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Unite States Patent [191 Pence et . [111 4,220,632 [45] Sep. 2, 1980 [54] REDUCTION OF NITROGEN OXIDES WITH CATALYTIC ACID RESISTANT ALUlVlllNOSILICATE MOLECULAR SIEVES AND AMMONIA Dallas T. Pence; Thomas R. Thomas, both of Idaho Falls, Id. The United States of America as represented by the United States Department of Energy, Washington, [75] Inventors: [73] Assignee: 11c. [21] App1.No.: 504,793 [22] Filed: Sep. 10,1974 Related US. Application Data [63] Continuation-impart of Ser. No. 284,810, Aug. 30, 1972, abandoned. [51] Int. (31.3 ........................ .. B01J 8/00; COlB 21/00 [52] US. Cl. .................................. .. 423/ 239; 423/237; 423/403 [58] Field of Search ............. .. 423/239, 219, 235, 212, 423/2132, 213.5, 213.7 [56] References Cited U.S. PATENT DOCUMENTS . 2,975,025 3/1961 Cohn .................................. .. 423/239 3,033,642 5/1962 Bukata et a1. ............ .. .. 3,279,884 10/ 1966 Nonnenmacher et a1. 3,346,328 10/1967 3,449,063 6/1969 3,454,355 7/1969 3,476,508 11/1969 3,599,427 8/ 1971 3,674,429 7/ 1972 3,767,764 10/1973 Dolbear ........................... .. 423/2137 3,895,094 7/1975 Carter et a1. ....................... .. 423/239 OTHER PUBLICATIONS Pence et a1. “NOX Abatement Using Ammonia with Zeolite Catalysts,” Proceedings of the AEC Pollution Control Conference, pp. 115-121, Oak Ridge 10/25/72-10/27/72, USAEC. Pence et a1. “Catalytic Reduction of Nitrogen Oxides”, Atomic Energy Commission Releases, US. Patents and Patent Applications for Licensing p. 22, May 4, 1973. Pence et a1. “NOx Abatement Using Ammonia with Zeolite Catalysts”, Nuclear Science Abstracts, vol. 28, p. 254, Abstract No. 2632, Jul. 31, 1973. Pence et a1. “Catalytic Reduction of Nitrogen Oxides,” Atomic Energy Commission Releases, U.SI Patents and Patent Applications for Licensing, p. 27, Aug. 31, 1973. Norton Bulletin Z-50; Norton Chemical Products Divi sion, Akron, Ohio, 1970. ' Chemical Abstracts, vol. 65, 1966 #l6,091g. Industrial and Engineering Chemistry vol. 53, No. 3, Mar. 1961, pp. 199-204. Primary Examiner-Brian E. Hearn Attorney, Agent‘, or Firm—-James E. Denny; Dean E. Carlson; Frank H. Jackson [57] ABSTRACT Noxious nitrogen oxides in a waste gas stream such as the stack gas from a fossil-fuel-?red power generation plant or other industrial plant off-gas stream is catalyti cally reduced to elemental nitrogen and/or innocuous nitrogen oxides employing ammonia as reductant in the presence of a zeolite catalyst in the hydrogen 9r sodium form having pore openings of about 3 to 10 A. 8 Claims, 7 Drawing Figures

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UniteS ta tesPa tent[ 1 9 1Pence et.[ 1 1 1 4 , 2 2 0 , 6 3 2[ 4 5 ] S ep .2 , 1 9 8 0[ 5 4 ] REDUCTION OF NITROGEN OXIDESWITH CATALYTIC ACID RES IS TANT ALUlVlllNOS ILICATE MOLECULAR S IEVESAND AMMONIA Da lla sT.Pence;Thoma sR.Thoma s ,b oth ofId a ho Fa lls ,Id .The UnitedS ta tesofAmericaa srep res entedb ythe UnitedS ta tesDep a rtment ofEnerg y ,Wa s hing ton,[ 7 5 ] Inv entors :[ 7 3 ] As s ig nee:1 1 c.[ 2 1 ] Ap p 1 . No. : 5 0 4 , 7 9 3[ 2 2 ] Filed : S ep .1 0 , 1 9 7 4Rela tedUS .Ap p lica tion Da ta[ 6 3 ] Continu a tion- imp a rtof S er. No. 2 8 4 , 8 1 0 , Au g . 3 0 ,1 9 7 2 ,a b a nd oned .[ 5 1 ] Int.( 3 1 . 3 . . . . . . . . . . . . . . . . . . . . . . . .. . B0 1 J 8 /0 0 ;COlB 2 1 /0 0[ 5 2 ] US .Cl. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . 4 2 3 /2 3 9 ;4 2 3 /2 3 7 ;4 2 3 /4 0 3[ 5 8 ] FieldofS ea rch . . . . . . . . . . . . .. . 4 2 3 /2 3 9 ,2 1 9 ,2 3 5 ,2 1 2 ,4 2 3 /2 1 3 2 ,2 1 3 . 5 ,2 1 3 . 7[ 5 6 ] Ref erencesCitedU. S .PATENT DOCUMENTS.2 , 9 7 5 , 0 2 5 3 /1 9 6 1 Cohn . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. . 4 2 3 /2 3 93 , 0 3 3 , 6 4 2 5 /1 9 6 2 Bu ka taet a 1 . . . . . . . . . . . . .. . . .3 , 2 7 9 , 8 8 4 1 0 / 1 9 6 6 Nonnenma cher et a 1 .3 , 3 4 6 , 3 2 8 1 0 /1 9 6 73 , 4 4 9 , 0 6 3 6 /1 9 6 93 , 4 5 4 , 3 5 5 7 /1 9 6 93 , 4 7 6 , 5 0 8 1 1 /1 9 6 93 , 5 9 9 , 4 2 7 8 / 1 9 7 13 , 6 7 4 , 4 2 9 7 / 1 9 7 23 , 7 6 7 , 7 6 4 1 0 /1 9 7 3 Dolb ea r . . . . . . . . . . . . . . . . . . . . . . . . . . .. . 4 2 3 /2 1 3 73 , 8 9 5 , 0 9 4 7 /1 9 7 5 Ca rter et a 1 . . . . . . . . . . . . . . . . . . . . . . . .. . 4 2 3 /2 3 9OTHER PUBLICATIONSPence eta 1 . NOX Ab a tement Us ing Ammoniaw ith Z eoliteCa ta ly s ts , Proceed ing s oftheAEC Pollu tion ControlConf erence, p p . 1 1 5 - 1 2 1 , Oa kRid g e 1 0 /2 5 /7 2 - 1 0 /2 7 /7 2 ,US AEC.Pence et a 1 . Ca ta ly tic Red u ction ofNitrog en Ox id es ,Atomic Energ yCommis s ion Relea s es , US . Pa tentsa ndPa tent Ap p lica tionsf or Licens ingp . 2 2 ,Ma y4 , 1 9 7 3 .Penceeta 1 . NOxAb a tement Us ing Ammoniaw ith Z eolite Ca ta ly s ts ,Nu clea r S cience Ab s tra cts ,v ol.2 8 ,p .2 5 4 ,Ab s tra ct No.2 6 3 2 ,Ju l. 3 1 , 1 9 7 3 .Pence et a 1 . Ca ta ly tic Red u ction ofNitrog en Ox id es , Atomic Energ yCommis s ion Relea s es ,U. S I Pa tentsa ndPa tent Ap p lica tionsf or Licens ing ,p .2 7 ,Au g .3 1 , 1 9 7 3 .Norton Bu lletin Z - 5 0 ;Norton Chemica l Prod u ctsDiv i s ion, Akron,Ohio,1 9 7 0 . 'Chemica l Ab s tra cts ,v ol. 6 5 , 1 9 6 6# l6 , 0 9 1 g .Ind u s tria la ndEng ineering Chemis try v ol. 5 3 , No. 3 ,Ma r.1 9 6 1 ,p p . 1 9 9 - 2 0 4 .Prima ryEx a miner- Bria n E.Hea rn Attorney ,Ag ent , or Firm - Ja mesE.Denny ;Dea n E.Ca rls on;Fra nk H.Ja cks on [ 5 7 ] ABS TRACT Nox iou snitrog en ox id esin aw a s te g a ss trea m s u ch a sthe s ta ck g a sf rom af os s il- f u el- ? red p ow er g enera tion p la nt or other ind u s tria l p la nt of f - g a ss trea m is ca ta ly ti ca lly red u cedto elementa l nitrog en a nd /or innocu ou snitrog en ox id esemp loy inga mmoniaa sred u cta nt in the p res ence ofaz eolite ca ta ly s t in the hy d rog en 9 r s od iu m f orm ha v ingp ore op ening sofa b ou t 3to1 0A.8Cla ims ,7Dra w ingFig u resUS a tentS ep .2 , 1 9 8 0 S heet1 of4 4 , 2 2 0 , 6 3 2NH3/MOM 5 5 . 0 f m5 6 3 5 0 02 . 0L0 0 L5 0m3/NOX 3 5 6 mm5 5 . 5 2 0 0 .@ g i' oichig ? w ei' ric Amou ni of NH3mm L2 0' 0o ( D O ' 6 )O S michiomei nc Amou ni' of NH34 , 2 2 0 , 6 3 2S ep .2 , 1 9 8 0 S heet 2of41 . 2 01 . 0 0. s o 1 8 . . %$ 0_ _ II BEIDDEPTH, I 2 5 0 3 5 0 4 5 0TEMPERATURE, C 2 5 0 3 5 0TEMPERATURE, C 4 5 0 7 Q EFFICIENCY 0 Pa tent S ep .2 , 1 9 8 0 S heet 3of 44 , 2 2 0 , 6 3 2FIE I0 0% EFFICIENCY | E1 | IIl . 5 L0 0S TOICHIOMETRICRATIO 6 0I0 08 0U3 l% H2 00 | O / H2 O TI5 % H2 O 1 . 0 L5 2 . 0S TOICHIOMETRICRATIO U a mtS ep . . 2 , 1 9 8 0 S heet4of 4 4 , 2 2 0 , 6 3 5 ?% EFFICIEHCY i)4 , 2 2 0 , 6 3 2I REDUCTION OF NITROGEN OXIDESWITH CATALYTIC ACID RES IS TANT ALUMINOS ILICATE MOLECULAR S IEVESAND AMMONIA CONTRACTUAL ORIGIN OF THE INVENTION Theinv entiond es crib ed hereinw a s ma d einthe cou rs eof , oru nd er, a contra ctw iththeUNITED S TATESATOMIC ENERGY COMMIS S ION.CROS SREFERENCE TO RELATED APPLICATIONSThisis acontinu a tion- in- p a rt ofou r a p p lica tion S er.Nu mb er 2 8 4 , 8 1 0? ledAu g .3 0 , 1 9 7 2 ,nowa b a nd oned .BACKGROUND OF THE INVENTION Thisinv entionrela tes totheca ta ly ticred u ctionofnitrog en ox id es .In more d eta il,the inv ention rela testo the ca ta ly tic red u ction ofnox iou snitrog en ox id esp resent in aw a s te g a ss trea m.In s tillmore d eta il,the inv en tion rela testo the ef f ectiv e elimina tion ofnitrog en oxid esa sas ou rce ofp ollu tion f rom f os s il- f u el- ? redp ow er g enera tionp la nts a nd otherind u s tria lp la ntof f - g a ss trea ms .Ititnowg enera llyrecog niz edtha t the a tmos p heric conta mina tiontha ta ccomp a nies ind u s tria ls ociety isone ofthe mos t s eriou sp rob lemsf a cingma nkinda ndtha tcerta innitrog en ox id escontrib u te hea v ilytothisp rob lem.There a rea tlea s t- s ix s ta b leox id es ofnitrog en b u t onlynitric ox id e ( NO)a ndnitrog en d iox id e ( N0 2 )a re trou b les ome f rom a p ollu tions ta nd p ointa ndthef or mu laNOX isg enera lly u s edto ref er to thes e tw o ox id es .In common w ith other ma j or a irp ollu ta ntsNOX a ris e chief lyf rom thep rod u ction ofenerg yinthe community , moe s p eci? ca lly b ythe? x a tionofa tmos p heric nitrog eninhig h- temp era tu rereg ions off u rna ces a ndinterna l comb u s tion eng ines .Another s ou rce ofNO, a sa tmos p heric p ollu ta ntsa re inorg a nic a ndorg a nic nitration rea ctionsin the chemica l p roces sind u s tries .Tra nsp ort, ind u s trya ndelectricity g enera tion a llcontrib u te to the p rob lem.The corros iv echa ra cterofw a s te g a s es conta iningnitrog en ox id esma ya ls o neces s ita te or a t lea s t rend er d es ira b lethe remov a l ofthes eox id esf rom w a s te g a ss trea ms ,ev en thou g h relea s e ofthe ox id esto the a tmo s p here ca n b e tolera ted .The p res ence ofNO, in aWa s te g a ss trea m ma yma ke it neces s a ryto cons tru ct p ollu tion control eq u ip ment throu g h w hich the w a s te g a ss trea m p a s s esofa n ex p ens iv e corros ion- res is ta nt ma teria l s u ch a s s ta inles s s teel, w herea sa chea p er ma teria ls u cha sca rb ons teelcou ld b eu s ed if theNOX a reremov edb ef orethew a s te s trea menters thep ollu tioncontrol eq u ip ment.Ox id esofnitrog en p la yad u a l role ina irp ollu tion,? rs t a sap ollu ta nt in their ow n rig ht a nds econda sthe initia torofcomp lexp hotochemica l rea ctionsw ith hyd roca rb ons . Whilep hotochemica ls mogis themos t v is ib lea nd immed ia tely s eriou s cons eq u ence ofNOxp ollu tion, itis recog niz edtha t the p res ence ofNOxin thea tmos p here w illa d v ers elya f f ecttheenv ironment ev enthou g hnop hotochemica ls mogha s ev erb een d etected inthea rea , a nd theS ta teofCa lif ornia ha ses ta b lis heda n a d v ers elev el a b ov e w hich the concen tra tion ofNOxin the a tmos p here s hou ldnot b e p ermit~tedto ris e.Unf ortu na tely ,thisa d v ers elev el ha sb een s u b s ta ntia lly ex ceed ed inma ny cities of theUnited2 02 53 54 55 05 56 06 52S ta tesw hich ra rely ,ifev er,ha v e ap rob lem w ith p hoto chemica l s mog .It f ollow stha t ox id esofnitrog en s hou ldb e controlledin a llcitiesa nda rea sin w hich there is aconcentra tion ofind u s tryin ord er to red u ce the NO, a ndox id a nt concentra tion b elowthe a d v ers elev el.There a re tw o comp letelyd if f erent a p p roa chesto the controlofNOxemis s ion; the? rs tis tomod if y the s ou rceins u ch a w a ya s tored u cethef orma tionofox id esofnitrog en a ndthe other is d es troyor ca p tu re the nitrog en ox id esa lrea d yf ormed ,thereb yp rev entingthem f rom es ca p ingto the a tmos p here.Ma nymethod sf or red u cingNO, p ollu tion ha v e b een s u g g es teda ndaf ewa re inp ra ctica lu s e. S ome ofthe s u g g es tedmethod sinclu d e:Mod i? ca tion oforig ina l s ou rce 1 . Mob ile s ou rcesa . Cha ng esin eng ine d es ig n b . Ex ha u s t g a srecircu la tion 0 . Us e g a stu rb inesra ther tha n g a s oline or d ies el eng inesd .Us e electric motorsra ther tha n interna l comb u stion eng ines2 . S ta tiona rys ou rcesa . Cha ng esin f u rna ce d es ig n b . Tw o- s ta g e comb u s tion 0 . Cha ng e in ty p e off u el d . Inclu s ion ofa d d itiv esin the f u el Remov a l ofox id esofnitrog en a . S orp tion b yliq u id s ,f or ex a mp le,f errou ss u lf a te or ca lciu m hy d rox id e s olu tionsb .S orp tion b ys olid s ,f or ex a mp le,s ilicag el or molec u la r s iev es0 . Therma l red u ction b yb u rningin af u el- rich ? a me d . Va p orp ha s erea ctionw ithothercomp ou nd s .Metz ler inNAS A TMX- 2 2 5 7 ,Ma rch1 9 7 1 , p ro p os estha t a mmoniab e rea ctedd irectlyw ith ox id esofnitrog en. How ev er,p otentia llyex p los iv e s olida mmoniu m nitra te is area ction p rod u ct a ndcon trolled d ecomp os itionofthis a mmoniu m nitra te ha snot b een d emons tra ted .e. Ca ta ly tic red u ction to nitrog en w ith or w ithou t the a d d ition ofared u cingg a s .And ers on et a l. in Ind .Eng .Chem,5 3 , 1 9 9( 1 9 6 1 )s howtha t NOxca n b e s electiv ely red u cedb ya mmoniaemp loy ingp la ti nu m a sca ta ly s t anu mb er ofp rob lems ,how ev er,ha v e b een rep orted w ith this p roces s . Firs t, f ree ox y g en,ev eninrela tiv ely s ma lla mou nts , ha s atend encyto p ois on the ca ta ly s t a nd ,s econd ,d if ?cu lties ha v eb eenex p erienced inob ta ining the p rop er cond itionsto p rev ent ox id a tion ofa mmoniap rior to its u s e a sthe red u cingg a s .Thef ollow ing p a tents a ls od es crib ep roces s es in w hich a mmoniaisu s eda sared u cingg a sin the p res ence ofaca ta ly s t.Nonnenma cher U. S . Pa t. No. 3 , 2 7 9 , 8 8 4 - Us esV2 0 3 ,M0 2 0 3or W2 0 3a sca ta ly s t in p res ence of0 - 15 %ox y g en S how s 9 9 . 2 % remov a lw ith3 . 5 % ox y g en p res ent.Grif ? nget a l. U. S .Pa t. No.3 , 4 4 9 , 0 6 3 - Emp loy sacop p erconta ining ca ta ly s ts u cha s cop p erox id eor s u p p ort s u ch a ss ilicaa lu mina .Cohn et a l. U. S . Pa t. No.2 , 9 7 5 , 0 2 5 ~ S u g g es tsu s e ofap la tinu m g rou pmeta l inp res ence ofO~ 2 2 %ox yg en.In a d d ition Kea rb yet a l. - . - U. S .Pa t.No.3 , 4 7 6 , 5 0 8 ~ emp loy sz eolitesto d ecomp os e u nb u rnedhy d roca rb onsp res ent in ex ha u s t g a s esa nds ta tesin one ex a mp le tha t 4 , 2 2 0 , 6 3 23Ni- ex cha ng ed z eolites conv erted CO a nd NO u nd er red u cingcond itions .In s p ite ofthe tremend ou sef f ort tha t ha sb een a ndisb eingp u t intothis p rob lem, thef a ctrema instha tno s a tis f a ctory p roced u ref orp ra ctica la nd ef f icientre mov a l ofNO, f rom ef f lu entstha t conta in hig h lev elsofox y g en ( 3 to 2 0 % )is nowknow n f or es s entia llycom p letelyd es troy ingNOxp res ent inaw a s te g a ss trea m,s u cha s thes ta ckg a s g iv enof fb ya f os s il- f u el- f iredp ow er g enera tion p la nt.S UMMARY OF THE INVENTION Accord ingto the p res ent inv ention,nox iou snitrog en ox id esa rered u cedtoN2a nd /or N2 0b ymix ingthe s trea m conta iningnox iou snitrog en ox id es w ith ag a ss trea m conta ininga mmoniaa t atemp era tu re of2 5 0 to 5 5 0 C.a ndconta ctingthe s a me w ith az eolite ca ta ly s t in the hy d rog en or s od iu m f orm ha v ingp ore op ening sofa b ou t 3to1 0A.For ex a mp le,the nox iou snitrog en ox id esp res ent in s ta ck g a s esconta iningox y g en,w a ter v a p or a nds u lf u r d iox id e ma yb e red u cedto innocu ou ss u b s ta ncesb ymix ingthe s ta ck g a sw ith ag a sconta ininga n ef f ectiv eq u a ntityofa mmoniaa tatemp era tu re of2 5 0 to 5 5 0 C.in the p res ence ofaz eolite in the hy d ro g en or s od iu m f orm a sca ta ly s t.BRIEF DES CRIPTION OF THE DRAWING FIG.1isag ra p h in w hich the conv ers ion ef f icienciesf or the red u ction ofNOxp res ent in ad rya ir s trea m a ndp a s s ed throu g ha f ou r- inchz eoliteca ta ly s tb ed a tas u p er? ca l f a ce v elocityof1 0 0f t/min. a re p lotteda saf u nction ofthe ra tioofa mmoniaconcentra tion tothe NOxconcentra tion a ndtemp era tu re;FIG.2is as imila rg ra p h f or a n eig ht- inch ca ta ly s t b ed ;FIG.3is ag ra p h in w hich the a mmoniareq u iredf or 9 9 %conv ers ion ofa b ou t 5 0 0 0p p m N0 2p res ent inad rya ir s trea m a ndp a s s edthrou g h az eolite ca ta ly s t b eda t af a ce v elocityof1 0 0f t/min.is p lotteda saf u nction oftemp era tu re;FIG.4isas imila r g ra p h f or ahu mida ir s trea m ( d ewp oint of4 6 C. ) ;FIG.5is ag ra p h in w hich the a b a tement ef ? ciencyf or NO, ( 1 5 %NO,8 5 %N0 2 )p res ent inas imu la tedWa s te Ca lciner Fa cilitya tmos p here isp lotteda saf u nc tion ofex it b edtemp era tu re a nds toichiometric ra tio ofNH3to NOxf or a n eig ht- inch b edconta iningl/ 1 6 - inch hy d rog en mord enite ex tru d a te;FIG.6is as imila r g ra p h f or 1 0 0 %NO,a ndFIG.7is as imila r g ra p h f or 1 0 0 %NO a ndatw elv e inch b edconta ining - inch hy d rog en mord enite ex tru da te.S PECIFIC EMBODIMENTSOF THE INVENTION Und erthecond itions emp loy ed inou rinv ention,nox iou snitrog en ox id es a rered u cedtonitrou s ox id e a nd /or nitrog en.The d is trib u tion ofthe rea ction p rodu ctsa p p ea rsto b e af u nction ofthe ca ta ly s t b edtemp er a tu re a ndthe a ctiv ityofthe ca ta ly s t a sw ell a s ofthe p a rticu la r red u cingg a semp loy ed .Althou g h red u ction ofNO, to elementa l nitrog en is p ref era b le, N2 0is not a nu nd es ira b lep rod u ct, b eca u s eitd oes notf orm a n a nhy d rid e,isd if f icu lt to ox id iz e a ndisnot cons id eredto b e ap ollu ta nt.The ex a ctrea ctions inv olv ed inthep roces softhe ins ta nt inv ention a re d ep end ent on the comp os ition of4 05 06 06 54theg a s eou s mix tu re, a ndtheca ta ly ticb ed op era tingcond itions . How ev er,the p rob a b le rea ctionsa re:3 N2 O+2 NH3 >4 N2 +3 H2 O( 4 )The a mou nt ofa mmoniaemp loy edmu s t b e s u f f icient toef f ectcomp lete red u ction ofthe nitrog en ox id esto elementa l nitrog en a nd / or nitrou sox id e.The a mou nt ofa mmoniareq u iredw ill f a llin ara ng e b etw een s lig htlys u b s toichiometrica nd s lig htly s u p ers toichiometric b a s edon comp lete red u ction to nitrog en.Ifno or v erylittle ox y g en isp res ent in the w a s te g a ss trea m the s ma ll a mou ntsofred u cingg a s( CO a ndH2 )p res ent therein ma yred u ce ap a rt ofthe NOX s o tha t les s tha n as toi chiometric q u a ntityofa mmoniaw ou ldb e s u f ? cient.Ifa llor ama j or p rop ortion ofNOX is N0 2 ,the a mmoniama yred u ce thisto N2 0w hereb yles s tha n as toichio metric q u a ntityb a s edon comp lete red u ction tonitro g en is req u ired . Als o p a rticu la rly a thig hertemp eratu resthe z eolite ca ta ly s t w ill red u ce the N0 2to NO s o tha t les sa mmoniaisreq u ired .On the other ha nd ,p a rtic u la rlya t hig her temp era tu res ,comp etingrea ctionsma yma ke it neces s a ryto emp loyalittle more a mmonia . -The ex a cta mou nt ofa mmoniareq u ired is d eterminedb yon- line continu ou smea s u rement ofthe NOxin the p ro ces sef ? u ent. ,It isnot neces s a rytha t the entire red u cingg a ss trea m ha v e a red u cing comp os ition s incethep roces s is re ma rka b lytolera nt to the p res ence ofmolecu la r ox y g en or other ox id iz ingg a s .For ex a mp le,the p roces sis v eryef f ectiv eona irs trea ms conta ining u p to2 0 v olu me p ercent ox y g en.Thisis as ig nif ica nt a d v a nta g e ofthe p roces s , s incema nycu rrently p rop os edp roces s es re q u ire tha t the ex ha u s t s trea m ha v e av erylowox y g en content.Asw ill b e s how n hereina f ter the p roces sisa ls o ef f ec tiv eon hu mida irs trea ms a nd on s trea ms conta inings u lf u r d iox id e.Thisis v eryimp orta nt s ince ma nyind u stria lw a s teg a s s trea ms conta inw a terv a p ora nd / or s u lf u r d iox id e.The z eolitesu s ef u l in the p ra ctice ofthe ins ta nt inv en tiona rea lu minos ilica tes w ithf ra mew ork s tru ctu resenclos ingla rg e ca v itiesca lleds u p erca g es ,w hich a re ofex cep tiona llyla rg e a ndu nif orm s iz e. The f u nd a menta l s tru ctu ra lu nits ofz eolites a res ilicona nd a lu minu m a toms tetra hed ra lly coord ina ted w ithf ou rox y g en a toms . Beca u s e the ox y g en a tomsa re mu tu a llys ha redb etw een tetra hed ra lu nits a ndcontrib u tea nef f ectiv e u nitcha rg e to ea ch tetra hed ron,ea ch a lu minu m tetra he d ra lu nitp os s es s es anetneg a tiv echa rg e. Ca tions a sreq u iredin the f ra mew ork s tru ctu re to ma inta in cha rg e neu tra lity . The ca tionsa re u s u a lly ,b u t not a lw a y s ,s o d iu mions , a ndthenu mb er req u ired p eru nitcellisd icta tedb ythe s ilicon- to- a lu minu m ra tio ofthe z eolite.Thes e ca tionsca n b e rep la cedb yother ionsb yion- excha ng e p roced u res .The s ilicon- to- a lu minu m ra tioa ndthep a rticu la rca tiona reca teg oriz ed b ythety p eofz eolite. While a nyz eoliteex hib itingca ta ly tica ctiv itycou ldb e u s edex cep t f or thos e in w hich the s od iu m ha sb een ex cha ng edf or ca tionsw hich a re s o a ctiv e tha t the red u cingg a sd ecomp os esb ef ore itca n rea ct w ith the NOX inv iewofthe ind ica ted u tility ofz eolites inthe 4 , 2 2 0 , 6 3 235u nex cha ng eds od iu m orhy d rog en f orm a ndthes u bs ta ntia llylow er cos t thereoftha n ofex cha ng edz eolites ,u s e onlyofthe hy d rog en a nds od iu m f ormsofz eolitesiscontemp la tedin a ccord a nce w ith thisinv ention.One ofthe p rop ertiesofz eolitesis their ca p a b ilityofs electiv ely a d s orb ing certa inmolecu les inp ref erence to, or tothecomp lete ex clu s ionof , othermolecu les ;they , theref orea ref req u ently know n a s molecu la r s iev es . While w e d onotw is h tob e b ou ndb ya nymecha nis tic interp reta tion,it isb eliev edtha t the z eolitesofthe ins ta nt inv ention f u nction b ys electiv elya d s orbingb oth thenitrog en ox id esa ndthe a mmoniaw ithin the p ore inters ticesw here s trongelectros ta tic f orcesofthe p romote the rea ction ofthe nitrog en ox id e a ndthe red u cingg a s . The rea ction p rod u ctsthereb yp rod u cedthenex itf romthez eolitef ra mew ork s tru ctu re. The p oresofd if f erent know n z eolitesv a ryin d ia meter f rom a b ou t 3Ang s tromsto a b ou t 1 0Ang s troms ,b u t f or a nyone z eolite, the p oresa re ofs u b s ta ntia llyu nif orm s iz e.Z eolitesu s ef u linthe p ra ctice ofthe ins ta ntinv ention ca n s u ita b lyha v e p oresra ng ingin s iz e f rom a b ou t 3to a b ou t 1 0Ang s tromsw hen s od iu m is the ca tion. Howev er,the p ore s iz e isa lteredb ythe ex cha ng e ofca tionsa td if f erents iz ea nd cha rg e. S u ita b lecommercia llya v a ila b le z eolites g enera llyha v e p a rticles iz esra ng ingf rom a b ou t 4 1to a b ou t 2 0mes h ( US .S ta nd a rdS eries ) .Ifd es ired ,the z eolite ma yb e d is p ers edw ith a n inert ca r rier s u ch a sa lu mina .Althou g hs y nthetica lly p rep a red z eolites a rep re f erred f oru s eina p p lica tionoftheins ta ntinv ention b eca u s e oftheir more u nif orm p rop erties , na tu ra l z eo litesca n b e u s ed .Na tu ra l z eolitesu s ef u l f or thisp u rp os e inclu d e, p rima rily , the f a u j a s ites , cha b a z ites , erionites ,a ndmord enites .The z eoliteu s edmu s t not b e s oa ctiv etha titw ill ox id iz ethea mmoniab ef ore itha stheop p ortu nityto rea ct w ith the corros iv e nitrog en ox id es .Thisreq u ire ment elimina tes z eolites w hich ha v e b eenca tionexcha ng edw ith meta lsw hich a re know n to b e ox id a tion ca ta ly s ts s u cha s thetra ns itionmeta ls a nd thenob le meta ls . For ex a mp le, 2 %p la tinu m ex cha ng edY- ty p e z eolite,as y nthetic f a u j a s ite w ith as lig htlyla rg er S i/Al ra tiotha n the X- ty p e, w a su s edw ith NO2 ( ~1 % )a nda mmoniain a n a ir s trea m a t a b ou t 3 0 0 C.The a mmoniaw a sox id iz edb y0 1b ef ore the N0 2cou ldb e red u ced .The z eolitema yb e ca tion ex cha ng edw ith a meta l w hich is not know n to b e a n ox id a tion ca ta ly s t s u ch a ss ilv era nd f u lly - ex cha ng ed s ilv erz eolite, ty p e X, ha sb een s how n to b e ef f ectiv e ( s ee b elow ) . Itis b eliev edhow ev er tha tthes ilv erta kes no p a rt intherea ction s ince itis clea r tha t z eolitesin the u nex cha ng edhy d ro g en or s od iu m f orm a re eq u a llyef f ectiv e.Unex cha ng edca ta ly s ts a reex cep tiona lly a d v a nta g eou snot onlyb e ca u s e theyw illnot ca ta ly z e ox id a tion ofthe a mmoniab u t a ls o b eca u s e theya re not p ois onedb ycons titu entss u ch a sS 0 ;w hich a re f req u entlyp res ent in ef f lu ent g a ss trea ms . Pref erred ca ta ly s ts a ccord ing tothep res ent inv entiona res y nthetichy d rog en mord enites s u cha sZ eolon 9 0 0 , ap rod u ct ofthe Norton Chemica l Com p a ny ,s ince the mord enitesa re more a cidres is ta nt tha n a re other z eolitesd u e to the hig her s ilicon to a lu minu m ra tiothereofa nds incehy d rog en mord enite is a p p a r ently ofs lig htly g rea ter s treng th tha n is s od iu m mor d enite.Asw illb ecome a p p a renthereina f terthehy d rog en mord enitesa re ef f ectiv e in ca ta ly z ingthe red u ction ofNO, ,w ith NH3ina irs trea msconta ining u pto1 5 , 0 0 0p p m N0 1 ,u pto2 0 %0 1 ,u pto 3 1 %w a ter,a ndu pto 02 53 03 54 55 563 0 0 0p p m 8 0 ; . All ofthes ev a ria b les , a s w ella s the rela tiv e p rop ortion ofNO a ndNO;inthe g a ss trea m,w ill ef f ect the temp era tu re a t w hich area s ona b le d eg ree of NO) ,a b a tementis a tta ined . How ev er, a ccep ta b le w orking cond itions ca nb ef ou nd reg a rd les s ofhowthes e p a ra metersv a ry .Althou g h thez eolites f u nctionef f ectiv ely f orp ro long edp eriod s ,their u s ef u l lif e, like tha t ofv irtu a llya ll ca ta ly s ts ,is , ofcou rs e,not ind e? nite.How ev er,u nlike ma nyofthe other ca ta ly s tsheretof ore p rop os edf or the red u ction ofthe corros iv e ox id esofnitrog en, the z eo lites ca n b e s u ita b lyres toredto s u b s ta ntia lly f u llca taly tica ctiv ityb yreg enera tion method sinclu d inghig h temp era tu re b u rn of f , i. e. hea tingto a b ou t 8 0 0 C.in the p res ence ofox y g en,or p u rg ingw ith hig h- p res s u re s tea m.The d eg ree ofreg enera tion a ndnu mb er ofreg en era tiv ecy cles p os s ib led ep endon thety p eofz eolite b a s e, ty p e a ndd eg ree ofex cha ng e,a ndthe ex tent a ndty p e ofconta mina nt on the ca ta ly s t b ed .Ev en w ithou t reg enera tion, thez eolites f u nctionef f ectiv ely f oralong erp eriod oftime tha n know n p riora rtnitrog en ox id e red u ction ca ta ly s ts .While itis know n tha t area ction p roceed sb etw een NOX a ndNH;in the a b s ence ofaca ta ly s t a ss how n in the p rior a rt, u s e ofaz eolite a sca ta ly s t ina ccord a nce w iththep res entinv entionp ermits g rea terrea ction ef ? ciency ,les s a mmoniacons u mp tion a ndens u resthe controlledtherma l d ecomp os ition on the ca ta ly s t ofthe p otentia llyex p los iv e a mmoniu m nitra te f ormedd u ringthe rea ction.One ofthe imp orta nt a d v a nta g esofthe p roces softhe ins ta nt inv ention is tha t v eryhig h conv ers ion ra tesa re a chiev ed . Und er a p p rop ria teop era ting cond itions , a sw ill b e d es crib ed ,es s entia llya ll, i. e. >9 8 % ,ofthe cor ros iv e nitrog en ox id esin the g a ss trea m w ill b e red u cedto elementa l nitrog en or N2 0 .Asp rev iou s lymentioned ,the p roces softhe ins ta nt inv ention ca n s u ita b ly b e ef f ected b yma inta ining the z eoliteca ta ly tic b eda tatemp era tu re ra ng ingf rom a t lea s t2 5 0 C. to a b ou t 5 5 0 C. The ex a ct temp era tu re req u iredto a tta in the d es iredred u ction d ep end son the ty p e ofz eolite,the comp os ition ofthe ef f lu ent g a s ,a ndres id ence time; g enera lly , there is no a d v a nta g e to exceed ing theminimu m temp era tu re. How ev er, if the concentra tionof u nb u rned hy d roca rb ons intheg a ss trea m is hig h, op era tion ofthe ca ta ly s t b eda t hig her temp era tu resw ill p rolongitsef f ectiv e lif e.The rea ction p res s u re is a ls o not critica l, p res s u resf rom a tmos p heric to a b ou t 1 5 0p s igb eingp a rticu la rlys u ita b le.The conta ct or res id ence time ofthe corros iv e nitro g en- ox id e- conta iningg a ss trea m p lu sthe red u cingg a sw iththez eoliteca ta ly s tca n b ea s lowa s a b ou t0 . 1s econdf or es s entia llycomp lete red u ction ofthe corro s iv enitrog enox id es . Long erconta cttimes a re, ofcou rs e,not ha rmf u l,b u t a sin v irtu a llya llp roces s esofthis ty p e , theminimu m ef f ectiv econta ct time, w hich ena b les thema x imu m throu g h- p u t ra te, is p ref era b le.The v olu me ra tio ofcorros iv e nitrog en ox id esthrou g h p ilot to z eolite a ls o is not critica l. We ha v e f ou ndtha t w ith q u a ntities ofz eolites a s lowa s 1 p a rt b yv olu me p er 1 0s ta nd a rdv olu mesofnitrog en ox id e throu g h- p u t p er minu te,es s entia llycomp lete red u ction ofthe corro s iv enitrog enox id es is a chiev ed . Asis a p p a rent, thisra tio ref ersto the nox iou snitrog en ox id e throu g h- p u t;thetota lg a s s trea mthrou g h- p u tca n, of cou rs e, b yma nyord ers ofma g nitu d eg rea ters inceinmos tg a ss trea ms ,inclu d ingp ow er- g enera ting - p la nt ef f lu entsa nda u tomob ileex ha u s t, thea mou ntofnox iou s nitrog en 4 , 2 2 0 , 6 3 27ox id esis u s u a llylow .For ex a mp le,the corros iv e nitro g en ox id e concentra tions inf os s il- f u el- p ow er- g enera t ing f a cilities , incinera tors , orothercomb u s tionu nit of f - g a s esa re u s u a llyles stha n 7 0 0p p m,w hile the ma x i mu m concentra tion ininterna lcomb u s tion eng ine exha u s t is les s tha n 4 0 0 0p p m a ndu s u a llyles s tha n 2 0 0 0p p m Asp rev iou s lymentioned ,toef f ectthe red u ction ofthe corros iv e nitrog en ox id es ,there mu s t b e p res ent a t lea s t a n ef f ectiv e a mou nt ofred u cingg a s .The req u ireda mou nt ofred u cingg a sca n b e a d d edto the g a ss trea m a t a nyp oint p rior to conta ctingthe g a ss trea m w ith the z eolite ca ta ly s t.The onlyreq u irement istha t as u f f icient q u a ntityofthe red u cingg a sb e f a irly w ell mix edw ith the g a ss trea m p rior to conta ctingthe z eolite ca ta ly s t.The inv ention ca n b e more f u llyu nd ers toodb yref er ence to the f ollow ingex a mp les .EXAMPLESA s eriesofp relimina ryex p erimentsw ere cond u ctedto a s certa in the ef f ectiv enes sofv a riou scommercia llya v a ila b le s y nthetic z eolitesa sca ta ly s tsf or the red u ction ofthecorros iv eox id esofnitrog en. Unles sotherw is e s ta ted , the p ercent comp os ition oftheg a s es ref ers to v olu me p ercents a nd a llinp u ttemp era tu res w erea t a mb ient temp era tu res( ~ 2 lC. ) .The f ollow inga b b rev ia tionsa re u s edin the ex a mp lesw hen ref erringto the ty p e ofz eolites :Na X Ty p e X z eolite,s od iu m ca tion,as y nthetic f a u j as ite- ty p e z eolite ma nu f a ctu redb yb oth Union Ca rb id e Corp .a ndGra ce Chemica l Corp ora tion.Ag X X- ty p e z eoliteinw hich thes od iu m ions ha v e b een rep la cedb yion ex cha ng e w ith s ilv er.AW5 0 0 - Arep roces s ed na tu ra lz eoliteconta iningmos tlys od iu m ca tions .Na Z A s y ntheticmord enite ca lled Z eolon ma nuf a ctu redb yNorton Chemica l Corp ora tion.( 1 )Ca ta ly s t Ma teria l 1 0 0 %Ag X 1 2 - 1 4mes h ~ 1 7cm3Op era tingCond itionsFlowra te 7 . 6l/min BedTemp - 2 0 0 to 2 5 0 C.Res id ence time ~ 0 . 1 5s ec Inp u t NO2 1 . 0 %Air rema ind er Ou tp u t ( 2 )Ca ta ly s t Ma teria l 1 0 0 %Na X 1 2 - 1 4mes h ~ 5 0cm3Op era tingCond itionsFlowra te 7 . 6l/min BedTemp . 2 7 5 to 3 2 5 C.Res id ence time 0 . 4s ec Inp u t NO2 - - l. 0 %1 02 003 51 5 05 5v 5 06 5l8. Air rema ind er Ou tp u tNOz -< 0 . 0 1 7NO< 0 . 0 1%N2 O 0 .8 %( 3 )Ca ta ly s t Ma teria l AW S OD- p rima rilys od iu m 1 1 2 - 1 4mes h ~5 0cm Op era tingCond itionsFlowra te- 7 . 6l/min Bedtemp . - 2 7 5 to 3 2 5 C.Res id ence time- 0 . 4s ec Ilnp u t NOZ 1 . 0 %NI- I3 ~ l. 9 %Air- rema ind er Ou tp u t NO2 < 0 . 0 1 %NO 7 /2 N2 +6 H2 0 ( 5 )In g enera tingthes e d a ta ,u pto s ev era l hou rsw ere u s edtoeq u ilib ra tetheNOx - NH3ca ta ly s ts y s tem. Asexp ected ,thes e d a taind ica te as ig ni? ca nt imp rov ement in conv ers ion ef ? ciencyw hen comp a ringthe res u ltsf rom the 8 - inch d eepca ta ly s t b edw ith thos e f rom the 4 - inch d eepb ed .Ef ? cienciesa shig h a s9 9 . 9 %w ere ob s erv eda t ca ta ly s t b edtemp era tu resin the ra ng e 3 0 0 to 4 0 0 C.The inf lu entNOxs trea ms w ere red u cedtoa tlea s t2p p m NOX,w hich w a sthe b a ckg rou ndlev el ofthe moni tor. Mea s u rements w erema d e f orb othNH3b rea k throu g h a ndox id a tion ofNH3to NO;a thig h NH] ,to NOX ra tiosa ndtemp era tu resin the ra ng e 4 0 0 to 4 5 0 C. , b u t no s ig ni? ca nta mou ntsofeithers p ecies w ere ob s erv ed .At the low er temp era tu resof3 0 0 to 3 5 0 C. ,s ma ll a mou ntsofNH3w ere ob s erv edto b rea kthrou g h the ca ta ly s t b edw hen the conv ers ion ef ? cienciesw ere in the ra ng e 9 9to 9 9 . 9 % .At ev en low er temp era tu res ,b elow3 0 0 C. ,cons id era b le a mou ntsofNH3w ere d e tectedin the ca ta ly s t b edef f lu ents ,b u t q u a ntita tiv e d a taw ere not collected .The a mou nt ofNH3req u iredto ob ta in 9 9 %conv er s ion ef f iciencyofNO, in d rya ir a t af a ce v elocityof1 0 0f t/min a nd4 -a nd8 - inch d eepb ed sisillu s tra tedin FIG.3 . The s toichiometryref ers toRea ction ( 5 ) . With the 8 - inch d eepb ed ,9 9 %conv ers ion ef ? cienciesw ere obta ined f rom 2 5 0 to 4 5 0 C.The 4 - inch d eepb edp er f ormednea rlya sw ell b u t req u ireds lig htlymore NH3 .In b oth b ed ss ome NH4 NO3w a sob s erv edin the ef f luentw hen theca ta ly s tb edw a sop era tedb elowa b ou t 2 7 5 to 3 0 0 C. ,b u t itw a snot p res ent a b ov e thistem p era tu re ra ng e.Cons id eringonlythea mou nt ofNH3req u ired , the p roces sw a smos t ef ? cient w hen the ca ta ly s t b edw a sop era tedinthe temp era tu re ra ng e of3 0 0 to3 5 0 C.There a re s ev era l rea s onsw hyconv ers ion ef ? cienciesof9 9 %w ere ob ta ineda t les stha n the a p p a rent s toichio metric a mou nt ofNH3 .Firs t, in the temp era tu re ra ng e ofa b ou t 2 7 5 to3 7 5 C. , incomp lete red u ction ofthe NO) ,occu rredres u ltingin s ome f orma tion ofN2 0in s tea dofa lltoelementa l nitrog en, thu s , req u iringles sNH3 .S econd ,w e ha v e ob s erv edtha t the z eolite ca taly s t w ill red u ce N0 2to NO ev en in the a b s ence ofNH3a b ov e a b ou t 3 0 0 C. ,b u t the ef ? ciencyofthe rea ction d oesnot a p p ea r to b e a p p recia b le u ntil a b ou t 3 5 0 C. ;a t 4 0 0 C.the conv ers ion ef f iciencyofN0 2to NO isa b ou t 9 0 % .Theref ore,thes e tw o p roces s estendto red u ce the a mou ntofNH3req u ired f orcomp letered u ctionofNO, ,to N2 .Als o,w hen the ca ta ly s t b edw a sop era teda b ov e 4 0 0 C. , la rg eex ces s es , 3 0to5 0 %a b ov e tha t req u ired f or9 9 %conv ers ion, cou ldb e u s ed w ithou t b eing d etected intheef f lu ent, ind ica ting theex ces sNH3w a sb eingox id iz edin the ca ta ly s t b ed .How ev er,ina s mu ch a s nos ig ni? ca nta mou ntsofN0 2 , NO,or N2 0w ere ob s erv edin the ef f lu ent a t thes e cond itions ,theox id a tion p rod u ct mu s t b e N2 , a ndthered u ction rea ctionsofthe NO, to N;b yNH3occu rsin p ref erence to ox id a tion ofNH;. . . a t lea s tov er the temp era tu re ra ng e s tu d ied ,4 0 0 to 4 5 0 C.Beca u s e s ev era l rea ctionsma yta ke p la ce concu rrently , theex a ct d es crip tion ofthe ov era ll p roces smecha nis m is not clea r,b u t the net res u lt is av eryef f icient red u ction p roces sw ith no a dv ers e b y - p rod u cts .FIG.4s how sthe res u ltsoftes tscond u ctedin hu mid i ? eda irs trea msw ith a llother cond itionsthe s a me a s3 56 06 51 0thos e ofthe d rya ir s trea m s how n in FIG.3 . Althou g h no d if ? cu ltyw a s encou nteredin ob ta iningg rea ter tha n 9 9 %NOxconv ers ion ef f iciency inthehu mid i? eda ir s trea m,more NH3w a sreq u iredtha n w ith the d rya ir tes ts .The error b a rss how n in FIGS .3a nd4ind ica te the u ncerta inty intheN0 2s ta nd a rd . The s ta nd a rd w a sa s s u medto b e 4 7 5 0p p m N0 2w ith a n u p p er limitof5 1 0 0p p m a ndalow er limit of4 4 0 0p p m.Other s y s tem a ticmea s u rementerrors a renotb eliev ed toex ceedi5 % .The f ollow ingtes ts w ere p erf ormedon as imu la tedtes t a tmos p here ty p ica l ofcoa l- ? redp ow er p la nts .The ca ta ly tic ef f ect ofthe hy d rog en f orm ofZ eolon 9 0 0on therea ctionef f iciency ofNO a nd NH3w a ss tu d iedin af lows y s tem.A v ertica l 2 . 2 - inch i. d . q u a rtztu b e conta ininga 1 2 - inch b edofthe ~ inch ex tru d a te ca ta ly s t w a shea tedto 3 5 0 C.w ith atu b e f u rna ce. A s imu la ted f lu eg a s , w hichw a sp rehea ted totheb edtemp era tu re, w a sp a s s edthrou g h the b eda tara teof2 . 6 5f t3 /min ( mea s u reda t 7 0 F.a nd1 a tm) ,p rod u cingas u p er? cia l f a ce v elocityof1 0 0f t/min. The tes tg a scons is tedof0 . 3 %8 0 ; ,0 . 0 5 %NO,1 2 %C0 2 ,7 %H2 0a ndthe rema ind er a ir. Comb u s tion s ta ck g a s esu s u a llyconta in3 to7 %0 2a s comp a redw ith the1 6 %u s edhere; how ev er,thehig h f lowra te ofthe tes tmix tu re ma d e the u s e ofb ottledN2imp ra ctica l.Theref ore,p la nt a irw a su s edres u lting inthehig her 0 2content. The w a ter v a p or content w a smonitoredw ith ap s y chrome ter, a ndrota metersw ere u s edto mea s u re the req u iredf low oftheotherg a s es tha tma d e u pthetes ta tmo s p here. Thermocou p les p os itioned ev ery tw oinchesa long thev ertica la x is oftheb edind ica ted tha tthe temp era tu re g ra d ient w a sles s tha n 6 8 F. throu g hou t the tes t b ed .The p res s u re d ropa cros sthe b edw a s1 2 . 9inchesofH2 0 .Af tertheb edha db eenex p os edtothetes ta tmo s p here f or1 2hou rs ,the NH3w a sintrod u cedu p s trea m ofthe b ed .At ? rs t,as ix - hou r eq u ilib ra tion p eriodw a sreq u iredto a tta inacons ta nt ef f lu entNO rea d ing ; b u t therea f ter, onlyone hou r w a sneed edw ith ea ch s ma ll cha ng e in the inf lu ent NH3concentra tion.The tes t w a scond u ctedcontinu ou s lyf ora b ou t2 0 0hou rs . Du ringthis time ad es iredin? u ent concentra tion ofNH3w a ss elected ,a ndNO ef f lu ent d a tacollectedf or three to s ixhou rsb ef ore cha ng ingto a nother s etting . Ef f lu ent NO,N0 2 ,N2 0 ,a ndNH3concentra tion d a taw ere collectedthrou g hou t the tes t p eriod .The NO a b a tement ef ? cienciesofthis p roces s , a s af u nction ofthe in? u ent NH3concentra tion,a re g iv en in Ta b le 1 .TABLE 1 .Nitric ox id e a b a tement ef f iciencyv ers u sNH3. concentra tion a t ab edtemp era tu re of6 6 0 F. ,in? u ent NO concentra tion of5 0 0p p m,a nds p a ce v elocityof6 0 0 0hr 1 .in? u entEf f lu entAb a tementS toichiometric NH3 ( p p m) NO ( p p m) ef f iciency( 7 0 ) a mou nt ofNH;3 3 4 4 1 . 9 9 1 . 6 t 1 . 3 1 . 03 6 7 2 4 . 3 9 5 . 2 i 1 . 4 1 . 14 0 0 7 . 7 9 8 . 5 i 0 . 2 1 . 24 6 7 6 . 9 1 . 4 9 8 . 6 i 0 . 2Da tacollectionw a slimited toin? u ent lev els ofNH3w hich y ield ed g rea tertha n9 0 %remov a l ofNO.Asind ica tedin colu mn three,the d a taw ere hig hlyrep ro d u cib le,a ndno d ecrea s e in ca ta ly s t a ctiv ityw a snoted4 , 2 2 0 , 6 3 21 1d u ringthe Z OO- hou r tes t p eriod .Und er thes e cond itions ,the ma x imu m a b a tement ef f iciencyofthe s y s tem,w hich occu rredw ith a2 0 %ex ces sofNH3 ,w a sa b ou t 9 8 . 5 % .The s toichiometric ca lcu la tionsw ere b a s edon the rea c tion 3 N0 +2 NH3 >3 H7 _ O+5 /2N2 ( 6 )w hich isa s s u medto b e the p red omina nt one occu rring .The othermonitored s p ecies , N0 2 , N2 0 , a nd NH3 ,w ere not d etectedin the ef f lu ent a t a nytime. A w hite cry s ta lline comp ou ndw a sob s erv edin the ef ? u ent.Thisma teria lw a sa na ly z ed b y x - ra y cry s ta llog ra p hy a ndd etermined tob ea mix tu reof a mmoniu m b is u lf a te ( NH4 HS O4 )a nda mmoniu m s u lf a te[ ( NH4 ) 2 S O4 ] .The res u ltsofthes e tes t d a tas howthe z eolite ca ta ly s t to ex hib itarema rka b le a b ility tos electiv ely p romote theNO NI- I3rea ctioninthe p res ence ofp otentia llyinterf ering p roces s es , s u ch a s p rema tu re ox id a tionofNH3b y0 2 ,b lockingofa ctiv e s itesb yhig h concentrationsofH2 0a ndCO2 ,a ndca ta ly s t p ois oningb y$ 0 2 .The f orma tion ofN0 2isnot kinetica llyf a v oreda nyw herein the tes t or s a mp lings y s tem.Ca lcu la tionsind i ca te tha tles s tha n1 %of5 0 0p p m NO ina irw illb e conv ertedto NO;in 4s ec a t 6 8 F.a ndin 1 2s ec a t 6 6 8 F.The res id ence time ofthe tes t g a sisa b ou t 4s ec tota l inthe tes ta p p a ra tu sa nds a mp lings y s tem. Theref ore,N0 1s hou ldnot ha v e b een ob s erv ed ;s u ch w a sthe ca s e.Itw a scons id eredp os s ib le tha t the rea ction 4 NO+NH3 +5 /2N2 O+3 /2H2 0 ( 7 )w ou ldcomp ete w ith rea ction ( 6 ) , b u t thes e d a taind i ca te tha tthis rea ctionoccu rsonlya s a n intermed ia te s tep ,ifa t a ll.The a b s ence ofNH3in the ef f lu ent,w hen the inf lu ent s toichiometric ra tio ofNH3 /NO w a s1 . 4 0 ,a ndthe p resence ofa mmoniu m b is u lf a te a nds u lf a te in the ef f lu ent ind ica te tha t the f ollow ingrea ctionsa re comp etingw ith rea ction ( 6 ) :Und er thes e cond itionsitis a p p a rent tha t the rea ction b etw een NH3a ndNO iskinetica llymore f a v ora b le tha n b etw een NH3a nd8 0 ; ,es p ecia llyw hen one cons id erstha t the in? u ent S Og /NO ra tio is a b ou t 6 . The f ormation ofthe a mmoniu m b is u lf a te a nds u lf a te a srea ction p rod u ctsw a snot s u rp ris ing .In p rev iou sinv es tig a tionsthep os s ib ility ofS O;a b a tementb ya mmoniainthe a b s ence ofNO w a sex a mined , a ndaconv ers ion ef ?ciencyofa b ou t 8 0 %ofthe S 0 ;to a mmoniu m s u lf a te w a sob ta ined . The s u lf a te/b is u lf a tep rod u ct ra tiow ill d ep endin p a rt on the a mou nt ofNH3w hich isa v a ila b le f or rea ction w ith S 0 3 .Thu saconcep tu a llya ttra ctiv e a nd s imp lecomb ined NOx S OX a b a tements y s tem w ou ldinv olv e inj ection ofNH3u p s trea m ofas ing le b edofmord enite ma inta ined a ta b ou t 6 6 0 F. Thiscou lds imu lta neou s lyca ta ly z e the red u ction ofNOxto N2a ndconv erttheS 0 , ,top a rticu la tea mmoniu m s u lf a teor a mmoniu m b is u lf a tew hichcou ld b eremov ed w ith electros ta tic p recip ita tion.Fu rther tes ts w ere ca rriedou t on ates ta tmos p here conta ining 3 1 %H2 0 ,5 %CO2a nd2 %CO w hich isty p ica loftheef f lu entg a s f romtheWa s teCa lciner 2 5. 3 03 54 56 5Fa cilitya t the Na tiona l Rea ctor Tes t S ta tion.The f ol low ingex p erimenta l cond itionsw ere u s ed :( a )Ca ta ly s t hy d rog en f orm ofZ eolon 9 0 0 .( b )BedDep th l2in w ith the 5 in ex tru d a te a nd8 in w ith theH1 6in in ex tru d a te.( c)Tes t Atm 3 l%H2 O+5 %CO2 +2 %CO+a ir.( d )Temp era tu re Ra ng e 3 0 0 to 5 5 0 C.a t the b edex it.( e) Fa ce Velocity l0 0f t/min a t s cf m.( f )Res id ence Time 0 . 6s ec in the l2 - in b eda nd0 . 4s ec inthe 8 - in b ed .( g )NOX Concentra tion- - u s u a llya b ou t 5 0 0 0p p m b u t u pto1 5 , 0 0 0p p m.( h)BedPres s .Drop 3 0to 4 2mm Hgin the temp eratu re ra ng e 3 0 0 to 5 5 0 C.( i)BedTemp era tu re Gra d ients a b ou t a4 0 C.increa s e in the d irection ofg a sf loww ith 5 0 0 0p p m NOxa nd1 0 0 C.w ith 1 5 , 0 0 0p p m NOX.FIGS .5a nd6illu s tra te the d a taob ta inedf rom the eig ht inch b ed .Asind ica ted ,p u re N0 2tes t a tmos p heresw ere not ob ta ina b le. Thisis p rob a b lyd u e tos ome therma l d is s ocia tion in the p rehea tings ta g e ofthe g a s . Th d a taind ica te ap ronou ncedd if f erence in the b eha v ior ofNO a ndN0 2b etw een 3 0 0 a nd3 8 0 C.The rea ction ef ?cienciesf or NO a re more temp era tu re d ep end ent tha n f orN0 2 . Als o, b etter a b a tementef ? ciencies a reobta ined f orN0 2w ithreg a rd s tob othma x imu m ef f i ciencya ndNH3req u ireda tcomp a ra b le temp era tu res . Other d a taw a sa ls o collectedw ith the eig ht inch b ed :( a ) Grea ter tha n 9 9 %a b a tement of 1 5 , 0 0 0 p p m "N0 2w a sob ta inedw ith a n ex it b edtemp era tu re of5 5 0 C.( b ) Below3 5 0 C. a b ou t 2 0 %ofthe in? u ent N0 2a pp ea reda sN2 0in the ef ? u ent.Ab ov e 4 4 0 N2 0w a snot d etecteda nda t no temp era tu re w a sN2 0d etectedw hen the in? u ent conta inedonlyNO.( 0 )An ef f ecton a b a tement ef ? ciencya saf u nction ofCO or CO;concentra tion w a snot ob s erv ed .( d )A w a ter ef f ect w a sob s erv ed .At 3 8 0 C.the ma x i mu m N0 2a b a tement ef ? ciencies w ere 9 7 , 9 9 . 3 a nd9 9 . 9 %f oraw a ter v a p or content of3 1 , 1 0a nd1 %res p ectiv ely .FIG. 7 illu s tra tes thed a ta ob ta inedu s ingthe1 2 - inch b ed .A comp a ris on ofthisd a taw ith FIG.6ind ica te tha t ma x imu m ob ta ina b le ef f icienciesa re a b ou t the s a me b u t tha t cons id era b lymore NH3is req u iredw hen u s ingthe la rg er ex tru d a te.Ofp erha p sg rea ter interes t isthe w a ter ef f ecton the cu rv es . There is ap os itiv e ef f ect a tlows toichiometric ra tio w hich cha ng esto aneg a tiv e ef f ect a tthe hig her ra tios a s thew a ter content is increa s ed . The ma x imu m ob ta ina b le ef ? ciencyis not g rea tly a ff ecteda t the hig h temp era tu re b u t v erymu ch s o a t the low er temp era tu re.Itw illb e noted tha tthed a tainFIG.7 ind ica teama x imu m ef ? ciencys omew here b etw een 8 0a nd9 3 %f or 7 %w a ter content a t3 5 0 C.The d a taf rom ex a m p les d es crib ed a b ov e ind ica tes a n ef ? ciencyofb etter tha n 9 8 %w hen the b edw a sop era teda t 3 5 0 C.a ndthe ef ? u ent conta ined5 0 0p p m NO a ndg rea ter tha n 9 9 %ef ? ciencyb etw een 3 0 0 a nd4 5 0 C.f or 5 0 0 0p p m NO;in a ir+ 1 0 %H2 O.While s ome ofthe d if f erencesa re d u e to d if f erencesin the tes t a tmos p here,itis p os s ib le tha t theex itb ed temp era tu res intheea rliertes ts w ere s lig htlyhig her ( p os s ib lyu pto5 0 ) tha n the mea s u redtemp era tu resd u e tola ck ofs op his tica tedtemp era tu re mea s u ringd ev ices .Ba s edon the a b ov e d a tarecommend edtemp era tu resofop era tion a re:( 1 )For aw a s te g a ss trea m ty p ica l ofthe Wa s te Ca lciner Fa cilityef ? u ent cons is tingofa ir, 3 0v olu me p ercent 4 , 2 2 0 , 6 3 21 3w a ter v a p or,5v olu me p ercent CO,2v olu me p ercent CO,0 . 9v olu me p ercent N0 2a nd0 . 4v olu me p ercent ( 2 )For aw a s te g a ss trea m ty p ica l ofap a rticu la r ind u stria lw a s te g a s s trea m cons is ting ofa ir, 1 0 v olu me p ercent w a ter v a p or, a nd0 . 5 v olu me p ercent NO 2 - ~ 3 5 0 C.( 3 ) For aw a s te g a ss trea m ty p ica l ofaf os s il- f u el- ? redp ow er p la nt cons is tingofa ir,7v olu me p ercent w a ter v a p or. 0 . 3 v olu me p ercent S 0 2 , 1 2 v olu me p ercent CO2a nd0 . 0 5v olu me p ercent NO 3 5 0 C.In g enera l temp era tu resofop era tion ca n ra ng e f rom 2 5 0 or 3 0 0 to 5 5 0 C.w ith the minimu m b eingd ep en d ent u p on the comp os ition ofthe w a s te g a ss trea m.Ins u mma ry , z eoliteca ta ly s ts of f erthef ollow inga d v a nta g esov er other ca ta ly s ts : ( l) the s y nthetic z eo lites d o not ca u s e the p rema tu re ox id a tion ofa mmoniaev en a t ox y g en concentra tionsa shig h a s2 0 %a ndtem p era tu resa shig h a s4 0 0 C. ,( 2 )the p roces sisop era b le ov er aw id er temp era tu re ra ng e, 2 5 0 5 5 0 C. ( 3 ) the u s e ofz eolite ca ta ly s tsreq u ire onlynea r- s toichiometric q u a ntities ofa mmoniacomp a redw ith la rg eex ces s esu s u a llyreq u iredf or other ca ta ly s ts ,( 4 )the ca ta ly s tsa re not s u s cep tib le to p ois oningb yconta mina nt g a s esa ndp erf orm w ell ev en in hig hlyhu mida tmos p heres ,a nd( 5 )theyp rov id e v eryhig h ef f iciencies , g rea ter tha n 9 9 % ,f or NO, c red u ction a t s p a ce v elocitiesa ndca ta ly s t b edp res s u re d rop stha t a re p ra ctica l f or ind u s tria l a p p lications .In a d d ition to b einghig hlyef f icient,the p roces selim ina testhe f ollow ingd is a d v a nta g esa s s ocia tedw ith liqu id s cru b b erp roces s es : ( 1 ) d is p os a lofliq u id w a s tesg enera tedin the s cru b b ingp roces s ,( 2 )the req u irement f or eq u imola r mix tu resofNO a ndN0 2to ens u re g oodremov a lef f iciencies , ( 3 ) rela tiv ely low throu g hp u t ra tes ,a nd( 4 )the needto rehea t the trea tedg a sto ob ta in g oodd is p ers a l ofthe s ta ck d is cha rg e.Als o the p roces sd oesnot req u ire the hig h energ yreq u irementsofther ma l d ecomp os ition method s .Fina lly ,the p roces ss hou ldw ith minor mod i? ca tion b e u s ef u lf orcomb inedS 0 2a ndNO) ,remov a l f rom w a s te g a ss trea ms .The emb od imentsofthe inv ention in w hich a n ex clus iv ep rop erty orp riv ileg eis cla imed a red e? ned a sf ollow s :1 . A p roces s f or conv ertingmore tha n 9 8 %ofthe nox iou s nitrog enox id es p res enting a s eou s ef f lu entsconta ining 3 to2 0v olu me p ercent ox y g en toN2a ndN2 0comp ris ingmix ingthe g a s eou sef ? u ent w ith ag a ss trea m conta ininga n ef f ectiv e a mou nt ofa mmoniaa ndconta cting the mix edg a s esw ith aca ta ly s tcons is tinges s entia lly ofas y nthetic hy d rog en mord enite ha v ingp ore op ening sof3to 1 0A,the temp era tu re ofthe ca taly s t b edb eing2 5 0 5 5 0 C.a t the b edex it.2 . A p roces sa ccord ingto cla im 1w herein the g a s e ou sef f lu ent conta ins1 6to 2 0 %ox y g en.3 . A p roces sa ccord ingto cla im 1w herein the g a s e ou sef f lu entis s ta ck g a sf rom af os s il- f u el- f lred p ow er p la nt inclu d ingthe f ollow ing :7v olu me p ercent w a ter 1 02 02 53 54 04 55 05 56 06 51 4v a p or,1 2v olu me p ercent CO1 ,0 . 3v olu me p ercent S 0 2a nd0 . 0 5v olu me p ercent NO,a nd3to 7v olu me p ercent 0 2a ndthe b edtemp era tu re is 3 5 0 C.a t the b edex it.4 . A p roces sa ccord ingto cla im 1w herein the g a s e ou sef f lu ent iss ta ck g a sf rom anu clea r p roces s ingp la nt ha v ingthe f ollow inga p p rox ima te comp os ition:3 0v ol u me p ercentw a terv a p or, 5 v olu me p ercentC0 2 , 2v olu me p ercent CO,0 . 9v olu me p ercent N0 2 ,0 . 4v ol u me p ercentNO,theb a la nceb eing a ira ndtheb edtemp era tu re is 4 0 0 - 5 0 0 C.a t the b edex it.5 . A p roces sa ccord ingto cla im 1w herein the g a s e ou sef ? u ent iss ta ck g a sf rom a n ind u s tria l p la nt ha v inga p p rox ima tely thef ollow ing comp os ition: 1 0 v olu me p ercent w a ter v a p or,0 . 5v olu me p ercent N0 2 ,the b a l a nce b einga ir a ndthe b edtemp era tu re is 3 5 0 C.a t the b edex it.6 . A p roces sf or s electiv elyred u cingox id esofnitro g en p res entinamix tu re ofg a s es conta ining ox y g en,red u cib leox id es ofnitrog ena nda n inert' g a s , w hich comp ris esconta ctingin area ction z one s a idmix tu re ofg a s es a nda n a p p rox ima telys toichiometrica mou nt ofa mmoniab a s ed onred u ctionofthenitrog enox id esp res ent to nitrog en a t atemp era tu re of2 5 0 to 5 5 0 C.in the p res ence ofaca ta ly s t cons is tingofa n a cidres ista nta lu minos ilica temolecu la rs iev eha v ing s u b s ta n tia lly u nif orm intercry s ta lline p oresw hereb ys electiv e red u ction ofthe ox id esofnitrog en to nitrou sox id e a ndnitrog en is ef f ected .7 . A p roces sf or s electiv elyred u cingox id esofnitro g en in amix tu re ofg a s esconta iningu pto 2 0 %ox y g en,u pto1 . 0 %NO or N0 2a ndthe rema ind er a n inert g a s ,w hichcomp ris es conta cting ina rea ctionz ones a idmix tu re ofg a s esa nda n a p p rox ima telys toichiometric a mou nt ofa mmoniab a s ed on red u ctionofnitrog en ox id es p res enttonitrog ena tas p a ce v elocity ofles stha n 3 6 , 0 0 0hr 1a ndatemp era tu re w ithin the ra ng e of2 5 0 C.to 5 5 0 C.in the p res ence ofaca ta ly s t cons is tingofa n a cidres is ta nt a lu minos ilica te molecu la r s iev e com p os itionha v ing s u b s ta ntia lly u nif ormintercry s ta lline p oresw ith d ia metersofa b ou t 3to 1 0A,w hereb ys elec tiv e red u ction ofthe ox id esofnitrog en to nitrou sox id e a ndnitrog en is ef f ected .8 . A p roces sf or s electiv elyred u cingox id esofnitro g en in amix tu re ofg a s esconta iningu pto 2 0 %ox y g en,f rom atra ce to 2 %ox id esofnitrog en a ndthe rema ind er a n inert g a s , w hich comp ris esconta ctingin area ction z one s a idmix tu re ofg a s esa nda n a p p rox ima telys toi chiometric a mou nt ofa mmoniab a s edon red u ction ofnitrog en ox id esp res ent to nitrog en a t as p a ce v elocityofles stha n 3 6 , 0 0 0hr * 1a nda t atemp era tu re w ithin the ra ng e of2 5 0 C.to 5 5 0 C.in the p res ence ofaca ta ly s t cons is tingofa n a cidres is ta nt a lu minos ilica te molecu la r s iev ecomp os itionha v ings u b s ta ntia lly u nif orminter cry s ta llinep ores w ithd ia meters of a b ou t3 - 1 0 A,w hereb ys electiv e red u ction ofthe ox id esofnitrog en to nitrou sox id e a ndnitrog en is ef f ected .* * * # = 1 4