CA1174014A - Pulp mill residual liquor recovery system - Google Patents

Pulp mill residual liquor recovery system

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Publication number
CA1174014A
CA1174014A CA000393971A CA393971A CA1174014A CA 1174014 A CA1174014 A CA 1174014A CA 000393971 A CA000393971 A CA 000393971A CA 393971 A CA393971 A CA 393971A CA 1174014 A CA1174014 A CA 1174014A
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CA
Canada
Prior art keywords
reducing gas
sulfur compounds
liquor
reaction zone
sulfur
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
CA000393971A
Other languages
French (fr)
Inventor
Xuan T. Nguyen
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Domtar Inc
Original Assignee
Domtar Inc
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Domtar Inc filed Critical Domtar Inc
Priority to CA000393971A priority Critical patent/CA1174014A/en
Application granted granted Critical
Publication of CA1174014A publication Critical patent/CA1174014A/en
Expired legal-status Critical Current

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/04Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste liquors, e.g. sulfite liquors
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C11/00Regeneration of pulp liquors or effluent waste waters
    • D21C11/12Combustion of pulp liquors
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/027Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment pyrolising or gasifying stage

Abstract

PULP MILL RESIDUAL LIQUOR RECOVERY SYSTEM
ABSTRACT OF THE DISCLOSURE
A method and apparatus for recovering chemical from residual liquor from a pulping operation, said residual liquor containing inorganic and organic compo-nents, pyrolyzing a portion of the organics in the liquor to produce a reducing gas and residual solids containing said inorganic component and the remainder of said organics, said reducing gas containing sulfur compounds, oxidizing the remainder of the organics and recombining the sulfur contained in said reducing gas with said inorganic components to produce sulfur compounds and reducing said sulfur compounds with said reducing gas.

Description

1~74014 Field of the Invention The present invention relates to a recovery system for kraft pulping process. More particularly, the present invention relates to an improved recovery system wherein at least a portion of the black liquor is pyrolyz-ed to produce a reducing gas, the pyrolyzed solids oxidiz-ed to provide oxidized inorganic solids and the gas gene-rated during pyrolyzing used to reduce the oxidized inor-ganic solids.

Background to the Invention As taught in U.S. patent 4,011,129 issued March 8, 1977 to Tomlinson, it is known to burn a portion of the black liquor from the kraft pulping in a fluidized bed oxidation zone and to direct the pellets formed during this fluidized bed oxidation onto the surface of the char bed in a conventional kraft recovery boiler and there to reduce the sodium sulfate in the pellets to sodium sulfide. This process has proved quite satisfactory and is currently being practiced at Domtar's Fine Paper Mill in Cornwall, Ontario. The reduction efficiency of the furnace has been found to have been, to some extent, adversely affected by the additional load applied thereto through the application of pellets on to the bed.
It is also well known to pyrolyze a residual pulping liquor and subsequently burn the gas generated while simultaneiously burning the remainder of the orga-nics in the liquor, thereby to generate sodium carbonate pellets and to subsequently contact the sodium carbonate pellets with SO~ derived from the burning of the remainder , 1~74~14 of the gas from the pyrolyzer to form sodium sulfate (see Canadian patent 960,811, issued January 14, 1975 to Shick).
It has also been proposed in United States Patent 4,135,968 issued January 23, 1979, to Dehass, to dry a portion of the black liquor from a kraft mill, pyrolyze~same and add the dry pyrolyzed solids to the remainder of the black liquor for injection into the recovery furnace whereby the inorganics in the pyrolyzed solids as well as in the remainder of the liquor are reduced in the recovery furnace. The gas from the pyrolyzer will generally be treated for sulfur removal and then burned in a separate unit.
In another arrangement dry residual liquor solids are pyrolyzed to produce a combustion of fuel gas from about 70% of the organics present in the dried liquor and the remaining organics and the inorganics are treated in a molten salt bath gasifier to produce further fuel gas and a smelt. The gasifier may be operated under reducing conditions so that the smelt when dissolved provides a green liquor. The fuel gases produced in the pyrolyzer and the gasifier may be burned to generate steam in a boiler.

Brief Descri tion of Present Invention p It is the ob~ect of the present invention to provide a process for recovering residual liquor from a kraft pulping operation.
Broadly the present invention relates to a process for the recovery of chemical from residual liquor , . ~ ,,, ,- 1 . ~;

1~74()14 resulting from a pulping cellulosic material comprising pyrolyzing at least a portion of the residual liquor to provide a reducing gas and residual solids containing inorganic and organic material, said reducing gas contain-ing sulfur compounds, oxidizing the organic material in said solids and recombining said sulfur in said reducing gas with said oxidized inorganics to produce other type of sulfur compounds and reducing said other type of sulfur compounds with said reducing gas. Recombining may be per-formed either in the oxidation stage or ghe reducing stage or both.
Brief Description of the Drawings Further features,-objects and advantages will be evident with the following detailed description of the preferred embodiments of the present invention taken in conjunction with the accompanying drawings in which:
Figure 1 is a schematic illustration of one form of the invention.
Figure 2 schematically illustrates a modified pyrolyzer system for incorporation into the present inven-tion.
Descri tion of the Preferred Embodiements p of the Invention As illustrated, the oxidized black liquor say, about 15% solids enters the system via line 10 and passes through a set of multiple effective evaporators 12 (only one shown) and is concentrated say, to about 50% solids leaving the system via line 14. Steam enters the evapor-ator via line 13 and condensate leaves via line 15.
The concentrated liquor in line 14 may be 1~74()~4 delivered into a spray dryer or the like 16 where it is dried and leaves as a coarse powder via line 18. The fines leaving the system via line 20 are separated from the gas stream in the cyclone 22 and pass via line 24 to line 18. Gases are removed from the cyclone 22 via line 26 and some may be recycled via line 28 back into the dryer 16.
Alternatively, the black liquor may simply be concentrated to the desired degree in the evaporators 12 and the liquor in line 14 pyrolyzed under pressure in the presence of water to provide a reducing gas and residual liquor solids containing both organic and inorganic com-ponents as will be described hereinbelow.
The powder liquor solids in line 18 passes into a pyrolyzer generally indicated at 30. During start up, fuel such as natural gas or the like enters via line 32 and the exhaust gases pass via line 34 into a fluidized bed boiler system 36. The air entering the pyrolyzer 30 passes through heat exchanger 38 to absorb heat from the exhaust gases in line 34 and then via line 40 into the pyrolyzer to provide oxygen for combustion of a natural gas or other fuel. In operation the heat necessary to operate the pyrolyzer will normally be derived from the organics in the liquor.
The pyrolyzed solids containing some of the organics, generally about 50% to 80% and normally about 70% of the organic originally in the liquor pass via line 42 to a pelletizer or the like 44 (if the particle size is so small that it would otherwise simply carry out in the A ~ ,:, 1:~74~

gas stream from the fluid bed) and are injected via line 46 into the fluid bed 36 where the organic components are burned and the inorganics accumulated in the ~orm o~
pellets. Some of the pyrolyzed powder may be recirculated to the pyrolyzer 30 via line 48. These pyrolyzed solids are relatively hot and are mixed to the powdered li~uor solids from line 18 to heat the liquor solids preferably to the temperature at which pyrolyzing may commence.
Reducing gas leaves the pyrolyzer via line 50 and may be treated in a variety of different ways depend-ing on the specific system to be employed and depending on the manner in which the pyrolyzer is operated. For example the gases may pass into a unit generally indicat-ed at 52 which may either be a sulfur separation unit or a sulfur oxidation unit or the unit may be completely by-passed. These alternatives will be discussed herein below.
The fluidized bed 36 in the illustrated arrange-ment preferably is provided with a heat exchanger gen-erally indicated at 78. In the illustrated arrangement thewater or steam enters via line 80, passes through the heat exchanger 78 which is shown in the bed and through a second heat exchanger 82 mounted in the freeboard area and steam leaves the system via 84. Alternatively fluid to be heated (steam or water) may flow in the opposite direc-tion, it being important to absorb heat from the combus-tion or oxidation occuring in the fluidized bed 36 to ensure the bed is not overheated. The bed temperature may be controlled by adding water but the use of indirect heat ~d 1: L74()~4 exchange improves the thermal efficiency of the system.
As will be apparent fluidizing air is introduced into the bed via the line 86 and oxidizes the organic materials entering the bed via the line 46 as a part of the pyrolyz-ed solids. ~aseous fuel may also be injected into theunit via line 70 either into the bed (if sufficient heat exchange surface is available) or into the freeboard and burned to generate heat which will be recovered in the boiler 78 and 82. Flue gases leave the fluidized bed 36 via line 88 and pass into the spray dryer 16 to dry the liquor entering this dryer in the figure 1 embodiment.
As above indicated the solids entering the fluid-ized bed via line 46 form pellets of sodium carbonate and sodium sulfate. These pellets as described above may be crushed in the crusher 68 to a smaller par-.
ticle size an~ then introduced into-the reducer-56. Crush-ing reduces the time required for reduction i.e the smaller the particle size the less time required for reduction. It has been found that if the particle size is too large the ceducing action is impaired, therefore, in some cases the particle size may require reduction, hcwever, the size range of the pellets normally extracted from the fluid bed (generally about 200-2000 microns range and an average of about 800 microns) are quite satisfact-ory.
While it is preferred to use the dry method i.espray dryer 16 etc. and to pyrolyze dry solids, it is also possible to take the liquor from the line 14 ~at say S0 solids~ as illustrated in figure 2, to pressurize same ..

1~74~4 with a pressurizing pump 29 and ~eed the liquor through a pressurized heater 31 heated by any suitable means and carry the heated liquor via the line 33 to a separator 35 where the reducing gas produced is separated and leaves via line 49 which connects to line sn in figure 1 ~or use in any of the three embodiments described hereinbelow.
The pyrolyzed liquor solids remaining after separation of the reducing gas passes via line 37 back to the heater 31 where heat is extracted and used to heat the liquor entering frorn line 14. The pyrolyzed solids together with any liquid (water) accompanying same passes from the heater 31 via line 45 to line 46 shown in figure 1 for injection into the fluidized bed 36. Any further heat required for pyrolyzing, may be added in the heater 31 by suitable means as indicated by the arrow 39 and the waste heat recovered, if desired, from line 41.
Either the figure 1 or figure 2 pyrolyzing con-figuration may be used with the first, second and third embodiments of the invention to be described herein below, but means may be required to treat the flue gases from the fluidized bed to ensure that sulfur loses are maintained with acceptable limits if the wet technique of figure 2 is used since the direct contacting of the liquor with the flue gas may not be used.
In either of the figure 1 or figure 2 arrange-ments, the amount of inorganics pyrolyzed will be at least sufficient to generate sufficient reducing gas to reduce the material ~inorganic solids from the residual liquor) in the reducer 56. Generally just enough reducing gas . , -s ." . , . ,.~
'~!~'';' 1~740~4 g will be generated to reduce the material unless the requirement for ~uel gas is significantly higher than the reducing gas requirements, but the sulfur content of the gas must be recovered.
First Embodiment If the unit 52 is bypassed the reducing gasses will pass directly via lines 54 and 58 into a reducer 56 which may be heated e.g. by fuel gas fed in line 59 or by a portion o~ the reducing gas line 54 directed to line 59 through a line not shown. The exhaust heating gases from the reducer pass via line 60 into the fluidized bed 36, while incoming air passes in exchange with the air in line 60 in the heat exchanger 62 and via line 64 to form combustion air for the gas entering via line 59.
Pellets formed in the fluidized bed 36 are removed from the bed, pass via line 66 and, if desired a crusher 68 into the reducer 56 where the sulfur components (Na2SO4) are reduced by the gases entering via lines 54 and 58.
Gases from the reducer pass via line ~0 into the fluidiz- -ed bed 36 for combustion and adso~btion of the SO2 by the inorganics forming the pellets and the reduced pellets leave the reducer via line 72.
It is normally preferred to introduce these ~ases from the reducer into the bed i.e directly into the fluidized bed portion where they are oxidized since these gases may contain $ulfur compound that react with the material in the bed thereby to prevent escape of SO2 and to retain the sulfur in the system. However, it is imperative that the bed temperature not exceed a certain -. . ; .

1~714~.4 maximum temperature level and if there is not adequate heat exchange available in the bed it may be necessary to introduce and burn this gas in the freeboard area where the sulfur compounds will combine with dust and the heat generated absorbed in the boiler section. Any SO2 so formed and not reacted with the dust can be scrubbed frorn the flue gas using, for example, the drier 16 or other suitable means (not shown) such as means for direct con-tact absorption by the black liquor from line 14.
Second Embodiment In an alternate arrangement the gases leaving the ~rolyzer in line 50 and containing sulfur compounds may be passed through the unit 52 which is a sulfur separator adapted to separate the reducing gas from SO2 and passes it into the reducer 56 via line 58 to reduce the pellets entering the reducer 56 via line 66.
The resu~tant reducing gases are now free of sulfur and thus may be either fed directly back to the fluidized bed as indicated via line 70 or alternatively can be passed via line 76 to form a fuel for any suitable application e.g. a calciner, power boiler, etc. The SO2 gases separated in the unit 52 pass via line 74 into the fluid bed 36 and are absorbed by the inorganics in the bed 36 or in the drier 16 or in both.
The unit 52 of the above identified arrangement may provide for catalytic oxidation and the adsorbtion of H2S and TRS emissions from the pyrolyzer using the follow-ing chemical reaction in one reactor.

~, J . ' .

1~740~4 TRS or H2S + Fe23 _ ~ Fe2S3 + ~2 (1) Sulfur is then desorbed from the iron to regenerate ferric oxide in a second reactor according to the following eq~ation.

Fe2S3 + O2(air) ~ S2 ~ Fe23 (2) The sulfur dioxide then passes via line 74 as above described into the fluidized bed 36 or some other suitable means where it contacts with the inorganics of the pulping liquor and is captured. These inorganics will include sodium sulfate and sodium carbonate. A portion of the later will react with the SO2 at the operating temperature in the fluidized bed of about 1250CF to form sodium sulfate according to the following equation:

S2 + Na2C3 ~ Na2SO4 + C2 (3) 15 Finally the sodium sulfate is reduced in the reducer 56 in accordance with the following reaction:
Na2SO4 + H2/CO~ ~ Na2 S + H2O+CO2 (4) Third Embodiment Alternatively unit 52 may function as a catalytic oxidation unit converting the H2S or TRS in the gasses leaving the pyrolizer as follows.

TRS or H2S ~ 2 - ? S2 + heat(5) -catalyst eg. activated carbon, bauxite The reducing gas now containing sulfur dioxide so generated may then be passed directly to the reducing zone via the line 58 to react with the pellets from the fluidized bed in particular the sodium carbonate in the pellets from the bed 36 as follows.

1~7~ 4 S2 + Na2a)3 ~_? Na2S04 ~ C2 ( 6 The sodium sulfate formed by the above reaction as well as any sodium sul~ate in the pellets from the fluid bed 36 further react under the reducing conditions 5 in the reducer 56 as follows:
Na2So4 + H2/C ~ Na2S + H20/C2 The gases leaving the reducer pass via line 70 back to the fluidized bed either directly into the bed or into the freeboard. Burning these gases in the freeboard 10 does not require as stringent SO2 recovery as with the first embodiment since the amount of SO~ in the gas is relatively small. Alternatively these gases may be directed via line 76 used in another suitable combustor since their sulfur content will be quite low.

Various test were conducted in the lab to prove the operability of the steps of the present invention.
1. Hardwood kraft pulping liquor was dried in a pilot plant scale co-current spray drying system having a 20 cross-sectional area and chamber height of about 1.0 ft2 and 8 ft respectively. Hot air was used as a drying gas and typical results obtained were as follows:
Drying Air StreamBlack Liquor Intlet R~sidua-l Liquor Inlet OutletFlow Temp. Solids Powder flow temp. Temp. Moisture (SCFI~I) (C) (F)Imp. Gal./hr. (C) (%) (96) 126-135 218-233 113-127 3.4 ~9-92 48.2 1.1-2.3 101-103 188 101 2.4 90 54.7 4.0
2. The burning of kraft pulping liquor produces pellets containing approximately 32% Na2SO4 by weight or ;,~, , , , . i . . . .

1~7~014 15.1 lb Na2SO4/100 lb black Liquor solids. To obtain a complete Na2SO4/Na2S conversion, assuming the following reduction reactions:
Na2So4 + ~H2 > Na2S ~ 4H20 ( 1 ) Na2SO4 + 4CO ~ Na25 + 4CO (2) A stoichiometric requir2ment of four moles of H2 or CO per mole of Na2SO4, corresponding to 0.42 lb moles reducing gas per 100 lb black liquor solids, would be required. Literature data indicated that for each 100 lb black liquor solids, the pyrolysis of kraft liquor at about 700C produced a non-condensible gas mixture with about 1.0 lb moles H2 0.15 lb moles CO, 0.10 lb moles CH4 and 0.40 lb moles of CO2. Obviously if the above gas mixture is the source of reducing gases, the completion of reactions (1) and/or (2) still leaves about 0.G8 moles of H2 and CO per 100 lb black liquor solids present in the spent reducing gas stream, i.e. more than 100% in excess of the stoichiometric requirement. Since the reducing process is not 100% efficient it will normally be necess_ ary to provide at least a slight excess of such gas over and above the ~toichiometric requirements.
3. Inorganic pellets, formed from oxidation of spent hardwood kraft pulping liquor in a fluidized bed type combustion unit, and containing about 67% sodium carbonate and 33% sodium sulfate were reduced in the solid state using CH4, CO or H2 which are known to be the principal vapour products of pyrolysis of spent kraft pulping liquor. The following sulate reduction results were obtained:

.~

~ ! ' ' , . : . ~ . , ' ~ . . !

1~74(~14 Reducing Gas Stream(3) Pellet Reducing Sulfate Reduc-Size Duration tion Effic.(l) Type Temp.
(C) (,~icrons) (hrs) (%) CH4 680254 5.0 24.7 CH4 680421 ~.~ 13.4 CO 620254 1.0 42.3 10 CO 620254 3.0 66.4 H2 620254 2.0 74.4 H2 620254 2.5 83.2 H2 620421 2.5 63.8 15 H2 620635 2.5 55.6 H2 6201060 1.0 24.2 H2 6201060 2.5 41.4 H2 6201060 5.0 83.3 20 50% H2 in Nitrogen 620254 2.0 71.2 25% H2 and 25% CO in 25 Nitrogen 620254 2.0 61.8 (1) (moles Na2S formed/initial moles Na2SO4 in pellet) (2) Temperature at the wall of the tube furnace (1.0" ID x 13" length) (3) Flow 0.3 - 0.5 l/min
4. Based on the above table and literature indica-tions that the composition of the non-condensable reducing gas produced by the pyrolysis of a spent krat pulping 35 liquor would contain about 60% H2, 10% CO2 and 6% CH4 and a typical mean pellet size from the fluid bed of abo~ 800 microns, it was estimated that to obtain about 90% overall sulfate reduction would require a total reducing time of about 6-10 hrs at a temperature of 620 to 650C.
Having described the invention, modifications will be evident to those skilled in the art without departing from the spirit of the invention as defined in the appended claims.

, ,i t~r .

Claims (7)

1. A method for the recovery of chemical from residual liquor resulting from kraft pulping of cellulosic material which sequentially comprises:
a) in a first reaction zone pyrolyzing the residual liquor to produce a reducing gas containing sulfur compounds and residual materials consisting of inorganic and organic components, with the proviso that said residual materials are in a solid or in a liquor of solid state, b) in a second reaction zone oxidizing in a fluidized bed provided therein with an internal heat extraction system said residual materials as to burn substantially all of said organic component and to accumulate said inorganic component as inorganic solids within said bed, said solids comprising at least a portion of sodium carbonate and sodium sulfate, c) thereafter in a third reaction zone reducing said inorganic solids in solid phase with said reducing gas of said first reaction zone said residual liquor from said first reaction zone being sufficient to generate the amount of said reducing gas required for reducing in said third reaction zone said inorganic solids combined with said sulfur compounds, d) directing the spent reducing gas containing sulfur compounds from said third reaction zone into said second reaction zone to convert said sulfur compounds of said reducing gas into sulfur dioxide gas and combining said sulfur dioxide gas with said inorganic solids in step b, and thereby at least partly to convert said sodium carbonate into sodium sulfate.
2. A method as defined in claim 1, which includes after said pyrolyzing removing from said first reaction zone at least a portion of the excess of reducing gas containing sulfur compounds not required to carry out step c, separating the sulfur compounds therefrom, to produce a substantially sulfur free fuel gas that is used in step c as a heat source during said reducing of said inorganic solids, and said sulfur compounds free from said reducing gas are catalytically oxidized and fed into said fluidized bed to react with said inorganic solids.
3. A method as defined in claim 1 wherein a portion of said sulfur compounds is separated from said reducing gas and converted into sulfur dioxide, said sulfur com-pounds being converted into sulfur dioxide into another zone, and then fed into at least one of said second and third zone to be combined with said sodium carbonate portion.
4. A method as defined in claim 1 wherein said residual materials oxidized in said fluidized bed form pellets comprising predominantly sodium carbonate and sodium sulfate and wherein in said third zone, said sodium sulfate contained in said pellets is reduced to sodium sulfide.
5. A method as defined in claims 1, 2 or 4 wherein substantially all of said sulfur compounds originally from said pyrolyzing and which is not combined with the inorganic solids is recycled into said second zone.
6. A method as defined in claims 1 or 4, wherein at least a major portion of said sulfur compounds from said pyrolyzing is fed to said third zone.
7. A method as defined in claim 2, wherein at least portion of the reducing gas is oxidized to generate recoverable heat.
CA000393971A 1982-01-12 1982-01-12 Pulp mill residual liquor recovery system Expired CA1174014A (en)

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Application Number Priority Date Filing Date Title
CA000393971A CA1174014A (en) 1982-01-12 1982-01-12 Pulp mill residual liquor recovery system

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Application Number Priority Date Filing Date Title
CA000393971A CA1174014A (en) 1982-01-12 1982-01-12 Pulp mill residual liquor recovery system

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0312742A2 (en) * 1987-10-23 1989-04-26 Klöckner-Humboldt-Deutz Aktiengesellschaft Process for the thermal treatment of organic or organically contaminated waste
US5582683A (en) * 1994-04-19 1996-12-10 International Paper Company Method for the recovery of chemical values from black liquor in multiple streams of different chemical values

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0312742A2 (en) * 1987-10-23 1989-04-26 Klöckner-Humboldt-Deutz Aktiengesellschaft Process for the thermal treatment of organic or organically contaminated waste
EP0312742A3 (en) * 1987-10-23 1990-03-28 Klöckner-Humboldt-Deutz Aktiengesellschaft Process for the thermal treatment of organic or organically contaminated waste
US5582683A (en) * 1994-04-19 1996-12-10 International Paper Company Method for the recovery of chemical values from black liquor in multiple streams of different chemical values

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