AP379A - Bacterial oxidation of metal containing materials. - Google Patents
Bacterial oxidation of metal containing materials. Download PDFInfo
- Publication number
- AP379A AP379A APAP/P/1992/000367A AP9200367A AP379A AP 379 A AP379 A AP 379A AP 9200367 A AP9200367 A AP 9200367A AP 379 A AP379 A AP 379A
- Authority
- AP
- ARIPO
- Prior art keywords
- process according
- oxidation
- bacteria
- gold
- thermotolerant
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C22—METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
- C22B—PRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
- C22B3/00—Extraction of metal compounds from ores or concentrates by wet processes
- C22B3/18—Extraction of metal compounds from ores or concentrates by wet processes with the aid of microorganisms or enzymes, e.g. bacteria or algae
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S423/00—Chemistry of inorganic compounds
- Y10S423/09—Reaction techniques
- Y10S423/17—Microbiological reactions
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geochemistry & Mineralogy (AREA)
- Manufacturing & Machinery (AREA)
- Microbiology (AREA)
- Environmental & Geological Engineering (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Biochemistry (AREA)
- Geology (AREA)
- Biotechnology (AREA)
- Materials Engineering (AREA)
- Mechanical Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Manufacture And Refinement Of Metals (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
A processing
Description
DESCRIPTION in .'r.e present invent ton relates tt a nrttess :;r the cf metal containing materials cv bacterial oxidation.
RIELS GE THE INVENTION
It Is kncwr. that reccverv of metals especially precious metals ar.d case metals from refrectcrv sulphide material; car be enhanced by bacterial oxidation or leacrir.g. The bacterial treatment subjects the sulpnioo materia^ to a pre-oxidation. The refractory sulphide materials can ta.wide variety of forms including mineral sulphides, ea .ment :aroor.acecus sui:
I o r-ι r- Π s, sulphide ration concentrate .vem sulphide gravity concentrates, sulphide tailings, sulphide mattes ard sulphidic fume.
The precious metals and some base metals remain in the oxidised solid residue and can be recovered by conventional carbon in pulp or other chemical leaching processes. Some case metals such as copper, sine and nickel gc into solution and may be recovered directly by conventional sc' extraction and eiectrowinnir.g.
In the cast, bacterial oxidation of precious cr containing sulphide materials has typically been conducted using bacteria cf the Thiobacillus species. However, the Thiobacillus species car cnly operate it temperatures up to about 40°C. Further, the oxidation effected by Thiobacillus bacteria is ar exothermic reaction and it is sometimes necessary to cool the process reactors to prevent the
APO00379
- 3 bacteria can operate.
SUMMARY OF THE INVENTION
The present invention provides a process for the bacterial oxidation of metal containing sulphide materials using thermotolerant bacteria which can operate at higher temperatures than conventional Thiobacillus bacteria.
In accordance with one aspect of the present invention there is provided a process fcr recovering metals from particulate refractory precious or base metal containing sulphide materials which comprises contacting the sulphide material with an aqueous solution containing a thermotolerant bacteria culture (as herein defined) capable of promoting oxidation of the sulphide material at a temperature in the range from 25 to 55°C, separating the oxidised residue from the aqueous liquid and treating the oxidised residue and/or the aqueous liquid to recover metal therefrom.
DESCRIPTION OF THE INVENTION
The thermotolerant bacteria used in the present invention are as described in Thermophiles General, Molecular, and
Applied Microbiology edited by Thomas D. Brock and published by John Wiley & Sons (1986). In Chapter 1 of this l publication, there is illustrated in Figure 1(b) a graph shewing that thermotolerant bacteria grow at temperatures lower than those preferred by moderate and obligate or extreme thermophiles.
In the context of the present invention, a thermotolerant bacteria is one which has an optimum growth temperature of 40 to 45°C and an operating temperature of 25 to 55’C.
BAD original
- 3a Thermotolerant bacteria are found in soil and water in certain locale. Any suitable method for isolation of the thermotolerant bacteria may be used, such as agar plating, critical end point dilution or solution growth, all of which are standard microbiology procedures.
The thermotolerant culture is preferentially acidophilic and operates most effectively in the temperature range of 40-45°C. An example of a thermotolerant acidophile is Sulfobacillus species. These bacteria are generally found in sulphide deposits and hot springs. Examples of the locale where such bacteria are found include hot springs located in Iceland and New Zealand.
Preferably, the aqueous solution used in the process of the
BAD ORIGINAL
AP Ο Ο Ο 3 7 9
- 4 present invention is acidic. It has been found that the optimum acidity of the aqueous Liquid for growth of the thermotoierant bacteria culture used in tne present invention ts ir. tne rance rrom ~r. l.j to 1.3, whilst the optimum acidity if the aqueous l^ruid for sceration of tne process of the present invention is in the range from pH
Z * z
The bacterial oxidation step tf tne process of the present invention is conducted in the presence of nutrients white arc typically cissem/cc sa_ts ~r nitrogen, potassium and phosphorus. The nutrients may already be present in the aqueous liquid or they may be added thereto. The nutrient materials promote the growth of the thermotoierant bacteria.
It is preferred that the thermetoierant bacteria be acidcphiiic in view of the pH conditions under which the process of the present invention is preferably conducted. Further, the thermotoierant bacteria used in the process of the present invention are typically aerobic and thus the aqueous liquid is preferably aerated during the operation of the process to ensure that there is an adequate supply cf oxygen for the bacteria. Still further, it is found that the thermotoierant bacteria culture used in the precess cf the present invention is typically capable of autotrophic growth. Tot further, the thermotoierant bacteria culture typically does not require additional CO over and above that normally available from ambient air.
the present invention may be capable of oxidising arsenic (III) to arsenic (V) in acidic aqueous solutions containing soluble iron salts. Further, the thermotolerant bacteria culture used in the process of the present invention may be capable of oxidising iron (II) to iron (III) in acidic aqueous solutions and may be capable of oxidising reduced sulphur species tc sulphate ion in acidic aqueous solutions.
Alsc, the thermotolerant bacteria culture used in the *
precess of the present invention is preferably capable of oxidising iron and sulphides in an aqueous liquid containing up to 20 grams/litre of sodium chloride without the addition of special nutrients or employment of the special conditions. Thus, in this case extracting the pH, temperature, oxygen, nitrogen phosphate and potassium levels are maintained as discussed above, oxidation will proceed.
Typically, a particular culture of thermotolerant bacteria contains one or more bacteria species.
The process of the present invention can be operated in heaps, dumps, agitated systems or dams.
After completion of the oxidation step the oxidised solid residue and the aqueous liquid are typically separated. In the case of precious metal recovery, the oxidised solid residue would preferably be washed and then the pH of the oxidised solid residue adjusted tc a level compatible with the use of a cyanide leaching agent. Alternatively, another reagent such as thiourea could be used under acidic conditions and so the need to adjust the pH is obviated.
BADORIGINAL
AP Ο Ο Ο 3 7 9 cn
- 6 β 9
EXAMPLES
The present invention will· now ce illustrated by the following examples.
EXAMPLE 1
A pyrite - gold concentrate designated P 1 was treated in accordance with the present invention. The concentrate contained pyrite as the major sulphide mineral with minor amounts of cnalccpyrite, sphalerite, galena and arsenopvrite. Other minerals present were quartz,'sericite 10 and siderite.
The concentrate had the following assay.
Table 1
| Assay of Pyrite Concentrate ? 1 | |||
| Element | Symbol | Assay (by | weight) |
| Gold | Au | 52.0 ppm | |
| Iron | Fe | 26.0% | |
| Sulphur | S | 27.5% | |
| Nickel | Ni | 113 ppm | |
| Copper | Cu | 880 ppm | |
| Zinc | Zn | 320 ppm | |
| Lead | ?b | 160 ppm | |
| Arsenic | As | 3750 ppm | |
| Silver | Ag | 8 ppm | |
| Samples of | the concentrate | were mixed | with a sulphuric |
| solution at | a pulp density | of 3% w/w | to provide a pH r |
of 1.2 to 1.5. Nutrients included in the acid solution were ammonium-sulphate at 200 mg/L, di-potassium hydrogen phosphate at 200 mg/L and magnesium sulphate heptahydrate
X at 400 mg/L.
The acid level (pH) may vary from the start value and may either rise and then fall or fall from the outset. In most tests, the variation can be significant with the final pH often less than 1.0.
The slurry was inoculated with a thermotoierant bacteria culture designated MTC 1. The inoculated slurry was shaken in conical flasks at a temperature of 43 °C. Samples were removed periodically and analysed for iron and arsenic extraction to determine the progress of the treatment.
The sample was treated by bacterial oxidation for 30 days to achieve 80% oxidation of the pyrite mineral. The solids weight loss due to the oxidation process was 52%. The solid residue was then separated from the residual acid solution. Leaching of the solid residue using alkaline cyanide solution recovered 92% of the gold. In comparison, cyanide leaching could recover only 74% of the gold from the concentrate in the untreated state. These results are summarised in Table 2. Table 2
Gold Recovery from Untreated and Oxidised Concentrate
Sample
Untreated
Sacterial
Iron Extracted (by weight)
0%
80%
Gold Recovered
3v Cyanide
Leaching (by weight)
4%
92%
Oxidation
The cyanide solution employed to recover the gold contained sodium cyanide at a concentration of 2 g/L.
BAD ORIGINAL
AP Ο Ο Ο 3 7 9 '%The iron in the solution from the bacterial oxidation process can be removed by adjusting the pH to above 5.0 by the addition of lime, limestone, alkaline tailings or sodium hydroxide.
The results of this test show that gold encapsulated with pyrite (FeS) can be released from the sulphide lattice by at least partial oxidation of the sulphur and iron by the thermotolerant bacteria culture MTC 1 to render the gold accessible to cyanide solution.
EXAMPLE 2
A nickel sulphide ore designated Ν 1 was treated in accordance with the present invention. The ore contained both sulphidic'nickel and .non-sulphidic nickel minerals including violarite, lizardite and niccolite (NiAs).
Approximately 70%' of the nickel was present as sulphidic nickel. Other minerals were siderite, goethite, pyrite, chlorite and quartz.
The ore had the following assay.
( ' Table 3
Assay of Nickel Ore Ν 1
Element Symbol Assay (by weight)
Nickel Ni 2.74%
Iron Ee 18.7%
Samples of the ore were mixed with a sulphuric acid solution at a pulp density cf 13% w/w to provide a pH range of 1.2 tc
1.5. Nutrients included in the acid solution were ammonium sulphate at 200 mg/L, di-potassium hydrogen phosphate at 200 mg/L and magnesium sulphate heptahydrate at 400 mg/L.
' ·*·
Γ)
(.
- 9 either rise and then fall or fall from the outset. In most tests, the variation can be significant with the final pH often less than 1.0.
The slurry was inoculated with the thermotolerant bacteria 5 culture designated MTC 1. The inoculated slurry was shaken ir.
conical flasks at a temperature of 47°c. Samples were removec periodically and analysed for iron and nickel extraction to determine the progress of the treatment.
At the completion of the bacterial oxidation treatment, 17 10 days, the solution was removed from the residual solids and the residual solids washed with sulphuric acid solution to remove any residual nickel. The nickel recovery was 93% after the residual nickel was washed out of the solids residue.
The nickel could be recovered from the solution by raising the pH to a value of about 8.5, by the addition of lime or sodium hydroxide.
For comparison,' the ore was also treated with iron (III) sulphate solution at pH 1.0 and 50°C for 24 hours to extract *
nickel. Only 16% of the nickel was recovered in this process.
These results are summarized in Table 4.
Table 4
Nickel Recovery from Ore Ν 1
| Treatment | Nickel in | Nickel |
| Method | Residue | Extraction |
5 (by weight) (by weight)
| Iron (III) | 2.0 3 % | 16% |
| Leaching | ||
| Bacterial | 0.60% | 78% |
Oxidation
BAD original
AP ο Ο Ο 3 7 9
- 10 Bacterial 0.19% 93%
Oxidation
S. Washing
The results of this rest showed -hat case metals in ore as sulphide minerals can be recovered 'ey the action of the thermotolerant bacteria culture MTC 1. The sulphidio minerals were oxidised to release the nickel into the acidic solution for conventional recovery.
EXAMPLE 3
A cold bearing arsenopyrite - pyrite concentrate was treated according to the present invention. This concentrate was designated AP 1. The major sulphide minerals were pyrite, 30% by weight and arsenopyrite, 35% by weight. Other minerals present were calcite, quartz and chlorite. The gold was present almost completely in the arsenopyrite.
The concentrate had the following assay.
Table 5
Assay of Arsenopyrite Concentrate AP 1
Element
Assay (by weight
Symbol
L 0
| Gold | Au | 30 ppm |
| Arsenic | . As * | 16.7% |
| Iron | Fe | 23.1% |
| Sulphur | «», | 30.0% |
| Nickel | Ni | 1. 5 % |
Samples of the concentrate were mixed with a sulphuric acid solution at a pulp density of 3% w/w to provide a pH range of 1.0 to 1.3. Nutrients included in the acid solution were ammonium sulphate at 200 mg/L, di-potassium hydrogen
BAD ORIGINAL ft (
( (
2Q (
2Q phosphate at 400 mg/L and magnesium sulphate heptahydrate at 400 mg/L.
The acid level (pH) may vary from the start value and may either rise and then fall or fall from the outset. In most tests, the variation can he significant with the final pH often less than 1.0.
The slurry was inoculated with the thermotolerant bacteria culture designated MTC 1. The inoculate slurry was shaken tn conical flasks at a temperature of 40°C. Samples were removed periodically and analysed for iron and arsenic extraction to determine the progress of the treatment.
The sample was treated by bacterial oxidation for 12 days tc achieve 90% break down of the arsenopyrite mineral. The solids weight loss due to the oxidation process was 30%.
The residual solids were then separated from the acid solution. Leaching of the separated solid residue using alkaline cyanide solution recovered 95% of the gold. In comparison, cyanide leaching could recover only 21% of the gold from the concentrate in the untreated state. These results-are summarised in Table’ 6.
Table 6
Gold Recovery from Untreated and Oxidised Concentrate
Sample
Arsenic
Gold Recovered
Untreated
Extracted by Cyanide ( by weight)
Leaching (by weight)
0%
3acterial Oxidation 90%
The cyanide solution employed to recover the gold contained
AP Ο Ο Ο 3 7 9
- 12 sodium cyanide at a concentration of 2 g/L.
The arsenic and iron in the solution frcm the bacterial oxidation process can be removed by adjusting the pH to above 5.0 by the addition of lime, limestone, alkaline tailings or sodium hydroxide.
The results of this test shew that gold encapsulated with arsenopyrite (FeAsS) can be released from the sulphide lattice by at least partial oxidation of the arsenic, sulphur and iron by the thermotolerant bacteria culture MTC
1 to render the gold accessible to cyanide solution.
EXAMPLE 4
A gold bearing arsenopyrite - pyrite concentrate was created according to the present invention. This concentrate was designated AP 2. The major sulphide minerals were pyrite, 90¾ by weight and arsenopyrite 9% by weight. Other minerals present were calcite, quartz and chlorite. The gold was distributed in both the arsenopyrite and the pyrite.
The concentrate had the following assay.
Table 7
Assay of Arsenopyrite - Pyrite Concentrate AP 2
| Element | Symbol | Assay (by weight) |
| Gold | Au | 5 4 ppm |
| Arsenic | As | 4.2% |
| Iron | Fe | 2 5.7% |
| Sulphur | S | 40.0% |
| Samples of the | concentrate were mixed | with a sulphuric acid |
| solution at a | pulp density of 10% w/w | to provide a pH range |
| of 1.0 to 1.3. | Nutrients included in | the acid solution |
BAD ORIGINAL mA . Λ^Γ·
- 13 were ammonium sulphate at 200 mg/L, di-potassium hydrogen phosphate at 400 mg/L and magnesium sulphate heptahydrate at 400 mg/L.
The acid level (pH) may vary from the start value and may either rise and then fall or fall from the outset. In most tests, the variation can be significant with the final pH often less than 1.0.
The slurry was inoculated with the thermotolerant bacteria culture designated MTC 1. The inoculated slurry was shaken .in conical flasks at a temperature of 53°C. Samples were removed periodically and analysed for iron and arsenic extraction to determine the progress of the treatment.
The sample was treated by bacterial oxidation for 12 days to achieve 90% oxidation of the arsenopyrite mineral and an additional 21 days for 70% pyrite oxidation as well as arsenopyrite oxidation. The weight loss due to the oxidation process was 25% for the arsenopyrite and 78% for the 100% arsenopyrite plus 70% pyrite. The solids residue was then separated from the acid solution.
Leaching of the solid residue using alkaline cyanide solution recovered 79% of gold for the oxidation of 90% arsenopyrite and 87% for complete oxidation of the arsenopyrite and 70% of the pyrite. In comparison, cyanide *
leaching could recover only 53% of the gold from the concentrate in the untreated state. These results are summarised in Table 8.
Table 3
Gold Recovery from Untreated and Oxidised Concentrate
Sample Arsenic Iron % Gold
BAD OR/G/WAL
AP Ο Ο Ο 3 7 9
- 14 Recovered
Extracted weight) (hy weight)
Untreated 0%
53%
Bacterial Oxidation 90%
79%
Bacterial Oxidation 100%
Extracted (by (by weight)
0%
25%
70%
37%
The cyanide solution employed to recover the gold contained sodium cyanide at a concentration of 2 g/L.
The arsenic and iron in the solution from the bacterial oxidation process can be removed by adjusting the pH to '15 above 5.0 by the addition of lime, limestone, alkaline tailings or sodium hydroxide.
The results of this test show that gold encapsulated with arsenopyrite (FeAsS) and in pyrite (FeS2) can be released from the sulphide lattice by at least partial oxidation of the arsenic, sulphur and iron by the thermotolerant bacteria culture MTC 1 to render the gold accessible to cyanide solution. This example also shows that the MTC 1 culture is able to operate according to the invention at
53°C.
The thermotolerant bacteria culture MTC 1 was isolated from a coal mine in Western Australia. Sludge and water samples
BAD ORIGINAL A
V
Basal Salts (NH4)2SO4 k2hpo4
MgSO47H20
FeSO4
H,S04 to reduce pH to 1.2
- 15 from the mine which contained acidophilic, thermotolerant bacteria were taken and used to inoculate volumes of a modified 9K medium containing yeast extract. The modified 9K medium had the following composition:Concentration
0.2 g/L 0.2 g/L 0.4 g/L to 9.000 mg/L iron
The samples were incubated at 30°C in a mineral salts solution containing 400mg/L (NH4)2SO4, 200 mg/L MgSO4 7H2O, lOOmg/L K2HPO4, lOOmg/L KC1, and pyrite 1.0 g/L at a pH of 2.0. Growth was observed after 7 days. These samples were then sub cultured in modified 9K medium without yeast extract.
Modifications and variations such as would be apparent to a skilled addressee are deemed within the scope of the present invention.
Claims (9)
1. A process for recovering metals from particulate refractory precious or base metal containing sulphide material characterised in that it comprises contacting the sulphide material with an aqueous solution at a temperature in the range from 25 to 55°C, the
5 aqueous solution containing a thermotolerant bacteria culture having an optimum growth temperature of 40 to 45 °C and capable of promoting oxidation of the sulphide material at a temperature in the range from 25 to 55°C, separating the oxidised residue from the aqueous liquid and treating the oxidised residue and/or the aqueous liquid to recover metal therefrom.
/10
2. A process according to claim 1, characterised in that the aqueous solution is acidic.
3. A process according to claim 2, characterised in that the aqueous solution has a pH in the range from 0.5 to 2.5.
4. A process according to any one of claims 1 to 3, characterised in that the thermotolerant bacteria is acidophilic.
15
5. A process according to any one of the preceding claims, characterised in that the thermotolerant bacteria is aerobic.
6. A process according to claim 5, characterised in that the aqueous liquid is aerated during the operation of the process.
7. A process according to any one of the preceding claims, characterised in that the
20 thermotolerant bacteria is capable of autotrophic growth.
/
8. A process according to any one of the preceding claims, characterised in that no CO, is supplied to the thermotolerant bacteria during the operation of the process other than that available from ambient air.
9. A process according to any one of the preceding claims, characterised in that the 25 aqueous liquid contains sodium chloride in an amount up to 20 grams per litre.
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| AUPK520491 | 1991-03-22 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| AP9200367A0 AP9200367A0 (en) | 1992-04-30 |
| AP379A true AP379A (en) | 1995-03-09 |
Family
ID=3775287
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| APAP/P/1992/000367A AP379A (en) | 1991-03-22 | 1992-03-20 | Bacterial oxidation of metal containing materials. |
Country Status (7)
| Country | Link |
|---|---|
| US (1) | US5429659A (en) |
| AP (1) | AP379A (en) |
| BG (1) | BG61110B1 (en) |
| CA (1) | CA2132440C (en) |
| WO (1) | WO1992016667A1 (en) |
| ZA (1) | ZA922051B (en) |
| ZW (1) | ZW4692A1 (en) |
Families Citing this family (25)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| SE468286B (en) * | 1991-06-19 | 1992-12-07 | Boliden Mineral Ab | PROCEDURES FOR THE TREATMENT OF COMPLEX METAL SULPHIDE MATERIAL |
| US6383458B1 (en) | 1991-07-10 | 2002-05-07 | Newmont Mining Corporation | Biooxidation process for recovery of metal values from sulfur-containing ore materials |
| AU694816B2 (en) * | 1994-10-25 | 1998-07-30 | Geobiotics, Inc. | Method for heap biooxidation of ore |
| CN1053475C (en) * | 1995-06-07 | 2000-06-14 | 陕西省地质矿产局第三地质队 | Bacterial amplification culture device used in microorganism preoxidation heap leaching gold technology |
| US5626648A (en) * | 1995-07-17 | 1997-05-06 | Bhp Minerals International Inc. | Recovery of nickel from bioleach solution |
| RU2180360C2 (en) * | 1997-03-03 | 2002-03-10 | Минтек | Method of chalcopyrite leaching |
| US5873927A (en) * | 1997-05-16 | 1999-02-23 | Echo Bay Mines, Limited | Integrated, tank/heap biooxidation process |
| US5948375A (en) * | 1997-06-10 | 1999-09-07 | Billiton Sa Limited | Biological oxidation of sulphide minerals to recover gold, silver, platinum group metals and base metals |
| US6103204A (en) * | 1997-12-11 | 2000-08-15 | Cominco Ltd. | Selective bioleaching of zinc |
| AUPP444298A0 (en) * | 1998-07-01 | 1998-07-23 | Bactech (Australia) Pty Limited | Leaching of low sulphur ores |
| PE20010393A1 (en) * | 1999-06-22 | 2001-04-04 | Paques Bio Syst Bv | PROCESS TO REMOVE ARSENIC WASTE |
| US7189527B2 (en) * | 1999-09-03 | 2007-03-13 | Bioheap Limited | Bacterial oxidation of sulphide ores and concentrates |
| AUPQ265199A0 (en) * | 1999-09-03 | 1999-09-30 | Pacific Ore Technology Limited | Improved bacterial oxidation of sulphide ores and concentrates |
| AU775042B2 (en) * | 1999-09-07 | 2004-07-15 | Billiton Intellectual Property B.V. | Bioleaching of sulphide minerals |
| US6451275B1 (en) * | 2000-03-10 | 2002-09-17 | Lakefield Research Limited | Methods for reducing cyanide consumption in precious metal recovery by reducing the content of intermediate sulfur oxidation products therein |
| PE20020912A1 (en) * | 2000-11-25 | 2002-10-19 | Billiton Sa Ltd | BIOPRODUCT PRODUCTION |
| GB0111699D0 (en) * | 2001-05-12 | 2001-07-04 | Gunn Robert I | Bioremediation process |
| CA2353002C (en) | 2001-07-13 | 2009-12-01 | Teck Cominco Metals Ltd. | Heap bioleaching process for the extraction of zinc |
| US7455715B2 (en) * | 2001-07-13 | 2008-11-25 | Teck Cominco Metals Ltd. | Heap bioleaching process for the extraction of zinc |
| AUPR655401A0 (en) * | 2001-07-23 | 2001-08-16 | Pacific Ore Technology (Australia) Ltd | Adaptation of bacteria for use in leaching |
| AUPR855201A0 (en) * | 2001-10-29 | 2001-11-29 | Technological Resources Pty Limited | Recovery of copper from chalcopyrite |
| PE20060789A1 (en) | 2004-10-22 | 2006-08-10 | Biosigma Sa | WENELEN BACTERIA STRAIN DSM 16786 AND LEACHING PROCESS BASED ON INOCULATION OF SAID STRAIN |
| WO2008015108A1 (en) * | 2006-08-02 | 2008-02-07 | H.C. Starck Gmbh | Recovery of molybdenum from molybdenum bearing sulfide materials by bioleaching in the presence of iron |
| PE20140641A1 (en) | 2011-04-13 | 2014-06-22 | Bioheap Ltd | LEACHING PROCEDURE |
| CN113122715B (en) * | 2021-04-12 | 2022-04-08 | 东北大学 | A method for accelerating bioleaching of sulfide ore by utilizing rice husk decomposition |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4729788A (en) * | 1987-01-23 | 1988-03-08 | Advanced Mineral Technologies, Inc. | Thermophilic microbial treatment of precious metal ores |
| US4740243A (en) * | 1984-12-31 | 1988-04-26 | Ensci, Inc. | Metal value recovery from metal sulfide containing ores |
| US4822413A (en) * | 1986-03-13 | 1989-04-18 | Davy Mckee (Stockton) Limited | Extraction of metal values from ores or concentrates |
Family Cites Families (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| PT69331A (en) * | 1978-03-23 | 1979-04-01 | Interox Chemicals Ltd | Leaching of minerals |
| US4752332A (en) * | 1984-12-31 | 1988-06-21 | Ensci, Inc. | Treating manganese-containing ores with a metal sulfide |
| US4987081A (en) * | 1987-07-10 | 1991-01-22 | Gb Biotech Inc. | Chemical/biological process to oxidize multimetallic sulphide ores |
| US5030426A (en) * | 1989-06-27 | 1991-07-09 | Technical Research, Inc. | Biomining of gallium and germanium containing ores |
| AU618177B2 (en) * | 1990-03-27 | 1991-12-12 | Biomin Technologies Sa | Biological oxidation of sulfide ore |
| US5244493A (en) * | 1990-09-21 | 1993-09-14 | Newmont Gold Co. | Biometallurgical treatment of precious metal ores having refractory carbon content |
| US5246486A (en) * | 1991-07-10 | 1993-09-21 | Newmont Gold Co. | Biooxidation process for recovery of gold from heaps of low-grade sulfidic and carbonaceous sulfidic ore materials |
| US5236677A (en) * | 1992-03-13 | 1993-08-17 | Grupo Cydsa S.A. De C.V. | Biological process for the elimination of sulphur compounds present in gas mixtures |
-
1992
- 1992-03-20 ZA ZA922051A patent/ZA922051B/en unknown
- 1992-03-20 WO PCT/AU1992/000117 patent/WO1992016667A1/en not_active Ceased
- 1992-03-20 AP APAP/P/1992/000367A patent/AP379A/en active
- 1992-03-20 CA CA002132440A patent/CA2132440C/en not_active Expired - Lifetime
- 1992-03-20 US US08/119,079 patent/US5429659A/en not_active Expired - Fee Related
- 1992-03-23 ZW ZW46/92A patent/ZW4692A1/en unknown
-
1993
- 1993-09-20 BG BG98117A patent/BG61110B1/en unknown
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4740243A (en) * | 1984-12-31 | 1988-04-26 | Ensci, Inc. | Metal value recovery from metal sulfide containing ores |
| US4822413A (en) * | 1986-03-13 | 1989-04-18 | Davy Mckee (Stockton) Limited | Extraction of metal values from ores or concentrates |
| US4729788A (en) * | 1987-01-23 | 1988-03-08 | Advanced Mineral Technologies, Inc. | Thermophilic microbial treatment of precious metal ores |
Also Published As
| Publication number | Publication date |
|---|---|
| ZA922051B (en) | 1993-09-20 |
| BG98117A (en) | 1994-07-29 |
| CA2132440A1 (en) | 1992-10-01 |
| CA2132440C (en) | 2003-09-23 |
| US5429659A (en) | 1995-07-04 |
| BG61110B1 (en) | 1996-11-29 |
| AP9200367A0 (en) | 1992-04-30 |
| WO1992016667A1 (en) | 1992-10-01 |
| ZW4692A1 (en) | 1992-07-08 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| AP379A (en) | Bacterial oxidation of metal containing materials. | |
| US4729788A (en) | Thermophilic microbial treatment of precious metal ores | |
| US4497778A (en) | Microbial leaching of sulphide-containing ores | |
| US5779762A (en) | Method for improving the heap biooxidation rate of refractory sulfide ore particles that are biooxidized using recycled bioleachate solution | |
| EP2066819B1 (en) | Recovery of molybdenum from molybdenum bearing sulfide materials by bioleaching in the presence of iron | |
| US4752332A (en) | Treating manganese-containing ores with a metal sulfide | |
| Ewart et al. | The extraction of metals from ores using bacteria | |
| WO2000017407A1 (en) | Method for treating precious metal bearing minerals | |
| Groudev et al. | Two-stage microbial leaching of a refractory gold-bearing pyrite ore | |
| Bruynesteyn | Mineral biotechnology | |
| US6383458B1 (en) | Biooxidation process for recovery of metal values from sulfur-containing ore materials | |
| US6696283B1 (en) | Particulate of sulfur-containing ore materials and heap made therefrom | |
| EP0129564A4 (en) | Bacterial beneficiation of minerals. | |
| WO2000037690A1 (en) | Silver-catalyzed bio-leaching process for copper extraction from chalcopyrite heap | |
| ZA200609686B (en) | Processing of acid-consuming mineral materials involving treatment with acidic biooxidation effluent | |
| Romano et al. | Reactivity of a molybdenite concentrate against chemical or bacterial attack | |
| Natarajan | Biotechnology in gold processing | |
| AU652231B2 (en) | Oxidation of metal sulfides using thermotolerant bacteria | |
| Natarajan | Bioprocessing for enhanced gold recovery | |
| AU736975B2 (en) | Oxidation of metal sulfides using thermotolerant bacteria | |
| US6379919B1 (en) | Method for isolating thiocyanate resistant bacteria | |
| Spasova et al. | Leaching of gold from a polymetallic sulphide ore | |
| AU592161B2 (en) | Extraction of metal values from ores or concentrates | |
| Harvey et al. | Thermophilic bioheap leaching of chalcopyrite concentrates | |
| Yannopoulos | Treatment of refractory gold ores |