DK142000B - Process for treating waste liquor from a soda-based sulfite pulp preparation. - Google Patents
Process for treating waste liquor from a soda-based sulfite pulp preparation. Download PDFInfo
- Publication number
- DK142000B DK142000B DK231271A DK231271A DK142000B DK 142000 B DK142000 B DK 142000B DK 231271 A DK231271 A DK 231271A DK 231271 A DK231271 A DK 231271A DK 142000 B DK142000 B DK 142000B
- Authority
- DK
- Denmark
- Prior art keywords
- conduit
- waste liquor
- soda
- treating waste
- sulfite pulp
- Prior art date
Links
Classifications
-
- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/0085—Introduction of auxiliary substances into the regenerating system in order to improve the performance of certain steps of the latter, the presence of these substances being confined to the regeneration cycle
- D21C11/0092—Substances modifying the evaporation, combustion, or thermal decomposition processes of black liquor
Landscapes
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Processing Of Solid Wastes (AREA)
Description
(11) FREMLÆGGELSESSKRIFT 1^2000 DANMARK (ευ int.ci.3 o 21 c 11 /02 «(21) Ansøgning nr. 2312/71 (22) Indleveret den 13· maj 1971 (23) Løbedag 1 3 · maj 19 11 (44) Ansøgningen fremlagt og . o0 fremlæggelsesakriftet offentliggjort den auS* DIREKTORATET FOR . .(11) PUBLICATION NOTICE 1 ^ 2000 DENMARK (ευ int.ci.3 o 21 c 11/02 '(21) Application No 2312/71 (22) Filed on 13 May, 1971 (23) Running Day 1 3 · May 19 11 (44) The application submitted and the o0 submission document published by the AuS * DIRECTORATE FOR.
PATENT-OG VAREMÆRKEVÆSENET <»» Pnontet begær* fra denPATENT AND TRADE MARKET <»» Pnontet desires * from it
14. maj 1970, 371o4, USMay 14, 1970, 371o4, US
(71) SONOCO PRODUCTS COMPANY, Hartsville, South Carolina 29550, US.(71) SONOCO PRODUCTS COMPANY, Hartsville, South Carolina 29550, US.
(72) Opfinder: Donald Robert Sheeley, Route 5, Harley Circle, Hartsville, S.C., US: James Henry Rion, 213 Kenwood Drive, Hartsville, S.C., US: William Roy £ook, 300 Warner Drive, Hartsville, S.C., US: William Ar= chibald Biggs Jr., Woodland Drive, Hartsville, S.C., US.(72) Inventor: Donald Robert Sheeley, Route 5, Harley Circle, Hartsville, SC, US: James Henry Rion, 213 Kenwood Drive, Hartsville, SC, US: William Roy £ ook, 300 Warner Drive, Hartsville, SC, US: William Ar = chibald Biggs Jr., Woodland Drive, Hartsville, SC, US.
(74) Fuldmægtig under sagens behandling;(74) Clerk of the case;
Skandinavisk Patent Bureau v/Prode Larsen._ (54) Fremgangsmåde til behandling af affaldslud fra en sodabaseret sulfit= pulpfremstilling.Scandinavian Patent Bureau v / Prode Larsen._ (54) Procedure for the treatment of waste liquids from a soda-based sulfite = pulp production.
Opfindelsen angår en fremgangsmåde til behandling af affaldslud fra en sodabaseret sulfitpulpfremstilling, ved hvilken affaldsluden koncentreres, blandes med aluminiumhydroxid eller dets hydrat og forbrændes til natriumalu-minat, behandling af den dannede aske med under forbrændingen dannet S0£ til gendannelse af sulfit og aluminium-hydroxid, som anvendes igen.The invention relates to a process for treating waste liquor from a soda-based sulfite pulp preparation, in which the waste liquor is concentrated, mixed with aluminum hydroxide or its hydrate and incinerated to sodium aluminate, treatment of the ash formed with sulfur and aluminum hydroxide formed during combustion. , which is used again.
Ved kendte processer til behandling af affaldslud kræves som regel kostbare ovnanlæg til omdannelse af natrium-og svovlindholdet til en smelte. En kendt fremgangsmåde 2 142000 af den angivne art, i hvilken affaldsludens faste stoffer smeltes til dannelse af en klæbrig masse eller smelte er omhandlet i USA-patent nr. 3*061.408. I denne kendte proces tilsættes der affaldsluden en reaktant, der inde-5 holdes siliciumoxid og aluminiumoxid i et sådant omfang, at der dannes en smelte. Inddampningen og forbrændingen af affaldsluden kan ske i kalcinerings- eller smelteovne.Known processes for treating waste liquids usually require expensive furnace plants to convert the sodium and sulfur content into a melt. A known method 2 142000 of the disclosed kind in which the solids of the waste liquor are melted to form a sticky mass or melt is disclosed in United States Patent No. 3 * 061,408. In this known process, the waste liquor is added to a reactant containing silica and alumina to the extent that a melt is formed. Evaporation and combustion of the waste liquor can take place in calcination or melting furnaces.
Der er formålet med opfindelsen at anvise en fremgangsmåde af den angivne art, hvilken fremgangsmåde kan udføres 10 på tilfredsstillende måde ved brug af billigere ovnanlæg. Fremgangsmåden ifølge opfindelsen er ejendommelig ved, at der til den koncentrerede lud med et indhold af aluminiumhydroxid eller dets hydrat tilsættes en tilstrækkelig mængde af tilbageført natriumaluminat-ovnaske fra forbræn-15 dingsprocessen til dannelse af faste piller, der forbrændes ved en temperatur under natriumaluminatets smeltepunkt, idet en del af natriumaluminatet recirkuleres til dannelse af nye piller.It is an object of the invention to provide a method of the kind indicated, which method can be carried out satisfactorily using cheaper furnace systems. The process of the invention is characterized in that a sufficient amount of recycled sodium aluminate furnace ash from the combustion process is added to the concentrated broth containing aluminum hydroxide or its hydrate, to form solid pellets which are burned at a temperature below the melting point of the sodium aluminate. part of the sodium aluminate being recycled to form new pills.
Herved opnås på en enkel måde, at hele affaldsludmassen 20 holdes i form af ikke klæbrige, adskilte piller. Yderligere bliver pilleformen bibeholdt gennem hele forbrændingsreak-tionsproces sen indtil en endelige natriumaluminataske, og på denne måde forenkles en effektiv askegenvinding. Fremgangsmåden kan tilfredsstillende udføres i et så enkelt apparatur /eller en roterovn 25 som en flertrinsherdovn'. Faktisk kan næsten enhver ovntype, der er beregnet til brænding af faste brændsler og til opsamling af aske, anvendes i processen, såsom kul- eller træfyrede ovne, fluid-bed-ristere og destruktionsovne.In this way, the whole waste mass 20 is obtained in a simple manner in the form of non-sticky, separated pills. Further, the pellet form is maintained throughout the combustion reaction process until a final sodium alumina bag, thereby simplifying effective ash recovery. The process can be satisfactorily carried out in such a simple apparatus / or rotary kiln 25 as a multistage hearth. In fact, almost any type of furnace intended for burning solid fuels and for collecting ash can be used in the process, such as charcoal or wood-fired ovens, fluid-bed grills, and destruction ovens.
Endvidere består den del af ovnasken, som bliver recirku-30 leret i processen, for en stor del af natriumaluminat, der virker som et effektivt absorberende bære-materiale, når det blandes med affaldslud. Dette bære-materiale danner tætte, ikke tilstoppende partikler, som er lette at behandle i den nævnte billige ovntype.Furthermore, the portion of the furnace ash which is recycled in the process consists of a large portion of sodium aluminate which acts as an effective absorbent carrier when mixed with waste liquor. This carrier material forms dense, non-clogging particles which are easy to process in said cheap furnace type.
35 Ifølge opfindelsen kan forbrændingsoperationen udføres ved en temperatur på mindst ca. 538°C og fortrinsvis mellem 816° C og 1095°C. Ovntemperaturen holdes tilstrækkeligt lav gennem hele operationen, så at reaktionsmassen ikke bliver 3 142000 plastisk eller klæbrig på noget tidspunkt.According to the invention, the combustion operation can be carried out at a temperature of at least approx. 538 ° C and preferably between 816 ° C and 1095 ° C. The oven temperature is kept sufficiently low throughout the operation so that the reaction mass does not become plastic or sticky at any time.
Ifølge opfindelsen kan der tilsættes en sådan mængde aluminiumoxid, at molarforholdet mellem Na20 og A120^ kommer til at ligge mellem 1:1 og 2:1. Dette forhold kan 5 hæves i nogle tilfælde til 3:1. Det er vigtigt, at det tilstedeværende aluminiumoxid reagerer med natrium i en sådan mængde, at dannelse af natriumsulfid og af en klæbrig masse eller smelte undgås.According to the invention, such an amount of alumina may be added so that the molar ratio of Na 2 O to Al 2 O 3 is between 1: 1 and 2: 1. This ratio can be raised to 3: 1 in some cases. It is important that the alumina present reacts with sodium in such an amount as to avoid the formation of sodium sulfide and of a sticky mass or melt.
Et illustrerende eksempel på fremgangsmåden ifølge op-10 findelsen samt den videre behandling af de ved fremgangsmådens forskellige trin opståede biprodukter skal forklares nærmere i det følgende under henvisning til tegningen, der viser et diagram over et anlæg til gennemførelse af fremgangsmåden ifølge opfindelsen.An illustrative example of the method according to the invention as well as the further treatment of the byproducts arising from the various steps of the process will be explained in more detail below with reference to the drawing, which shows a diagram of a plant for carrying out the method according to the invention.
15 Fremgangsmåden udføres i det viste anlæg på følgende måde:The process is performed in the system shown as follows:
Fortyndet sodabaseret sulfitaffaldslud koncentreres i flertrinsfordampere 1. Den koncentrerede væske føres gennem en ledning 2 til en kontinuert blander 3, hvori den 20 blandes omhyggeligt med recirkuleret hydratiseret aluminiumoxid fra en ledning 4 samt med recirkuleret pulveriseret natriumaluminat-ovnaske fra en ledning 5. Blandingen fra blandetrinet fremkommer som adskilte piller, der føres gennem en ledning 6 til en ovn 7, såsom en rotorovn, 25 hvori den tablettiserede blanding forbrændes til omdannelse af svovlindholdet og det organiske indhold til luftformige produkter som S02, C02 og damp og til reaktion af natriumindholdet med aluminiumoxid til dannelse af natrium-aluminat.Dilute soda-based sulfite waste liquor is concentrated in multi-stage evaporators 1. The concentrated liquid is passed through a conduit 2 to a continuous mixer 3, where it is mixed thoroughly with recycled hydrated alumina from a conduit 4 as well as with recycled powdered sodium aluminate furnace from a conduit 5. appear as separate pellets passed through a conduit 6 to a furnace 7, such as a rotor furnace, 25 in which the tableted mixture is combusted to convert the sulfur content and organic content into gaseous products such as SO 2, CO 2 and steam and to react the sodium content with alumina to form sodium aluminate.
30 Natriumaluminatproduktet i form af en partikkelformet usmeltet aske kommer fra ovnen gennem en ledning 8, hvori det deles i to dele, idet en passende mængde af asken ledes gennem en ledning 9 og et knuseapparat 10 tilbage til blanderen 3. Den resterende del af asken føres gennem en 35 ledning 11 til en opløsebeholder 12. Vand tilføres gennem en ledning 13 til opløsning af natriumaluminatasken. Den resulterende opløsning med meget små mængder af uopløselige 142000 4 urenheder føres gennem en ledning 14 til et klaringsapparat 15, hvor det uopløselige bundfald fjernes.The sodium aluminate product in the form of a particulate unmelted ash comes from the furnace through a conduit 8, dividing it into two parts, passing an appropriate amount of the ash through a conduit 9 and a crusher 10 back to the mixer 3. The remaining portion of the ash is fed through a conduit 11 to a solvent container 12. Water is supplied through a conduit 13 to dissolve the sodium alumina bag. The resulting solution with very small amounts of insoluble 142000 4 impurities is passed through a conduit 14 to a clarifier 15 where the insoluble precipitate is removed.
Den klarede natriumaluminatopløsning føres gennem en ledning 16 til en reaktor 17. I reaktoren bliver natrium-5 aluminatopløsningen gjort sur med NaHSO^ fra en ledning 18 til dannelse af Na^O^ og udfældning af aluminiumhydroxid eller -hydrat. Reaktionsopslemningen føres gennem en ledning 19 til et kontinuert filter 20, hvor det hydrati-serede aluminiumoxid fjernes, udvaskes og recirkuleres 10 gennem en ledning 4. En del af Na2S0^-filtratet føres gennem en ledning 21 til et absorptionståm 22. Den tilbageblivende mængde af Na^O^-opløsning føres tilbage til · pulpanlægget til genbrug gennem en ledning 23.The clarified sodium aluminate solution is passed through a conduit 16 to a reactor 17. In the reactor, the sodium 5 aluminate solution is acidified with NaHSO 2 from a conduit 18 to form Na 2 O 2 and precipitate aluminum hydroxide or hydrate. The reaction slurry is passed through a conduit 19 to a continuous filter 20 where the hydrated alumina is removed, leached and recycled 10 through a conduit 4. A portion of the Na2 SO4 filtrate is passed through a conduit 21 to an absorption vessel 22. The residual amount of Na 2 O 2 solution is returned to the pulp plant for recycling through a conduit 23.
Røggasserne fra ovnen 7, som indeholder S02, C02, inaktiv 15 gas og damp føres gennem en ledning 24 til en cyklonudskiller 25 til fjernelse af medrevne ovnaskepartikler og recirkulation til opløsebeholderen eller blanderen. Den rensede gasstrøm passerer efter cyklonen gennem en ledning 26 ind i en spildvarme-koger 27, hvori varmen udveksles til 20 produktion af damp til fordamperne. De tilbageblevne gasser, som indeholder S02> føres gennem en ledning 28 ind i absorptionstårnet 22. I absorptionstårnet reagerer S02 med Na2S0^-opløsningen fra ledningen 21 til dannelse af NaHSO^ til brug ved syrningsreaktionen i reaktoren 17.The flue gases from furnace 7 containing SO2, CO2, inert gas and vapor are passed through a conduit 24 to a cyclone separator 25 to remove entrained furnace ash particles and recycle to the solvent container or mixer. The purified gas stream passes after the cyclone through a conduit 26 into a waste heat boiler 27, in which the heat is exchanged for the production of steam to the evaporators. The residual gases containing SO 2> are passed through a conduit 28 into the absorption tower 22. In the absorption tower, SO 2 reacts with the Na 2 SO 2 solution of conduit 21 to form NaHSO 2 for use in the acid reaction in the reactor 17.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US3718470A | 1970-05-14 | 1970-05-14 | |
US3718470 | 1970-05-14 |
Publications (2)
Publication Number | Publication Date |
---|---|
DK142000B true DK142000B (en) | 1980-08-04 |
DK142000C DK142000C (en) | 1980-12-15 |
Family
ID=21892911
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
DK231271A DK142000B (en) | 1970-05-14 | 1971-05-13 | Process for treating waste liquor from a soda-based sulfite pulp preparation. |
Country Status (7)
Country | Link |
---|---|
JP (1) | JPS506561B1 (en) |
CA (1) | CA958159A (en) |
DK (1) | DK142000B (en) |
FI (1) | FI55064C (en) |
GB (1) | GB1319417A (en) |
NO (1) | NO132938C (en) |
SE (1) | SE366565B (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP3578128B2 (en) * | 2001-09-17 | 2004-10-20 | 新菱冷熱工業株式会社 | Method and apparatus for incinerating shochu waste liquid or soy sauce waste liquid |
-
1971
- 1971-04-05 CA CA109,666A patent/CA958159A/en not_active Expired
- 1971-05-11 NO NO176171A patent/NO132938C/no unknown
- 1971-05-11 SE SE607171A patent/SE366565B/xx unknown
- 1971-05-13 DK DK231271A patent/DK142000B/en unknown
- 1971-05-13 JP JP3219071A patent/JPS506561B1/ja active Pending
- 1971-05-13 GB GB1482371A patent/GB1319417A/en not_active Expired
- 1971-05-13 FI FI133471A patent/FI55064C/en active
Also Published As
Publication number | Publication date |
---|---|
FI55064C (en) | 1979-05-10 |
GB1319417A (en) | 1973-06-06 |
NO132938C (en) | 1976-02-04 |
FI55064B (en) | 1979-01-31 |
NO132938B (en) | 1975-10-27 |
SE366565B (en) | 1974-04-29 |
DK142000C (en) | 1980-12-15 |
DE2123201B2 (en) | 1976-04-29 |
JPS506561B1 (en) | 1975-03-15 |
DE2123201A1 (en) | 1971-12-02 |
CA958159A (en) | 1974-11-26 |
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