CA1205930A - Method for the purification of condensates from the sulfate process - Google Patents
Method for the purification of condensates from the sulfate processInfo
- Publication number
- CA1205930A CA1205930A CA000400790A CA400790A CA1205930A CA 1205930 A CA1205930 A CA 1205930A CA 000400790 A CA000400790 A CA 000400790A CA 400790 A CA400790 A CA 400790A CA 1205930 A CA1205930 A CA 1205930A
- Authority
- CA
- Canada
- Prior art keywords
- condensates
- condensate
- column
- accordance
- compounds
- 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
Links
- 238000000034 method Methods 0.000 title claims abstract description 28
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 title claims abstract description 9
- 238000000746 purification Methods 0.000 title claims description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000007789 gas Substances 0.000 claims abstract description 12
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 6
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 6
- 239000001301 oxygen Substances 0.000 claims abstract description 6
- 239000003921 oil Substances 0.000 claims description 13
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 9
- 238000004581 coalescence Methods 0.000 claims description 8
- 238000011282 treatment Methods 0.000 claims description 7
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 4
- 239000007787 solid Substances 0.000 claims description 4
- 238000001914 filtration Methods 0.000 claims description 3
- 239000005864 Sulphur Substances 0.000 claims 1
- 239000012670 alkaline solution Substances 0.000 claims 1
- 239000003575 carbonaceous material Substances 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract 1
- 231100000719 pollutant Toxicity 0.000 abstract 1
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 29
- 150000001875 compounds Chemical class 0.000 description 19
- LSDPWZHWYPCBBB-UHFFFAOYSA-N Methanethiol Chemical compound SC LSDPWZHWYPCBBB-UHFFFAOYSA-N 0.000 description 18
- 238000001704 evaporation Methods 0.000 description 13
- 230000008020 evaporation Effects 0.000 description 13
- 230000003647 oxidation Effects 0.000 description 12
- 238000007254 oxidation reaction Methods 0.000 description 12
- 239000000126 substance Substances 0.000 description 11
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
- 229910052717 sulfur Inorganic materials 0.000 description 7
- 239000011593 sulfur Substances 0.000 description 7
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 6
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 6
- 239000000463 material Substances 0.000 description 6
- 238000002474 experimental method Methods 0.000 description 5
- 239000002655 kraft paper Substances 0.000 description 5
- 238000012360 testing method Methods 0.000 description 5
- 241000196324 Embryophyta Species 0.000 description 4
- 238000004458 analytical method Methods 0.000 description 4
- 239000003054 catalyst Substances 0.000 description 4
- 230000029087 digestion Effects 0.000 description 4
- 238000004817 gas chromatography Methods 0.000 description 4
- 239000012071 phase Substances 0.000 description 4
- 230000008929 regeneration Effects 0.000 description 4
- 238000011069 regeneration method Methods 0.000 description 4
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 description 4
- 231100000331 toxic Toxicity 0.000 description 4
- 230000002588 toxic effect Effects 0.000 description 4
- 239000001913 cellulose Substances 0.000 description 3
- 229920002678 cellulose Polymers 0.000 description 3
- 229920001021 polysulfide Polymers 0.000 description 3
- 239000005077 polysulfide Substances 0.000 description 3
- 150000008117 polysulfides Polymers 0.000 description 3
- 238000011160 research Methods 0.000 description 3
- 239000000344 soap Substances 0.000 description 3
- 235000011121 sodium hydroxide Nutrition 0.000 description 3
- 229910052979 sodium sulfide Inorganic materials 0.000 description 3
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 3
- RTZKZFJDLAIYFH-UHFFFAOYSA-N Diethyl ether Chemical compound CCOCC RTZKZFJDLAIYFH-UHFFFAOYSA-N 0.000 description 2
- 241000779819 Syncarpia glomulifera Species 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- WQOXQRCZOLPYPM-UHFFFAOYSA-N dimethyl disulfide Chemical compound CSSC WQOXQRCZOLPYPM-UHFFFAOYSA-N 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 125000002496 methyl group Chemical group [H]C([H])([H])* 0.000 description 2
- 150000002898 organic sulfur compounds Chemical class 0.000 description 2
- 239000001739 pinus spp. Substances 0.000 description 2
- 235000010265 sodium sulphite Nutrition 0.000 description 2
- 238000004448 titration Methods 0.000 description 2
- 229940036248 turpentine Drugs 0.000 description 2
- 238000011144 upstream manufacturing Methods 0.000 description 2
- RSWGJHLUYNHPMX-UHFFFAOYSA-N Abietic-Saeure Chemical class C12CCC(C(C)C)=CC2=CCC2C1(C)CCCC2(C)C(O)=O RSWGJHLUYNHPMX-UHFFFAOYSA-N 0.000 description 1
- 241000972773 Aulopiformes Species 0.000 description 1
- DKPFZGUDAPQIHT-UHFFFAOYSA-N Butyl acetate Natural products CCCCOC(C)=O DKPFZGUDAPQIHT-UHFFFAOYSA-N 0.000 description 1
- XDTMQSROBMDMFD-UHFFFAOYSA-N Cyclohexane Chemical compound C1CCCCC1 XDTMQSROBMDMFD-UHFFFAOYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- KHPCPRHQVVSZAH-HUOMCSJISA-N Rosin Chemical class O(C/C=C/c1ccccc1)[C@H]1[C@H](O)[C@@H](O)[C@@H](O)[C@@H](CO)O1 KHPCPRHQVVSZAH-HUOMCSJISA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- NEDPBMIBOQZRIS-UHFFFAOYSA-N [Na].S=S Chemical compound [Na].S=S NEDPBMIBOQZRIS-UHFFFAOYSA-N 0.000 description 1
- 230000001154 acute effect Effects 0.000 description 1
- 238000007792 addition Methods 0.000 description 1
- 230000002730 additional effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000004587 chromatography analysis Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 238000006073 displacement reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 150000002148 esters Chemical class 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 239000000727 fraction Substances 0.000 description 1
- 239000003205 fragrance Substances 0.000 description 1
- ZZUFCTLCJUWOSV-UHFFFAOYSA-N furosemide Chemical compound C1=C(Cl)C(S(=O)(=O)N)=CC(C(O)=O)=C1NCC1=CC=CO1 ZZUFCTLCJUWOSV-UHFFFAOYSA-N 0.000 description 1
- FUZZWVXGSFPDMH-UHFFFAOYSA-M hexanoate Chemical compound CCCCCC([O-])=O FUZZWVXGSFPDMH-UHFFFAOYSA-M 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 235000019988 mead Nutrition 0.000 description 1
- -1 methanol Chemical class 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- HEDOODBJFVUQMS-UHFFFAOYSA-N n-[2-(5-methoxy-1h-indol-3-yl)ethyl]-n-methylpropan-2-amine Chemical group COC1=CC=C2NC=C(CCN(C)C(C)C)C2=C1 HEDOODBJFVUQMS-UHFFFAOYSA-N 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 229920001515 polyalkylene glycol Polymers 0.000 description 1
- 238000003918 potentiometric titration Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 235000019515 salmon Nutrition 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- APSBXTVYXVQYAB-UHFFFAOYSA-M sodium docusate Chemical compound [Na+].CCCCC(CC)COC(=O)CC(S([O-])(=O)=O)C(=O)OCC(CC)CCCC APSBXTVYXVQYAB-UHFFFAOYSA-M 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-M sodium hydrosulfide Chemical compound [Na+].[SH-] HYHCSLBZRBJJCH-UHFFFAOYSA-M 0.000 description 1
- HYHCSLBZRBJJCH-UHFFFAOYSA-N sodium polysulfide Chemical compound [Na+].S HYHCSLBZRBJJCH-UHFFFAOYSA-N 0.000 description 1
- AKHNMLFCWUSKQB-UHFFFAOYSA-L sodium thiosulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=S AKHNMLFCWUSKQB-UHFFFAOYSA-L 0.000 description 1
- 235000019345 sodium thiosulphate Nutrition 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 150000004763 sulfides Chemical class 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
- 239000003784 tall oil Substances 0.000 description 1
- 125000004055 thiomethyl group Chemical group [H]SC([H])([H])* 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000820 toxicity test Toxicity 0.000 description 1
- KHPCPRHQVVSZAH-UHFFFAOYSA-N trans-cinnamyl beta-D-glucopyranoside Chemical class OC1C(O)C(O)C(CO)OC1OCC=CC1=CC=CC=C1 KHPCPRHQVVSZAH-UHFFFAOYSA-N 0.000 description 1
- 239000003039 volatile agent Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
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
- D21C11/06—Treatment of pulp gases; Recovery of the heat content of the gases; Treatment of gases arising from various sources in pulp and paper mills; Regeneration of gaseous SO2, e.g. arising from liquors containing sulfur compounds
- D21C11/08—Deodorisation ; Elimination of malodorous compounds, e.g. sulfur compounds such as hydrogen sulfide or mercaptans, from gas streams
-
- 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
- D21C11/0057—Oxidation of liquors, e.g. in order to reduce the losses of sulfur compounds, followed by evaporation or combustion if the liquor in question is a black liquor
Landscapes
- Treating Waste Gases (AREA)
- Paper (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Carbon And Carbon Compounds (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Abstract
ABSTRACT OF THE DISCLOSURE
Condensates from the sulfate process are freed from a main portion of the pollutants and foul components by being passed with an oxygen-containing gas concurrently through a column containing activated carbon.
Condensates from the sulfate process are freed from a main portion of the pollutants and foul components by being passed with an oxygen-containing gas concurrently through a column containing activated carbon.
Description
`` ~205~3~
-r~he present invention relates to a method for the purification o~ condensates from the sulfa~e process.
In the production of cellulose according to the sulfate process the fibrous raw material (generally wood chips) i~ treated under high pressure and high temperature with so called white liquor~ the 'active chemicals of which are so-dium hydroxide and sodium sulfide (l,Z). Additionally, some manufacturers use other chemicals, e.g. polysulfide.
lQ
After digestion the' fibrous materi~l (sulfate cellulose or kraft pulp) is separated from the dissolved organi~ material and the inorganic chemicals. Because of its colour the liquid phase is now called black liquor.
Said black liquor is now concentxated to such a high solids content that it can ~e burnt. Heat is, thus, released (possibly electric power can be obtained), and inorganic chemicals are recovered and may be converted to white liquor chemicals, which is necessary ~o make the process economical. Some volatile compounds (turpentine methanol and others) and air are 'removed separately from the digester or are separated from the black liquor when it is subjected to reduced pressure (as compared to the digestion pressure).
Aftex cooling, certain of said components will leave with the water steam to ~e condensed. The water insoluble phase is generally called sulfate turpentine. The condensates from this process are generally called digester condensates.
Concen'tration of the black liquor, including the ' 3Q washing water from the'displacement of black liquor from the cellulose,'is generally carried out in a multi-step evaporation plant, partly in a vacuum. Evaporated water is discharged as con-~Z05~3~ -, . .
densates. To~ether with any water from the vacuum pump of the plant, the wa-ter dlscharged at this sta~e is called evapora-tion condensa-tes. Apart from the portion origina-ting from indirect heatin~ with live steam, said evaporation condensates are also more or less polluted In some plants part of the s-team from the digèstion process is used for pre-evaporation of the black liquor. Such pre-evaporation results in condensates considered as something between digester and evaporation condensatesO rrhe different kinds of stripping steam and condensates can be lin~ed to-;
s ~ ~o~ , A.'s gether in various manh~Es in the process~ ~L~Y:, th~t is~
of no concern in this connection~
A soap (sulfate soap) is separated from black liquor. It consists mainly of saponified fatty acids and rosin acids (abietic acids), but it also contains unsaponified com-pounds. Said soap is generally recovered and typically con-verted to so called tall oil. The evaporation condensates will also contain more or less finely divided "oil", i.e. a water insoluble phase that is disadvantageous to any fur-ther treatment of the condensates.
It is common to all the above mentioned condensates that they contain various volatile substances, some of which are lower sulfur containing compounds. Especially during evapo-ration foul and toxic gases, e.g. hydro~en sulfide (H2S), methyl mercap~an (C~3S~I) and the like, escape from the black liquor, and quite a significant portion of these wiil be found in the condensates. Thus, said condensates have an obnoxious smell and are toxic.
Their content of methanol and the ]ike makes condensate effluents a pollution load on the recipient because dis-solved organic material will cause a chemical oxygen demand(COD) and a biochemical oxygen demand (BOV). These three factors, namelythe obnoxious smell, the toxicity to aquatic life, and the organlc~` load cause the c~nden,~tes from the . ' ~
. :
.
lZ~9;~
kraft process to represen-t a serious environmental hazard.
The possibili-ties of reusing unpurified condensates as a - source of li~uor in the process are also limited because they release toxic and foul gases and contain finely divided oils.
The methods in use today for puri:Fying the condensates from the kraft process are primarily based on the removal of volatile compounds (among others methanol and substances having an obnoxious smell) by the`aid of steam and air (stripping) (2a,2b). The removed gases/vapours are typical-ly destroyed by burning together with any non-condensable gases from the digestion and recovery process.
A process of purification based on decomposition by the aid of microorganisms is also used (3).
.
It is an object of the`present inven-tion to remove the foul substances in the condensates by combined oxidation and ad-sorption after a preceding removal of finely divided oil, inter alia by coalescence when that is necessary. A smallpilot plant has been tested for a few years in a Norwegian kraft mill for examination of various types of condensates, catalysts, life times and possib~e means of regeneration of the catalysts and so on.
It is known that hydrogen sulfide gas in air is oxidized on a suitable catalyst, e.g. activated carbon. In said gas reaction H2S is converted to elemental sulfur. Said process may be extended to sulfur diox~de (S02), which is also (to-gether with some S03) the final product when H2S, sulfur and many other sulfur compounds are burned~ I-t has also been sugges-ted to purify foul gases by the aid of alkali and activa-ted carbon.
Hydrogen sulfide is soluble in alkali, e.g. caustic soda with formation of sulfides(NaHS and /or Na2S in NaOH). In ~- the very stron~ly basic white liquor from the sulfate pro-- ~205~30 ,, ~ . , cess sodium hydroxide and sodium sulfide are as mentioned the active digestion chemieals. Such a white liquor is slowly oxidized by air, and the oxidation pr~ducts will be sodium sulfite~ sodium thiosulfate and sodium sul~ate. In the presence of a suitable oxygen converter or eatalyst the oxidation time may be eonsiderably reduced, and sodium poly-sulfide and sodium thiosulfide are formed. By way of example admixture of a eertain portion of blaek liquor (PFI-patent) or use of a speeial eatalyst mass (Meads Moxy proeess) (4,5) 1~ may be mentioned.
Activated carbon is generally known in the art of purification for the removal of small amoun-ts of eontamin-ants. This is based on the large internal surface area of the substanee~ The surfaee will be blocked by the adsorbed substance, and some kind of regeneration will be neeessary in eases of larger amounts of eontaminants.
According to the present invention there is provided a method for the purification o~ condensates from the sulfate proeess which com-prises passiny the condensates eoncurrelltly with an oxygen-containing gas through a column containing activated earbon.
~, EXPERIMENTS
Polluted and fou`l condensates from a kraft mill are passed with air through a eolumn filled with aetivated earbon.
Preliminary tests showed that 1) The obnoxious smell was removed by said treatment.
-r~he present invention relates to a method for the purification o~ condensates from the sulfa~e process.
In the production of cellulose according to the sulfate process the fibrous raw material (generally wood chips) i~ treated under high pressure and high temperature with so called white liquor~ the 'active chemicals of which are so-dium hydroxide and sodium sulfide (l,Z). Additionally, some manufacturers use other chemicals, e.g. polysulfide.
lQ
After digestion the' fibrous materi~l (sulfate cellulose or kraft pulp) is separated from the dissolved organi~ material and the inorganic chemicals. Because of its colour the liquid phase is now called black liquor.
Said black liquor is now concentxated to such a high solids content that it can ~e burnt. Heat is, thus, released (possibly electric power can be obtained), and inorganic chemicals are recovered and may be converted to white liquor chemicals, which is necessary ~o make the process economical. Some volatile compounds (turpentine methanol and others) and air are 'removed separately from the digester or are separated from the black liquor when it is subjected to reduced pressure (as compared to the digestion pressure).
Aftex cooling, certain of said components will leave with the water steam to ~e condensed. The water insoluble phase is generally called sulfate turpentine. The condensates from this process are generally called digester condensates.
Concen'tration of the black liquor, including the ' 3Q washing water from the'displacement of black liquor from the cellulose,'is generally carried out in a multi-step evaporation plant, partly in a vacuum. Evaporated water is discharged as con-~Z05~3~ -, . .
densates. To~ether with any water from the vacuum pump of the plant, the wa-ter dlscharged at this sta~e is called evapora-tion condensa-tes. Apart from the portion origina-ting from indirect heatin~ with live steam, said evaporation condensates are also more or less polluted In some plants part of the s-team from the digèstion process is used for pre-evaporation of the black liquor. Such pre-evaporation results in condensates considered as something between digester and evaporation condensatesO rrhe different kinds of stripping steam and condensates can be lin~ed to-;
s ~ ~o~ , A.'s gether in various manh~Es in the process~ ~L~Y:, th~t is~
of no concern in this connection~
A soap (sulfate soap) is separated from black liquor. It consists mainly of saponified fatty acids and rosin acids (abietic acids), but it also contains unsaponified com-pounds. Said soap is generally recovered and typically con-verted to so called tall oil. The evaporation condensates will also contain more or less finely divided "oil", i.e. a water insoluble phase that is disadvantageous to any fur-ther treatment of the condensates.
It is common to all the above mentioned condensates that they contain various volatile substances, some of which are lower sulfur containing compounds. Especially during evapo-ration foul and toxic gases, e.g. hydro~en sulfide (H2S), methyl mercap~an (C~3S~I) and the like, escape from the black liquor, and quite a significant portion of these wiil be found in the condensates. Thus, said condensates have an obnoxious smell and are toxic.
Their content of methanol and the ]ike makes condensate effluents a pollution load on the recipient because dis-solved organic material will cause a chemical oxygen demand(COD) and a biochemical oxygen demand (BOV). These three factors, namelythe obnoxious smell, the toxicity to aquatic life, and the organlc~` load cause the c~nden,~tes from the . ' ~
. :
.
lZ~9;~
kraft process to represen-t a serious environmental hazard.
The possibili-ties of reusing unpurified condensates as a - source of li~uor in the process are also limited because they release toxic and foul gases and contain finely divided oils.
The methods in use today for puri:Fying the condensates from the kraft process are primarily based on the removal of volatile compounds (among others methanol and substances having an obnoxious smell) by the`aid of steam and air (stripping) (2a,2b). The removed gases/vapours are typical-ly destroyed by burning together with any non-condensable gases from the digestion and recovery process.
A process of purification based on decomposition by the aid of microorganisms is also used (3).
.
It is an object of the`present inven-tion to remove the foul substances in the condensates by combined oxidation and ad-sorption after a preceding removal of finely divided oil, inter alia by coalescence when that is necessary. A smallpilot plant has been tested for a few years in a Norwegian kraft mill for examination of various types of condensates, catalysts, life times and possib~e means of regeneration of the catalysts and so on.
It is known that hydrogen sulfide gas in air is oxidized on a suitable catalyst, e.g. activated carbon. In said gas reaction H2S is converted to elemental sulfur. Said process may be extended to sulfur diox~de (S02), which is also (to-gether with some S03) the final product when H2S, sulfur and many other sulfur compounds are burned~ I-t has also been sugges-ted to purify foul gases by the aid of alkali and activa-ted carbon.
Hydrogen sulfide is soluble in alkali, e.g. caustic soda with formation of sulfides(NaHS and /or Na2S in NaOH). In ~- the very stron~ly basic white liquor from the sulfate pro-- ~205~30 ,, ~ . , cess sodium hydroxide and sodium sulfide are as mentioned the active digestion chemieals. Such a white liquor is slowly oxidized by air, and the oxidation pr~ducts will be sodium sulfite~ sodium thiosulfate and sodium sul~ate. In the presence of a suitable oxygen converter or eatalyst the oxidation time may be eonsiderably reduced, and sodium poly-sulfide and sodium thiosulfide are formed. By way of example admixture of a eertain portion of blaek liquor (PFI-patent) or use of a speeial eatalyst mass (Meads Moxy proeess) (4,5) 1~ may be mentioned.
Activated carbon is generally known in the art of purification for the removal of small amoun-ts of eontamin-ants. This is based on the large internal surface area of the substanee~ The surfaee will be blocked by the adsorbed substance, and some kind of regeneration will be neeessary in eases of larger amounts of eontaminants.
According to the present invention there is provided a method for the purification o~ condensates from the sulfate proeess which com-prises passiny the condensates eoncurrelltly with an oxygen-containing gas through a column containing activated earbon.
~, EXPERIMENTS
Polluted and fou`l condensates from a kraft mill are passed with air through a eolumn filled with aetivated earbon.
Preliminary tests showed that 1) The obnoxious smell was removed by said treatment.
2) EIydrogen sulfide and methyl mercaptan were removed (de-monstrated by potensiometrie titrations).
.
.
3) The smell, hydrogen sulfide and methyl mereaptan were not ~rt ~- 4 -lZ~93(;~
. .
removed, unless sufficient amounts of air were passed with the liquid.
. .
removed, unless sufficient amounts of air were passed with the liquid.
4~ The column lost its efficency after some time.
In addition to the fact that it was possible to remoye the obnoxious smell, hydrogen sulfide, and methyl mercaptan ~y this method, the tests disclosed that what had taken place had to be an air oxidation (items 1, ~, 3) 1~ and that the . .
.
~ - 4a -., ~
: ~Z~S~3(~
column material had been active (item 4), i.e. that a cata-lytic oxidation had occurred.
It was assumed that hydrogen sulfide was oxidized to elemen-tary sulfur, which remained on the column material. This assumption was corroborated by the fact that hot white li-;
quor passed through a column was enriched with polysulfide. (Colour yellow/orange/red, dependent on the concentration. Determined quantitatively by potensiometriG
titration after conversion to an equivalent amount of thio-~- sulfate by sodium sulfite.~ It is known that elementary sulfur is dissolved in sulfide solutions, e.g~ white and green liquor. The test, thus, also showed -thai th~ sulfate process itself provides chemicals that may be used to libe-- 15 rate the column material from the deposited sul~ur.
.
The untreated condensate contained oil-li~e droplets of varying amounts and droplet sizes. After havin~ passed through said column the condensate, however, was perfectly - 20 clear. Such oil deposition assumedly must reduce the active surface of the column material. This was corroborated by the fact that the column after losing its efficiency was made efficient again after treatment with steam at approxi-mately l~O til 190C.
Observations of the condensates for some time showed that the amount of oil could var~ within wide limits . Efforts were, thus, made to remove the oil before the condensate reached ~he column. An efficient oil removal was achieved by first removing large droplets that were allowed to float on top of the aquous phase and then removing the finely divided floating oil droplets from the water phase by coa-lescence.
Samples of the cleared condensates after coalescence fil-tra-tion were extracted with organic solvents and -the extracts were examined by gas chromatography. The analyses showed that a large amoun-t of polar and non-polar orqanic com-~ ' ' .
12~ 306 pounds were present. Corresponding analyses of samples taken aEter the condensates had passed through -the column showec1 that said compounds were almost cornpletely removed by -the treatment. The compounds detec-ted by said method oE~
analysis were assumed to be higher organic sulfur compounds.
Since these compounds as well as hydrogen sulfide and lower organic sulfur compounds are expected to have an acute toxic effect on the life in the recipient, condensate samples were used for mortality tests with salmon fry. I-t was found that the untrea-ted condensates were 3 to 35 times more toxic than the treated on~s.
.
The toxicity tests ~96 hours - LC50) were carried out at the Norwegian Institute of Water Research (NIV~). The gas chromatographic investigations were carried out at the Norwegian Central Institute for Indus-trial Research (SI), among others by the aid of a ~lass capillary column and a `
flame ionization detector. The content of low boilin~ orga-nic compounds, e.g. methanol, was studied at -the Norwegian Pulp and Paper Research Institute (PFI) ~y the aid of gas chromatography with a polyalkylene glycol column and a hot wire detector. In addi-tion to methanol there were ound traces of another compound (assessed at less than 1,5% of the amount of methanol). This indicatès that methanol could in pratice be enriched from the purified condensates with-out too great demands on fractionated separa-tion. Examina-tions oE volatiles by head-space-technique showed a re-duction of the num~er and the total content of escaping odourants at 40C (SI).
The pilot plant used is shown in a flow sheet of the accom-panying drawings. Its construction is as follows:
By the aid of valves (1,2) and pumps (Pl,P2) a portion of the flow was taken from the condensate line ~in the embodi-ment shown in the drawing it is taken from the outlet of the evaporation stage). Any solids and larger oil droplets are separated in a preliminary filter (3) having an over-. ~ , .
. .
IZ~ 3t~
flow (4). The coalescence uni-t consists of two parallel coalescence filter cartridges (5~ of the Bdls-ton type. The oxidation is carried out in a 4 m long steel column contain-ing 8 l of catalyst mass. The column receives condensate (alternatively white liquor for the removal of deposited sulfur) via pump (P3) and a flowmeter (9), it receives compressed air via a meter (l8) and steam for regeneration.
The efficiency of the column is monitored by a H2S detector mounted below the cover of the collecting tank and additio-nal control is achieved by sampling for assessment of theodour and for potentiometric titration of H2S and CH3SH.
.
-Examination of the Efficiency of the Oxidation Column:
~ `
15 Column material: Activated carbon, 8 litres, ~rain size 0~5-2 r5 mm Type Lurgi Hydraffin LS supra Note: Preliminary tests carried out with inter alia ordinary activated carbon lacking technical specifications and bought in a shop in Oslo yielded corresponding results às regards odour, H2S and CH2SH.
The column was filled on Oc-t. 2nd/ 1979.
Experiments were carried out from Oct. 2nd to Oct. 4th, 1979.
Incoming condensate: EVAPORATION CONDENSATES:
H2S Orl - 0~9 g S/l CH3SH o 0 3 Ei2S + CH3SH O~l - lr2 g S/l pH 7,~6 - 8~0 Outgoing condensate:
H2S + CH3SH O g S/l pH approx. 9~7 Amount of condensate 15 l/h, totally 720 l Amount of air approx. 40 l/h,totally 1800 l Totally removed H2S ~ CH3SH corresponding to 360 ~ S
Regenerated with approx. 5 kg steam (190C, 13 kg/cm Continued Oct. 15 - Oct. 17.
~ , .
.
l2~8sg~ `
Incoming condensate: -S 0~0~7 ~ S/l 13SH 0~0,r3 H2S + HC3S11 0~.2 ~ 0 g S/l pH approx~ 8 Outgoing condensateo H2S + CH3SH O g S/l pH approx. 9~.6 Amount of condensate 15 l/h, totally~ ~50 1 Amount of air ~ 40 r~ 1/ (31.0 1 Totally removed l12S -~ CH3SH corresponding to 2 O ~ S
Continued Oct. 22, - Oct. 25, Amoun-t of condensate totally 600 1 Amount of air " 1630 1 ~ pH (in) approx. 8 pH (out) " 9~5 Totally removed H2S + CH3SH corresponding to 310 g S
Amount of condensate after previous steam regeneration:
350 1 + 600 1 = 950 1 Amount of condensate totally: 720 1 + 950 1 = 1470 1 Removed 112S + CH3SH totally corresponding to 54Q g S
Regenerated wi h approx. 6 kg steam (190C, 12~ kg/cm2) Regenerated with approx. 4~1 1 hot white liquor, 30 min.
Drained off Li~uor containing polysulfide. Washed with approximately 40 l water.
Continued February 25th - 27th, 1~80 ~mount of condensate totally 330 1 ~ount of air " 1000 1 pH (in) approx. 7~8 pH (out) " 9~7 Totally removed H2S + CH3SH corresponding to 230 g/S
Continued March 4th Rn~ount of condensate totally 470 i Amount of air ~ " 1400 1 Totally removed H2S -~ CH3SH corresponding to 330 g/S
- 560 g/S
:
: ..
~205~30 The series of experiments was ended after the -treatment of totall~ 2270 1 of non-purified evaporation condensate and removal of ~2S ~ CH3SH corresponding to 1430 g sulfur.
Experiment carried out May 28th - Oct. 9th 1980: Di~ester Condensate Column ma-terial as above Column filled May 21st Incoming condensate:
~ H2S + CH3SH traces pH 9~0 - 9 Outgoing condensate:
H2S + CH3SH O ~/
pH 9t`5 10 p Amount of condensate: 15 l/h, totally approx. 5000 1 Amount o air ~0 " " " 13300 1 Experiment completed, column still efficient.
Gas Chromatographic Analyses (carried out by SI) Extraction with cyclohexane involves non-polar compounds, ~ollowe~ by acidification and extraction with butyl acetate and deri~ation with a trimethylsilyl-reagent to determine the more polar compounds. The first mentioned were studied in a ~lass capillary column, the last mentioned in a packed column, both by the aid of a flame ionization detector.
Evaporation Condensate from Oct. 17th, 73 The amounts of both non-polar and polar compounds were very much reduced after the condensate treatment in -the oxida-tion ~olumn. The main component of the non-polar compounds was reduced approximately ?0 000 times ~from 60 ppm to 3.10 3 ppm). A reduction of approximately 600 times was found for the main component of polar compounds.
~205~30 Digester Condensate from early in June 1980 For the non-polar compounds a reduction of approx. 160 times was found. In the polar frac-tion no compounds were found in the sample taken after the oxidation column, which corresponds to a reduction of at least 200 times, based on;
the detection limit.
.
Odour Analyses by ~ead-space Technique (carried out by SI) The evaporation condensate samples from upstreams and down-streams the oxidation column were heated to ~0Cfbr 1 hour, and the gas above the liquid (head-space) was extracted, concentrated on activated carbon and analyzed by gas chro-matography. Great difference of the samples was re~orted,approximately hàlf of the compounds from the sample up-streams of the oxidation ~eing absent in the sample down-streams of the oxidation. The total content is approximate-ly 4 times higher in the untreated sample. A few new vola-tile compounds seemed to have been produced, but these werepresent in very small amounts. The main compound present seems to be dimethyl disulfide.
Destillation of Metanol and Determina-tion of its Purity Methanol was destilled off (amounting to approx. 5 g/l) and was analysed by gas chromatography at PFI. The chromato~rams only showed traces of one compound in addition to methanol, ~ the amount of which was assessed to be less than 1~.5% of the amount of metanol.
Coalescence The efficiency of coalescence filtration was proven by the fact that 1) "oil" accumulated on top of the unit and that 2) the condensate was often mil~ upstreams of the unit and clear downstreams. The oil content in the un-treated condensates varies within very wide llmits.
~ , :
... ... . ,. .. ~.. .
In addition to the fact that it was possible to remoye the obnoxious smell, hydrogen sulfide, and methyl mercaptan ~y this method, the tests disclosed that what had taken place had to be an air oxidation (items 1, ~, 3) 1~ and that the . .
.
~ - 4a -., ~
: ~Z~S~3(~
column material had been active (item 4), i.e. that a cata-lytic oxidation had occurred.
It was assumed that hydrogen sulfide was oxidized to elemen-tary sulfur, which remained on the column material. This assumption was corroborated by the fact that hot white li-;
quor passed through a column was enriched with polysulfide. (Colour yellow/orange/red, dependent on the concentration. Determined quantitatively by potensiometriG
titration after conversion to an equivalent amount of thio-~- sulfate by sodium sulfite.~ It is known that elementary sulfur is dissolved in sulfide solutions, e.g~ white and green liquor. The test, thus, also showed -thai th~ sulfate process itself provides chemicals that may be used to libe-- 15 rate the column material from the deposited sul~ur.
.
The untreated condensate contained oil-li~e droplets of varying amounts and droplet sizes. After havin~ passed through said column the condensate, however, was perfectly - 20 clear. Such oil deposition assumedly must reduce the active surface of the column material. This was corroborated by the fact that the column after losing its efficiency was made efficient again after treatment with steam at approxi-mately l~O til 190C.
Observations of the condensates for some time showed that the amount of oil could var~ within wide limits . Efforts were, thus, made to remove the oil before the condensate reached ~he column. An efficient oil removal was achieved by first removing large droplets that were allowed to float on top of the aquous phase and then removing the finely divided floating oil droplets from the water phase by coa-lescence.
Samples of the cleared condensates after coalescence fil-tra-tion were extracted with organic solvents and -the extracts were examined by gas chromatography. The analyses showed that a large amoun-t of polar and non-polar orqanic com-~ ' ' .
12~ 306 pounds were present. Corresponding analyses of samples taken aEter the condensates had passed through -the column showec1 that said compounds were almost cornpletely removed by -the treatment. The compounds detec-ted by said method oE~
analysis were assumed to be higher organic sulfur compounds.
Since these compounds as well as hydrogen sulfide and lower organic sulfur compounds are expected to have an acute toxic effect on the life in the recipient, condensate samples were used for mortality tests with salmon fry. I-t was found that the untrea-ted condensates were 3 to 35 times more toxic than the treated on~s.
.
The toxicity tests ~96 hours - LC50) were carried out at the Norwegian Institute of Water Research (NIV~). The gas chromatographic investigations were carried out at the Norwegian Central Institute for Indus-trial Research (SI), among others by the aid of a ~lass capillary column and a `
flame ionization detector. The content of low boilin~ orga-nic compounds, e.g. methanol, was studied at -the Norwegian Pulp and Paper Research Institute (PFI) ~y the aid of gas chromatography with a polyalkylene glycol column and a hot wire detector. In addi-tion to methanol there were ound traces of another compound (assessed at less than 1,5% of the amount of methanol). This indicatès that methanol could in pratice be enriched from the purified condensates with-out too great demands on fractionated separa-tion. Examina-tions oE volatiles by head-space-technique showed a re-duction of the num~er and the total content of escaping odourants at 40C (SI).
The pilot plant used is shown in a flow sheet of the accom-panying drawings. Its construction is as follows:
By the aid of valves (1,2) and pumps (Pl,P2) a portion of the flow was taken from the condensate line ~in the embodi-ment shown in the drawing it is taken from the outlet of the evaporation stage). Any solids and larger oil droplets are separated in a preliminary filter (3) having an over-. ~ , .
. .
IZ~ 3t~
flow (4). The coalescence uni-t consists of two parallel coalescence filter cartridges (5~ of the Bdls-ton type. The oxidation is carried out in a 4 m long steel column contain-ing 8 l of catalyst mass. The column receives condensate (alternatively white liquor for the removal of deposited sulfur) via pump (P3) and a flowmeter (9), it receives compressed air via a meter (l8) and steam for regeneration.
The efficiency of the column is monitored by a H2S detector mounted below the cover of the collecting tank and additio-nal control is achieved by sampling for assessment of theodour and for potentiometric titration of H2S and CH3SH.
.
-Examination of the Efficiency of the Oxidation Column:
~ `
15 Column material: Activated carbon, 8 litres, ~rain size 0~5-2 r5 mm Type Lurgi Hydraffin LS supra Note: Preliminary tests carried out with inter alia ordinary activated carbon lacking technical specifications and bought in a shop in Oslo yielded corresponding results às regards odour, H2S and CH2SH.
The column was filled on Oc-t. 2nd/ 1979.
Experiments were carried out from Oct. 2nd to Oct. 4th, 1979.
Incoming condensate: EVAPORATION CONDENSATES:
H2S Orl - 0~9 g S/l CH3SH o 0 3 Ei2S + CH3SH O~l - lr2 g S/l pH 7,~6 - 8~0 Outgoing condensate:
H2S + CH3SH O g S/l pH approx. 9~7 Amount of condensate 15 l/h, totally 720 l Amount of air approx. 40 l/h,totally 1800 l Totally removed H2S ~ CH3SH corresponding to 360 ~ S
Regenerated with approx. 5 kg steam (190C, 13 kg/cm Continued Oct. 15 - Oct. 17.
~ , .
.
l2~8sg~ `
Incoming condensate: -S 0~0~7 ~ S/l 13SH 0~0,r3 H2S + HC3S11 0~.2 ~ 0 g S/l pH approx~ 8 Outgoing condensateo H2S + CH3SH O g S/l pH approx. 9~.6 Amount of condensate 15 l/h, totally~ ~50 1 Amount of air ~ 40 r~ 1/ (31.0 1 Totally removed l12S -~ CH3SH corresponding to 2 O ~ S
Continued Oct. 22, - Oct. 25, Amoun-t of condensate totally 600 1 Amount of air " 1630 1 ~ pH (in) approx. 8 pH (out) " 9~5 Totally removed H2S + CH3SH corresponding to 310 g S
Amount of condensate after previous steam regeneration:
350 1 + 600 1 = 950 1 Amount of condensate totally: 720 1 + 950 1 = 1470 1 Removed 112S + CH3SH totally corresponding to 54Q g S
Regenerated wi h approx. 6 kg steam (190C, 12~ kg/cm2) Regenerated with approx. 4~1 1 hot white liquor, 30 min.
Drained off Li~uor containing polysulfide. Washed with approximately 40 l water.
Continued February 25th - 27th, 1~80 ~mount of condensate totally 330 1 ~ount of air " 1000 1 pH (in) approx. 7~8 pH (out) " 9~7 Totally removed H2S + CH3SH corresponding to 230 g/S
Continued March 4th Rn~ount of condensate totally 470 i Amount of air ~ " 1400 1 Totally removed H2S -~ CH3SH corresponding to 330 g/S
- 560 g/S
:
: ..
~205~30 The series of experiments was ended after the -treatment of totall~ 2270 1 of non-purified evaporation condensate and removal of ~2S ~ CH3SH corresponding to 1430 g sulfur.
Experiment carried out May 28th - Oct. 9th 1980: Di~ester Condensate Column ma-terial as above Column filled May 21st Incoming condensate:
~ H2S + CH3SH traces pH 9~0 - 9 Outgoing condensate:
H2S + CH3SH O ~/
pH 9t`5 10 p Amount of condensate: 15 l/h, totally approx. 5000 1 Amount o air ~0 " " " 13300 1 Experiment completed, column still efficient.
Gas Chromatographic Analyses (carried out by SI) Extraction with cyclohexane involves non-polar compounds, ~ollowe~ by acidification and extraction with butyl acetate and deri~ation with a trimethylsilyl-reagent to determine the more polar compounds. The first mentioned were studied in a ~lass capillary column, the last mentioned in a packed column, both by the aid of a flame ionization detector.
Evaporation Condensate from Oct. 17th, 73 The amounts of both non-polar and polar compounds were very much reduced after the condensate treatment in -the oxida-tion ~olumn. The main component of the non-polar compounds was reduced approximately ?0 000 times ~from 60 ppm to 3.10 3 ppm). A reduction of approximately 600 times was found for the main component of polar compounds.
~205~30 Digester Condensate from early in June 1980 For the non-polar compounds a reduction of approx. 160 times was found. In the polar frac-tion no compounds were found in the sample taken after the oxidation column, which corresponds to a reduction of at least 200 times, based on;
the detection limit.
.
Odour Analyses by ~ead-space Technique (carried out by SI) The evaporation condensate samples from upstreams and down-streams the oxidation column were heated to ~0Cfbr 1 hour, and the gas above the liquid (head-space) was extracted, concentrated on activated carbon and analyzed by gas chro-matography. Great difference of the samples was re~orted,approximately hàlf of the compounds from the sample up-streams of the oxidation ~eing absent in the sample down-streams of the oxidation. The total content is approximate-ly 4 times higher in the untreated sample. A few new vola-tile compounds seemed to have been produced, but these werepresent in very small amounts. The main compound present seems to be dimethyl disulfide.
Destillation of Metanol and Determina-tion of its Purity Methanol was destilled off (amounting to approx. 5 g/l) and was analysed by gas chromatography at PFI. The chromato~rams only showed traces of one compound in addition to methanol, ~ the amount of which was assessed to be less than 1~.5% of the amount of metanol.
Coalescence The efficiency of coalescence filtration was proven by the fact that 1) "oil" accumulated on top of the unit and that 2) the condensate was often mil~ upstreams of the unit and clear downstreams. The oil content in the un-treated condensates varies within very wide llmits.
~ , :
... ... . ,. .. ~.. .
Claims (5)
PROPERTY OR PRIVILEGE IS CLAIMED ARE DEFINED AS FOLLOWS:
1. A method for the purification of condensates from the sulfate process which comprises passing the conden-sate and an oxygen-containing gas concurrently through a column containing activated carbon.
2. A method in accordance with claim 1, in which deposited sulphur on the carbon material is removed by treat-ment with a sulfide containing alkaline solution such as white liquor.
3. A method in accordance with claim 1, in which organic components deposited in/on the activated carbon are removed by steam stripping.
4. A method in accordance with claim 1, in which the condensate is previously freed from "oils" or solids.
5. A method in accordance with claim 4 r in which the condensate is freed from "oils" or solids by coalescence and/or filtration.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NO811259A NO150971C (en) | 1981-04-10 | 1981-04-10 | PROCEDURE FOR CLEANING OF CONDENSATIVES FROM THE SULPHATE PROCESS |
NO81.1259 | 1981-04-10 |
Publications (1)
Publication Number | Publication Date |
---|---|
CA1205930A true CA1205930A (en) | 1986-06-10 |
Family
ID=19886021
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CA000400790A Expired CA1205930A (en) | 1981-04-10 | 1982-04-08 | Method for the purification of condensates from the sulfate process |
Country Status (5)
Country | Link |
---|---|
JP (1) | JPS57180484A (en) |
CA (1) | CA1205930A (en) |
FI (1) | FI73254C (en) |
NO (1) | NO150971C (en) |
SE (1) | SE462169B (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016174308A1 (en) * | 2015-04-27 | 2016-11-03 | Metsä Fibre Oy | Method of regenerating catalysts used for production of polysulphide cooking liquors |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
SE9403818L (en) * | 1994-11-08 | 1996-05-09 | Kvaerner Pulping Tech | Method of ozone bleaching |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
ZA737730B (en) * | 1972-10-26 | 1974-09-25 | St Regis Paper Co | Process for reducing the organic carbon content and improving the color of aqueous plant effluents |
JPS5066480A (en) * | 1973-10-18 | 1975-06-04 | ||
JPS562887A (en) * | 1979-06-20 | 1981-01-13 | Toshiba Corp | Treatment of waste alkali washing liquid for deodorizing |
-
1981
- 1981-04-10 NO NO811259A patent/NO150971C/en unknown
-
1982
- 1982-04-07 SE SE8202251A patent/SE462169B/en not_active IP Right Cessation
- 1982-04-08 CA CA000400790A patent/CA1205930A/en not_active Expired
- 1982-04-08 FI FI821271A patent/FI73254C/en not_active IP Right Cessation
- 1982-04-10 JP JP57058998A patent/JPS57180484A/en active Pending
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016174308A1 (en) * | 2015-04-27 | 2016-11-03 | Metsä Fibre Oy | Method of regenerating catalysts used for production of polysulphide cooking liquors |
CN107660162A (en) * | 2015-04-27 | 2018-02-02 | 安德里兹公司 | The renovation process of polysulfide cooking liquor production catalyst |
CN107660162B (en) * | 2015-04-27 | 2021-08-20 | 安德里兹公司 | Regeneration method of catalyst for polysulfide cooking liquor production |
US11219881B2 (en) | 2015-04-27 | 2022-01-11 | Andritz Oy | Method for regenerating catalysts used for production of polysulphide cooking liquors |
Also Published As
Publication number | Publication date |
---|---|
NO811259L (en) | 1982-10-11 |
FI73254C (en) | 1987-09-10 |
NO150971C (en) | 1985-01-23 |
FI821271L (en) | 1982-10-11 |
FI73254B (en) | 1987-05-29 |
JPS57180484A (en) | 1982-11-06 |
SE8202251L (en) | 1982-10-11 |
NO150971B (en) | 1984-10-08 |
SE462169B (en) | 1990-05-14 |
FI821271A0 (en) | 1982-04-08 |
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