DE19731616A1 - Metal ion removal from electrolyte - Google Patents
Metal ion removal from electrolyteInfo
- Publication number
- DE19731616A1 DE19731616A1 DE1997131616 DE19731616A DE19731616A1 DE 19731616 A1 DE19731616 A1 DE 19731616A1 DE 1997131616 DE1997131616 DE 1997131616 DE 19731616 A DE19731616 A DE 19731616A DE 19731616 A1 DE19731616 A1 DE 19731616A1
- Authority
- DE
- Germany
- Prior art keywords
- cell
- catholyte
- primary
- cathode
- electrolyte
- 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.)
- Withdrawn
Links
- 239000003792 electrolyte Substances 0.000 title claims abstract description 17
- 229910021645 metal ion Inorganic materials 0.000 title 1
- 238000000034 method Methods 0.000 claims abstract description 26
- 238000005868 electrolysis reaction Methods 0.000 claims abstract description 5
- 238000000909 electrodialysis Methods 0.000 claims abstract 3
- 229910052751 metal Inorganic materials 0.000 claims description 8
- 239000002184 metal Substances 0.000 claims description 8
- 238000005341 cation exchange Methods 0.000 claims description 6
- 239000012528 membrane Substances 0.000 claims description 6
- 239000004615 ingredient Substances 0.000 claims description 4
- 239000003011 anion exchange membrane Substances 0.000 claims description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims 2
- 229910052799 carbon Inorganic materials 0.000 claims 1
- 239000002131 composite material Substances 0.000 claims 1
- 238000010276 construction Methods 0.000 claims 1
- 229910002804 graphite Inorganic materials 0.000 claims 1
- 239000010439 graphite Substances 0.000 claims 1
- 238000002347 injection Methods 0.000 claims 1
- 239000007924 injection Substances 0.000 claims 1
- 238000000053 physical method Methods 0.000 claims 1
- 238000002604 ultrasonography Methods 0.000 claims 1
- 239000000463 material Substances 0.000 abstract description 5
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 23
- 229910052759 nickel Inorganic materials 0.000 description 11
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 7
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 150000001450 anions Chemical class 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 238000009713 electroplating Methods 0.000 description 3
- 238000001465 metallisation Methods 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 229920000557 Nafion® Polymers 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 150000001768 cations Chemical class 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- KRVSOGSZCMJSLX-UHFFFAOYSA-L chromic acid Substances O[Cr](O)(=O)=O KRVSOGSZCMJSLX-UHFFFAOYSA-L 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- AWJWCTOOIBYHON-UHFFFAOYSA-N furo[3,4-b]pyrazine-5,7-dione Chemical compound C1=CN=C2C(=O)OC(=O)C2=N1 AWJWCTOOIBYHON-UHFFFAOYSA-N 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000008929 regeneration Effects 0.000 description 2
- 238000011069 regeneration method Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
- VEQPNABPJHWNSG-UHFFFAOYSA-N Nickel(2+) Chemical compound [Ni+2] VEQPNABPJHWNSG-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000003139 buffering effect Effects 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000001784 detoxification Methods 0.000 description 1
- 238000000502 dialysis Methods 0.000 description 1
- 230000005684 electric field Effects 0.000 description 1
- 238000005530 etching Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- -1 halide ions Chemical class 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910001453 nickel ion Inorganic materials 0.000 description 1
- 238000007747 plating Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000008237 rinsing water Substances 0.000 description 1
- 238000007086 side reaction Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000004381 surface treatment Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 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
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
-
- 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
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
- C02F1/4676—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
- C02F1/4678—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction of metals
-
- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25D—PROCESSES FOR THE ELECTROLYTIC OR ELECTROPHORETIC PRODUCTION OF COATINGS; ELECTROFORMING; APPARATUS THEREFOR
- C25D21/00—Processes for servicing or operating cells for electrolytic coating
- C25D21/16—Regeneration of process solutions
- C25D21/18—Regeneration of process solutions of electrolytes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/46115—Electrolytic cell with membranes or diaphragms
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/4618—Supplying or removing reactants or electrolyte
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Molecular Biology (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Electrolytic Production Of Metals (AREA)
Abstract
Description
Die Erfindung betrifft ein Verfahren und eine Zelleneinheit zur Entfernung von Inhaltsstoffen aus Elektrolyten, wie sie z. B. in der Oberflächentechnik oder in Gaswäschern verwendet werden. Ty pische Vertreter sind nickelhaltige Systeme, die als galvanische Bäder eingesetzt werden. In die sen Bädern reichern sich durch nichtadäquate Anoden- und Kathodenreaktionen Nickelionen an, die den Vernickelungsprozeß negativ beeinflussen können. Besonders moderne Hochglanzelek trolyte müssen nach relativ kurzer Zeit verworfen und durch neue ersetzt werden. Weiterhin ist für diese Prozesse eine Metallanreicherung in Spülwässern charakteristisch. Für alle drei beschrie benen Fälle ergibt sich somit die Notwendigkeit der Metallentfernung. Dialytische Prozesse in An lagenstacks sind Stand der Technik, jedoch gelingt es damit nur, Prozeßlösungen zu konzentrie ren, aber nicht, den Prozeß der gewünschten Metallabscheidung durchzuführen. Z. B. für ver brauchte Prozeßbäder ist diese Methode absolut ungeeignet. Unvorteilhafterweise existieren der zeit keine befriedigenden Lösungen, die mit moderaten Kosten zu realisieren wären. Am Beispiel des Nickels wird dies besonders kraß deutlich. Zwar ist es relativ einfach, Nickel aus konzentrier ten Lösungen in einfachen , ungeteilten Elektrolysezellen abzuscheiden (Hartinger, L.: Handbuch der Abwasser- und Recyclingtechnik, München 1991), das Problem der Prozeßbedingungen steht jedoch als nicht hinreichend gelöst dagegen. Besonders die Einhaltung des notwendigen konstan ten pH-Wertes ist problematisch. Pufferungen scheiden in vielen Fällen aus, die ständige Nachstel lung mittels Natronlauge ist in der Regel ökonomisch nicht vertretbar oder führt zum Verderben der Prozeßlösung. Es existieren andere Vorschläge auf der Basis elektrolytischer Prinzipien zur Entfernung ähnlicher Inhaltsstoffe. So wird z. B. vorgeschlagen (Läser, L.: Wertstoffrückgewin nung mit einem neuartigen System in galvanischen und anderen Prozeßlösungen, Galvanotechnik 88 (1997) 4, 1134-1137), Kationen über einen Separator im elektrischen Feld im Kathodenraum einer Zelle anzureichern und mittels Hydroxidzugabe auszufüllen, was ebenfalls einer Metallrück gewinnung entgegensteht. In verschiedenen Beiträgen (Blatt, W.: Elektrolytische Nickelrückge winnung, Galvanotechnik, 87 (1996) 4, 1118-1124; Hurschmann, H.: Metallrückgewinnung aus Prozeßwasser Galvanotechnik 84 (1993) 10, 3429-3432) werden kationenaustauschermembran geteilte Elektrolysezellen vorgeschlagen, um an der Anode unerwünschte Reaktionen zu unter drücken. Eine ähnliches Prinzip wird auch bei der Chromsäureregeneration (DE PS 40 32 856) an gewandt. In einer früheren Arbeit (Patrick, K und Dexter, D.: Combining Elektrolysis and Dialy sis for Regeneration of Chromic Acid Etching Solution, Journal of Membrane Science 13 (1983) 327-336) wird die paarweise stoffstrommäßige Verschaltung zweier Teilzellen eines einfachen Dialysators und einer kationenaustauschermembrangeteilten Zelle vorgestellt, die aber z. B. im Falle des Nickels auch nicht die geschilderten Probleme löst. Gleiches gilt für die Offenlegungsschrift DE OS 41 18 725. In der DE OS 195 32 784 wird der Kathodenkreislauf ei ner Zweikammerzelle mit dem Kreislauf der Mittelkammer oder in einer Untervariante mit dem Katholytkreislauf einer zweiten Dreikammerelektrolysezelle verbunden. Auch diese Variante er laubt nicht die Überwindung der oben geschilderten Probleme, wie Metallabscheidung in metalli scher Form unter pH-Wert-Konstanthaltung ohne Chemikalieneinsatz.The invention relates to a method and a cell unit for removing ingredients from Electrolytes such as z. B. used in surface technology or in gas scrubbers. Ty Typical representatives are nickel-containing systems that are used as galvanic baths. In the baths accumulate nickel ions due to inadequate anode and cathode reactions, that can negatively affect the nickel plating process. Particularly modern high-gloss elek trolytes have to be discarded after a relatively short time and replaced with new ones. Still is metal enrichment in rinsing water is characteristic of these processes. Described for all three In these cases, there is a need for metal removal. Dialytic processes in An Layer stacks are state-of-the-art, but it is only possible to concentrate process solutions ren, but not to carry out the process of the desired metal deposition. E.g. for ver needed process baths this method is absolutely unsuitable. Unfortunately, the exist time no satisfactory solutions that could be realized with moderate costs. Exemplary The nickel is particularly clear. While it is relatively easy to concentrate nickel to separate solutions in simple, undivided electrolysis cells (Hartinger, L .: manual the waste water and recycling technology, Munich 1991), the problem of the process conditions however, it was not sufficiently resolved. In particular, compliance with the necessary constant pH value is problematic. Buffering is ruled out in many cases, the constant adjustment Treatment with sodium hydroxide solution is usually not economically viable or leads to spoilage the process solution. There are other proposals based on electrolytic principles Removal of similar ingredients. So z. B. proposed (Läser, L .: recycling of valuable materials with a new system in electroplating and other process solutions, electroplating 88 (1997) 4, 1134-1137), cations via a separator in the electric field in the cathode compartment to enrich a cell and fill it in by adding hydroxide, which is also a metal back production stands in the way. In various articles (Blatt, W .: electrolytic nickel recoil Winnung, Galvanotechnik, 87 (1996) 4, 1118-1124; Hurschmann, H .: Metal recovery from Process water electroplating 84 (1993) 10, 3429-3432) become cation exchange membrane divided electrolytic cells proposed to prevent undesirable reactions at the anode to press. A similar principle is also applied to chromic acid regeneration (DE PS 40 32 856) agile. In a previous work (Patrick, K and Dexter, D .: Combining Elektrolysis and Dialy sis for Regeneration of Chromic Acid Etching Solution, Journal of Membrane Science 13 (1983) 327-336), the pair-wise interconnection of two sub-cells becomes a simple one Dialysers and a cation exchange membrane-divided cell presented, but z. B. in Case of nickel also does not solve the problems described. The same applies to the Publication DE OS 41 18 725. In DE OS 195 32 784 the cathode circuit is egg ner two-chamber cell with the circuit of the middle chamber or in a sub-variant with the Catholyte circuit of a second three-chamber electrolysis cell connected. This variant, too does not allow overcoming the problems outlined above, such as metal deposition in metalli form while keeping the pH constant without the use of chemicals.
Der Erfindung liegt die Aufgabe zugrunde, ein Verfahren und eine Zelleneinheit zur Verfügung zu steilen, die es erlauben, unter problematischen Verhältnissen Inhaltsstoffe aus Elektrolyten mög lichst in reiner Form mit hoher Effektivität und ohne äußeren Chemikalienzusatz zu separieren.The object of the invention is to provide a method and a cell unit steep, which allow ingredients from electrolytes under problematic conditions If possible, in pure form with high effectiveness and without separating external chemical additives.
Die Aufgabe der Erfindung wird - ausgehend vom Oberbegriff des 1. Patentanspruches - gemäß den Merkmalen im gekennzeichneten Teil gelöst. Die Fig. 1 zeigt die Merkmale des Anspruchs 1, wobei eine Kombination zweier Teilzellen in einfacher Grund- oder multipler Struktur, die die Grundstruktur mehrfach wiederholt, verwendet wird und eine stoffstrommäßige Verschaltbarkeit der Teilzellen, hier als Primär- (1) und Sekundärzelle (2) bezeichnet, gegeben ist. Die Stoffstrom führung durch den hier dargestellten und von dem Separator (4) begrenzten Katholytraum mit der Kathode (7) und durch den hier dargestellten Katholytraum mit der Kathode (9), begrenzt durch den Separator (8), kann gleichzeitig oder zeitlich getaktet erfolgen. Wird ein zu behandelnder Elektrolyt (11) aus einer Vorlage 14 durch den Katholytraum der Primärzelle (1) geführt, kann z. B. ein Metall in reiner Form abgeschieden werden, wobei durch die Nebenreaktion der kathodi schen Wasserstoffbildung sich der pH-Wert verschiebt, was die Effektivität der Metallabschei dung verschlechtert. Dies kann erfindungsgemäß ausgeglichen werden durch einen Stoffstrom (12) aus dem Katholytraum der Sekundärzelle (2), in den über den Separator (8) an der Anode (10) produzierte Protonen übertreten. Zur Korrektur des pH-Wertes kann auch ein Teil (13) des Elektrolyten aus der Mittelkammer (5) der Primärzelle (1) verwendet werden. In diese Mittelkam mer treten über den Separator (3) z. B. an der Kathode (6) gebildete Protonen sowie über den Separator (4) Anionen über und bilden im geschilderten Fall eine Säure. Auf die mittlere Kammer (5) könnte im Prinzip verzichtet werde, da jedoch viele Elektrolyte Halogenidionen beinhalten, wird durch die Dreikammerstruktur eine Halogenbildung an der Anode (6) wirksam verhindert. Auf diese Art und Weise erhält man überraschenderweise einen sich nahezu selbstregelnden Me tallabscheidungsprozeß unter optimalen Bedingungen. Eine störende Schlammbildung wird ver mieden. Ein weiterer wesentlicher Vorteil der Erfindung ist es, daß keine kostenaufwendigen Korrektur- oder Entgiftungschemikalien von außen zugeführt werden müssen - im Gegenteil, man erhält sogar verwertbare Säure (im geschilderten Fall), die dem Oberflächenbehandlungsprozeß wieder zugeführt werden kann. Für eine Anwendung zur Entsorgung von Elektrolyten erhält man weiterhin neben der Entfernung der Kationen über metallische Abscheidung eine Entfernung von Anionen aus der verbrauchten Prozeßlösung. Die Erfindung ist aber hauptsächlich dann lohnenswert praktikabel, wenn Ionenseparierungsprozesse in starkem Maße vom pH-Wert abhän gen, wie es für viele nickel-, zink-, eisen-, cobalt- oder chromhaltige Systeme der Fall ist.The object of the invention is achieved - starting from the preamble of the first claim - according to the features in the marked part. Fig. 1 shows the features of claim 1, wherein a combination of two sub-cells in a simple basic or multiple structure, which repeats the basic structure used multiple times, and a material flow even interconnectability of the subcells, here as a primary (1) and secondary cell (2 ) is given. The flow of material through the catholyte space shown here and delimited by the separator ( 4 ) with the cathode ( 7 ) and through the catholyte space shown here with the cathode ( 9 ), delimited by the separator ( 8 ), can be carried out simultaneously or at intervals. If an electrolyte to be treated ( 11 ) is guided from a template 14 through the catholyte space of the primary cell ( 1 ), z. B. a metal can be deposited in pure form, the pH shifting due to the side reaction of the cathodic hydrogen formation, which deteriorates the effectiveness of the metal deposition. According to the invention, this can be compensated for by a material stream ( 12 ) from the catholyte space of the secondary cell ( 2 ) into which protons produced at the anode ( 10 ) pass through the separator ( 8 ). A part ( 13 ) of the electrolyte from the middle chamber ( 5 ) of the primary cell ( 1 ) can also be used to correct the pH. In this Mittelkam mer occur through the separator ( 3 ) z. B. protons formed on the cathode ( 6 ) and via the separator ( 4 ) anions and form an acid in the case described. In principle, the middle chamber ( 5 ) could be dispensed with, but since many electrolytes contain halide ions, the three-chamber structure effectively prevents halogen formation at the anode ( 6 ). In this way, surprisingly, an almost self-regulating metal separation process is obtained under optimal conditions. A disturbing sludge formation is avoided. Another important advantage of the invention is that no costly correction or detoxification chemicals have to be added from the outside - on the contrary, even usable acid (in the case described) is obtained, which can be returned to the surface treatment process. For an application for the disposal of electrolytes, in addition to the removal of the cations via metallic deposition, removal of anions from the used process solution is also obtained. However, the invention is mainly worthwhile if ion separation processes depend to a large extent on the pH, as is the case for many systems containing nickel, zinc, iron, cobalt or chromium.
Die Ausführung der Erfindung wird mit Hilfe eines Beispiels näher erklärt (Fig. 2). In einer halb technischen Elektrolyseeinheit mit einem Gesamtvolumen von 0,0105 m3 wurden zwei Teilzel len entsprechend Fig. 2 miteinander unter stromkonstanten Betriebsbedingungen (Strombelastung 30 A) miteinander verschaltet. Aus einem Vorlagegefäß mit einem Volumen von 25 l wurde ein abgearbeiteter Standspülelektrolyt (11) (Anfangssulfatkonzentration: 40 g/l, Anfangschloridkon zentration: 10 g/l) über die Katholytkammer der Primärzelle (1) geführt. Diese Katholytkammer war durch eine Anionenaustauschermembran (4) von der Mittelkammer (5) getrennt, in die selek tiv ein elektrodialytischer Anionentransport (Sulfat- und Chloridionen) erfolgte. Aus der Anoden kammer der Primärzelle (1), getrennt von der Mittelkammer (5) mit einer Nafion- Kationenaustauschermembran (3) traten Protonen in die Mittelkammer (5) ein. Ein zweiter Ka tholytstrom (12) verband die Katholytkammern von Primär- und Sekundärzelle. Die Sekundärzel le (2) wurde wie auch die Nichtkatholytkammern der Primärzelle (1) zu Beginn mit 3%-iger Schwefelsäure gefüllt. In der Mittelkammer der Primärzelle (1) befand sich zu Versuchsbeginn 1%-ige Schwefelsäure. Der Separator (8) in der Sekundärzelle (2) war eine Kationenaustau schermembran (Nafion). Unter den Bedingungen des Versuches (Versuchszeit 20,5 Stunden) än derte sich der pH-Wert in den Katholytkammern von anfangs 5 auf 5,5 am Versuchsende. An den Nickelplattenkathoden wurde reines, metallisches Nickel in hervorragender Qualität abge schieden. Der Nickelgehalt der Vorlage (14) verringerte sich von 12 g Nickel/l auf 0,02 g Nickel/l. In der Mittelkammer (5) bildete sich ein Gemisch aus Schwefelsäure (60 g/l) und Salzsäure (12 g/l).The embodiment of the invention is explained in more detail with the aid of an example ( FIG. 2). In a semi-technical electrolysis unit with a total volume of 0.0105 m 3 , two sub-cells according to FIG. 2 were interconnected under constant current operating conditions (current load 30 A). A processed standing rinsing electrolyte ( 11 ) (initial sulfate concentration: 40 g / l, initial chloride concentration: 10 g / l) was passed over a catholyte chamber of the primary cell ( 1 ) from a storage vessel with a volume of 25 l. This catholyte chamber was separated by an anion exchange membrane ( 4 ) from the middle chamber ( 5 ) into which an electrodialytic anion transport (sulfate and chloride ions) was carried out selectively. From the anode chamber of the primary cell ( 1 ), separated from the middle chamber ( 5 ) with a Nafion cation exchange membrane ( 3 ), protons entered the middle chamber ( 5 ). A second Ka tholytstromstrom ( 12 ) connected the catholyte chambers of the primary and secondary cells. The secondary cell ( 2 ) as well as the non-catholyte chambers of the primary cell ( 1 ) were initially filled with 3% sulfuric acid. At the beginning of the experiment, 1% sulfuric acid was in the middle chamber of the primary cell ( 1 ). The separator ( 8 ) in the secondary cell ( 2 ) was a cation exchange membrane (Nafion). Under the conditions of the test (test time 20.5 hours), the pH in the catholyte chambers changed from initially 5 to 5.5 at the end of the test. Pure, metallic nickel of excellent quality was deposited on the nickel plate cathodes. The nickel content of the template ( 14 ) decreased from 12 g nickel / l to 0.02 g nickel / l. A mixture of sulfuric acid (60 g / l) and hydrochloric acid (12 g / l) formed in the middle chamber ( 5 ).
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE1997131616 DE19731616A1 (en) | 1997-07-23 | 1997-07-23 | Metal ion removal from electrolyte |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE1997131616 DE19731616A1 (en) | 1997-07-23 | 1997-07-23 | Metal ion removal from electrolyte |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| DE19731616A1 true DE19731616A1 (en) | 1999-01-28 |
Family
ID=7836622
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| DE1997131616 Withdrawn DE19731616A1 (en) | 1997-07-23 | 1997-07-23 | Metal ion removal from electrolyte |
Country Status (1)
| Country | Link |
|---|---|
| DE (1) | DE19731616A1 (en) |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1533398A1 (en) * | 2003-10-24 | 2005-05-25 | Siemens Aktiengesellschaft | Process for producing an electrolyte ready for use out of waste products containing metal ions |
| US7378010B2 (en) | 2004-07-22 | 2008-05-27 | Phelps Dodge Corporation | System and method for producing copper powder by electrowinning in a flow-through electrowinning cell |
| US7393438B2 (en) | 2004-07-22 | 2008-07-01 | Phelps Dodge Corporation | Apparatus for producing metal powder by electrowinning |
| US7452455B2 (en) | 2004-07-22 | 2008-11-18 | Phelps Dodge Corporation | System and method for producing metal powder by electrowinning |
| US7494580B2 (en) | 2003-07-28 | 2009-02-24 | Phelps Dodge Corporation | System and method for producing copper powder by electrowinning using the ferrous/ferric anode reaction |
| US7736475B2 (en) | 2003-07-28 | 2010-06-15 | Freeport-Mcmoran Corporation | System and method for producing copper powder by electrowinning using the ferrous/ferric anode reaction |
| US8273237B2 (en) | 2008-01-17 | 2012-09-25 | Freeport-Mcmoran Corporation | Method and apparatus for electrowinning copper using an atmospheric leach with ferrous/ferric anode reaction electrowinning |
-
1997
- 1997-07-23 DE DE1997131616 patent/DE19731616A1/en not_active Withdrawn
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7494580B2 (en) | 2003-07-28 | 2009-02-24 | Phelps Dodge Corporation | System and method for producing copper powder by electrowinning using the ferrous/ferric anode reaction |
| US7736475B2 (en) | 2003-07-28 | 2010-06-15 | Freeport-Mcmoran Corporation | System and method for producing copper powder by electrowinning using the ferrous/ferric anode reaction |
| EP1533398A1 (en) * | 2003-10-24 | 2005-05-25 | Siemens Aktiengesellschaft | Process for producing an electrolyte ready for use out of waste products containing metal ions |
| US7288170B2 (en) | 2003-10-24 | 2007-10-30 | Siemens Aktiengesellschaft | Process for producing a ready-to-use electrolyte |
| US7378010B2 (en) | 2004-07-22 | 2008-05-27 | Phelps Dodge Corporation | System and method for producing copper powder by electrowinning in a flow-through electrowinning cell |
| US7393438B2 (en) | 2004-07-22 | 2008-07-01 | Phelps Dodge Corporation | Apparatus for producing metal powder by electrowinning |
| US7452455B2 (en) | 2004-07-22 | 2008-11-18 | Phelps Dodge Corporation | System and method for producing metal powder by electrowinning |
| US7591934B2 (en) | 2004-07-22 | 2009-09-22 | Freeport-Mcmoran Corporation | Apparatus for producing metal powder by electrowinning |
| US8273237B2 (en) | 2008-01-17 | 2012-09-25 | Freeport-Mcmoran Corporation | Method and apparatus for electrowinning copper using an atmospheric leach with ferrous/ferric anode reaction electrowinning |
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