 e 0 5 ) & D 8  h u   D 8 3 1 (4.14) whe e D 8 is he adius o pa icle and ) & is he shell hickness o ac i e ma e ial. The e ec i e di usi i y o CO 2 in a po ous ca alys is gi en as: Expe imen al me hod and da a analysis 50 D |} ~  #$$ F E 8 7 8 D |} ~  8FG# F E 8 7 8 e 0 D |} ~  EFQ < 0 D |} ~  IJ h  @ 1 (4.15) In he p esen s udy, mass anspo in he po es depends bo h on molecula di usion and Knudsen di usion. The molecula di usion coe icien s o CO 2 in he gas mix u e we e calcula ed by a compu e da abase p og am while Knudsen di usion coe icien s we e calcula ed by using Eq. (4.16) as D |}~IJ F   8FG# 3 9 K  9  L M  N |} ~  1 (4.16) whe e  8FG# is he po e diame e , R is he gas cons an , T is he empe a u e, and N |}~ he molecula weigh o CO 2 . The o uosi y ac o depends upon na u e o in e connec ing pa hs which is in luenced by he connec i i y, shapes, and speci ic limi ing cons ic ions. In his wo k, a ypical alue o 7 8 o 1.6 was assumed o Ni ca alys . The calcula ion o he modi ied Thiele modulus o he shell ca alys needs he modi ied eac ion a e cons an U E  W, which is gi en o a sphe ical ca alys pa icle o adius D 8 and shell hickness ) & as:  E  F  8  &   E  6 8 6 &   E 1 (4.17) The ac o V p /V s is he a io o olume o he pa icle o he olume o he shell: 6 8 6 & F  0 5 e 0 5 ) & D 8  h u   @ 1 (4.18) Fo he Ni ca alys used in his wo k V p /V s is abou 2.4. By Eq. (4.17) and Eq. (4.13),  E  can be calcula ed as  E  F  0 5 e 0 5 ) & D 8  h u   @  E 1 (4.19) Inse ion o he cha ac e is ic leng h (7 8 ) om Eq. (4.14) and o he modi ied a e cons an ( E  4 om Eq. (4.19) in o Eq. (4.13), yields he modi ied Thiele modulus o a shell ca alys ha ing ac i e ma e ial only in he shell: Expe imen al me hod and da a analysis 51 8  F  0 5 e 0 5 ) & D 8  h u   [ ¡  D 8 3  9 1 4 < 0 = 6   E  : 8   |}~   @   ~ E ; |} ~  #$$ 1 (4.20) Fo he case o ) & FD 8 , Eq. (4.19) leads o he same equa ion ha is used o he calcula ion o he Thiele modulus o a ca alys wi h a homogeneous dis ibu ion o he ac i e componen (Eq. (4.12)). 4.4.1.4 Calcula ion o ex e nal mass anspo limi a ions The e ec i e eac ion a e due o ex e nal mass ans e is calcula ed as D E  | } ~  #$$ F R  S E  #T U  |} ~ 5  |} ~  & W 1 (4.21) The ex e nal mass ans e coe icien 3 (m/s) depends upon he pa icle size and geome y, molecula di usion coe icien o gas (D |}~EFQ 4, and he hyd odynamic condi ions such as eloci y and iscosi y o he luid. 3 as a unc ion o he dimensionless She wood numbe ( ¢ ) o he mass ans e can be calcula ed as R F 3 C  D |} ~  EFQ  8  1 (4.22) The ex e nal su ace a ea A m,ex (m 2 /kg) o sphe ical pa icle is S E  #T F Y  8  : 8   1 (4.23) whe e d p and 6 p a e he pa icle diame e and densi y o pa icle, espec i ely. When gas lows h ough a ca alys ixed bed, he She wood numbe is gi en as whe e 4 b is he bed po osi y. The pa icle She wood numbe ( ¢ £ ) o gas low a ound he pa icle and o lamina low, co ela ed o he Schmid numbe ( ¢¤ ) and he Reynolds numbe (Re) is gi en as [20]: 3 C 8 F = < Z [ Y  ] 9A  ] 3B  ^ 1 (4.25) The Reynolds numbe ( ¥ ) depends upon he in e s i ial eloci y u (m/s), he kinema ic iscosi y o gas ¦ (m 2 /s), and he pa icle diame e d p (m): 3 C F _ 0 < 0 [ `  2 0 5 H a 4 b  3 C 8  1 (4.24) Expe imen al me hod and da a analysis 52 9A F *   8 c   1 (4.26) Simila ly, Schmid numbe ( ¢¤ ) depending upon he kinema ic iscosi y 7 (m 2 /s) and he molecula di usion coe icien o gas D |}~EFQ (m 2 /s) as: 3B F c D |} ~  EFQ   1 (4.27) Now he e ec i e eac ion a e due o he combined in luence o in e nal and ex e nal mass ans e esis ances is gi en in app oxima ion ( o an almos i e e sible eac ion) by d E  #$$ F  e 0 %  E   |} ~     ~ E < 0 R  g E  #T    ~ h  @ 1 (4.28) CO hyd ogena ion (me hana ion) eac ion 4.4.2 4.4.2.1 Con e sion o CO and yield o CO 2 and CH 4 Simila o CO 2 hyd ogena ion, he con e sion o CO and he yield o CO 2 and CH 4 a gi en eac ion condi ion is calcula ed depending upon he ou le ca bon pe cen age alues ob ained o e he analyse . As he me hane and ca bon dioxide a e he main p oduc s o CO hyd ogena ion eac ions, he CO con e sion is calcula ed as: i  B-4AAD.,-4  2  |} 4  F 2 i P 4 FJ < 2 j 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.29) and he yield o CO 2 and CH 4 in CO hyd ogena ion is calcula ed as: i P  {,A+  2  |} ~ 4  F 2 i P 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.30) j  {,A+  2  |   4  F 2 j 4 FJ 2 i 4 FJ < 2 j 4 FJ < 2 i P 4 FJ  0ZZ 1 (4.31) 4.4.2.2 Kine ic analysis and mass anspo calcula ions The calcula ions wi h ega d o he in insic kine ics and in e nal and ex e nal mass ans e limi a ions o CO hyd ogena ion we e pe o med by using he equa ions applied o CO 2 hyd ogena ion (see sec ion 4.4.1). Expe imen al me hod and da a analysis 53 Wa e gas shi (WGS) eac ion 4.4.3 4.4.3.1 Con e sion o CO and yield o CO 2 and CH 4 The con e sion o CO and he yield o CO 2 and CH 4 in wa e gas shi eac ion we e calcula ed by using he same equa ions as o he CO hyd ogena ion (Eq. (4.29) o (4.31)). 4.4.3.2 Kine ic analysis and mass anspo calcula ions The kine ic analysis o he WGS eac ion was also done by using he equa ions o CO 2 hyd ogena ion eac ion (see sec ion 4.4.1). 54 Resul s and discussion 55 5. Resul s and discussion As al eady men ioned in Chap e 4, his wo k is di ided in o ou pa s. In he i s pa (Chap e 5.1), expe imen al esul s a e discussed o CO 2 hyd ogena ion s udied by using a ixed bed eac o . This pa mainly includes he eac ion pa ame e s udy, he in insic kine ics o CO 2 hyd ogena ion, and he in luence o po e di usion and ilm di usion on he e ec i e eac ion a e o CO 2 hyd ogena ion. The second pa (Chap e 5.2) consis s o a simila pa ame ic s udy o CO hyd ogena ion (me hana ion eac ion). Simila o he i s and second pa , he hi d pa (Chap e 5.3) includes he pa ame e s udy o wa e gas shi eac ion (as he e e se eac ion o CO 2 hyd ogena ion), again he in insic kine ics as well as he in luence o po e di usion and ilm di usion. The ou h and las pa (Chap e 5.4) includes he ixed bed eac o modelling o CO 2 hyd ogena ion a echnical condi ions. 5.1 CO 2 hyd ogena ion (RWGS) The s udies on CO 2 hyd ogena ion (CO 2 + H 2 9 CO + H 2 O) we e ca ied ou in a ixed bed qua z eac o o e a wide empe a u e ange (300 – 900 °C) and a a mosphe ic p essu e. The comme cial Ni ca alys was used. Fo compa ison, 8-Al 2 O 3 was also es ed o in es iga e he ca aly ic ac i i y o he suppo only. E ec o educ ion empe a u e on CO 2 hyd ogena ion (RWGS) 5.1.1 The comme cial NiO/Al 12 O 19 (G-90.B) ca alys was educed a wo di e en empe a u es (500 and 800 °C) o examine he e ec o he educ ion empe a u e on he ca alys pe o mance and he yield o p oduc s. Fig. 5-1 shows he con e sion o CO 2 and he yield o CO and CH 4 ob ained o e he ca alys educed a 500 and 800 °C. A s ong dependence o ac i i y and p oduc yield on he educ ion empe a u e was obse ed. On he Ni ca alys educed a a low empe a u e o 500 °C o 15 h, me hane was o med almos exclusi ely along wi h CO in he low eac ion empe a u e ange (below 600 °C), while on he ca alys samples educed a high empe a u e o abou 800 °C o 3 h, he me hane o ma ion s ongly dec eased in he same ange o eac ion empe a u e. The o e all con e sion o CO 2 ob ained a any eac ion empe a u e is high o he ca alys educed a 500 °C compa ed o 800 °C. This could be due o he deac i a ion o he ac i e species (pa icula ly me hane o ming species) a high educ ion empe a u es. Resul s and discussion 56 Fig. 5-1: CO 2 con e sion and CO and CH 4 yield e sus empe a u e; open symbol: ca alys educed a 800 °C o 3 h; closed symbol: ca alys educed a 500 °C o 15 h (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 66 ol.-%, y CO2 = 11 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). O e he educed ca alys bo h a 500 °C and 800 °C, me hana ion eac ion occu s (mos a ou ed he modynamically a low empe a u e) along wi h he e e se wa e gas shi (RWGS) eac ion. The yield o CO inc eases con inuously wi h inc ease in empe a u e bu no he con e sion o CO 2 . This is a clea indica ion o di ec me hane o ma ion ia CO 2 hyd ogena ion (Saba ie eac ion) wi hou in e media e CO o ma ion. The o e all CH 4 o ma ion obse ed could be due o bo h CO 2 and CO hyd ogena ion bu i is qui e di icul o quan i y because bo h eac ions occu simul aneously. Fig. 5-2 shows he XRD pa e n o he Ni/Al 12 O 19 ca alys (11 w .-% Ni). The di ac og am (A) o he esh Ni ca alys shows s ong NiO lines a 2B alues o 37.3, 43.3, and 62.9 con i ming he p esence o ee nickel oxide [84]. Fo bo h he educed and used ca alys no ee nickel oxide lines we e obse ed. On he di ac og am (B) o he educed ca alys , he lines we e obse ed o nickel c ys alli es a 44.5 and 51.8 while o he used ca alys (C) a line was obse ed a 44.5. F om he di ac og am (B) i is clea ha he ca alys s ge comple ely educed e en a low empe a u e o 500 °C. On he di ac og am (C) o he used ca alys , he ee NiO lines we e no obse ed which means ha no oxida ion o Ni happens by he wa e o med du ing he eac ion a 500 °C. 0 20 40 60 80 100 300 400 500 600 700 800 900 XCO2, YCO, YCH4 [C-%] Tempe a u e [3C] Equilib ium con e sion o CO2 (bo h o CO and CH4) YCO YCH4 XCO2 Resul s and discussion 57 Fig. 5-2: XRD pa e ns o esh NiO/Al 12 O 19 (A), educed ca alys a 500 °C (B), and used ca alys a 500 °C (C). To de e mine he exac empe a u e needed o he educ ion o he Ni ca alys and he numbe o educible species p esen in he ca alys , a TPR expe imen was pe o med by using C HEMBET -3000. TPR analysis begins by passing he analysis gas (10% hyd ogen in Resul s and discussion 64 Ni ca alys 40% CO 2 con e sion is eached a abou 9 kg s m -3 (Fig. 5-5). Hence, he ac i i y o he Ni ca alys is abou 10 imes highe . Fig. 5-9: E ec o modi ied esidence ime on CO 2 con e sion and selec i i y o CO and CH 4 (T = 700 °C, p = 1 a m, m ca = 10 g, ca alys = Al 2 O 3 , d p = 1 – 3 mm, y H2 = 66 ol.-%, y CO2 = 11 ol.-%, es N 2 ). Acco ding o he da a ob ained in his s udy, me hane o ma ion du ing CO 2 hyd ogena ion may be due o he di ec me hana ion (CO 2 + 4H 2 5 CH 4 + 2H 2 O) o o he consecu i e eac ion o CO hyd ogena ion (CO + 3H 2 5 CH 4 + H 2 O). The consecu i e eac ion mechanism in CO 2 hyd ogena ion implies he di icul y ha he op imum eac ion condi ions o each o he eac ions a e di e en (high empe a u e o RWGS and low empe a u e o CO hyd ogena ion). E ec o ca alys pa icle size (RWGS and consecu i e me hana ion) 5.1.5 To de e mine he e ec o pa icle size on he ca alys pe o mance, pa icles o Ni ca alys wi h less han 0.5 mm diame e (c ushed ca alys ) and 6 mm diame e we e used. Fig. 5-10 shows he con e sion o CO 2 and he yield o CO and CH 4 a di e en empe a u es. The ca alys pa icles wi h diame e o less han 0.5 mm show a highe con e sion han he 6 mm pa icles wi h he ac i e ma e ial only a he shell side which may due o wo easons. One is he esh ca alys which is no ea ed a high empe a u e o long ime has highe 2 2 2 2 2 422 2 2 422 42 22 2 XCO2, SCO, SCH4 [C-%] Modi ied esidence ime [kg s m-3] Equilib ium con e sion o CO2 SCO SCH4 XCO2 Resul s and discussion 65 ac i i y han he used one (see Fig. 5-4). On he hand he in luence o di usion esis ances may be smalle o small pa icles. This will be analysed in mo e de ail in sec ion 5.1.7. Fig. 5-10: CO 2 con e sion and CO and CH 4 yield a di e en pa icle size in CO 2 hyd ogena ion (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , gas low a e = 138 l/h (NTP), y H2 = 66 ol.-%, y CO2 = 11 ol.-%, es N 2 ,). S abili y o he Ni ca alys o he RWGS eac ion a high empe a u e 5.1.6 The ime on s eam s abili y o Ni/Al 12 O 19 ca alys was es ed a 900 °C and a mosphe ic p essu e wi h he o al gas low a e o 138 l/h in he ixed bed eac o . The es was ca ied ou o ou days wi h in e media e cooling cycles. A he beginning o he expe imen , he Resul s and discussion 66 ca alys bed empe a u e was inc eased om ambien empe a u e o 900 °C a he a e o 10 °C/min wi h a small low a e o N 2 and hen held cons an o 30 min o ge a s able empe a u e. Then he equi ed gas composi ion (CO 2 /H 2 /N 2 ) in he eac ion mix u e was adjus ed and ed o he eac o sys em. Fig. 5-11 shows he con e sion o CO 2 ob ained o e ime on s eam o he eac ion mix u e. A such a high empe a u e o 900 °C, he CO 2 is p ac ically only con e ed by he e e se wa e gas shi eac ion and CO is he main p oduc . On he i s day o ime on s eam, he ca alys showed some deac i a ion whe e CO 2 con e sion dec eased om 68% o 66% in 8 h. A e ha he ca alys was cooled o 300 °C and kep cons an o e nigh . No deac i a ion was obse ed on u he ime on s eam, bu a small loss in ca alys ac i i y du ing hea ing and cooling cycle was obse ed which may be due o su ace modi ica ions. Fig. 5-11: Con e sion o CO 2 e sus ime on s eam a 900 °C in CO 2 hyd ogena ion (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y CO2 = 11 ol.-%, y H2 = 66 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). Kine ic analysis o he RWGS on he Ni ca alys 5.1.7 In insic kine ics Fo he kine ic analysis, he concen a ions o CO 2 and H 2 we e a ied (Fig. 5-12 and Fig. 5-13). The empe a u e was kep low (340 °C) o a oid an in luence o mass anspo on he e ec i e eac ion a e, which hen equals he in insic a e. Resul s and discussion 67 Fig. 5-12: E ec o CO 2 concen a ion on he CO 2 con e sion and he CO and CH 4 yield in CO 2 hyd ogena ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 66 ol.-%, y CO2 = 11 – 22 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). Fig. 5-13: E ec o H 2 concen a ion on he CO 2 con e sion and he CO and CH 4 yield in CO 2 hyd ogena ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 44 – 66 ol.-%, y CO2 = 11 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). 2    4 4 34 3 3 XCO2, YCO, YCH4 [C-%] CCO2 [mol/m3] 0E 1E 1E2 nCO2= 0 nCO2= 1 2    4 4 3 423 43 XCO2, YCO, YCH4 [C-%] CH2 [mol/m3] 0E 1E 1E2 mH2= 0 mH2= 1 Resul s and discussion 68 The eac ion o de wi h espec o each eac an can be de e mined by using he ollowing equa ion:   ~ F 0 5 § E  |} ~   ¨    ~ E  2  5 0 4   |} ~   @ < 0 © @ @    (5.1)  Fig. 5-14 shows he plo o X CO2 e sus C CO2 . The o de was calcula ed by he in eg al me hod i.e. he alue o he eac ion o de was de e mined by he bes i o he measu ed da a. Fo he expe imen al condi ions used, he eac ion o de o CO 2 is 0.1. Fig. 5-14: Dependence o CO 2 con e sion upon CO 2 concen a ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y CO2 = 11 – 22 ol.-%, y H2 = 66 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). Simila ly, he eac ion o de wi h espec o hyd ogen was de e mined (Fig. 5-15), which leads o a alue o 0.4. The eac ion a e and he eac ion a e cons an o CO 2 hyd ogena ion was calcula ed by using Eq. (4.6) and Eq. (4.7), espec i ely. The A henius plo is shown in Fig. 5-16. Only he alues o k m,CO2 o T < 410 °C a e included, because hen he eac ion a e is solely de e mined by he in insic kine ics. Abo e his empe a u e, he eac ion a e is hen also con olled by mass anspo limi a ions. 0.02 0.04 0.06 0.08 0.10 0.12 0.14  3  3  3  XCO2 CCO2 [mol/m3] n = -0.1 n = 0.1 n = 0.3 nCO2= 0.1 Fixed poin Resul s and discussion 69 Fig. 5-15: Dependence o CO 2 con e sion upon H 2 concen a ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 44 – 66 ol.-%, y CO2 = 11 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). Fig. 5-16: A henius plo (1/T e sus ln k m,CO2 ) o CO 2 con e sion (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 66 ol.-%, y CO2 = 11 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). The equency ac o and ac i a ion ene gy (Fig. 5-16) a e 5.55 C 10 2 m 1.5 mol 0.5 kg -1 s -1 and 65 kJ/mol, espec i ely. The alue o E A (65 kJ/mol) ob ained in his s udy is wi hin he ange ound by o he au ho s o CO 2 hyd ogena ion eac ion o e Ni ca alys s (Table 5-1). 0.07 0.08 0.09 0.10 0.11 0.12   42 44 4 4 4 XCO2 C H2 [mol/m3] 0.4 0.7 mH2= 0.4 Fixed poin Resul s and discussion 70 Table 5-1: Ac i a ion ene gies epo ed o CO 2 hyd ogena ion on nickel ca alys s. Ca alys Tempe a u e (°C) P essu e (a m) E A (kJ/mol) Re e ences 75.3-84.6% Rany Ni 160 – 270 1 88 – 91 [33] 20% Ni/Al 2 O 3 250 – 400 1 87 [76] 3% Ni/SiO 2 227 – 277 1 81 [87] 59% Ni-88 283 – 397 2 – 30 58 – 55 [88] 58% Ni-104 277 – 318 6 – 18 61 [89] 33.6% Ni (G-65) 200 – 230 1 106 [90] 42% NiO/Al 2 O 3 210 – 315 1 80 – 92 [91] 11% Ni (G.90-B) 305 – 410 1 65 This wo k In luence o in e nal mass anspo (po e di usion) The po e di usion limi a ions we e de e mined o bo h he shell and non-shell ca alys (homogeneous ma e ial). The model pa ame e s equi ed in he calcula ion o he e ec i e eac ion a e a e gi en in Table 5-2. The e ec i e a e o chemical eac ion is gi en as: D E  | } ~  #$$ F %  D E  | } ~ 1 (5.2)  The Thiele modulus o an i e e sible, iso he mal, n h o de eac ion and o he sphe ical pa icle o 0.5 mm and 6 mm diame e (non-shell ca alys ) was calcula ed by using Eq. (4.12) while o he shell ca alys Eq. (4.17) was used. The e ec i eness ac o as a unc ion o he Thiele modulus was de e mined by Eq. (4.11). The Knudsen di usion coe icien D |}~IJ was calcula ed by using Eq. (4.16) and he combined po e di usion coe icien D |}~8FG# was calcula ed by using Eq. (4.15). The di usion coe icien o CO 2 in he ca alys po e a 500 °C and 1 ba is shown in Fig. 5-17. Fo he a e age po e diame e o 230 nm, he di usion o CO 2 in he po es o he Ni ca alys is de e mined by bo h Knudsen and molecula di usion ( ansi ion a ea). The Knudsen Resul s and discussion 71 di usion domina es he anspo phenomenon a po e diame e o less han 100 nm while molecula di usion domina es abo e he po e diame e o 10000 nm. Table 5-2: Model pa ame e s used o he calcula ion o e ec i e eac ion a e o CO 2 hyd ogena ion o e Ni ca alys (p = 1 a m). Pa ame e s 2345671 F equency ac o (k m,0 ) 5.55 · 10 2 m 1.5 mol 0.5 kg -1 s -1 Ac i a ion ene gy (E A ) 65 kJ/mol Pa icle densi y (6 p ) 1910 kg/m 3 Po osi y o pa icle (4 p ) 0.33 To uosi y o pa icle A p (assump ion) 1.6 Molecula di usion coe icien (D CO2,mol ) a 773 K 1.83 · 10 -4 m 2 /s Knudsen di usion coe icien (D CO2,knu ) a 773 K 4.68 · 10 -5 m 2 /s Po e di usion coe icien (D CO2,po e ) a 773 K 3.72 · 10 -5 m 2 /s Kinema ic iscosi y o CO 2 (7 CO2 ) a 773 K 1.63 · 10 -4 m 2 /s Fig. 5-17: Di usion coe icien o CO 2 in he po es o he Ni/Al 12 O 19 and Al 2 O 3 ca alys s de e mined a 500 °C and 1 ba . Resul s and discussion 72 The plo o he e ec i eness ac o e sus empe a u e is shown in Fig. 5-18. In e nal mass ans e esis ance in he ca alys po es is no negligible o T > 400 °C e en o he shell ca alys wi h 0.5 mm shell hickness o ac i e ma e ial (Ni). Fig. 5-18: E ec i eness ac o o ca alys pa icle e sus empe a u e (p = 1 a m, ca alys = Ni/Al 12 O 19 , y CO2 = 11 ol.-%, y H2 = 66 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). In luence o ex e nal mass anspo (bounda y laye di usion) To de e mine he in luence o ilm di usion, he e ec i e eac ion a eD E|}~#$$ as a unc ion o ex e nal mass ans e coe icien 3 and ex e nal su ace a ea pe mass o he ca alys A m,ex has been calcula ed by Eq. (4.21). All he calcula ions o he ex e nal mass ans e coe icien (3), ex e nal su ace a ea o he ca alys (A m,ex ), She wood numbe (Sh), Reynolds numbe (Re), and Schmid numbe ( ¢¤ ) a e gi en in sec ion 4.4.1.4. The e ec i e eac ion a e due o he combined in luence o in e nal and ex e nal mass anspo is calcula ed as: d E  #$$ F  e 0 %  E  | } ~   |} ~   [ @   ~  [ < 0 R  g E  #T  U   ~ 5   ~  ª« W h  @ 1 (5.3)  Fig. 5-19 shows a good ag eemen o he calcula ions and he measu emen s o he used shell ca alys . I also e eals ha o he hypo he ic case o a non-shell ca alys (pa icle 2324 2342 4322 22 22 22 22 22 22 22 E ec i eness ac o (1) Tempe a u e [8C] o pa icle (dp= 0.5 mm) in luence o po e di usion o ca alys o 0.5 mm shell hickness o pa icle (dp= 6 mm) homogeneous dis ibu ion Resul s and discussion 73 diame e o 6 mm) he e ec i e eac ion a e is lowe han o he shell ca alys . Fo a e y small pa icle size (d p = 0.5 mm) he e ec i e eac ion a e is only in luenced by po e di usion a empe a u e abo e 700 °C while no in luence o ex e nal mass anspo was obse ed in he s udied ange o empe a u e (no shown he e). Conside ing 6 = 1 in Eq. (5.3) enables o sepa a e he kine ic limi a ion om in e nal mass ans e limi a ion. In Fig. 5-19, he e ec i e eac ion a e wi hou in e nal mass ans e limi a ion di e s signi ican ly om he e ec i e eac ion a e wi h in e nal mass anspo limi a ion o he shell ca alys as well as o he non-shell ca alys o 6 mm pa icle diame e . Fig. 5-19 shows ha he shell ca alys ope a es in a mixed egime wi h bo h in e nal and ex e nal mass ans e . The ca alys pe o mance is mo e and mo e con olled by ex e nal mass ans e abo e a empe a u e o abou 900 °C. No e ha Eq. (5.3) is only an app oxima ion because o wo easons: • The e e se eac ion (CO + H 2 O 5 CO 2 + H 2 ) is no conside ed in he po e di usion e m. • Fo he ex e nal mass ans e , he equilib ium concen a ion is assumed a he ex e nal su ace. In eali y, his alue is highe and only eached, i he chemical eac ion is e y as . Eq. (5.3) is he e o e only exac i only po e di usion o only ex e nal mass ans e plays a ole. Fo he egime in be ween hese wo ex emes, Eq. (5.3) is only a hope ully good app oxima ion. Fu he mo e, in Fig. 5-19, in insic a e o he chemical eac ion ( m ) Eq. (4.6), he eac ion a e o di usion bounda y laye ( m,ex ) Eq. (4.21), and he e ec i e eac ion a e due o in e nal and ex e nal mass anspo ( m,e ) Eq. (5.3) a e shown. The e ec i e eac ion a es ( m,e (calcula ed) ) we e calcula ed based on he inle concen a ions while he measu ed alues ( m,e (measu ed) ) we e calcula ed based on he con e sion, inle concen a ion, and mass o ca alys . No e ha o empe a u es be ween abou 500 °C and 900 °C, he equilib ium con e sion is no 100% (see Fig. 2-13 o R = 6) and eaches a minimum alue o a ound 75% a 600 °C. This was no conside ed o he calcula ions o m,e and was only included o calcula e m,ex (FRg E#T 2 ~ 5 ~ª« 4). Resul s and discussion 80 wi h empe a u e un il abou 450 °C a e eached. No ca alys deac i a ion was obse ed. In he low empe a u e ange, he eac ion is con olled kine ically and no coke o ma ion ook place. A low empe a u es (below 450 °C) a small amoun o CO 2 was p oduced by he wa e gas shi eac ion [93]. A a e y high empe a u e o abou 800 °C, also no ca alys deac i a ion was obse ed, bu he coke o med in he empe a u e ange o 480 o 710 °C may no comple ely gasi ied a 800 °C, and he e o e he con e sion o CO was low and a om equilib ium. The dec ease in con e sion due o he ca alys deac i a ion o e ime on s eam is shown below (see sec ion 5.2.2 (Fig. 5-26)). The coke o ma ion may occu ia Boudoua d eac ion (2CO k C + CO 2 ) which is ela ed o CO dissocia ion ac i i y in CO hyd ogena ion [94] and/o di ec ca bon monoxide hyd ogena ion (CO + H 2 k C + H 2 O) o e he Ni ca alys [95]. Fig. 5-24 shows he equilib ium con e sion o CO o e he empe a u e by bo h Boudoua d eac ion and di ec CO hyd ogena ion. A high empe a u es bo h eac ions a e limi ed he modynamically. Fig. 5-24: The equilib ium con e sion o CO in he Boudoua d eac ion (CO = 1 mole) and di ec hyd ogena ion eac ion (H 2 /CO = 1) as unc ion o empe a u e and a a mosphe ic p essu e. S abili y o he Ni ca alys in CO me hana ion 5.2.2 Fig. 5-25 shows ime on s eam beha iou o he Ni ca alys o he CO con e sion and he yield o CO 2 and CH 4 (450 °C, a mosphe ic p essu e). The maximum deac i a ion o he 2 2 2 2 2 422 22 22 22 22 22 22 22 4222 XCO, Equilib ium [C-%] Tempe a u e [3C] 2CO 1 C + CO2 CO + H21 C + H2O Resul s and discussion 81 ca alys s occu s gene ally in he ini ial s age o he eac ion [93, 96]. In his expe imen , no deac i a ion was obse ed in 2 h ime on s eam a 450 °C, and he s eady s a e o eac ion was eached wi hin some minu es. When he empe a u e inc eased u he (keeping all o he condi ions cons an ), he coke o ma ion s a s abo e 480 °C, whe e CO con e sion dec eases o e ime on s eam in he empe a u e ange o 480 o 710 °C (Fig. 5-26). Fo example, a 620 °C, he con e sion o CO dec eases om 7 o 6.3% in 100 min o eac ion ime. A he empe a u e o 710 and 810 °C, a small inc ease in con e sion o e ime on s eam was obse ed which may be due o he gasi ica ion o coke o med in he empe a u e ange o 480 o 710°C. Fig. 5-25: CO con e sion and he yield o CO 2 and CH 4 e sus ime on s eam in CO hyd ogena ion (T = 450 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 , ca alys = Ni/Al 12 O 19 , gas low a e = 138 l/h (NTP)). A e he comple ion o he expe imen a 810 °C, he eac o empe a u e was dec eased o 300 °C in he p esence o small N 2 s eam. Then he eac o empe a u e was inc eased again om 300 o 700 °C a he a e o 10 °C/min by adding 10% O 2 in N 2 . The p esence o CO and CO 2 species in he ou le gas s eam du ing he oxida ion o ca alys shows ha he coke o med was no comple ely gasi ied a 810 °C. 2   4 4 2 2 2 2 2 2 422 42 42 XCO, YCO2, YCH4 [C-%] Time on s eam [min] XCO YCO2 YCH4 Resul s and discussion 82 Fig. 5-26: Time on s eam s abili y o ca alys in CO hyd ogena ion a di e en empe a u e (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). E ec o esidence ime on me hana ion 5.2.3 The e ec o he esidence ime on he con e sion o CO and yield o CO 2 and CH 4 o e empe a u e (300 – 800 °C) was s udied a wo di e en gas low a es o 48 l/h and 138 l/h. In bo h cases, a simila end o CO con e sion as well as yield o CO 2 and CH 4 was ob ained. In he low empe a u e ange o 300 o 450 °C, me hane p oduc ion inc eases apidly wi h empe a u e and he eac ion is con olled kine ically. Abo e 450 °C, ca alys deac i a ion due o coke o ma ion may also dec ease CO con e sion and he yield o CH 4 . A a empe a u e o abou 800 °C and a low gas low a e o 48 l/h, he con e sion o CO almos eached equilib ium. The e ec o he esidence ime on he ca alys pe o mance a cons an empe a u e is gi en below (sec ion 5.2.4) in de ail. Resul s and discussion 83 Fig. 5-27: CO con e sion and CO 2 and CH 4 yield a di e en gas low a e e sus empe a u e in CO hyd ogena ion (p = 1 a m, ca alys = Ni/Al 12 O 19 , d p = 6 mm, m ca = 1.2 g, y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 ). The e ec o dec ease in CO con e sion wi h inc easing empe a u e is no he esul o he equilib ium (a leas o T < 700 °C) and also no o a a he slow deac i a ion by coke o ma ion (sees Fig. 5-26 and Fig. 5-27). Hence, he inc ease o he empe a u e ob iously leads o a e e sible deac i a ion o he ca alys o he me hana ion eac ion. This s ong shi in selec i i y wi h empe a u e (less me hane) was also ound in case o CO 2 hyd ogena ion (Fig. 5-4). I mus be no ed ha he wo expe imen s shown in Fig. 5-27 we e done one a e he o he , i.e. he expe imen wi h he lowe low a e (48 l/h) was done a e he expe imen wi h Resul s and discussion 84 138 l/h. In be ween hese expe imen s, he ca alys was only oxidised (coke bu n-o ) and hen educed wi h H 2 (600 °C). In bo h expe imen s, he ac i i y p o ile is simila . Hence, a high empe a u e does no lead an i e e sible deac i a ion and only o a s ong dec ease o he CH 4 selec i i y ( o T > 400 °C). Whe he and o wha ex en his selec i i y shi is induced by he empe a u e and/o by he o ma ion o coke is s ill an open ques ion. E ec o esidence ime a cons an empe a u e 5.2.4 The in luence o modi ied esidence ime on ca alys pe o mance as well as on he yield o CO 2 and CH 4 was measu ed by a ying he o al gas low a e a 405 °C and a mosphe ic p essu e. As shown in Fig. 5-28, he con e sion o CO and he yield o CH 4 and CO 2 inc eases wi h an inc easing modi ied esidence ime. Fig. 5-28: In luence o modi ied esidence ime on CO con e sion and yield o CO 2 and CH 4 in CO hyd ogena ion (T = 405 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 ). In e es ingly he e was no in luence o he modi ied esidence ime (and hus o he CO con e sion) on he selec i i y o CO 2 and CH 4 (Fig. 5-29). The ex apola ion owa ds ze o CO con e sion a ze o esidence ime esul ed in o no change in selec i i y o CH 4 and CO 2 . Hence mos p obably, di ec con e sion o CO o CO 2 (2CO + 2H 2 5 CO 2 + H 2 O) may ake place (pa allel o he CO me hana ion i.e. CO + 3H 2 5 CH 4 + H 2 O). By compa ing he 2  42 4 2  2  2 42 2 2 2 2 2 XCO, YCO2, YCH4 [C-%] Modi ied esidence ime [kg s m-3] XCO YCH4 YCO2 Resul s and discussion 85 con e sion da a ob ained o CO hyd ogena ion (Fig. 5-28) and o CO 2 hyd ogena ion (Fig. 5-7) a 405 °C, i is clea ha he ca alys has a simila ac i i y o CO and CO 2 hyd ogena ion, bu less CH 4 and mo e CO a e ob ained in CO 2 hyd ogena ion compa ed o he CH 4 and CO 2 in he CO hyd ogena ion. Fig. 5-29: CO con e sion e sus selec i i y o CO 2 and CH 4 o e Ni ca alys in CO hyd ogena ion (T = 405 °C, p = 1 a m, 4 m = 10 – 49.7 kg s m -3 , m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 ). E ec o ca alys pa icle size on me hana ion 5.2.5 The pe o mance o he Ni ca alys o a pa icle diame e o less han 0.5 mm and 6 mm o e he empe a u e is shown in Fig. 5-30. Fo bo h sizes o ca alys pa icles a simila end o CO con e sion and yield o CO 2 and CH 4 was ob ained. The con e sion o CO inc eases up o 450 °C and hen con inuously dec eases due o he dec ease o he me hane selec i i y by coke o ma ion and/o inc easing empe a u e. 2 2 2 2 2 422 2  42 4 2  2  SCO2, SCH4 [C-%] XCO [C-%] SCH4 SCO2 Resul s and discussion 86 Fig. 5-30: CO con e sion and CO 2 and CH 4 yield a di e en pa icle size o ca alys e sus empe a u e in CO hyd ogena ion (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). The p e iously used ca alys pa icles o 6 mm diame e in CO 2 hyd ogena ion s udy we e applied in his expe imen . As men ioned in sec ion 5.1.2, he long- ime ea men o his ca alys a high empe a u e educed i s me hana ion ac i i y. The 0.5 mm size ca alys pa icles applied in his expe imen we e used be o e only in he pa icle size e ec s udy in CO 2 hyd ogena ion. The e o e he ca alys pa icles o 0.5 mm ha e a highe ac i i y han he 6 mm pa icles. Due o his eason, in he low empe a u e kine ic egime a highe con e sion o CO and a highe yield o CH 4 was ob ained o e 0.5 mm size ca alys . Hence, Resul s and discussion 87 he di ec compa ison o eac ion a e o e pa icle size wi h di e en ea men is no possible. Kine ic analysis and in luence o in e nal and ex e nal mass ans e on 5.2.6 me hana ion In insic Kine ics The in luence o CO and H 2 concen a ions on he me hana ion is shown in Fig. 5-31 and Fig. 5-32. To de e mine he eac ion o de wi h espec o each eac an , a simila equa ion ha was al eady applied in CO 2 hyd ogena ion (Eq. (5.1)) was used:   F 0 5 § E  |}   ¨    ~   2 £ 5 0 4   |} 8  @ < 0 © @ @  8  (5.4)  The con e sion o CO was measu ed by a ying he espec i e concen a ion o he eac an s CO and H 2 a 340 °C and a mosphe ic p essu e. Fi ing his da a by Eq. (5.4) shows a nega i e eac ion o de o CO (p = -0.3) and a posi i e o de o H 2 (q = 0.7) ( o de ail see Appendix B.1.1). These alues a e in good ag eemen wi h ypical alues epo ed in he li e a u e [97, 98]. Fig. 5-31: E ec o CO concen a ion on he CO con e sion and he CO 2 and CH 4 yield (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 13.2 – 22 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). 2 4     3 3 3 XCO, YCO2, YCH4 [C-%] CCO [mol/m3] 0E 1E 1E2 pCO = 1 pCO = 0 Resul s and discussion 88 Fig. 5-32: E ec o H 2 concen a ion on he CO con e sion and he CO 2 and CH 4 yield (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 11 ol.-%, y H2 = 44 – 66 ol.-%, N 2 = emaining p opo ion, gas low a e = 48 l/h (NTP)). The in insic a e o CO hyd ogena ion eac ion is he e o e gi en as D E  |} F  E  |}   |}  [ ¬    ~  [ u 1 (5.5)  whe e k m,CO is he eac ion a e cons an o CO hyd ogena ion eac ion which can be calcula ed as: E  |} F 2 0 5   4 @   5 0 2 £ 5 0 4   E   |} 8  @    ~     Æ C ADA  ¯ B F 5 Z [ 3 ° F Z [ ± 1 (5.6)  The A henius plo is shown in Fig. 5-33. Only he alues o k m,CO o T < 420 °C a e included whe e he eac ion a e is exclusi ely de e mined by he in insic kine ic. The ac i a ion ene gy E A and equency ac o k m,0 calcula ed om he A henius equa ion (Eq. (4.9)) a e 102 kJ/mol and 2.35 · 10 5 m 1.2 mol 0.6 kg -1 s -1 , espec i ely. The alue o E A ob ained in his s udy (102 kJ/mol) o CO hyd ogena ion (me hana ion) is wi hin he ange ound by o he au ho s using Ni ca alys s (see Table 5-5). 2 4       3 423 43 XCO, YCO2, YCH4 [C-%] CH2 [mol/m3] 0E 1E 1E2 qH2 = 1 qH2 = 0 Resul s and discussion 89 Fig. 5-33: Reac ion a e cons an (1/T e sus ln k m,CO ) o CO hyd ogena ion (p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2 = 66 ol.-%, y CO = 11 ol.-%, es N 2 , gas low a e = 138 l/h (NTP)). Table 5-5: Ac i a ion ene gies epo ed in li e a u e o CO hyd ogena ion on Ni ca alys s. Ca alys Tempe a u e (°C) P essu e (a m) E A (kJ/mol) Re e ences Monoli hic Ni 200 – 350 6.8 104 – 89 [98] 3% Ni/SiO 2 227 – 277 1.38 96 [99] Ni/MgAl 2 O 4 205 – 290 1.4 96.7 [100] 10% Ni/SiO 2 270 – 320 1 112 [101] 1.04Ni/K-Al 2 O 4 339 – 364 1 94  ²  3 [102] 11% Ni (G.90-B) 305 – 345 1 102 This wo k In luence o mass ans e limi a ion The in luence o in e nal mass anspo on he e ec i e eac ion a e o CO hyd ogena ion was de e mined o he shell ca alys as well as non-shell ca alys (6 mm pa icle diame e wi h homogeneous dis ibu ion). Fo ex e nal mass anspo , ex e nal su ace pe mass o 2242 (42 ( ( ( ( ( 23224 23224 23224 232244 23224 23224 T [8C] ln km,CO [m1.2 mol-0.6 kg-1 s-1] 1/T [1/K] T endline in insic eac ion a e cons an EA= 102 kJ/mol Km,o = 2.35 2 105m1.2 mol0.6 kg-1 s-1 Resul s and discussion 96 Fig. 5-38: In luence o modi ied esidence ime on CO con e sion and he yield o CO 2 and CH 4 in wa e gas shi eac ion (T = 405 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2O = 44 ol.-%, y CO = 11 ol.-%, es N 2 ). S abili y o he Ni ca alys in he WGS eac ion 5.3.3 5.3.3.1 Low empe a u e s abili y In he wa e gas shi eac ion, he Ni ca alys beha es di e en ly a di e en empe a u e. No deac i a ion was obse ed below 450 °C, bu he ca alys shows deac i a ion due o coke o ma ion in he empe a u e ange o 450 o 700 °C. So, depending upon his beha iou he ime on s eam s abili y o ca alys was s udied a bo h low and high empe a u es. The low empe a u e ca aly ic s abili y o he Ni/Al 12 O 19 ca alys in he WGS eac ion was es ed o abou 100 min a 340 °C and 450 °C, and a mosphe ic p essu e. Fig. 5-39 shows he con e sion o CO o e he ime on s eam. The Ni/Al 12 O 19 ca alys showed a good s abili y a hese low empe a u es (340 °C and 450 °C). 0 10 20 30 40 0 10 20 30 40 XCO, YCO2, YCH4 [C-%] Modi ied esidence ime [kg4s/m3] T = 405 0C XCO 3 YCO2 YCH4 Resul s and discussion 97 Fig. 5-39: CO con e sion e sus ime on s eam in WGS eac ion a low empe a u e (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , gas low a e = 48 l/h (NTP)). 5.3.3.2 High empe a u e s abili y The ime on s eam beha iou o he Ni ca alys in he high empe a u e ange o 500 °C o 900 °C and a a mosphe ic p essu e o wa e gas shi eac ion is shown in Fig. 5-40. I was di icul o de e mine he amoun o coke o med ia he mog a ime ic analysis because a e y small amoun o coke is o med and he mass loss by bu ning o he coke and he mass gain by ca alys oxida ion akes place simul aneously. The expe imen al p ocedu e was as ollows: A i s , he wa e gas shi eac ion was pe o med a a ce ain empe a u e, e.g. a 500 °C (Fig. 5-40). Then he empe a u e was inc eased o 900 °C, whe e no only he WGS eac ion akes place bu also he gasi ica ion o he coke o med a he low empe a u e expe imen (Fig. 5-41). Fig. 5-40 indica es ha a 900 °C, no coke is o med, i.e. he coke ha may be o med is gasi ied wi h s eam a an app op ia e a e. Hence, he ca alys s used o WGS eac ion a lowe empe a u es o abou 100 min egain hei ac i i y by gasi ica ion, i he empe a u e o 900 °C is adjus ed a e wa ds. This is shown in Fig. 5-41. 2  4   2 2 2 2 2 2 422 42 XCO [C-%] Time on s eam [min] 450 4C 340 4C Resul s and discussion 98 Fig. 5-40: CO con e sion e sus ime on s eam in WGS eac ion a high empe a u es (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , d p = 6 mm, y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , gas low a e = 48 l/h (NTP)). Fig. 5-41: CO con e sion e sus ime on s eam in WGS eac ion a 900 °C a e he lowe empe a u e expe imen s (p = 1 a m, m ca = 1.2 g, d p = 6 mm, y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , ca alys = Ni/Al 12 O 19 , gas low a e = 48 l/h (NTP)). In ano he expe imen , he eshly educed Ni ca alys (800 °C) was applied o 6 h in he eac ion a 650 °C whe e he ca alys shows deac i a ion wi h ime on s eam (Fig. 5-42). Then his used ca alys was oxidised in he same eac o using 5.5 ol.-% O 2 in N 2 by inc easing he empe a u e om 300 o 700 °C a a a e o 10 °C/min. The p esence o CO 2 4 2  2  2 2 2 2 2 422 42 42 XCO [C-%] Time on s eam [min] 500 4C 700 4C 800 4C 600 4C900 4C 2 42 2 2 2 2 2 2 2 2 2 2 422 42 XCO [C-%] Time on s eam [min] 2215E 2215E 2215E 2215E TWGS = 900 4C Resul s and discussion 99 and CO 2 species in he ou le gas s eam du ing oxida ion o ca alys (coke bu ning) we e analysed using a mic o-gas analyse and he amoun o coke o med was quan i ied om he CO 2 p oduced du ing he ca alys oxida ion. The ac i i y o he ca alys was hen eco e ed by oxida ion/ educ ion. The egene a ed ca alys was again used o 3 h and he same p ocedu e was epea ed o con i m he coke o ma ion. Fig. 5-42: Time on s eam s abili y and coke o ma ion o e eshly educed ca alys in WGS eac ion (T = 650 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , ca alys = Ni/Al 12 O 19 , gas low a e = 48 l/h (NTP)). Fig. 5-42 clea ly shows ha he egene a ion by coke bu n-o is possible. The amoun o coke is a he small compa ed o he ca bon (as CO) ha has passed h ough he eac o . Du ing he 6 h expe imen , abou 17 g o ca bon (as CO) ha e en e ed he eac o bu only 0.45 mg o coke was o med. Ne e heless his small amoun o coke is su icien o a s ong deac i a ion o he ca alys , al hough he amoun o coke (0.04 mmol C) is s ill small compa ed o he amoun o Ni (2 mmol), bu a leas in he same o de o magni ude (and no all o he Ni ma e ial is accessible by eac an s). Resul s and discussion 100 Kine ic analysis and in luence o in e nal and ex e nal mass ans e on he WGS 5.3.4 eac ion In insic kine ics The eac ion o de s o he wa e gas shi eac ion wi h espec o eac an and p oduc componen s o e he Ni/Al 12 O 19 ca alys we e de e mined by i ing he expe imen al da a o Eq. (5.8).   F 0 5 § E  |}   ¨    ~ } &    ~ J  |} ~ ³  |} G  @  2 d 5 0 4 < 0 © @ @  G  (5.8)  The espec i e expe imen al esul s a e shown in he Fig. 5-43 o Fig. 5-46. The eac ion o de s wi h espec o eac an CO and H 2 O a e 0.8 and 0.4 while he p oduc s H 2 and CO 2 shows a -0.15 and -0.1 o de dependencies on he eac ion a e o WGS eac ion. (see Appendix B.1.2). Bo h o hese nega i e o de dependencies o p oduc s we e no conside ed in he in insic a e calcula ion. Fig. 5-43: E ec o CO concen a ion on he CO con e sion and he CO 2 and CH 4 yield in WGS eac ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, y H2O = 44 ol.-%, y CO = 5.5 – 14.3 ol.-%, N 2 = es p opo ion, ca alys = Ni/Al 12 O 19 , gas low a e = 48 l/h (NTP)). 2  42 4 2  2 432 434 34 34 XCO, YCO2, YCH4 [C-%] C CO [mol/m3] 0E 1E 1E2 CO = 1 CO = 0 Resul s and discussion 101 Fig. 5-44: E ec o H 2 O concen a ion on he ca alys ac i i y and he CO 2 and CH 4 yield in WGS eac ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, y CO = 11 ol.-%, y H2O = 34 – 54 ol.-%, N 2 = es p opo ion, ca alys = Ni/Al 12 O 19 , gas low a e = 48 l/h (NTP)). Fig. 5-45: E ec o H 2 addi ion in o he eed gas o WGS eac ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y CO = 11 ol.-%, y H2O = 44 ol.-%, y H2 = 0 – 18.75 ol.-%, N 2 = es p opo ion, gas low a e = 48 l/h (NTP)). 2  42 4 2  2 3 3 4232 XCO, YCO2, YCH4 [C-%] CH2O [mol/m3] 0E 1E 1E2 sH 2 O = 0 sH2O = 1 2    4 4 4 4  2 43 3 3 XCO, YCO2, YCH4 [C-%] C H2 [mol/m3] 0E 1E 1E2 uH2= 0 Resul s and discussion 102 Fig. 5-46: E ec o CO 2 addi ion in o he eed gas o WGS eac ion (T = 340 °C, p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y CO = 11 ol.-%, y H2O = 44 ol.-%, y CO2 = 0 – 16.67 ol.-%, N 2 = es p opo ion, gas low a e = 48 l/h (NTP)). The in insic eac ion a e o WGS eac ion has been calcula ed as D E  |} F  E  |}   |}  [ n    ~ }  [ F  E    A    !"   |}  [ n    ~ }  [ 1 (5.9)  whe e k m,CO is he eac ion a e cons an o WGS eac ion which can be calcula ed as: E  |} F 2 0 5   4 @   [ n 5 0 2 Z [ K 5 0 4   E   |}  [ n  @    ~ }  [ 1 (5.10)  The empe a u e dependency o k m,CO is shown in Fig. 5-47. To de e mine he in insic kine ic, only he alues o k m,CO o T < 345 °C a e included whe e no mass anspo o he modynamic limi a ions occu . The equency ac o k m,0 and appa en ac i a ion ene gy o eac ion E A a e 3.46 · 10 5 m 3.6 mol -0.2 kg -1 s -1 and 96 kJ/mol, espec i ely. The ac i a ion ene gy da a epo ed in li e a u e o he wa e gas shi eac ion o e Ni con aining ca alys is gi en in Table 5-7. The alue o E A (96 kJ/mol) ob ained in his s udy is wi hin he ange ound by o he au ho s. 2    4 4 4 4  2 43 3 3 XCO, YCO2, YCH4 [C-%] C CO2 [mol/m3] 0E 1E 1E2 CO2= 0 Resul s and discussion 103 Fig. 5-47: Reac ion a e cons an (1/T e sus ln k m,CO ) o he WGS eac ion (p = 1 a m, m ca = 1.2 g, d p = 6 mm, ca alys = Ni/Al 12 O 19 , y H2O = 44 ol.-%, y CO = 11 ol.-%, es N 2 , gas low a e = 48 l/h (NTP)). Table 5-7: Ac i a ion ene gies epo ed o wa e gas shi eac ion on nickel ca alys s. Ca alys Temp (°C) P essu e (a m) E A (kJ/mol) Re . 5% Ni/Al 2 O 3 monoli h 300 – 1000 1 85 [104] 5% Ni/5% Ce/Al 2 O 3 monoli h 300 – 1000 1 85 [104] 5 a .% Ni/Ce(10% La)O x 275 – 300 1 38 [105] Black NiO 200 – 300 1 96 ²  p [106] G een NiO 200 – 300 1 89 ²  p [106] 11% Ni (G.90-B) 305 – 345 1 96 This wo k In luence o mass anspo To de e mine he in luence o mass anspo on he e ec i e eac ion a e o wa e gas shi eac ion, all he calcula ions we e made by using he equa ions om sec ion 4.4.1. Simila o 22422222 ( (3 ( (3 ( (3 ( (3 ( 232242 23224 23224 23224 23224 23224 T [8C] ln km,CO [m3.6 mol-0.2 kg-1 s-1] 1/T [1/K] EA= 96 kJ/mol km,0 = 3.46 61105m3.6 mol-0.2 kg-1 s-1 T endline in insic eac ion a e cons an Resul s and discussion 104 CO 2 and CO hyd ogena ion, he in luence o mass ans e in WGS eac ion was calcula ed o bo h shell ca alys ( hickness o 0.5 mm) and non-shell ca alys (d p = 6 mm). The e ec i e eac ion a e due o he in luence o bo h in e nal and ex e nal mass anspo was calcula ed as: d E  #$$ F  e 0 %  E  |}   |}   [ n   ~ }  [ < 0 R  g E  #T  U   5    ª« W h  @ 1 (5.11)  The model pa ame e s equi ed in he calcula ion o e ec i e eac ion a es o wa e gas shi eac ion a e gi en in Table 5-8. The de ailed po e di usion calcula ion o Ni/Al 12 O 19 ca alys is gi en in appendix B.2 (Fig. B-8). Table 5-8: Model pa ame e s used o he calcula ion o e ec i e eac ion a e o he wa e gas shi eac ion o e Ni ca alys (p = 1 a m). Pa ame e s Values F equency ac o (k m,0 ) 3.46 · 10 5 m 3.6 mol -0.2 kg -1 s -1 Ac i a ion ene gy (E A ) 96 kJ/mol Pa icle densi y (6 p ) 1910 kg/m 3 Po osi y o pa icle (4 p ) 0.33 To uosi y o pa icle A p (assump ion) 1.65 Molecula di usion coe icien o CO (D CO,mol ) a 773 K 1.07 · 10 -4 m 2 /s Knudsen di usion coe icien (D CO,knu ) a 773 K 5.86 · 10 -5 m 2 /s Po e di usion coe icien (D CO,po e ) a 773 K 3.78 · 10 -5 m 2 /s Kinema ic iscosi y o CO (7 CO ) a 773 K 8.17 · 10 -5 m 2 /s In he wa e gas shi eac ion, he in luence o po e di usion on he e ec i e eac ion a e was e alua ed om e ec i eness ac o 6. Fig. 5-48 shows he e ec i eness ac o e sus empe a u e o he shell as well as o a hypo he ic non-shell ca alys . Fo bo h ca alys s he e ec i eness ac o dec eases s ongly wi h inc easing empe a u e close o 345 °C. Fig. 5-49 compa es he e ec i e eac ion a es (conside ing 6 = 1 and wi h ac ual 6). The e is a clea in luence o po e di usion o bo h he shell and non-shell ca alys . Resul s and discussion 105 Fig. 5-48: E ec i eness ac o o ca alys e sus empe a u e (p = 1 a m, m ca = 1.2 g, ca alys = Ni/Al 12 O 19 , y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , gas low a e = 48 l/h (NTP)). Fig. 5-49: In luence o in e nal and ex e nal mass anspo on he e ec i e eac ion a e o WGS eac ion (p = 1 a m, m ca = 1.2 g, y CO = 11 ol.-%, y H2O = 44 ol.-%, es N 2 , ca alys = Ni/Al 12 O 19 , gas low a e = 48 l/h (NTP)). 23224 2324 234 4 22 22 22 22 22 22 E ec i eness ac o (1) Tempe a u e [8C] po e di usion egion *D197D8 6A1#911""$ C"'AA3!1!8D438 *D197D8 6A1*1231"" !CA6618C &A!!11 Resul s and discussion 112 Fig. 5-51: Axial p o iles o CO 2 con e sion o he Ni/Al 12 O 19 ca alys and h ee di e en cases (Eq. (5.19);  E|}~ » R », and egula model (H 2 /CO 2 = 3). The simula ed adiaba ic empe a u e p o iles a di e en gas supe icial eloci ies along he axial eac o coo dina e a e shown in Fig. 5-52 bo h o Ni/Al 12 O 19 and Al 2 O 3 as ca alys . The eac ion empe a u e dec eases along he leng h due o he p e ailing endo he mic Resul s and discussion 113 RWGS eac ion, i.e. he ene gy consump ion by he eac ion leads o a cooling o he gas. Fo an inle gas empe a u e o 1200 °C and he highes supe icial gas eloci y o 15 m/s (a T 0 ), he adiaba ic inal empe a u e o 998 °C is eached a a eac o leng h o abou 0.4 m o he Ni ca alys and a abou 25 m o he Al 2 O 3 ca alys . The espec i e esidence imes ( ela ed o he emp y ube) a e only abou 30 ms o he Ni ca alys and abou 2 s o he Al 2 O 3 . Fo lowe gas eloci ies, he equi ed leng hs (and esidence imes) a e smalle . Fig. 5-52: Axial empe a u e p o iles o an adiaba ic eac o o Ni/Al 12 O 19 and Al 2 O 3 as ca alys s (H 2 /CO 2 = 3). Simila ly, he axial p o iles o he CO 2 con e sion a e shown in Fig. 5-53 o he simula ed adiaba ic and iso he mal case bo h o he Ni and Al 2 O 3 ca alys . The con e sion o CO 2 and Resul s and discussion 114 hus he yield o CO inc eases along he eac o leng h and eaches he maximum (equilib ium) alue a he eac o ou le . As he gas supe icial eloci y inc eases, he eac o leng h equi ed o each he equilib ium also inc eases. As al eady s a ed, an inc easing gas eloci y also inc eases he equi ed leng h o he eac o o each (almos ) he inal equilib ium alue. Fo he Ni ca alys and an inle empe a u e o 1200 °C, an inc ease om 0.5 m/s o 15 m/s leads o an inc ease o he eac o leng h om abou 0.013 m o 0.4 m o he adiaba ic eac o and om 0.01 m o 0.3 m o he iso he mal eac o . Fig. 5-53: Con e sion o CO 2 o e Ni/Al 12 O 19 and Al 2 O 3 ca alys s a di e en gas supe icial eloci ies e sus axial eac o co-o dina e (H 2 /CO 2 = 3). The con e sion o CO 2 o CO ob ained a he eac o ou le is abou 82% o he adiaba ic eac o and 87% o he iso he mal eac o . Resul s and discussion 115 Fig. 5-54 shows he con e sion o CO 2 along he eac o leng h a di e en H 2 /CO 2 a ios o he adiaba ic and iso he mal simula ion (again bo h o he Ni and Al 2 O 3 ca alys ). As he a io H 2 /CO 2 inc eases, he con e sion o CO 2 aises along he eac o leng h. Fo example, i he inle a io o H 2 /CO 2 is inc eased om 1 o 6, he con e sion o CO 2 a he eac o ou le inc eases om abou 55% o 91% o he adiaba ic eac o and om 62% o 93% o he iso he mal eac o . Bu high inle H 2 /CO 2 a ios also inc ease he H 2 /CO a io o he p oduced syngas, which hen may no be op imal o a subsequen Fische T opsch syn hesis. The H 2 /CO a io o he syngas a he eac o ou le (R syngas ) o di e en H 2 /CO 2 a ios o he eed o he RWGS eac o is shown in Fig. 5-55. Fig. 5-54: Con e sion o CO 2 o e Ni/Al 12 O 19 and Al 2 O 3 ca alys s a di e en inle gas composi ion e sus axial eac o co-o dina e (u s = 15 m/s, R = H 2 /CO 2 ). Resul s and discussion 116 Fig. 5-55: Mola H 2 /CO a io o he syngas (R syngas ) a he eac o ou le o di e en mola H 2 /CO 2 a ios o he eed (R eed ) o he RWGS eac o (p = 1 ba ). Fig. 5-55 indica es ha an almos op imal H 2 /CO a io o he syngas o sligh ly abo e wo ( o accoun o he me hana ion, which always akes place du ing Fische T opsch) is eached o a H 2 /CO 2 a io o he eed o abou h ee. This a io was he e o e used o u he simula ions. As men ioned be o e, he eac o leng h equi ed o ge a pa icula con e sion depends upon he gas inle empe a u e, he gas supe icial eloci y, and he inle gas composi ion. Fo he RWGS eac ion o e he Ni/Al 12 O 19 ca alys (inle empe a u e o 1200 °C, inle H 2 /CO 2 a io o 3), he eac o leng h equi ed o each 99% o he equilib ium con e sion in he adiaba ic and iso he mal case is shown in Fig. 5-56. Fig. 5-57 shows he simila pa e n o Al 2 O 3 ca alys . As he e ec i e a e o he RWGS eac ion o e Al 2 O 3 is by abou a ac o o 40 lowe compa ed o he Ni ca alys , he eac o leng h equi ed is much highe compa ed o Ni/Al 12 O 19 ca alys o ge he same con e sion. 2 4       4 Rsyngas = H2/CO ( eac o ou le ) R eed = H2/CO2 Iso he mal Adiaba ic T0= 1200 4C T0= 1000 4C Resul s and discussion 117 Fig. 5-56: Reac o leng h equi ed o 99% o equilib ium con e sion in adiaba ic eac o (X CO2 = 81%) and iso he mal eac o (X CO2 = 86%) e sus supe icial gas eloci y o e Ni/Al 12 O 19 ca alys (H 2 /CO 2 = 3, p = 1 ba ). Fig. 5-57: Reac o leng h equi ed o 99% o equilib ium con e sion in adiaba ic eac o (X CO2 = 81%) and iso he mal eac o (X CO2 = 86%) e sus supe icial gas eloci y o e Al 2 O 3 ca alys (H 2 /CO 2 = 3, p = 1 ba ). Resul s and discussion 118 P essu e d op in ixed bed echnical RWGS eac o s 5.4.3 Acco ding o E gun [107], he p essu e loss in a ixed (packed) bed is gi en by z B a F e / a  7  8  : $  * & P = h 1 (5.27)  whe e : $ is he densi y o he luid (kg/m 3 ), / a he ic ion ac o o a packed bed, which is gi en by he ollowing equa ion based on he pa icle Reynolds numbe , 9AF* &  8 Oc: / a F 2 0 5 ¼ a 4 ¼ a u 1 3 [ ` < 2 0 5 ¼ a 4 3ZZ 9A 6 1 (5.28)  Fo non-sphe ical pa icles an equi alen pa icle diame e is used  8 F e  Y  6 8 S E  #T h 1 (5.29)  which is he diame e o a sphe e wi h he same ex e nal su ace a ea pe uni olume as he ac ual pa icle. Fo a packed bed o sphe es (equal diame e , po osi y ¼ a = 0.4), Eq. (5.28) simpli ies o / a F 33 < 0 ZZ 9A 1 (5.30)  The pa icle diame e and he luid eloci y ha e a s ong in luence onzB a . As we can see by inse ion o Eq. (5.30) in o Eq. (5.27), 1B a is p opo ional o * & O 8 P o low alues o 9Aand o * &P O 8 o high alues. The p oduc ion o syngas by CO 2 hyd ogena ion would mos p obably been done a he ypical p essu e o he subsequen p oduc ion o liquid uels ia Fische T opsch syn hesis. Hence, a o al p essu e o 30 ba , a maximum p essu e d op o 1 ba , and an inle empe a u e o 1200 °C a e assumed o he inal simula ion o a echnical RWGS eac o . In addi ion, only adiaba ic ope a ion is subsequen ly conside ed, as his ype o ope a ion is much easie o ealize in a echnical eac o compa ed o iso he mal ope a ion. The luid densi y and iscosi y a e calcula ed a 1100 °C (a e age empe a u e in adiaba ic eac o ). Values o he equi ed pa ame e s o calcula e zB a a e gi en in Table 5-11. Fig. 5-58 shows ha he p essu e d op pe me e leng h s ongly inc eases wi h inc easing supe icial gas eloci y. In case o he Al 2 O 3 ca alys and an adiaba ic ixed bed eac o , he supe icial gas Resul s and discussion 119 eloci y should be less han 1.7 m/s o limi he p essu e d op o he assumed alue o 1 ba . The eac o leng h is hen 2.8 m ( o ge 99% o he equilib ium con e sion) (Fig. 5-57). A his eloci y, zB a O7 is abou 0.38 ba /m and so 1B a D 1 ba o e he o al eac o leng h. In case o he Ni/Al 12 O 19 ca alys and a same supe icial gas eloci y o 1.7 m/s, a eac o leng h o 0.05 m (Fig. 5-56) would be su icien and zB a would only be abou 0.02 ba . The espec i e gas eloci y o he Ni/Al 12 O 19 ca alys , whe e he assumed limi ing alue o zB a o 1 ba is eached, is 6.7 m/s ( eac o leng h o 0.18 m). Table 5-11: Model pa ame e s used o calcula e he p essu e d op o a RWGS eac o . Pa ame e s (30 ba , 1100 °C) Values Kinema ic iscosi y (7), m 2 /s 6 · 10 -6 Fluid densi y (3 ), kg/m 3 4.65 Pa icle diame e (d p ), m 0.006 Pa icle Reynolds numbe (Re) a u s = 1 m/s 1000 F ic ion ac o ( b ) a u s = 1 m/s 34.7 Fig. 5-58: P essu e d op in ixed bed eac o pe me e leng h o di e en supe icial gas eloci ies. 23224 2324 234 4 42 422 234 4 42 5pb/L [ba /m] Supe icial gas eloci y, us[m/s] T = 1100 4C p = 30 ba 5pb 31 ba (Al2O3) 5pb 30.02 ba (Ni/Al12O19) 5pb 31 ba (Ni/Al12O19) Resul s and discussion 120 Es ima ion o he size o he RWGS eac o wi h ega d o a subsequen Fische 5.4.4 T opsch ixed bed eac o I is in e es ing o es ima e he size o an adiaba ic RWGS eac o (bo h o he in es iga ed Ni- and he Al 2 O 3 ca alys ) needed o a subsequen Fische -T opsch (FT) eac o . Acco - ding o he da a gi en by Jess and Ke n [48], he pa ame e s o a echnical FT eac o a e as ollows: o The FT eac o is a mul i ubula eac o wi h 8000 ubes each wi h a diame e o 5 cm. o The o al olume a e o esh (d y) syngas is abou 160,000 m 3 /h (NTP). o The o al p essu e is a ound 30 ba . The eac o leng h equi ed o ge 99% o he equilib ium con e sion o CO 2 is calcula ed as 7 mm  ½|} P  # F 7   * & 111111111111(i: Ni- o Al 2 O 3 -ca alys )1 (5.31)  And he leng h o each a ce ain zB a (in his calcula ion zB a = 1 ba ) as 7 z 8 ¾ F =  z B a   8 / a  : $   * & P 1 (5.32)  Fo he es ima ion o he design o he adiaba ic RWGS eac o , he ollowing assump ions we e made: o Fo he assumed olume a e o d y syngas o 160,000 m 3 /h (NTP), he olume a e h ough he RWGS eac o is 201,000 m 3 /h (NTP), because o a CO 2 con e sion o 81% ( eached in adiaba ic ope a ion) 20% o he syngas is wa e , which is sepa a ed. A a mean empe a u e o 1100 °C and 30 ba , his co esponds o 34,000 m 3 /h (= 9.4 m 3 /s). o Fo he Ni/Al 12 O 19 ca alys , he esidence ime equi ed o ge 99% o he equilib ium con e sion o CO 2 is 0.027 s (see Fig. 5-56); he espec i e alue o he Al 2 O 3 ca alys is 1.65 s (see Fig. 5-57). (Rema k: Po e di usion is only de e mined by Knudsen di usion. Hence, he e is p ac ically no in luence o he o al p essu e on he e ec i e eac ion a e (cons an ) and hus also no on he equi ed esidence ime.) o Fo he p essu e d op in he RWGS eac o a limi ing alue o 1 ba is assumed. The dimensions o he ixed bed o he RWGS eac o a e hen es ima ed as ollows. (a) Ni/Al 12 O 19 ca alys : A a supe icial gas eloci y o 6.7 m/s, he eac o leng h equi ed o ge he 99% o he equilib ium con e sion o CO 2 is 0.18 m and he assumed p essu e Resul s and discussion 121 d op o 1 ba is also jus eached (Fig. 5-59). As his leng h is a he small, a leng h o 0.5 m can be assumed o be app op ia e ( o be on he sa e side wi h ega d o bypass e ec e c.), e en i he p essu e d op hen inc eases o 2.5 ba . The c oss-sec ional a ea o he RWGS eac o is 1.4 m 2 ( a io o olume a e o 9.4 m 3 /s and gas eloci y o 6.7 m/s), he eac o diame e 1.3 m, and he olume o he ca alys is 0.7 m 3 . Fig. 5-59: Reac o leng h e sus supe icial gas eloci y: dashed-do ed line: leng h, whe e a p essu e d op o 1 ba is jus eached; lines: leng h equi ed o each 99% o equilib ium con e sion (X CO2 = 81%). (b) Al 2 O 3 ca alys : Now a lowe supe icial gas eloci y o 1.7 m/s has o be adjus ed o each 99% o he equilib ium con e sion o CO 2 and also a p essu e d op o 1 ba (Fig. 5-59). The co esponding leng h o he ixed bed is abou 2.8 m, and he c oss- sec ional a ea 5.5 m 2 (2.6 m diame e ). Inc easing he eac o leng h by 1 m ( o al leng h o 3.8 m) o be on he sa e side hen co esponds o a olume o he Al 2 O 3 ca alys o abou 21 m 3 , which is by a ac o o 30 highe compa ed o he Ni-ca alys . These es ima ions clea ly show ha o bo h ca alys s, he equi ed olume is a he small o deli e he syngas o a huge echnical FT eac o . The ques ion, whe he he Ni- o he Al- ca alys should be used is hen a ques ion o he cos s o he ca alys and e en mo e impo an o he long e m s abili y o he ca alys , which should be de e mined by u he in es iga ions. 234 4 42 2     42 Reac o leng h [m] Supe icial gas eloci y, us[m/s] 5pb= 1 ba Al2O3 5pb= 1 ba Adiaba ic eac o 5pb= 1 ba Ni/Al12O19 Zusammen assung und Ausblick 128 In de o liegenden A bei wu de de d i e Sch i , die RWGS-Reak ion, un e such . Dabei wu de o allem ein aluminiumoxidge äge e Nickelka alysa o (Ni/Al 12 O 19 ) e wende . Da die RWGS-Reak ion endo he m e läu , wu de die Reak ion bei hohen Tempe a u en du chge üh , um CO (und H 2 O) als Haup p oduk e zu e hal en. Übe sich zu den expe imen ellen Un e suchungen: Die expe imen ellen Un e suchungen alle Teilsch i e (Me hanisie ung, Wasse -Gas-Shi bzw. RWGS) wu den in einem Fes - be eak o un e Ve wendung des oben genann en Nickelka alysa o s bei No mald uck du chge üh . Neben de Tempe a u wu den auch die Konzen a ionen de Reak an en, die Ve weilzei und die Ka alysa o pa ikelg öße a iie . Fü jede Reak ion e olg e eine Bes immung sowohl de in insischen als auch de e ek i en Reak ionskine ik. Neben dem Nickelka alysa o wu den auch ande e Ka alysa o en wie z.B. Al 2 O 3 ge es e . Die expe imen ellen E gebnisse lassen sich olgende maßen zusammen assen. CO 2 -Hyd ie ung: Zunächs wu den e schiedene komme zielle Ka alysa o en un e such (siehe Tab. 5-4), um ein g undsä zliches Ve s ändnis ü die Ak i i ä de Ka alysa o en ü die CO 2 -Hyd ie ung zu e hal en. Hie bei zeig e de Ni/Al 12 O 19 -Ka alysa o die höchs e Ak i i ä . Dahe wu den die wei e gehenden kine ischen Un e suchungen zu CO 2 - Hyd ie ung mi diesem Ka alysa o du chge üh . E wa ungsgemäß e höhen sich de CO 2 -Umsa z und die CO-Ausbeu e mi s eigende Tempe a u (300 – 950 °C). Bis zu eine Tempe a u on 500 °C s eig zunächs auch die Me hanausbeu e an, um dann au g und de he modynamischen Limi ie ung wiede abzu- allen. Bei hohen Tempe a u en wu den Umsä ze e ziel , die seh nahe am Gleichgewich liegen. So konn e beispielsweise bei 950 °C ein Umsa z on 94 % des Gleichgewich s- umsa zes e hal en we den (lee oh bezogene Ve weilzei : 18 ms). Die Pa ikelg öße wu de mi wenige als 0,5 mm so gewähl , dass de äuße e S o anspo keinen Ein luss ha . De Nickelka alysa o zeig e bei 900 °C zudem eine seh gu e Langzei s abili ä . Die Be echnung de in insischen kine ischen Pa ame e e gab eine Ak i ie ungsene gie on 65 kJ/mol und einen Häu igkei s ak o on 5,55 · 10 2 m 1,5 mol 0,5 kg -1 s -1 . Die Reak ions a e de CO 2 - Hyd ie ung kann du ch olgenden Ansa z besch ieben we den: D E  | } ~ F  E  | } ~   |} ~   @    ~   1 2 ¿ 04  Zusammen assung und Ausblick 129 Die Be echnung des S o anspo ein lusses au die e ek i e Reak ions a e de CO 2 -Hy- d ie ung zeig , dass die expe imen ellen und be echne en E gebnisse gu übe eins immen. Bei dem e wende en Schalenka alysa o (Du chmesse 3 mm, Schich dicke 0,5 mm) beein- luss sowohl die Po endi usion als auch de ex e ne S o anspo die e ek i e Reak ions- a e. Bei den expe imen ell einges ell en ge ingen Gasgeschwindigkei en wi d die Ka aly- sa o leis ung obe halb on 900 °C zunehmend du ch den ex e nen Massen ans e bes imm . CO-Hyd ie ung (Me hanisie ung): Die Me hanisie ung is exo he m und somi bei nied igen Tempe a u en he modynamisch begüns ig . Dahe s eig de CO-Umsa z mi wachsende Tempe a u an, um ab ca. 450 °C schließlich zu allen. Zwischen 480 und 710 °C deak i ie de Ka alysa o au g und de hie einse zenden Koksbildung. Die Reak ionso dnungen wu den bei 340 °C und A mosphä end uck bes imm . Fü CO e gib sich ein We on -0,3 und ü Wasse s o on 0,7. Die Ak i ie ungsene gie be äg 102 kJ/mol und de Häu igkei s ak o ha einen We on 2,35 · 10 5 m 1,2 mol 0,6 kg -1 s -1 . Die Be echnungen zum S o anspo lassen ü den Schalenka alysa o einen Ein luss de Po endi usion obe halb on 420 °C e wa en. Die be echne en We e de e ek i en Reak ions a e weichen alle dings bei hohen Tempe a u en on den expe imen ellen We en ab. Dies is au die dann au e ende Deak i ie ung des Ka alysa o s zu ückzu üh en. Wasse -Gas-Shi Reak ion (WGS): Die WGS-Reak ion wu de eben alls un e such , da es sich hie um die Rück eak ion de CO 2 -Hyd ie ung (RWGS) handel . Die Haup p oduk e de WGS-Reak ion sind dahe Wasse s o und Kohlendioxid. Diese Reak ion is exo he m und wi d olglich bei nied igen Tempe a u en he modynamisch begüns ig . Bis zu eine Tempe a u on 450 °C e höhen sich sowohl de CO-Umsa z als auch die CO 2 - Ausbeu e. Gleichzei ig konn e in dem un e such en Tempe a u ens e wede eine Me hanbildung noch eine Deak i ie ung des Ka alysa o s beobach e we den. Im Tempe a u be eich on 500 bis 700 °C zeig de Nickelka alysa o eine Deak i ie ung, die du ch eine Ve kokung des Ka alysa o s he o ge u en wi d. Die Zugabe beide Reak an en (CO, H 2 O) üb einen posi i en Ein luss au die WGS- Reak ion aus, wäh end (wie zu e wa en) die Beimischung de P oduk e (CO 2 , H 2 ) einen nega i en Ein luss au die Reak ions a e au weis . Die Bes immung de Reak ionso dnung ü die einzelnen Komponen en e gab: 0,8 (CO), 0,4 (H 2 O), -0,1 (CO 2 ) und -0,15 (H 2 ). Die Bildung on Me han and im un e such en Pa ame e be eich nu un e geo dne s a . Zusammen assung und Ausblick 130 Die Ak i ie ungsene gie de WGS-Reak ion (Ni-Ka alysa o ) be äg 96 kJ/mol. De We des Häu igkei s ak o s lieg bei 3,46 · 10 5 m 3,6 mol -0,2 kg -1 s -1 . S o anspo be echnungen ü den Schalenka alysa o zeigen obe halb on 350 °C einen Ein luss de Po endi usion. Beding du ch eine Ka alysa o deak i ie ung nimm die e ek i e Reak ions a e im Tempe a u be eich zwischen 500 und 700 °C ab. Obe halb on 900 °C wi d die e ek i e Reak ionsgeschwindigkei meh und meh du ch den ex e nen Massen ans e bes imm . Zu Modellie ung eines echnischen Reak o s zu He s ellung on Syn hesegas du ch die CO 2 -Hyd ie ung wu de ü beide Ka alysa o en (Ni/Al 12 O 19 ; Al 2 O 3 ) das Modell eines ein- dimensionalen Fes be eak o s e wende , d.h. die axialen Tempe a u - und Umsa z-P o ile wu den be echne . Dabei wu de de adiaba e und auch de iso he me Fall be ücksich ig . Die e ek i e Reak ions a e de RWGS-Reak ion am Ni/Al 12 O 19 -Ka alysa o is im Ve - gleich zum Al 2 O 3 -Ka alysa o um den Fak o 40 höhe . Fü einen gegebenen Umsa z kann die Reak o länge ü den Ni-Ka alysa o en sp echend wesen lich kü ze gewähl we den. Ausblick Ausgehend on den in diese A bei e hal enen E gebnissen soll en in wei e üh enden Un e suchungen sowohl ü den Ni-Ka alysa o als auch ü den Al 2 O 3 -Ka alysa o ih e Langzei s abili ä en un e such we den. Hie zu sind Ve suchszei en on einigen Wochen anzus eben, um aussagek ä ige Da en zu gene ie en. Wei e hin soll en Tempe a u en on meh als 1000 °C einges ell we den, da dann de e eichba e CO 2 -Umsa z bei de RWGS allein schon aus he modynamischen G ünden noch höhe is (> 90%). Hie zu muss die bes ehende Ve suchsanlage mi einem Reak o , de diesen Tempe a u en s andhäl , sowie einem en sp echenden Heizsys em ausges a e we den. Appendix A 131 Appendix A A.1 U iliza ion o CO 2 in ca aly ic con e sion p ocesses The de ailed desc ip ion o he syn hesis o alue added p oduc s using CO 2 is gi en in his sec ion. A.1.1 Salicylic acid o ma ion The di ec syn hesis o salicylic acid ia he coupling o CO 2 wi h phenol is a “g een p ocess”, use ul o he chemical ixa ion o CO 2 . Salicylic acid is widely used in he indus y as a aw ma e ial and in e media e o he p oduc ion o pha maceu ical and ine chemicals.  x j ¡ ij  <   i P  À   x j 2 ij 4 iij 1 2g ¿ 04  Salicylic acid can be ob ained by ca boxyla ion o phenol wi h a ca bon dioxide in p esence o Lewis acid ca alys s. AlB 3 as a ca alys showed he bes ac i i y and selec i i y owa ds salicylic acid among he a ious Lewis acids examined [108]. A 80 °C and 8 MPa, he yield o salicylic acid eached o 60% wi h he selec i i y o 100% in 1 h. Se e al ypes o base me al oxides such as alumina, zi conia, ce ia, and alkali me al and alkaline ea h me al sal s ha e been used o he syn hesis o salicylic acid [109, 110]. Po assium ca bona e as a ca alys unde op imum condi ion yields 68% o salicylic acid wi h 99% selec i i y. The sys ema ic in es iga ion o he di ec eac ion o supe c i ical CO 2 and phenol o e he ca alys s like Z O 2 , TiO 2 , and KF/NaY+Mn 2+ , Z O 2 was in es iga ed [1]. A.1.2 Syn hesis o u ea and u ea de i a i es The p ocess o u ea syn hesis om ca bon dioxide and ammonia was de eloped in 1922, and is called he Bosch-Meise u ea p ocess. This non-ca aly ic p ocess s ill exis s and ope a es a ela i ely high p essu e and high empe a u e. = Á j u  <   i P  À  j P ÁiiÁ j 1 2g ¿ =4  j P ÁiiÁ j  À  Á j P i Áj P <  j P i 1 2g ¿ 34  Appendix A 132 The p oduc ion o u ea in ol es o ma ion o ammonium ca bama e (NH 2 COONH 4 ) using ammonia and CO 2 . Ammonium ca bama e subsequen ly ge s dehyd a ed in o u ea and wa e by he applica ion o hea . The i s eac ion is as , exo he mic, and basically goes o comple ion, while he second one is ela i ely slow, endo he mic, and does no go o comple ion [111]. Bo h o hese eac ions a e e e sible and he e o e ammonia and ca bon dioxide exi he eac o along wi h ammonium ca bama e and u ea. Thus, he con e sion based on CO 2 is usually in he o de 50 o 80% [111]. The componen s o his mix u e in he p oduc s eam a e hen sepa a ed by s ipping o gaseous ammonia ollowed by ca bon dioxide. The wo ldwide u ea p oduc ion in 2008 was 146 million me ic ons which co esponds o 107 million me ic ons o CO 2 consump ion pe annum [112]. Hence in he chemical indus y, only his p ocess has a ce ain po en ial o CO 2 educ ion. U ea is mainly used o e ilize s bu u ea de i a i es a e used in he a ious o he a eas such as ag ochemicals, pha maceu icals, an ioxidan s in gasoline, and co osion inhibi o s [113]. Comme cially u ea de i a i es a e syn hesised by using oxic phosgene as well as ca bon monoxide. In a new app oach, u ea de i a i es a e p oduced by using amines and CO 2 as a ca bonyl agen ia ca aly ic and non-ca aly ic p ocesses. The ca bonyla ion o amines using CO 2 is simple, sa e, and a clean p ocess which a oids he use o poisonous compounds like phosgene and CO [114, 115]. The eac ion o CO 2 wi h p ima y alipha ic amines also leads o u ea de i a i e [114]. The p ocess using he ionic liquid [Bmim]Cl wi h CsOH as ca alys yields abou 98% o an u ea de i a i e [115]. A.1.3 S y ene syn hesis Comme cially s y ene is p oduced by e hylbenzene dehyd ogena ion using po assium p omo ed i on oxide as a ca alys wi h a la ge excess o supe hea ed s eam a 600 o 650 °C. The s eam plays an impo an ole in e hylbenzene dehyd ogena ion as i shi s he equilib ium owa ds highe con e sions, dec eases he amoun o coke o ma ion and supply he hea o he eac ion. A new ou e uses ca bon dioxide o he dehyd ogena ion: Appendix A 133 Con en ional ou e: 1 2g¿p4 New CO 2 -based ou e: 1 2g¿`4 The ca aly ic con e sion o e hylbenzene using CO 2 ha e been discussed ecen ly by Pa k e al. [116]. The di ec u iliza ion o CO 2 as an oxidan in he dehyd ogena ion o e hylbenzene o s y ene o e s se e al ad an ages. The main ad an ages shown in di e en s udies [117-119] a e he accele a ion o he eac ion a e, he d op in empe a u e, he enhancemen o he con e sion o e hylbenzene and o he selec i i y. Mo eo e , he ene gy consump ion o he e hylbenzene dehyd ogena ion using ca bon dioxide is much lowe han he cu en ly ope a ing p ocess using s eam [116]. The dehyd ogena ion o e hylbenzene o s y ene in he p esence o CO 2 was also s udied o e MnO 2 -Z O 2 [117], SnO 2 –Z O 2 mixed oxide nano-composi e [118], c omia based ca alys [119], Co, Mo and CoMo ca alys s suppo ed on na u al and aluminium-pilla ed clays [120], and a CeO 2 –Z O 2 mixed oxide suppo ed SBA-15 ca alys [121]. In hese ca aly ic sys ems, acidic and basic si es coope a i ely ac i a e CO 2 as well as e hylbenzene, which lead o a highe con e sion o e hylbenzene. An a emp o use CO 2 as a diluen and oxidan o e an ac i a ed ca bon-suppo ed i on ca alys ha e made by Sugino e al. [122]. The addi ion o 20 o 30 mol% li hium ni a es o he i on ca alys esul ed in a signi ican inc ease in he ca aly ic ac i i y. A.1.4 Dime hyl ca bona e (DMC) syn hesis The con en ional DMC syn hesis use oxic phosgene. The use o ca bon dioxide in he syn hesis o DMC p esen s an en i onmen ally iendly and a ac i e app oach since i eplaces phosgene and chlo ine [123, 124]. Appendix A 134 Con en ional ou e:  i + P  <  = j u ij   j u iii j u  <  = j+  2g ¿ Y4  New CO 2 -based ou e: i P  <  = j u ij   j u iii j u  <  j P i  2g ¿ 4  DMC has been syn hesized using CO 2 and me hanol o e solid oxide ca alys s like Z O 2 [125, 126]. The dissocia i e adso p ion o CO 2 occu s as e han he adso p ion o me hanol on Z O 2 and species o med om me hanol a e bound mo e s ongly. DMC also has been syn hesized using base ca alys s like K 2 CO 3, Na 2 CO 3, Cs 2 CO 3 and CH 3 I as a p omo e [127]. The use o an ionic liquid along wi h CH 3 I as a p omo e o e KOH ca alys shows an inc ease in he yield o DMC [128]. The u iliza ion o CO 2 o syn hesis o DMC is e y bene icial because DMC i sel is a unique molecule and can be used in new en i onmen ally iendly eac ions o eplace some o he en i onmen ally ha m ul p ocesses like ans- es e i ica ion o DMC wi h phenol ha p oduces me hyl phenyl ca bona e [129]. A.1.5 Me hanol syn hesis Me hanol is used as an impo an chemical eeds ock o he syn hesis o many compounds such as ace ic acid, o maldehyde, me hyl e -bu yl e he (MTBE), me hyl me hac yla e (MMA) and chlo ome hane. The i s indus ial plan o me hanol p oduc ion using syn hesis gas was cons uc ed by he BASF in 1923. This p ocess was ope a ing unde high p essu e o abou 20 MPa and a 300 °C using a zinc oxide/ch omium oxide ca alys [5]. Due o he en i onmen al impac , me hanol syn hesis h ough he ca bon dioxide hyd ogena ion has a ac ed wo ldwide esea ch in e es . The po en ial use o CO 2 o eplace CO in he me hanol syn hesis is also an e ec i e way o CO 2 u iliza ion [130]. The me hanol syn hesis om CO 2 has wo possible mechanisms. One is he di ec con e sion o ca bon dioxide o me hanol (Eq. (A-8)) and he second one is he con e sion o CO 2 o CO and H 2 O ia he RWGS eac ion wi h subsequen con e sion o CO and H 2 o me hanol (Eq. (A-9)). Comme cially me hanol has been p oduced om coal and na u al gas con aining small amoun o CO 2 along wi h CO and H 2 as a eeds ock [131]. i P  <  3 j P   j u ij  <  j P i       1 j l Pmn  o  F  5 p [ `K  q O -+  2g ¿ K4  Appendix A 135 i  <  = j P   j u ij  1 j l Pmn  o  F  5 Z [  q O -+  2g ¿ 4  The me hanol o ma ion is an exo he mic eac ion, so he modynamically a o ed a low empe a u es and high p essu es. Du ing he eac ion hyd ogen can be consumed by CO 2 in e e se wa e gas shi eac ion and educe he me hanol o ma ion. A ecen s udy show ha a mix u e o a p ope p opo ion o CO 2 and CO o me hanol syn hesis is no only inc eases he me hanol yield bu also dec ease he appa en ac i a ion ene gy o he eac ion [132]. The p esence o CO 2 could main ain he ac i e coppe si es in he oxida ion s a e o p e en an o e - educ ion o he ZnO componen o Cu/Zn ca alys s du ing me hanol syn hesis [132]. Table A-1 shows he da a epo ed o con e sion o CO 2 and he selec i i y o me hanol using CO 2 o e Cu/Zn/Z O 2 con aining ca alys . Table A-1: Me hanol syn hesis by CO 2 hyd ogena ion using Cu/Zn/Z O 2 con aining ca alys . Ca alys P epa a ion me hod T, °C X CO2 , % S MeOH , % Re . Cu/Zn/Z O 2 cop ecipi a ion 250 19.4 29.3 [133] Cu/Zn/Z O 2 cop ecipi a ion 220 21 68 [134] Cu/Zn/Z O 2 cop ecipi a ion 200 5.9 47.5 [135] Cu/Zn/Z O 2 u ea ni a e combus ion 240 17 56.2 [136] Cu/Zn/Z O 2 glycine ni a e combus ion 220 12 71.1 [137] Cu/Zn/Al/Z O 2 cop ecipi a ion 240 18.7 47.2 [138] Cu/Zn/Ga/Z O 2 cop ecipi a ion 250 - 75 [139] The p esence o Z O 2 enhances Cu dispe sion which leads o an imp o ed ca aly ic ac i i y and s abili y owa ds me hanol o ma ion [133, 136]. The addi ion o an op imum amoun o me al oxides like Ga 2 O 3 , Al 2 O 3 , Z O 2 , and C 2 O 3 as a modi ie s inc eases he me hanol syn hesis ac i i y and he s abili y o Cu/ZnO-based e na y ca alys s [135, 138-140]. A no el app oach was employed using low empe a u e o abou 170 °C and 5 MPa p essu e in a semi-ba h au ocla e eac o wi h 2-bu anol as a sol en [141]. CO 2 con e sion and Appendix A 136 selec i i y owa ds me hanol ob ained o e a Cu ca alys was abou 26% and 73%, espec i ely. Al hough much a en ion has been gi en o he me hanol syn hesis om CO/H 2 , CO 2 /H 2 and CO/CO 2 /H 2 using ixed bed echnology, some impo an subjec s o in es iga ion a e s ill unde discussion: (1) whe he he ac i e si e is Cu 0 o Cu n+ , (2) whe he he ca bon sou ce o me hanol syn hesis is CO 2 o CO, (3) whe he he e is special in e ac ion be ween he Cu me al and oxide suppo , and (4) whe he he wa e o med du ing me hanol syn hesis has any in luence on he ca aly ic ac i i y. A.1.6 Fo mic acid syn hesis The syn hesis o o mic acid is ano he al e na i e o con e ca bon dioxide in o aluable p oduc s. Fo mic acid is widely used as a pickling agen , as a educing agen , as an an ibac e ial agen , a mo dan in he dyeing indus y, disin ec an and p ese a i e agen in sani a y s a ions, and as a neu alize in he anning indus y [142]. I has been also used as a aw ma e ial in he chemical indus y o he p oduc ion o o ma e es e , which is impo an eeds ock o he syn hesis o a ious o ganic de i a i es like aldehydes, ke ones, amides, and ca boxylic acids [142]. Fo mic acid has been p oduced di ec ly by he hyd a ion o ca bon monoxide, and by he hyd olysis o me hyl o ma e. The syn hesis o o mic acid by di ec CO 2 hyd ogena ion was i s epo ed by Fa low and Adkins in 1935 using Raney nickel as a ca alys unde 20 o 40 MPa and 80 o 150 °C in p esence o amines [143]. A a empe a u e o 250 °C, he shee b ass used in ab ica ing line s o s eel eac ion essel ac s as an ac i e ca alys o he hyd ogena ion eac ion: i P  <  j P  À jiij 1 2g ¿ 0Z4  Mos o he ca aly ic s udies o o mic acid syn hesis a e based he me al complexes o he second and hi d ow ansi ion me als, whe e he me al like u henium, palladium, and hodium has been used wi h he combina ion o halides o hyd ides as anionic ligands and phosphines as neu al ligands [142]. The ca aly ic hyd ogena ion o CO 2 o o mic acid o e ansi ion me al ca alyzed complexes RuH 2 (PPh 3 ) 4 and Pd(Ph 2 PCH 2 CH 2 PPh 2 ) 2 , has been epo ed [144]. Simila ly, o mic acid has been p oduced by ca bonyla ion o CO and H 2 O using a me al complex, i.e. Appendix A 137 [Ru II (EDTA-H)CO] - in he WGS eac ion [145]. The highly ac i e me al complex RuCl(O 2 CMe)(PMe 3 ) 4 as a ca alys wi h acidic alcohols was used o enhance he a e o he hyd ogena ion eac ion. The o ganic bases wi h in e media e basici y we e added o he eac ion mix u e o ex ac he o mic acid [146]. Al hough much a en ion has been paid o syn hesize o mic acid using a homogeneous ca alys , he p oblem o sepa a ion o o mic acid om he ca alys and he base s ill emains. The hyd ogena ion o CO 2 o o mic acid o e alumina suppo ed u henium hyd oxide as a he e ogeneous ca alys was ca ied ou using ie hylamine and e hanol as a sol en a 80 °C and 13.5 MPa [142]. Also he Ru henium(II) complex ca alyzed hyd ogena ion o CO 2 o o mic acid was heo e ically in es iga ed using cis-RuH 2 (PH 3 ) 4 as a model ca alys [147, 148]. The hyd ogena ion o e his ca alys ook place h ough he inse ion o CO 2 in o he Ru-H bond ollowed by he H-OCOH educ i e elimina ion, whe e CO 2 inse ion was he a e de e mining s ep. A.1.7 CO 2 e o ming o me hane The e o ming o CO 2 wi h me hane has also a ac ed a con inuous esea ch in e es . This p ocess was ca ied ou no only o he u iliza ion o wo undesi able g eenhouse gases (CO 2 , CH 4 ) bu also o he p oduc ion o uels by Fische T opsch and me hanol syn hesis. The d y e o ming o me hane wi h CO 2 is no ye easible, and gi es incomple e con e sion o CO 2 due o he modynamic cons ain s [149]. D y e o ming: i P  <  j   = i  <  = j P       1 j l Pmn  o  F  =p  q O -+  2g ¿ 004  S eam e o ming: j  <  j P i   i  <  3 j P       1 j l Pmn  o  F  =ZY  q O -+  2g ¿ 0=4  The d y e o ming o CO 2 wi h me hane was i s s udied by Fische and T opsch in 1928. A e ha many esea che s in es iga ed his eac ion using a ious ca alys s o he p oduc ion o syngas. Syngas can be p oduced wi h CO/H 2 a io o abou a uni y depending upon he eac ion condi ions. This is an endo he mic eac ion, gene ally ca ied ou in he empe a u e ange o 300 o 830 °C and a a mosphe ic p essu e [150]. The g oup VIII me als (e.g. Ni, Co, P , Pd, I , Ru, Rh e c.) a e mo e o less ca aly ically ac i e o he ca bon