BE1011880A4 - Method of treatment of brine. - Google Patents
Method of treatment of brine. Download PDFInfo
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- BE1011880A4 BE1011880A4 BE9800297A BE9800297A BE1011880A4 BE 1011880 A4 BE1011880 A4 BE 1011880A4 BE 9800297 A BE9800297 A BE 9800297A BE 9800297 A BE9800297 A BE 9800297A BE 1011880 A4 BE1011880 A4 BE 1011880A4
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- BE
- Belgium
- Prior art keywords
- solution
- added
- brought
- sodium
- chlorine
- Prior art date
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- 238000000034 method Methods 0.000 title claims abstract description 30
- 239000012267 brine Substances 0.000 title claims description 6
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 title claims description 6
- 239000000243 solution Substances 0.000 claims abstract description 30
- 239000007864 aqueous solution Substances 0.000 claims abstract description 17
- 150000002894 organic compounds Chemical class 0.000 claims abstract description 16
- 239000007800 oxidant agent Substances 0.000 claims abstract description 14
- 230000001590 oxidative effect Effects 0.000 claims abstract description 13
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 15
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims description 5
- 239000000460 chlorine Substances 0.000 claims description 5
- 229910052801 chlorine Inorganic materials 0.000 claims description 5
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 claims description 4
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical class S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 4
- 239000005708 Sodium hypochlorite Substances 0.000 claims description 2
- 125000001309 chloro group Chemical group Cl* 0.000 claims description 2
- IXCSERBJSXMMFS-UHFFFAOYSA-N hcl hcl Chemical compound Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 2
- 150000003385 sodium Chemical class 0.000 claims description 2
- 125000004436 sodium atom Chemical group 0.000 claims description 2
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 claims description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 10
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 9
- OWUGVJBQKGQQKJ-UHFFFAOYSA-M trimethylsulfanium;chloride Chemical compound [Cl-].C[S+](C)C OWUGVJBQKGQQKJ-UHFFFAOYSA-M 0.000 description 8
- BDAGIHXWWSANSR-UHFFFAOYSA-N methanoic acid Natural products OC=O BDAGIHXWWSANSR-UHFFFAOYSA-N 0.000 description 7
- QMMFVYPAHWMCMS-UHFFFAOYSA-N Dimethyl sulfide Chemical compound CSC QMMFVYPAHWMCMS-UHFFFAOYSA-N 0.000 description 6
- 239000002585 base Substances 0.000 description 5
- 239000011780 sodium chloride Substances 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 4
- 235000019253 formic acid Nutrition 0.000 description 4
- 238000000746 purification Methods 0.000 description 4
- OSWFIVFLDKOXQC-UHFFFAOYSA-N 4-(3-methoxyphenyl)aniline Chemical compound COC1=CC=CC(C=2C=CC(N)=CC=2)=C1 OSWFIVFLDKOXQC-UHFFFAOYSA-N 0.000 description 3
- XTEGARKTQYYJKE-UHFFFAOYSA-M Chlorate Chemical class [O-]Cl(=O)=O XTEGARKTQYYJKE-UHFFFAOYSA-M 0.000 description 3
- -1 etc.) Chemical class 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- IAZDPXIOMUYVGZ-UHFFFAOYSA-N Dimethylsulphoxide Chemical compound CS(C)=O IAZDPXIOMUYVGZ-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- AMQJEAYHLZJPGS-UHFFFAOYSA-N N-Pentanol Chemical compound CCCCCO AMQJEAYHLZJPGS-UHFFFAOYSA-N 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- 150000001450 anions Chemical class 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 238000009279 wet oxidation reaction Methods 0.000 description 2
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- IKHGUXGNUITLKF-XPULMUKRSA-N acetaldehyde Chemical compound [14CH]([14CH3])=O IKHGUXGNUITLKF-XPULMUKRSA-N 0.000 description 1
- 235000011054 acetic acid Nutrition 0.000 description 1
- 150000001243 acetic acids Chemical class 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 150000001298 alcohols Chemical class 0.000 description 1
- 150000001299 aldehydes Chemical class 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000008044 alkali metal hydroxides Chemical class 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 125000000217 alkyl group Chemical group 0.000 description 1
- BWZOPYPOZJBVLQ-UHFFFAOYSA-K aluminium glycinate Chemical compound O[Al+]O.NCC([O-])=O BWZOPYPOZJBVLQ-UHFFFAOYSA-K 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 125000003710 aryl alkyl group Chemical group 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000005587 bubbling Effects 0.000 description 1
- 238000005251 capillar electrophoresis Methods 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 150000001732 carboxylic acid derivatives Chemical class 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 238000005660 chlorination reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 239000011261 inert gas Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000003014 ion exchange membrane Substances 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 238000006385 ozonation reaction Methods 0.000 description 1
- 230000000750 progressive effect Effects 0.000 description 1
- 238000011002 quantification Methods 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 150000003463 sulfur Chemical class 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- NRZWQKGABZFFKE-UHFFFAOYSA-N trimethylsulfonium Chemical class C[S+](C)C NRZWQKGABZFFKE-UHFFFAOYSA-N 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D3/00—Halides of sodium, potassium or alkali metals in general
- C01D3/14—Purification
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/025—Thermal hydrolysis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Inorganic Chemistry (AREA)
- Materials Engineering (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Procédé d'épuration d'une solution aqueuse en composés organiques, selon lequel : (a) le pH de la solution est porté à au moins 13; (b) la solution est chauffée à au moins 100 degré C pendant au moins 1 heure; (c) au moins un oxydant chloré est progressivement ajouté à la solution.Process for purifying an aqueous solution of organic compounds, according to which: (a) the pH of the solution is brought to at least 13; (b) the solution is heated to at least 100 degrees C for at least 1 hour; (c) at least one chlorinated oxidant is gradually added to the solution.
Description
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Procédé d'épuration de saumures
La présente invention concerne un procédé d'épuration de solutions aqueuses, et en particulier de saumures, en composés organiques.
Les solutions aqueuses recueillies comme effluents de procédés de synthèse organique sont souvent chargées en composés organiques gênants, dont l'élimination est souhaitable dans de nombreux cas, et tout particulièrement dans le cas où il s'agit de saumures qu'on envisage de valoriser par électrolyse dans des installations munies de membranes échangeuses d'ions, par exemple en vue de produire des solutions aqueuses d'hydroxyde de sodium.
En effet, plusieurs composés organiques affectent gravement les performances desdites membranes,
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notamment le cation triméthy) su ! fbnium ( (CHS)
On connaît certes des procédés d'élimination de composés organiques, par exemple des procédés de chloration, mais ces procédés connus ne permettent pas de réduire suffisamment la teneur en composés organiques (telle que mesurée par exemple par la teneur totale en carbone organique, couramment dénommée "TOC") des solutions aqueuses. En outre, ces procédés connus sont inefficaces par rapport à certains composés organiques particuliers, par exemple des sels de triméthylsulfonium.
Il a déjà été proposé de soumettre des eaux usées contenant des substances organiques non souhaitées à un traitement thermochimique par oxydation, lesdites substances étant ainsi oxydées en anhydride carbonique et en eau Un tel procédé, décrit par exemple dans le document DE 26 40 603, est connu de manière générale sous le nom d'oxydation humide
Le procédé d'oxydation humide est comparable à une combustion en phase liquide Pour atteindre une décomposition satisfaisante des composés organiques et des vitesses de conversion suffisantes,
une concentration déterminée en oxygène ainsi que des températures et des pressions élevées sont nécessaires Ce procédé de traitement est donc très coûteux en raison de sa grande consommation d'énergie et des appareillages onéreux utilisés Les températures et les pressions mises en oeuvre peuvent certes être réduites par l'addition de catalyseurs à base de métaux lourds, mais cela mène à une étape supplémentaire d'épuration pour éliminer ces catalyseurs
La présente invention vise dès lors à fournir un procédé d'épuration de
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solutions aqueuses en composés organiques, qui soit simple et efficace, à la fois en termes de la variété des composés organiques éliminés et en termes des teneurs finales des solutions en composés organiques
A cette fin,
la présente invention concerne un procédé d'épuration d'une solution aqueuse en composés organiques, selon lequel (a) le pH de la solution est porté à au moins 13 ; (b) la solution est chauffée à au moins ! 00 C pendant au moins 1 heure ; (c) au moins un oxydant chloré est progressivement ajouté à la solution
Ce procédé peut se dérouler de façon continue ou discontinue (batch) On préfère le réaliser en discontinu
On applique avantageusement ce procédé à une saumure. Par saumure, on entend désigner, de manière usuelle, une solution aqueuse de chlorure de sodium (NaCI), dans laquelle un ou plusieurs autres constituants peuvent éventuellement être présents en plus faibles quantités.
Le procédé donne de bons résultats lorsqu'on l'applique à des saumures dont la teneur en chlorure de sodium est d'au moins 100 g/t. Leur teneur maximale en chlorure de sodium est celle qui correspond à la saturation ; en pratique, leur teneur en NaCI n'excède généralement pas 300 g/ !.
Les composés organiques que le procédé selon l'invention vise à éliminer sont notamment les composés des types acide carboxylique (acides formique, acétique,...), alcools (méthanol, pentanol,..), aldéhydes (acétaldéhyde,...), amines (alamine,.), et en particulier les dérivés soufrés (diméthylsulfure, diméthylsulfoxyde, chlorure de triméthylsulfonium,.) Le procédé donne des résultats particulièrement remarquables lorsque la solution à épurer contient au moins un sel de sulfonium.
Par sel de sulfonium, on entend désigner tout composé de formu) e (R} RRS) X, où RI, R2 et R3 sont identiques ou différents et désignent des radicaux alkyle, aryle, aralkyl ou alkaryl, substitués ou non, et X désigne un anion de valence n L'anion X est généralement un halogène, habituellement le chlore (n= 1). L'invention s'applique spécialement au cas où le sel de sulfonium est le chlorure de triméthylsulfonium.
Dans ce cas, de bons résultats ont été obtenus avec des teneurs en chlorure de triméthylsulfonium de l'ordre de 50 à 280 mg/l, sans que ces valeurs n'aient toutefois de caractère limitatif
Dans le procédé selon l'invention, la solution à épurer peut présenter naturellement une valeur de pH égale ou supérieure à 13 Ce n'est toutefois généralement pas le cas, et il est alors nécessaire de porter le pH à au moins 13
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par ajout d'une base forte, ou par tout moyen équivalent (par exemple par des moyens électrochimiques) On utilise de préférence une base hydrosoluble, par exemple choisie parmi les hydroxydes et les sels des métaux alcalins (carbonate de sodium, etc. ) Les hydroxydes des métaux alcalins sont préférés, en particulier l'hydroxyde de sodium (NaOH).
La quantité de base forte à mettre en oeuvre va dépendre de la solution à épurer, de son pH initial et du pH recherché.
Avantageusement, la teneur en base forte de la solution à l'issue de l'étape (a) est d'au moins 10 mmol par kg de solution, de préférence d'au moins 300 mmollkg.
Durant l'étape de chauffage (b), la température de la solution aqueuse est avantageusement portée à au moins 120 C, sans dépasser toutefois sa température d'ébullition De très bons résultats ont été obtenus au-delà de 130 C, par exemple à environ 140OC. De préférence, la durée de l'étape (b) est de 2 à 6 heures. Cette étape se déroule avantageusement sous pression autogène, afin notamment d'éviter l'ébullition de la solution aqueuse.
Si la solution aqueuse contient un sel de sulfonium, les étapes (a) et (b) ont pour effet de décomposer ce sel en alcool d'une part et en sulfure d'autre part Par exemple, dans le cas où la solution contient du chlorure de triméthylsulfonium, l'étape (b) conduit généralement à la formation de méthanol et
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de diméthylsulfure ( (CHS).
Selon une variante avantageuse, après l'étape (b), on ajoute à la solution de l'acide chlorhydrique (HCI) Ceci permet de réduire la quantité d'oxydant chloré utilisé lors de l'étape (c) Dans cette variante, la quantité d'acide chlorhydrique mis en oeuvre est avantageusement telle que le pH de la solution soit inférieur à 5 ou bien supérieur à 9.
L'étape d'oxydation (c) permet de décomposer la plupart des composés organiques encore présents dans la solution aqueuse (par exemple du méthanol ou du diméthylsyulfure, ou encore un acide organique tel que par exemple l'acide formique)
L'oxydant chloré est ajouté progressivement à la solution aqueuse, de façon à éviter la formation de chlorates.
A cette fin, le débit d'oxydant chloré est ajusté de préférence de telle façon que la quantité totale d'agent oxydant soit introduite en 5 à 30 minutes
Avantageusement, l'oxydant chloré utilisé à l'étape (c) est choisi parmi le chlore gazeux (C12) et l'hypochlorite de sodium (NaCIO) Si un oxydant chloré gazeux est utilisé, il peut être mis en oeuvre de toute manière classique, par exemple par barbotage dans la solution aqueuse, le cas échéant après dilution au
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moyen d'un gaz inerte tel que l'azote
A la fin de l'étape (c), la solution peut être aussi bien acide que basique Toutefois, de préférence, durant l'étape (c), on ajoute à la solution une quantité d'oxydant chloré suffisante pour que le pH devienne inférieur à 2, et de préférence inférieur à 1.
L'obtention d'un très faible pH en fin de réaction est avantageuse en ce sens qu'elle conduit à une épuration plus poussée, et ce même dans les cas où l'utilisation ultérieure de la solution aqueuse épurée exige un pH plus élevé, par exemple voisin de 7 (solution neutre) ; à cette fin, on peut utiliser une technique classique, par exemple une réaction avec une base
Selon une variante avantageuse, à l'étape (a), le pH de la solution est porté à au moins 13 par ajout d'un dérivé alcalin du sodium, et le rapport entre le nombre d'atomes de chlore de l'oxydant chloré ajoutés lors de l'étape (c) et le nombre d'atomes de sodium ajoutés lors de l'étape (a) est de 0,5 à 1,5.
Les étapes (a) et (b) d'une part, et (c) d'autre part, se déroulent dans le même réacteur ou dans des réacteurs séparés Le ou les réacteurs utilisés doivent être constitués ou intérieurement revêtus d'un matériau présentant une résistance mécanique et chimique suffisante, par exemple de titane.
L'étape (c) peut éventuellement être suivie d'une ou plusieurs étapes d'épuration classiques, telles qu'une filtration, une épuration complémentaire au moyen de charbon actif ou par ozonisation, etc.
Exemple
A un kg de saumure contenant 270 g/l de chlorure de sodium, 60 mg/l de chlorure de triméthylsulfonium (TMSC) (c'est-à-dire 19 mg C/1) et 383 mg/l d'acide formique (HCOOH) (soit environ 100 mg C/1), présentant globalement
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un TOC de 232 mg C/1, on a ajouté 300 mmol (12 g) de NaOH, puis on l'a chauffée à l3 OOC, en autoclave agité, sous pression autogène (environ 2,7 bars après 3 heures) Après 3 heures de réaction, la concentration en TMSC était réduite à 37 % de sa valeur initiale.
Du chlore a ensuite été ajouté, en large excès par rapport à la quantité de composés organiques (quantité totale de chlore : 7, 06 g) Après 15 minutes, le TOC a été réduit à environ 30 ppm (30 mg de carbone organique par litre), la concentration en TMSC étant quant à elle réduite à une valeur inférieure au seuil de quantification par électrophorèse capillaire ( < 5 mg/1) L'acide formique a été pratiquement totalement consommé
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On a constaté qu'une addition progressive du chlore (en environ 25 minutes) permettait d'obtenir une teneur finale en chlorate plus faible que dans le cas d'une addition rapide Le pH final fut de 13,4 (pH normalisé à température ambiante)
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Brine cleaning process
The present invention relates to a process for purifying aqueous solutions, and in particular brines, into organic compounds.
The aqueous solutions collected as effluents from organic synthesis processes are often loaded with troublesome organic compounds, the elimination of which is desirable in many cases, and in particular in the case of brines which it is intended to recover by electrolysis in installations provided with ion-exchange membranes, for example in order to produce aqueous solutions of sodium hydroxide.
Indeed, several organic compounds seriously affect the performance of said membranes,
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especially the cation trimethy) su! fbnium ((CHS)
There are certainly known methods for removing organic compounds, for example chlorination methods, but these known methods do not make it possible to sufficiently reduce the content of organic compounds (as measured for example by the total content of organic carbon, commonly known as "TOC") aqueous solutions. In addition, these known methods are ineffective with respect to certain particular organic compounds, for example trimethylsulfonium salts.
It has already been proposed to subject wastewater containing unwanted organic substances to a thermochemical treatment by oxidation, said substances thus being oxidized to carbon dioxide and water. Such a process, described for example in document DE 26 40 603, is generally known as wet oxidation
The wet oxidation process is comparable to combustion in the liquid phase. To achieve satisfactory decomposition of organic compounds and sufficient conversion rates,
a determined oxygen concentration as well as high temperatures and pressures are necessary. This treatment process is therefore very expensive because of its high energy consumption and the expensive apparatuses used. The temperatures and pressures used can certainly be reduced by the addition of heavy metal catalysts, but this leads to an additional purification step to remove these catalysts
The present invention therefore aims to provide a process for purifying
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simple and effective aqueous solutions of organic compounds, both in terms of the variety of organic compounds removed and in terms of the final contents of the organic compound solutions
To this end,
the present invention relates to a process for purifying an aqueous solution of organic compounds, according to which (a) the pH of the solution is brought to at least 13; (b) the solution is heated to at least! 00 C for at least 1 hour; (c) at least one chlorinated oxidant is gradually added to the solution
This process can take place continuously or discontinuously (batch) We prefer to carry it out discontinuously
This process is advantageously applied to a brine. The term "brine" is intended to denote, in the usual manner, an aqueous solution of sodium chloride (NaCl), in which one or more other constituents may possibly be present in smaller amounts.
The process gives good results when applied to brines with a sodium chloride content of at least 100 g / t. Their maximum sodium chloride content is that which corresponds to saturation; in practice, their NaCI content generally does not exceed 300 g /!.
The organic compounds which the process according to the invention aims to eliminate are in particular the compounds of the carboxylic acid (formic, acetic acids, etc.), alcohols (methanol, pentanol, etc.), aldehydes (acetaldehyde, etc.) types. , amines (alamine ,.), and in particular the sulfur derivatives (dimethylsulfide, dimethylsulfoxide, trimethylsulfonium chloride.) The process gives particularly remarkable results when the solution to be purified contains at least one sulfonium salt.
The term “sulfonium salt” is intended to denote any compound of formu) e (R} RRS) X, in which RI, R2 and R3 are identical or different and denote alkyl, aryl, aralkyl or alkaryl radicals, substituted or not, and X denotes a valence anion n Anion X is generally a halogen, usually chlorine (n = 1). The invention applies especially to the case where the sulfonium salt is trimethylsulfonium chloride.
In this case, good results have been obtained with trimethylsulfonium chloride contents of the order of 50 to 280 mg / l, without however these values being limiting in nature.
In the process according to the invention, the solution to be purified can naturally have a pH value equal to or greater than 13 This is however generally not the case, and it is then necessary to bring the pH to at least 13
<Desc / Clms Page number 3>
by adding a strong base, or by any equivalent means (for example by electrochemical means) A water-soluble base is preferably used, for example chosen from hydroxides and salts of alkali metals (sodium carbonate, etc.). alkali metal hydroxides are preferred, especially sodium hydroxide (NaOH).
The amount of strong base to be used will depend on the solution to be purified, its initial pH and the desired pH.
Advantageously, the strong base content of the solution at the end of step (a) is at least 10 mmol per kg of solution, preferably at least 300 mmollkg.
During the heating step (b), the temperature of the aqueous solution is advantageously brought to at least 120 ° C., without however exceeding its boiling point. Very good results have been obtained above 130 ° C., for example at about 140OC. Preferably, the duration of step (b) is 2 to 6 hours. This step advantageously takes place under autogenous pressure, in particular in order to avoid boiling of the aqueous solution.
If the aqueous solution contains a sulfonium salt, steps (a) and (b) have the effect of decomposing this salt into alcohol on the one hand and into sulfide on the other hand For example, in the case where the solution contains trimethylsulfonium chloride, step (b) generally leads to the formation of methanol and
EMI3.1
dimethyl sulfide ((CHS).
According to an advantageous variant, after step (b), hydrochloric acid (HCl) is added to the solution. This makes it possible to reduce the amount of chlorinated oxidant used during step (c) In this variant, the amount of hydrochloric acid used is advantageously such that the pH of the solution is less than 5 or even more than 9.
The oxidation step (c) makes it possible to decompose most of the organic compounds still present in the aqueous solution (for example methanol or dimethylsyulfide, or also an organic acid such as for example formic acid)
The chlorinated oxidant is gradually added to the aqueous solution, so as to avoid the formation of chlorates.
To this end, the flow rate of chlorinated oxidant is preferably adjusted so that the total amount of oxidizing agent is introduced in 5 to 30 minutes
Advantageously, the chlorinated oxidant used in step (c) is chosen from chlorine gas (C12) and sodium hypochlorite (NaCIO) If a chlorinated oxidant gas is used, it can be used in any conventional manner , for example by bubbling through the aqueous solution, if necessary after dilution with
<Desc / Clms Page number 4>
using an inert gas such as nitrogen
At the end of step (c), the solution can be both acidic and basic. However, preferably, during step (c), a quantity of chlorinated oxidant is added to the solution sufficient for the pH to become less than 2, and preferably less than 1.
Obtaining a very low pH at the end of the reaction is advantageous in that it leads to further purification, even in cases where the subsequent use of the purified aqueous solution requires a higher pH, for example close to 7 (neutral solution); for this purpose, a conventional technique can be used, for example a reaction with a base
According to an advantageous variant, in step (a), the pH of the solution is brought to at least 13 by adding an alkaline sodium derivative, and the ratio between the number of chlorine atoms of the chlorinated oxidant added during step (c) and the number of sodium atoms added during step (a) is 0.5 to 1.5.
Steps (a) and (b) on the one hand, and (c) on the other hand, take place in the same reactor or in separate reactors The reactor (s) used must be made up or internally coated with a material having sufficient mechanical and chemical resistance, for example titanium.
Step (c) may optionally be followed by one or more conventional purification steps, such as filtration, additional purification using activated carbon or by ozonization, etc.
Example
To one kg of brine containing 270 g / l of sodium chloride, 60 mg / l of trimethylsulfonium chloride (TMSC) (i.e. 19 mg C / 1) and 383 mg / l of formic acid ( HCOOH) (i.e. around 100 mg C / 1), overall
EMI4.1
a TOC of 232 mg C / 1, 300 mmol (12 g) of NaOH was added, then it was heated to 13 OOC, in a stirred autoclave, under autogenous pressure (approximately 2.7 bars after 3 hours) After 3 hours of reaction, the concentration of TMSC was reduced to 37% of its initial value.
Chlorine was then added, in large excess relative to the amount of organic compounds (total amount of chlorine: 7.06 g) After 15 minutes, the TOC was reduced to about 30 ppm (30 mg of organic carbon per liter ), the concentration of TMSC being reduced to a value below the threshold of quantification by capillary electrophoresis (<5 mg / 1) The formic acid was practically completely consumed
<Desc / Clms Page number 5>
It was found that a progressive addition of chlorine (in about 25 minutes) made it possible to obtain a lower final chlorate content than in the case of rapid addition The final pH was 13.4 (pH normalized at room temperature )
Claims (10)
Priority Applications (5)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| BE9800297A BE1011880A4 (en) | 1998-04-21 | 1998-04-21 | Method of treatment of brine. |
| GB9908550A GB2336584A (en) | 1998-04-21 | 1999-04-14 | Process for the purification of brines |
| NL1011815A NL1011815C2 (en) | 1998-04-21 | 1999-04-15 | Method for purifying saline solutions. |
| FR9904937A FR2777558A1 (en) | 1998-04-21 | 1999-04-16 | Removal of organic compounds from aqueous solutions, e.g. sulfonium salts from brine |
| BR9901378-9A BR9901378A (en) | 1998-04-21 | 1999-04-20 | Purification process of an aqueous solution in relation to organic compounds .. |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| BE9800297A BE1011880A4 (en) | 1998-04-21 | 1998-04-21 | Method of treatment of brine. |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| BE1011880A4 true BE1011880A4 (en) | 2000-02-01 |
Family
ID=3891205
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| BE9800297A BE1011880A4 (en) | 1998-04-21 | 1998-04-21 | Method of treatment of brine. |
Country Status (5)
| Country | Link |
|---|---|
| BE (1) | BE1011880A4 (en) |
| BR (1) | BR9901378A (en) |
| FR (1) | FR2777558A1 (en) |
| GB (1) | GB2336584A (en) |
| NL (1) | NL1011815C2 (en) |
Families Citing this family (16)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP2053034B1 (en) | 2003-11-20 | 2018-01-24 | Solvay Sa | Process for producing a chlorohydrin |
| TWI333945B (en) | 2005-05-20 | 2010-12-01 | Solvay | Process for preparing a chlorohydrin by converting polyhydroxylated aliphatic hydrocarbons |
| KR20080037615A (en) | 2005-05-20 | 2008-04-30 | 솔베이(소시에떼아노님) | Method for producing chlorohydrin |
| BRPI0618325A2 (en) | 2005-11-08 | 2011-08-23 | Solvay | process stop dichloropropanol production |
| BRPI0712775A2 (en) | 2006-06-14 | 2012-09-04 | Solvay | PRODUCT BASED ON RAW GLYCEROL, AND, PROCESSES FOR PURIFICATION OF PRODUCT BASED ON RAW GLYCEROL, FOR THE MANUFACTURING OF DICHLOROPROPANOL STARTING FROM GLYCEROL, FOR THE MANUFACTURING OF EPOCCHLOROHYDRIN, FOR THE MANUFACTURING OF EPOXY RESINS, AND FOR THE MANUFACTURING DICHLOROPROPANOL |
| FR2913421B1 (en) | 2007-03-07 | 2009-05-15 | Solvay | PROCESS FOR PRODUCING DICHLOROPROPANOL |
| FR2913684B1 (en) | 2007-03-14 | 2012-09-14 | Solvay | PROCESS FOR PRODUCING DICHLOROPROPANOL |
| TW200911740A (en) | 2007-06-01 | 2009-03-16 | Solvay | Process for manufacturing a chlorohydrin |
| TWI500609B (en) | 2007-06-12 | 2015-09-21 | Solvay | Product containing epichlorohydrin, its preparation and its use in various applications |
| TW200911693A (en) | 2007-06-12 | 2009-03-16 | Solvay | Aqueous composition containing a salt, manufacturing process and use |
| KR20100089835A (en) | 2007-10-02 | 2010-08-12 | 솔베이(소시에떼아노님) | Use of compositions containing silicon for improving the corrosion resistance of vessels |
| FR2925045B1 (en) | 2007-12-17 | 2012-02-24 | Solvay | GLYCEROL-BASED PRODUCT, PROCESS FOR OBTAINING THE SAME AND USE THEREOF IN THE MANUFACTURE OF DICHLOROPROPANOL |
| EP2085364A1 (en) * | 2008-01-31 | 2009-08-05 | SOLVAY (Société Anonyme) | Process for degrading organic substances in an aqueous composition |
| TWI478875B (en) | 2008-01-31 | 2015-04-01 | Solvay | Process for degrading organic substances in an aqueous composition |
| EA201071157A1 (en) | 2008-04-03 | 2011-04-29 | Солвей (Сосьете Аноним) | COMPOSITION CONTAINING GLYCERIN, METHOD OF ITS RECEPTION AND APPLICATION IN PRODUCTION OF DICHLORPROPANOL |
| FR2935968B1 (en) | 2008-09-12 | 2010-09-10 | Solvay | PROCESS FOR THE PURIFICATION OF HYDROGEN CHLORIDE |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4246104A (en) * | 1975-11-29 | 1981-01-20 | Bayer Aktiengesellschaft | Pressure-hydrolytic treatment of effluent |
| DE4229355A1 (en) * | 1992-09-06 | 1994-03-10 | Solvay Deutschland | Process and appts for the removal of chlorinated organic cpds from effluent - esp. from epichlorohydrin prodn |
| US5386079A (en) * | 1992-05-19 | 1995-01-31 | Ciba-Geigy Corporation | Wastewater treatment process |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB1459284A (en) * | 1974-09-25 | 1976-12-22 | Bp Chem Int Ltd | Effluent treatment |
| JPH06157007A (en) * | 1992-11-13 | 1994-06-03 | Godo Shigen Sangyo Kk | Method for recovering iodine from waste liquor containing organic iodine compound |
| DE4244482A1 (en) * | 1992-12-30 | 1994-07-07 | Solvay Deutschland | Wastewater treatment process |
-
1998
- 1998-04-21 BE BE9800297A patent/BE1011880A4/en not_active IP Right Cessation
-
1999
- 1999-04-14 GB GB9908550A patent/GB2336584A/en not_active Withdrawn
- 1999-04-15 NL NL1011815A patent/NL1011815C2/en not_active IP Right Cessation
- 1999-04-16 FR FR9904937A patent/FR2777558A1/en not_active Withdrawn
- 1999-04-20 BR BR9901378-9A patent/BR9901378A/en not_active Application Discontinuation
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4246104A (en) * | 1975-11-29 | 1981-01-20 | Bayer Aktiengesellschaft | Pressure-hydrolytic treatment of effluent |
| US5386079A (en) * | 1992-05-19 | 1995-01-31 | Ciba-Geigy Corporation | Wastewater treatment process |
| DE4229355A1 (en) * | 1992-09-06 | 1994-03-10 | Solvay Deutschland | Process and appts for the removal of chlorinated organic cpds from effluent - esp. from epichlorohydrin prodn |
Also Published As
| Publication number | Publication date |
|---|---|
| NL1011815C2 (en) | 1999-10-25 |
| FR2777558A1 (en) | 1999-10-22 |
| BR9901378A (en) | 2000-04-11 |
| GB9908550D0 (en) | 1999-06-09 |
| GB2336584A (en) | 1999-10-27 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| RE | Patent lapsed |
Owner name: S.A. SOLVAY Effective date: 20010430 |