NO884048L - ELECTROLYSE OF COPPER IN THIN SOLUTIONS CONTAINING LARGE AMOUNTS OF IRON. - Google Patents
ELECTROLYSE OF COPPER IN THIN SOLUTIONS CONTAINING LARGE AMOUNTS OF IRON.Info
- Publication number
- NO884048L NO884048L NO88884048A NO884048A NO884048L NO 884048 L NO884048 L NO 884048L NO 88884048 A NO88884048 A NO 88884048A NO 884048 A NO884048 A NO 884048A NO 884048 L NO884048 L NO 884048L
- Authority
- NO
- Norway
- Prior art keywords
- electrolysis
- copper
- iron
- value
- solutions containing
- Prior art date
Links
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 title claims description 26
- 229910052742 iron Inorganic materials 0.000 title claims description 12
- 238000005868 electrolysis reaction Methods 0.000 claims description 28
- 239000010949 copper Substances 0.000 claims description 23
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 22
- 229910052802 copper Inorganic materials 0.000 claims description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- 239000011701 zinc Substances 0.000 claims description 9
- 229910052751 metal Inorganic materials 0.000 claims description 8
- 239000002184 metal Substances 0.000 claims description 8
- 238000000034 method Methods 0.000 claims description 7
- 229910052725 zinc Inorganic materials 0.000 claims description 7
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 6
- 150000004679 hydroxides Chemical class 0.000 claims description 5
- 150000002739 metals Chemical class 0.000 claims description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 claims description 4
- 150000004649 carbonic acid derivatives Chemical class 0.000 claims description 3
- 239000002243 precursor Substances 0.000 claims 1
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 18
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 8
- 235000011121 sodium hydroxide Nutrition 0.000 description 6
- 229910000019 calcium carbonate Inorganic materials 0.000 description 5
- 239000002351 wastewater Substances 0.000 description 5
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 4
- 239000010970 precious metal Substances 0.000 description 4
- 239000004576 sand Substances 0.000 description 4
- -1 Fe+++ ions Chemical class 0.000 description 3
- JJLJMEJHUUYSSY-UHFFFAOYSA-L copper(II) hydroxide Inorganic materials [OH-].[OH-].[Cu+2] JJLJMEJHUUYSSY-UHFFFAOYSA-L 0.000 description 3
- 239000003792 electrolyte Substances 0.000 description 3
- 229910001447 ferric ion Inorganic materials 0.000 description 3
- 239000000706 filtrate Substances 0.000 description 3
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 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
- 230000008021 deposition Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229960004887 ferric hydroxide Drugs 0.000 description 1
- IEECXTSVVFWGSE-UHFFFAOYSA-M iron(3+);oxygen(2-);hydroxide Chemical compound [OH-].[O-2].[Fe+3] IEECXTSVVFWGSE-UHFFFAOYSA-M 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229910000000 metal hydroxide Inorganic materials 0.000 description 1
- 150000004692 metal hydroxides Chemical class 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000001105 regulatory effect Effects 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
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/463—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation
-
- 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
- C02F1/4602—Treatment of water, waste water, or sewage by electrochemical methods for prevention or elimination of deposits
-
- 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
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Electrolytic Production Of Metals (AREA)
- Chemical Or Physical Treatment Of Fibers (AREA)
- Chemically Coating (AREA)
- Soft Magnetic Materials (AREA)
Description
Denne oppfinnelsen omfatter en metode for å kunne elektro-This invention includes a method for being able to electro-
lysere kobber fra tynne vannløsninger som inneholder større mengder jern, ved å innføre til elektrolyseinnretningen under elektrolysen et medium som feller ut ferri (Fe+++) ionene og gjør disse inerte med hensyn til selve elektrolysen av kobber. Dette skjer fortrinnsvis ved en pH-verdi på 3-4 pH-enheter. lighter copper from thin water solutions containing larger amounts of iron, by introducing a medium to the electrolysis device during the electrolysis which precipitates the ferric (Fe+++) ions and renders them inert with regard to the electrolysis of copper itself. This preferably takes place at a pH value of 3-4 pH units.
Det er kjendt for de som er kjendt med elektrolyse av verdimetaller såsom kobber, nikkel, kobolt, sink og kadmimum at såkalte red/ox-par, såsom paret Fe++/Fe+++ (f erro/ferri ) ioner, senker det teoretiske strømutbyttet med hensyn til det verdimetallet som skal elektrolyseres, at selve elektrolysen først blir ulønnsom for deretter ved større konsentrasjoner av Fe++/ Fe+++ ioner i løsningen, uteblir hele deponeringen av verdimetallet på katoden. It is known to those familiar with the electrolysis of valuable metals such as copper, nickel, cobalt, zinc and cadmium that so-called red/ox pairs, such as the pair Fe++/Fe+++ (f erro/ferri ) ions, lower the theoretical current yield with regard to the precious metal to be electrolysed, that the electrolysis itself first becomes unprofitable and then, with larger concentrations of Fe++/ Fe+++ ions in the solution, the entire deposition of the precious metal on the cathode fails.
Elektrolyse i tynne vannløsninger er godt kjendt. Imidlertid, ingen omtaler elektrolyse av kobber i tynne vannløsninger som inneholder større mengder jern, såsom av-vannet fra kobbergruver, som er kjendt for oss. Electrolysis in thin water solutions is well known. However, no one mentions the electrolysis of copper in thin water solutions containing larger amounts of iron, such as the waste water from copper mines, which is known to us.
Vi forsøkte elektrolyse av tynne kobberløsninger på bare 200 mg/l kobber som også inneholdt 2300 mg/l jern. Ved normal elektrolyse, der strømmen påført elektrolyseinnretningen var bare stor nok for teoretisk å utelektrolysere kobberet, gikk dette ikke i det hele tatt. Absolutt ingen kobber ble avsatt på katoden. We attempted electrolysis of thin copper solutions of only 200 mg/l copper which also contained 2300 mg/l iron. In normal electrolysis, where the current applied to the electrolysis device was only large enough to theoretically electrolyse the copper, this did not work at all. Absolutely no copper was deposited on the cathode.
Imidlertid, til vår store forbauselse, ved å innføre et medium, her skje1lsand(CaC03) eller natronlut (NaOH) til løsningen inne i selve elektrolyseinnretningen hadde en pH på mellom 3-4, However, to our great astonishment, by introducing a medium, here spoon sand (CaC03) or caustic soda (NaOH) to the solution inside the electrolysis device itself had a pH of between 3-4,
ble alle ferri (Fe+++) ionene som ellers forstyrret elektrolysen av kobber, feldt ut som et hydroksyd, og elektrolysen av kobber gikk som forventet. all the ferric (Fe+++) ions that otherwise interfered with the electrolysis of copper were precipitated as a hydroxide, and the electrolysis of copper proceeded as expected.
Dette med å elektrolysere verdimetallet fra vannløsningenThis by electrolysing the valuable metal from the water solution
og samtidig kontrollere pH i elektrolytten til en verdi påand at the same time control the pH in the electrolyte to a value of
3-4 pH-enheter ved før eller under elektrolysen å innføre et medium som gjør ferri-ionene inerte med hensyn til verdimetall-elektrolysen , er selve kjernen i denne oppfinnelsen. 3-4 pH units by introducing a medium before or during the electrolysis which makes the ferric ions inert with respect to the precious metal electrolysis, is the very core of this invention.
Her skal nevnes at vi har brukt her kalsiumkarbonat og natronlut, for å felle ferri-ionene som et hydroksyd. Selvsagt er det også innenfor denne oppfinnelsen å bruke andre medier som høyner pH-verdien til over pH-verdien for utfelling av ferri-hydroksyd i elektrolytten som anvendes. Her kan nevnes kalilut(KOH),metall-karbonater,metall-hydroksyder såsom for eksempel hydroksyder og karbonater av det verdimetallet som skal utelektrolyseres. It should be mentioned here that we have used calcium carbonate and caustic soda to precipitate the ferric ions as a hydroxide. Of course, it is also within this invention to use other media which raise the pH value to above the pH value for precipitation of ferric hydroxide in the electrolyte used. Mention may be made here of potassium hydroxide (KOH), metal carbonates, metal hydroxides such as, for example, hydroxides and carbonates of the precious metal to be electrolysed.
Det er vår følelse at denne oppfinnelsen ikke bare kan anvendesIt is our feeling that this invention cannot only be applied
på tynne gruve av-vann, men også selvsagt på alle tynne løsninger hvorfra verdimetaller skal gjennvinnes og jernet skal felles ut og fjernes det også. on thin mine waste water, but also of course on all thin solutions from which valuable metals are to be recovered and the iron is to be precipitated and removed as well.
Løsningen etter kobberelektrolysen inneholdt noen rester avThe solution after the copper electrolysis contained some residues of
jern (Fe++ ioner) og sink. Disse metallene ble deretter helt fjernet ved å forsette elektrolysen med innføring av kalsiumkarbonat eller natronlut til pH var mellom 6-7 enheter. iron (Fe++ ions) and zinc. These metals were then completely removed by continuing the electrolysis with the introduction of calcium carbonate or caustic soda until the pH was between 6-7 units.
Filtratet fra dette steget viste at samme teknikk som beskrevet ovenfor kan også brukes om alle metall ionene i elektrolytten skal fjernes. The filtrate from this step showed that the same technique as described above can also be used if all the metal ions in the electrolyte are to be removed.
Ovenfor beskrevet oppfinnelse skal beskrives nærmere i eksempelene nedenfor. The invention described above shall be described in more detail in the examples below.
Eksempel 1Example 1
Gruve av-vann ble elektrolysert i en elektrolyseinnretning som den nevnt i norsk søknad no 87.2388. Mine waste water was electrolysed in an electrolysis device such as the one mentioned in Norwegian application no 87.2388.
Strøm = 13 amp, celle spenning = 6,3 volt, temperatur = 20 °C. Væskeføding = 12 liter/time. Current = 13 amp, cell voltage = 6.3 volts, temperature = 20 °C. Liquid feeding = 12 litres/hour.
pH justert med skjellsand (72% CaC03)pH adjusted with shell sand (72% CaC03)
Eksempelet viser at med (her) tilsats av skjellsand til elektrolyse-enheten til utløpet viste en pH på 3,56, ble kobber fjernet fra dette gruve av-vannet fra 200 mg/l til 29 mg/l. Eksempelet viser også at uten denne pH justeringen var det The example shows that with (here) addition of shell sand to the electrolysis unit to the outlet showed a pH of 3.56, copper was removed from this mine wastewater from 200 mg/l to 29 mg/l. The example also shows that without this pH adjustment it was
ikke mulig å fjerne kobberet.not possible to remove the copper.
Eksempel 2Example 2
Objektet med dette eksempelet var å bevise at der finnes en pH-nisje mellom pH-verdiene på ca 3-4 der praktisk talt alt ferri-jern (Fe+++) er utfelt men at ikke noe kobber er utfelt som Cu(0H)2, og at en elektrolyse i dette pH-området er en reell elektrolyse av kobber. The object of this example was to prove that there is a pH niche between the pH values of about 3-4 where practically all ferric iron (Fe+++) is precipitated but that no copper is precipitated as Cu(0H)2, and that an electrolysis in this pH range is a real electrolysis of copper.
2 liter av et gruvevann ble titrert med en 1 molar NaOH-løsning fra en pH-verdi på 1,95 og opp til en pH-verdi på 5,08. Prøver ble tatt med jevne mellomrom og filtratet analysert på metall-konsentrasjonene ved forskjellige pH-verdier. 2 liters of a mine water was titrated with a 1 molar NaOH solution from a pH value of 1.95 up to a pH value of 5.08. Samples were taken at regular intervals and the filtrate analyzed for the metal concentrations at different pH values.
Eksempelet viser at ved pH-verdier > 4 felles kobber ut da sansynligvis som et Cu(0H)2-hydroksyd og at ved pH-verdier The example shows that at pH values > 4 copper probably precipitates as a Cu(0H)2 hydroxide and that at pH values
>5 begynner Fe(0H)2 og Zn(0H)2 type hydroksyder å felles ut. >5 Fe(0H)2 and Zn(0H)2 type hydroxides begin to precipitate.
Dette er kjendt kjemi for de som er kjendt med dette. This is familiar chemistry to those familiar with it.
Eksempel 3Example 3
Objektet med dette eksempelet var å vise at hvis det ikke er av interesse å ta vare på kobberet separat så virker denne teknikken også om en vil fjerne alle elementene med en høyere pH-verdi enn 4. The object of this example was to show that if it is not of interest to take care of the copper separately, this technique also works if you want to remove all the elements with a higher pH value than 4.
Et gruve av-vann ble ledet inn i en elektrolyse innretning som den nevnt i norsk søknad no 87.2388. Gruvevannet ble pumpet inn i ca 1 time uten strøm påsatt, men med pH regulert til ca 5,5-5,8. Denne pH verdien er i praksis rett under den pH-verdien som feller ut Fe(0H)2 og Zn(0H)2 hydroksydene, men over pH-verdiene som feller ut både Cu(0H)2 og Fe(0H)3 hydroksydene. A mine waste water was led into an electrolysis device such as the one mentioned in Norwegian application no 87.2388. The mine water was pumped in for about 1 hour without electricity applied, but with the pH regulated to about 5.5-5.8. This pH value is in practice just below the pH value that precipitates Fe(0H)2 and Zn(0H)2 hydroxides, but above the pH values that precipitate both Cu(0H)2 and Fe(0H)3 hydroxides.
Hensikten var å, vise at ved å sette på strømmen ble jern og tildels sink utfelt, noe som ellers ikke ville skjedd. The purpose was to show that by switching on the current, iron and partly zinc were precipitated, which would not otherwise have happened.
Skjellsand (CaC03) brukt til å justere pH.Shell sand (CaC03) used to adjust pH.
Eksempelet viser at strømmen lager ferri-ioner og at disse felles ut ved påsatt strøm. Videre at hvis det er ønskelig, kan alle tungmetaller som her vist fjernes, hvis det er snakk om miljøvern. The example shows that the current creates ferric ions and that these precipitate when current is applied. Furthermore, if it is desired, all heavy metals as shown here can be removed, if it is a question of environmental protection.
Eksempel 4Example 4
Dette eksempelet ble utført for ytterligere å bevise at alle tungmetallene Cu,Fe,Zn kunne fjernes fra en tynn løsning, ved en høyere pH. NaOH er her brukt for å justere pH. Eksempelet viser at ved å utføre elektrolysen ved en pH-verdi på 6,20 ble filtratet praktisk talt fritt for tungmetallene kobber, jern og sink. This example was carried out to further prove that all the heavy metals Cu,Fe,Zn could be removed from a thin solution, at a higher pH. NaOH is used here to adjust the pH. The example shows that by performing the electrolysis at a pH value of 6.20, the filtrate was practically free of the heavy metals copper, iron and zinc.
Claims (1)
Priority Applications (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NO88884048A NO884048L (en) | 1988-09-12 | 1988-09-12 | ELECTROLYSE OF COPPER IN THIN SOLUTIONS CONTAINING LARGE AMOUNTS OF IRON. |
PCT/NO1989/000091 WO1990002709A1 (en) | 1988-09-12 | 1989-09-11 | Buffered electrolysis |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NO88884048A NO884048L (en) | 1988-09-12 | 1988-09-12 | ELECTROLYSE OF COPPER IN THIN SOLUTIONS CONTAINING LARGE AMOUNTS OF IRON. |
Publications (2)
Publication Number | Publication Date |
---|---|
NO884048D0 NO884048D0 (en) | 1988-09-12 |
NO884048L true NO884048L (en) | 1990-03-13 |
Family
ID=19891238
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
NO88884048A NO884048L (en) | 1988-09-12 | 1988-09-12 | ELECTROLYSE OF COPPER IN THIN SOLUTIONS CONTAINING LARGE AMOUNTS OF IRON. |
Country Status (2)
Country | Link |
---|---|
NO (1) | NO884048L (en) |
WO (1) | WO1990002709A1 (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AU643217B2 (en) * | 1989-05-22 | 1993-11-11 | F. Hoffmann-La Roche Ag | Methods for tagging and tracing materials with nucleic acids |
ES2118037B1 (en) * | 1996-04-30 | 1999-09-16 | Acuna Arranz Ladislao | METHOD OF PURIFYING INDUSTRIAL WASTEWATER AND OBTAINING THE NECESSARY REAGENT FOR PURIFICATION. |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
SE188897C1 (en) * | 1963-01-01 | |||
DE1177081B (en) * | 1960-04-06 | 1964-08-27 | Guldager Electrolyse | Process for the electrolytic removal of colloidal substances from wastewater containing wetting agents |
DE1459451A1 (en) * | 1962-05-29 | 1968-12-19 | Asendorf Dr Erich | Process for removing copper from sulfuric acid and nitric acid waste water with simultaneous destruction of water-insoluble copper compounds |
EP0007325B1 (en) * | 1975-07-18 | 1982-06-02 | William Edward Lindman | Process and assembly for removing a dissolved or suspended contaminant from a polar liquid as a solid substance |
DE2548620C2 (en) * | 1975-10-30 | 1977-12-22 | Duisburger Kupferhütte, 4100 Duisburg | Process for the production of retouched electrolytic copper by reducing electrolysis |
CH647421A5 (en) * | 1980-06-04 | 1985-01-31 | Ciba Geigy Ag | METHOD FOR SEPARATING OIL-IN-WATER EMULSIONS THAT MAY TENSIDE BY ELECTROLYSIS. |
DE3867327D1 (en) * | 1987-06-18 | 1992-02-13 | Andco Environmental Processes | METHOD FOR REMOVING ORGANIC COLORS AND HEAVY METALS FROM SEWAGE. |
-
1988
- 1988-09-12 NO NO88884048A patent/NO884048L/en unknown
-
1989
- 1989-09-11 WO PCT/NO1989/000091 patent/WO1990002709A1/en unknown
Also Published As
Publication number | Publication date |
---|---|
NO884048D0 (en) | 1988-09-12 |
WO1990002709A1 (en) | 1990-03-22 |
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