EP0140226A2 - Procédé pour l'obtention de lignine à partir de solutions de lignine alcalines - Google Patents

Procédé pour l'obtention de lignine à partir de solutions de lignine alcalines Download PDF

Info

Publication number
EP0140226A2
EP0140226A2 EP84112077A EP84112077A EP0140226A2 EP 0140226 A2 EP0140226 A2 EP 0140226A2 EP 84112077 A EP84112077 A EP 84112077A EP 84112077 A EP84112077 A EP 84112077A EP 0140226 A2 EP0140226 A2 EP 0140226A2
Authority
EP
European Patent Office
Prior art keywords
lignin
stage
anode
alkali
cell
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.)
Granted
Application number
EP84112077A
Other languages
German (de)
English (en)
Other versions
EP0140226B1 (fr
EP0140226A3 (en
Inventor
Eugen Dipl.Ing. Edel
Josef Dr. Dipl.-Chem. Feckl
Clemens Dipl.-Chem. Grambow
Albert Huber
Dietrich Dr. Wabner
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.)
Organocell Gesellschaft fur Zellstoff- und Umwelt
Original Assignee
MD ORGANOCELL ZELLST UMWELTTEC
Organocell Gesellschaft fur Zellstoff- und Umwelttechnik Mbh
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 MD ORGANOCELL ZELLST UMWELTTEC, Organocell Gesellschaft fur Zellstoff- und Umwelttechnik Mbh filed Critical MD ORGANOCELL ZELLST UMWELTTEC
Priority to AT84112077T priority Critical patent/ATE76079T1/de
Publication of EP0140226A2 publication Critical patent/EP0140226A2/fr
Publication of EP0140226A3 publication Critical patent/EP0140226A3/de
Application granted granted Critical
Publication of EP0140226B1 publication Critical patent/EP0140226B1/fr
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Images

Classifications

    • 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
    • D21C11/0042Fractionating or concentration of spent liquors by special methods

Definitions

  • the invention relates to a process for obtaining lignin by precipitation from alkaline lignin solutions by means of neutralization and for recovering the alkali.
  • Alkali water can e.g. B. be neutralized by introducing C0 2 and the carbonate formed are caustified with calcium oxide.
  • the invention has for its object to provide a method in which the lignin is obtained from an alkaline lignin solution, preferably a waste liquor (alkaline extract) from a pulp process in a form suitable for further processing, with little equipment, so that destruction omitted and in which there is also the possibility of supplying the water fraction and the alkali of the extract for reuse in the process.
  • an alkaline lignin solution preferably a waste liquor (alkaline extract) from a pulp process in a form suitable for further processing, with little equipment, so that destruction omitted and in which there is also the possibility of supplying the water fraction and the alkali of the extract for reuse in the process.
  • the object is achieved in a method of the type mentioned in the invention in that the lignin solution is continuously anodized by electrolysis and the alkali is regenerated cathodically in the same process.
  • the alkaline extract lignin solution
  • the cell is expediently divided by an ion exchange membrane, which enables the selective transport of the cations from the anode into the cathode space.
  • a Nafion membrane is particularly suitable and fulfills the demands placed on it with a long service life. The precipitation and the alkali recovery are effected at the same time by supplying only one amount of energy.
  • the new method is generally applicable to alkaline lignin solutions. It is mainly used for alkaline lignin solutions, which are an extract or a lye from a pulp process, and in this case preferably for lignin solutions, which are obtained from the extract of an organosolve process for pulp production by separating off the organic solvent.
  • Sodium hydroxide solution is mainly used as the alkali.
  • the neutralization is only carried out until the beginning of the lignin precipitation in the anode compartment, which, according to experience, corresponds to approximately pH9.5.
  • the majority of the sodium hydroxide solution is already recovered in the cathode compartment.
  • the second stage acidification is carried out in the anode compartment until the lignin has completely precipitated, experience has shown it to be about pH 4. Since, due to the low conductivity of the solution below pH 8, sufficient electrolysis only takes place at elevated voltage, the separation into two steps noticeably saved energy.
  • the oxygen that develops at the anode of the flocculation cell forms foam together with the precipitated lignin and part of the neutralized solution, so that the lignin suspension can be removed via a flotation device.
  • the flotation process does not require any additional energy since the oxygen is generated by the amount of electricity that is required for the electrolysis anyway.
  • the electrolytic precipitation in the second stage has the advantage that the precipitated lignin is not contaminated with inorganic salts.
  • the acidic anolyte can be returned to the cellulose process as a digestion medium or its component after appropriate regeneration, addition of methanol and optionally alkali enrichment, into the cathode compartment of the first stage and from there.
  • the alkaline extract can thus be worked up in a closed circuit and no waste water leaves the process.
  • the electrolysis is carried out in both stages at temperatures as high as possible below the boiling point, since the conductivity of the solution increases with increasing temperature.
  • the waste heat generated during electrolysis is sufficient to maintain this temperature, so that additional heating on the electrolysis cells is generally not necessary.
  • the catholyte and / or the anolyte can be circulated in the first process stage.
  • a partial section of the circuits is formed by the electrolytic cell.
  • the controllability of the process stage is improved by guiding the anolyte and the catholyte in the circuit when a part of the electrolyte is introduced and discharged.
  • the acidification of the waste liquor in the first stage of the process is preferably carried out up to a pH of 9.5. However, this value is not absolute but depends on the circumstances such as lignin levels in the waste liquor, temperature and the like. In order to avoid contamination of the circulation sections of the circuit, the aim is that no flocculation takes place in the first process stage.
  • the flocculation of the lignin components only takes place in the second process stage, which is provided with a floatation device.
  • the resulting lignin-containing foam is removed via the flotation device.
  • the weakly acidic electrolyte obtained at the end of the second process stage still contains several g / l of dissolved lignin-like substances which are difficult to precipitate (even if the pH is lowered further).
  • this is not a disadvantage for the overall process, since the electrolyte is circulated and ultimately as a solution after the pH has been increased again, e.g. B. by adding NaOH, is used again in the alkaline pulp boiling. With repeated repetition in such a cycle, there is no concentration of non-precipitable lignin-like substances in the deflocculated electrolyte; d. that is, the lignin is ultimately obtained quantitatively.
  • the weakly acidic electrolyte is used in a particularly advantageous manner in the first and / or second process step in the cathode compartment.
  • This makes it possible for the sodium hydroxide solution which inevitably forms in the cathode compartment (in addition to hydrogen) from H 2 O to be returned directly to the circuit.
  • this catholyte can be conducted in countercurrent to the anolyte of the cell, which consists of the extract of the first stage of the process and has a pH of approximately 9.5.
  • the alkaline electrolyte obtained in the neutralization cell in the cathode compartment is mixed with an organic solvent, in particular methanol, and added to the pulp process for renewed boiling.
  • alkali metal hydroxide can be added to the catolyte in the first and second process stages in order to achieve a certain minimum conductivity from the start.
  • This two-stage process is particularly suitable for working up the waste liquor from the pulping according to the Organosolv process.
  • the housing 2 has the shape of a flat cuboid, in the middle of which the membrane 3 is inserted.
  • the size of the membrane 3 corresponds approximately to the size of a side surface 6 of the housing 2.
  • the membrane 3 divides the interior of the housing 2 into the anode and cathode compartments 7 and 8. In the spaces -7 and 8 mentioned, the anode 4 and the Cathode 5 arranged. Both are adapted in their shape and size to the membrane 3.
  • the cathode is approximately in the middle of the cathode space 8, while the anode 4 lies next to the membrane 3, so that there is only a relatively narrow gap 9 between the anode 4 and membrane 3. Power connections lo and 11 for the anode 4 and cathode 5 are led out of the housing 2.
  • the waste liquor previously freed of methanol from the pulp process of cell 1 is fed via connection 12.
  • foam of lignin and oxygen is formed in the anode compartment, which is drawn off via the trigger 13.
  • the foam formation is indicated by the bubbles 14 shown.
  • the lignin foam 14 from the trigger 13 is centrifuged, whereby pure lignin and a solution which can be recycled into the pulp process is obtained.
  • the hydrogen produced can escape via the connecting piece 15 on the cathode compartment 8. * )
  • the electrolytic cell has an anode and a cathode, the areas of which are each 50 cm 2 .
  • Anode and cathode compartments are separated by a Nafion membrane.
  • the anode * Water, dilute alkali metal solution or the centrifugate of the 'lignin foam (pH 6) is fed in via connection 16.
  • Concentrated alkali metal hydroxide solution is withdrawn from the cathode compartment via the connection 17.
  • the fume cupboard is equipped with a flotation device and holds 3oo ml.
  • the anode compartment is filled with 2 00 ml lignin-containing lye (pH 13.6).
  • 0.1N NaOH serves as the initial filling of the catholyte.
  • the cathode compartment also holds 3oo ml and is completely filled.
  • Fresh lignin-containing waste liquor with approx. 60 g / 1 dissolved lignin (pH 13.6) is now continuously introduced into the cell from below (approx. 100 - 150 ml / h). The entire amount of electrolyte leaves the cell again neutralized in the lignin / oxygen foam via the flotation device.
  • lignin About 40 g of lignin can be obtained from the foam per 1 waste liquor.
  • the method shown in Fig. 2 has two stages.
  • the resulting lignin and methanol-containing extract is drawn off from the cellulose cooker 20 and freed of the methanol in a methanol recovery device 21 and the methanol is fed back to the cooking process via line 21 b.
  • the extract freed from methanol is fed via line 21 a to the first electrolytic cell 22, which essentially represents the first process stage.
  • the extract is passed into the anode compartment 23.
  • the extract is acidified electrolytically until a pH of 9.5 is reached. From The extract, which has this pH value, is continuously fed to the anode compartment via line 24 to the anode compartment 25 of the second electrolytic cell 26, which forms the second process stage.
  • a further electrolytic acidification and thus the foaming takes place in this cell 26.
  • the foam is drawn off as a lignin suspension via a removal device 27 and fed to a separating device 28 in which the precipitated lignin contained in the foam is separated from the extract.
  • the pure lignin is supplied for further use via the device indicated at 29, while the remaining extract is returned via line 30 as an almost lignin-free solution into the cathode space 31 of the cell 26.
  • the extract is electrolytically enriched with alkali.
  • the resulting hydrogen is discharged through the outlet 33.
  • the extract reaches the cathode compartment 34 of the first cell 22 via the line 32, where a further alkaline enrichment of the extract takes place, which then reaches the collecting container 36 via the line 35.
  • the NaOH concentration can be regulated via line 35 a.
  • the extract is fed back to the cellulose cooker 20 as a sodium hydroxide solution via line 37.
  • the hydrogen is removed via 4o.
  • the Nafion membranes between the anode and cathode spaces are designated 38 and 39.
  • process stages 41 and 42 are provided with electrolytic cells 43 and 44, and the deflocculated electrolyte obtained in second process stage 42 is returned to the first process stage.
  • the first process stage 41 consists essentially of the cell 43, which is divided by the membrane 45 and the two circuits 46 and 47 for the catholyte and the anolyte.
  • Process stage 42 essentially consists of cell 44, which also has a membrane 48, and flotation device 49.
  • the extract containing all-ignignin at the pulp also known as waste liquor, with a pH of 14 and a lignin content of about 2 to 10% by weight is fed to the storage vessel 51 via the line 50.
  • This supply is controlled via a control system 52, 53, 59 (pH and level controller) in such a way that a pH of approximately 9.5 is maintained in the storage vessel.
  • the pump 54 conveys the waste liquor into the cell 43, specifically into the anode compartment 55. In the anode compartment 55, the waste liquor is lowered in pH, which enters the gas separator 56 after leaving the anode compartment 55. In the gas separator 56, the anode gas generated during the electrolysis is predominant. Oxygen, separated.
  • the liquid in the cathode compartment 62 consists of deflocculated electrolyte which has already been enriched with NaOH in the cathode compartment 73 of the cell 44 and has a pH of approximately 12.
  • This catholyte is also about one Storage vessel 6o and then fed to the cathode chamber 62 of the cell 43 via the line 61. From the cathode compartment 62, the catholyte passes through self-convection into the gas separator 63, from which the resulting cathode gas (hydrogen) is separated. The catholyte is returned from the gas separator 63 to the storage vessel 6o. In this case, the catholyte is recycled in the same way as for anolyte. Part of the catholyte is discharged from the gas separator 63 via the line 64. This is done via a level controller 65 in the storage vessel 6o and the valve 66.
  • the pH is about 14.
  • the NaOH concentration may have to be adjusted by diluting it with H 2 O or adding NaOH.
  • the catholyte circuit 46 and the anolyte circuit 47 in which the main part of the catholyte or the anolyte is circulated.
  • a lignin-containing extract with a pH value of 14 is fed to the circulation of the anolyte before the neutralization cell 43 and after the neutralization cell 43 a lignin-containing extract with a pH value of about 9 is removed.
  • an electrolyte which is enriched with sodium hydroxide to a pH of 12 is fed in before the cell 43, and after the cell 43, an electrolyte with a pH of 14 is discharged and used for the production of pulp.
  • the lignin-containing extract obtained in the first stage with a pH of about 9.5 is introduced into the anolyte space 7o of the cell 44 of the second process stage, which is also referred to as a flocculation cell.
  • the lignin fractions are flocculated with the simultaneous formation of oxygen gas at the anode.
  • Oxygen foam is drawn off on the flotation device 49.
  • the device 71 separates the lignin sludge from the electrolyte, the electrolyte having a pH of approximately 4.
  • the resulting lignin sludge is subjected to a washing, drying and workup process in a manner known per se, so that pure lignin is formed.
  • the electrolyte is returned to the catholyte space 73 of the cell 44 via the line 72.
  • water and sodium hydroxide can be added to the electrolyte from a reservoir 74 in order to compensate for the water losses which occur during the floatation and to achieve the properties of the electrolyte which are favorable for the electrolyte process.
  • the electrolyte is drawn off and fed via line 75 to the reservoir 6o of the catholyte circuit 46 of the first stage 41.
  • Sodium hydroxide and optionally water can also be entered in line 75.
  • the electrolyte returned to the pulp process can also be added via the device 76 methanol.
  • the neutralization cell has an anode and cathode area of 18 cm 2 each. Anode and cathode compartments are separated by a cation exchange membrane.
  • the cathode (V2A expanded metal) lies directly on this membrane, while the anode ( * platinum.) Has a distance of approx. 1 mm from the membrane.
  • the anolyte storage vessel holds approx. 2oo ml.
  • the anolyte is pumped with the help of a peristaltic pump via cell and gas separator from the storage vessel in a circuit (approx. 8 l / h), which means that the anode compartment volume is approx. 2 ml of approx. 0.9 s.
  • the catholyte moves through the gas separator through self-convection in the circuit; there is no storage vessel.
  • the pH of the anolyte is determined using a glass electrode.
  • the cell voltage is approx. Lo - 11 V.
  • lignin-containing waste liquor pH 13.6
  • 0.1 M sodium hydroxide solution serves as the first filling in the catholyte circuit.
  • each lo ml of fresh waste liquor (pH 13.6) is poured into the storage vessel and at the same time the anolyte (pH 9.5) is continuously discharged in the same amount behind the neutralization cell.
  • the Ent speaks a throughput of the neutralization cell of approx. 2oo ml / h; the discharge is therefore approx. 2.5% of the anolyte cycle current.
  • the flocculation cell has a cathode and anode area of approx. 20 cm 2 , anode and cathode space are separated by a cation exchange membrane.
  • the anode compartment is open and has a floating device. Its volume is approximately 3oo ml.
  • the electrodes are arranged below.
  • the anolyte (pH9: .5) discharged from the neutralization cell anolyte circuit is introduced into the flocculation cell and electrolyzed (approx. 200 ml / h).
  • a viscous light brown foam is formed from lignin flakes, deflocculated anolyte (pH 5) and anode gas (0 2 ), which is removed using the flotation device. Allowing this foam to settle gives approx. 0.5 l of leachate (deflocculated, pH 5) per liter of anolyte (pH9.5) and approx. 1 - 2 1 of highly lignin-containing, no longer removable foam, from which approx. 40 g Let Rohlignin win.
  • the deflocculated waste liquor (pH 5) is again admixed with the catolyte of the neutralization cell (approx. 100 ml / h) after the foam settling and filtration, and NaOH is continuously discharged in the same amount (pH 14). After suitable dilution and solvent addition, this NaOH is incorporated into the new pulp cooking process.
  • Example 1 Another flocculation cell with an upstream settling device is connected in series behind the flocculation cell and both cells are operated with 2A.
  • the first flocculation cell creates a foam with a pH of around 7, which settles into an electrolyte of pH 7 after some time.
  • Separated lignin flakes are filtered and the electrolyte is fed into the second flocculation cell.
  • the second cell produces a foam like example 1.
  • the cell voltages in the flocculation cells are approx. 7 and 7.5 V.

Landscapes

  • Compounds Of Unknown Constitution (AREA)
  • Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
  • Paper (AREA)
  • Electrolytic Production Of Metals (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
EP84112077A 1983-10-31 1984-10-09 Procédé pour l'obtention de lignine à partir de solutions de lignine alcalines Expired - Lifetime EP0140226B1 (fr)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AT84112077T ATE76079T1 (de) 1983-10-31 1984-10-09 Verfahren zur gewinnung von lignin aus alkalischen lignin-loesungen.

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE3339449 1983-10-31
DE19833339449 DE3339449A1 (de) 1983-10-31 1983-10-31 Verfahren zur gewinnung von lignin aus alkalischen lignin-loesungen

Publications (3)

Publication Number Publication Date
EP0140226A2 true EP0140226A2 (fr) 1985-05-08
EP0140226A3 EP0140226A3 (en) 1988-08-31
EP0140226B1 EP0140226B1 (fr) 1992-05-13

Family

ID=6213154

Family Applications (1)

Application Number Title Priority Date Filing Date
EP84112077A Expired - Lifetime EP0140226B1 (fr) 1983-10-31 1984-10-09 Procédé pour l'obtention de lignine à partir de solutions de lignine alcalines

Country Status (10)

Country Link
US (1) US4584076A (fr)
EP (1) EP0140226B1 (fr)
AT (1) ATE76079T1 (fr)
BR (1) BR8405541A (fr)
CA (1) CA1269345A (fr)
DE (2) DE3339449A1 (fr)
ES (1) ES537170A0 (fr)
FI (1) FI76849C (fr)
NO (1) NO169289C (fr)
PT (1) PT79434B (fr)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1993022490A1 (fr) * 1992-05-05 1993-11-11 Granit S.A. Procede de recuperation de produits chimiques de cuisson a partir de la liqueur noire dans la fabrication de la cellulose selon le procede organosolver
WO2012054947A3 (fr) * 2010-10-29 2012-08-23 Annikki Gmbh Procédé d'extraction de lignine
WO2015086772A1 (fr) * 2013-12-12 2015-06-18 Annikki Gmbh Procédé de purification et d'isolement de lignine
WO2016062676A1 (fr) * 2014-10-20 2016-04-28 Max Planck Gesellschaft Zur Förderung Der Wissenschaft E.V. Procédé de précipitation de la lignine à partir de liqueurs de cuisson d'organosolve
EP3722501A1 (fr) * 2019-04-12 2020-10-14 Lenzing Aktiengesellschaft Procédé de récupération de solution alcaline ainsi que procédé de fabrication de corps moulé cellulosique régénéré comprenant un tel procédé

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA1335976C (fr) * 1989-05-31 1995-06-20 Mahmoud Kamran Azarniouch Recuperation de naoh et d'autres produits a partir de liqueurs usees et d'effluents d'usines de blanchiment
US5589053A (en) * 1995-11-03 1996-12-31 Huron Tech Incorporated Electrolysis process for removal of caustic in hemicellulose caustic
WO2013003941A1 (fr) * 2011-07-04 2013-01-10 Hydro-Quebec Procédé pour le traitement de liqueur noire
FI128466B (en) * 2016-03-29 2020-05-29 Ch Bioforce Oy Process for the preparation of hemicellulose extracts
RU2641901C1 (ru) * 2016-11-22 2018-01-23 федеральное государственное автономное образовательное учреждение высшего образования "Южный федеральный университет" (Южный федеральный университет) Способ получения окисленного лигнина
DE102017115391A1 (de) * 2017-07-10 2019-01-10 Rwe Power Aktiengesellschaft Verfahren zur Gewinnung von Huminstoffen und Einrichtung zur Durchführung des Verfahrens
HRP20190259A2 (hr) * 2019-02-07 2020-08-21 Marinko Mikulić Kontinuirani postupak proizvodnje celulozne pulpe iz travnatih sirovina
KR102140217B1 (ko) * 2020-01-30 2020-07-31 구동찬 활성화 미네랄 용액의 제조 방법

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE507969C (de) * 1927-05-13 1930-09-22 Gustaf Haglund Verfahren zur Gewinnung von Zellstoff
US2354553A (en) * 1940-01-10 1944-07-25 Daniel L Sherk Method of recovering constituents of waste sulphite liquor
FR1071173A (fr) * 1952-10-28 1954-08-26 Monsanto Chemicals Perfectionnements relatifs à un procédé d'obtention de produits intéressants de dégradation oxydante à partir d'une forme de lignine

Family Cites Families (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3440159A (en) * 1965-08-26 1969-04-22 Ionics Separation of un-ionized substances by electro-osmosis
US3897319A (en) * 1971-05-03 1975-07-29 Carus Corp Recovery and recycle process for anodic oxidation of benzene to quinone
US3905886A (en) * 1974-09-13 1975-09-16 Aqua Chem Inc Ultrafiltration and electrodialysis method and apparatus
US4049490A (en) * 1976-02-23 1977-09-20 Veniamin Petrovich Zaplatin Electrodialysis of bleaching effluent
US4043896A (en) * 1976-03-25 1977-08-23 Aqua-Chem, Inc. Ultrafiltration and electrodialysis apparatus
US4140615A (en) * 1977-03-28 1979-02-20 Olin Corporation Cell and process for electrolyzing aqueous solutions using a porous anode separator
GB2038872B (en) * 1978-10-06 1983-01-26 Asahi Chemical Ind Electrolytic process for preparing nitrites
DE2855052A1 (de) * 1978-12-20 1980-06-26 Nicolaus Md Papier Verfahren und vorrichtung zum kontinuierlichen aufschliessen von pflanzenfasermaterial
US4273628A (en) * 1979-05-29 1981-06-16 Diamond Shamrock Corp. Production of chromic acid using two-compartment and three-compartment cells
US4476025A (en) * 1983-05-09 1984-10-09 The United States Of America As Represented By The United States Department Of Energy Separation of certain carboxylic acids utilizing cation exchange membranes

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE507969C (de) * 1927-05-13 1930-09-22 Gustaf Haglund Verfahren zur Gewinnung von Zellstoff
US2354553A (en) * 1940-01-10 1944-07-25 Daniel L Sherk Method of recovering constituents of waste sulphite liquor
FR1071173A (fr) * 1952-10-28 1954-08-26 Monsanto Chemicals Perfectionnements relatifs à un procédé d'obtention de produits intéressants de dégradation oxydante à partir d'une forme de lignine

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
TAPPI, Band 54, Nr. 10, Oktober 1971, Seiten 1641-1645, Technical Association of the Pulp and Paper Industry, New York, US; E. SANTIAGO: "Electrolytic treatment of spent liquors from pulp mills" *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1993022490A1 (fr) * 1992-05-05 1993-11-11 Granit S.A. Procede de recuperation de produits chimiques de cuisson a partir de la liqueur noire dans la fabrication de la cellulose selon le procede organosolver
WO2012054947A3 (fr) * 2010-10-29 2012-08-23 Annikki Gmbh Procédé d'extraction de lignine
WO2015086772A1 (fr) * 2013-12-12 2015-06-18 Annikki Gmbh Procédé de purification et d'isolement de lignine
WO2016062676A1 (fr) * 2014-10-20 2016-04-28 Max Planck Gesellschaft Zur Förderung Der Wissenschaft E.V. Procédé de précipitation de la lignine à partir de liqueurs de cuisson d'organosolve
EP3722501A1 (fr) * 2019-04-12 2020-10-14 Lenzing Aktiengesellschaft Procédé de récupération de solution alcaline ainsi que procédé de fabrication de corps moulé cellulosique régénéré comprenant un tel procédé
WO2020207766A1 (fr) * 2019-04-12 2020-10-15 Lenzing Aktiengesellschaft Procédé de récupération d'une solution alcaline, ainsi que procédé pour fabriquer des corps moulés cellulosiques régénérés présentant un tel procédé

Also Published As

Publication number Publication date
BR8405541A (pt) 1985-09-10
FI843766L (fi) 1985-05-01
EP0140226B1 (fr) 1992-05-13
FI843766A0 (fi) 1984-09-25
FI76849B (fi) 1988-08-31
PT79434B (en) 1986-09-15
NO169289B (no) 1992-02-24
US4584076A (en) 1986-04-22
ES8506820A1 (es) 1985-08-16
FI76849C (fi) 1988-12-12
NO843879L (no) 1985-05-02
DE3339449C2 (fr) 1987-12-03
PT79434A (en) 1984-11-01
ATE76079T1 (de) 1992-05-15
DE3485719D1 (de) 1992-06-17
EP0140226A3 (en) 1988-08-31
ES537170A0 (es) 1985-08-16
DE3339449A1 (de) 1985-05-09
CA1269345A (fr) 1990-05-22
NO169289C (no) 1992-06-03

Similar Documents

Publication Publication Date Title
DE68908850T2 (de) Verfahren und Vorrichtung für die Elektrolyse von Wasser.
EP0140226B1 (fr) Procédé pour l'obtention de lignine à partir de solutions de lignine alcalines
DE1254610B (de) Verfahren zur Herstellung von Hydroxyden und Carbonaten des Natriums durch Elektrolyse von Natriumchlorid
DE19710510C2 (de) Verfahren zum Reinigen einer elektrolytischen Kupferlösung
DE3739580C2 (fr)
EP1004348A2 (fr) Procédé de séparation d'acides organiques de solutions aqueuses
DE69402154T2 (de) Verfahren zum Reinigen und Rückführen der Auflösungen in den Kreislauf
DE2260392A1 (de) Verfahren zur behandlung einer schwefelwasserstoffhaltigen salzloesung
WO2012062353A1 (fr) Procédé d'utilisation d'eaux usées produites lors de la production de substances fibreuses lignocellulosiques
DE2260771A1 (de) Elektrolyseverfahren und -vorrichtung
EP0608244A4 (fr) Procede de fabrication de tallols.
DE2908592C3 (de) Verfahren zur Abtrennung und Gewinnung eines chalcophilen Elements aus einer wäßrigen Lösung
DE2248178C3 (de) Verfahren zur Aufbereitung und Gewinnung von Molybdän und/oder Rhenium
DE102009037946A1 (de) Verfahren zur Nutzung von bei der Erzeugung lignozellulosischer Faserstoffe anfallendem Abwasser
EP0040709B1 (fr) Procédé pour la production d'acide diacétone-céto-gulonique
DE19624023B4 (de) Verfahren zur Sanierung saurer, eisenhaltiger Tagebaurestlochgewässer
DE2500455B2 (de) Verfahren zur behandelung von abwasser mittels flotation
DE3619086A1 (de) Verfahren zum entsalzen von wasserhaltigen loesungen, vorrichtung zur durchfuehrung desselben sowie deren verwendung
DE4306260C2 (de) Verfahren und Anlage zu einer elektrochemischen Behandlung von Zellstoffablauge
DE2322665A1 (de) Verfahren und einrichtung zur abtrennung von emulgierten oelen, fetten und anderen industriellen verunreinigungen aus abwaessern
DE19506242C2 (de) Verfahren zur direkten elektrochemischen Oxidation von sulfithaltigen Lösungen, insbesondere Abwässern aus Gasreinigungsanlagen
DE4408337C2 (de) Verwendung eines Diaphragmas zur Elektrodialyse von sauren Galvanikbädern
DE10031018B4 (de) Chloralkalielektrolyse-Verfahren in Membranzellen unter Elektrolyse von ungereinigtem Siedesalz
DE2757776C2 (de) Verfahren zum Reinigen von ölhaltigem Abwasser durch Elektrolyse
DE3314877A1 (de) Verfahren zur behandlung einer entnahmeloesung, insbesondere fuer ein zinkextraktionsverfahren auf elektrolytischem weg

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

AK Designated contracting states

Designated state(s): AT CH DE FR LI SE

PUAL Search report despatched

Free format text: ORIGINAL CODE: 0009013

AK Designated contracting states

Kind code of ref document: A3

Designated state(s): AT CH DE FR LI SE

RAP1 Party data changed (applicant data changed or rights of an application transferred)

Owner name: ORGANOCELL GESELLSCHAFT FUER ZELLSTOFF- UND UMWELT

17P Request for examination filed

Effective date: 19890427

17Q First examination report despatched

Effective date: 19900706

GRAA (expected) grant

Free format text: ORIGINAL CODE: 0009210

AK Designated contracting states

Kind code of ref document: B1

Designated state(s): AT CH DE FR LI SE

REF Corresponds to:

Ref document number: 76079

Country of ref document: AT

Date of ref document: 19920515

Kind code of ref document: T

REF Corresponds to:

Ref document number: 3485719

Country of ref document: DE

Date of ref document: 19920617

ET Fr: translation filed
PLBE No opposition filed within time limit

Free format text: ORIGINAL CODE: 0009261

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: NO OPPOSITION FILED WITHIN TIME LIMIT

26N No opposition filed
EAL Se: european patent in force in sweden

Ref document number: 84112077.7

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: SE

Payment date: 19951017

Year of fee payment: 12

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: FR

Payment date: 19951020

Year of fee payment: 12

Ref country code: AT

Payment date: 19951020

Year of fee payment: 12

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: DE

Payment date: 19951026

Year of fee payment: 12

PGFP Annual fee paid to national office [announced via postgrant information from national office to epo]

Ref country code: CH

Payment date: 19951101

Year of fee payment: 12

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: AT

Effective date: 19961009

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: SE

Effective date: 19961010

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: LI

Effective date: 19961031

Ref country code: CH

Effective date: 19961031

REG Reference to a national code

Ref country code: CH

Ref legal event code: PL

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: FR

Effective date: 19970630

PG25 Lapsed in a contracting state [announced via postgrant information from national office to epo]

Ref country code: DE

Effective date: 19970701

EUG Se: european patent has lapsed

Ref document number: 84112077.7

REG Reference to a national code

Ref country code: FR

Ref legal event code: ST