CN116694521A - Thiobacillus ferrooxidans derived from volcanic ash and application thereof - Google Patents
Thiobacillus ferrooxidans derived from volcanic ash and application thereof Download PDFInfo
- Publication number
- CN116694521A CN116694521A CN202310667854.4A CN202310667854A CN116694521A CN 116694521 A CN116694521 A CN 116694521A CN 202310667854 A CN202310667854 A CN 202310667854A CN 116694521 A CN116694521 A CN 116694521A
- Authority
- CN
- China
- Prior art keywords
- leaching
- bioreactor
- thiobacillus ferrooxidans
- magnetic field
- circuit board
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 241000605222 Acidithiobacillus ferrooxidans Species 0.000 title claims abstract description 69
- 238000002386 leaching Methods 0.000 claims abstract description 122
- 238000005516 engineering process Methods 0.000 claims abstract description 39
- 238000005728 strengthening Methods 0.000 claims abstract description 34
- 229910052751 metal Inorganic materials 0.000 claims abstract description 29
- 239000002184 metal Substances 0.000 claims abstract description 29
- 238000004321 preservation Methods 0.000 claims abstract description 5
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 52
- 239000000126 substance Substances 0.000 claims description 50
- 238000000034 method Methods 0.000 claims description 44
- 239000007788 liquid Substances 0.000 claims description 42
- 230000005684 electric field Effects 0.000 claims description 38
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 32
- 229910052802 copper Inorganic materials 0.000 claims description 32
- 239000010949 copper Substances 0.000 claims description 32
- 238000009423 ventilation Methods 0.000 claims description 29
- 229910052759 nickel Inorganic materials 0.000 claims description 26
- 239000002068 microbial inoculum Substances 0.000 claims description 25
- 238000010438 heat treatment Methods 0.000 claims description 20
- 230000003647 oxidation Effects 0.000 claims description 18
- 238000007254 oxidation reaction Methods 0.000 claims description 18
- 239000001963 growth medium Substances 0.000 claims description 17
- 230000001580 bacterial effect Effects 0.000 claims description 14
- 239000002245 particle Substances 0.000 claims description 14
- 239000002054 inoculum Substances 0.000 claims description 6
- 150000002739 metals Chemical class 0.000 claims description 6
- 239000003795 chemical substances by application Substances 0.000 claims description 5
- 238000000855 fermentation Methods 0.000 claims description 4
- 230000004151 fermentation Effects 0.000 claims description 4
- 238000011049 filling Methods 0.000 claims description 4
- 238000005273 aeration Methods 0.000 claims description 2
- 230000000813 microbial effect Effects 0.000 claims 1
- 244000005700 microbiome Species 0.000 abstract description 5
- 230000008878 coupling Effects 0.000 abstract description 3
- 238000010168 coupling process Methods 0.000 abstract description 3
- 238000005859 coupling reaction Methods 0.000 abstract description 3
- 238000003487 electrochemical reaction Methods 0.000 abstract 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 33
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 22
- 230000009286 beneficial effect Effects 0.000 description 16
- 210000001822 immobilized cell Anatomy 0.000 description 14
- 230000000052 comparative effect Effects 0.000 description 8
- 238000001514 detection method Methods 0.000 description 8
- 238000009630 liquid culture Methods 0.000 description 7
- 239000002609 medium Substances 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- 239000011435 rock Substances 0.000 description 5
- 238000004904 shortening Methods 0.000 description 5
- 239000004575 stone Substances 0.000 description 5
- 229920001817 Agar Polymers 0.000 description 4
- 239000008272 agar Substances 0.000 description 4
- 230000001276 controlling effect Effects 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 238000011081 inoculation Methods 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 239000001569 carbon dioxide Substances 0.000 description 3
- 238000012258 culturing Methods 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 2
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 2
- 238000000498 ball milling Methods 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 239000012153 distilled water Substances 0.000 description 2
- 238000009472 formulation Methods 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 229910000510 noble metal Inorganic materials 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 230000001105 regulatory effect Effects 0.000 description 2
- 239000004065 semiconductor Substances 0.000 description 2
- 238000012163 sequencing technique Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 108020004465 16S ribosomal RNA Proteins 0.000 description 1
- 229910001369 Brass Inorganic materials 0.000 description 1
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 1
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 description 1
- 101000993059 Homo sapiens Hereditary hemochromatosis protein Proteins 0.000 description 1
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 description 1
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 241000605118 Thiobacillus Species 0.000 description 1
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 239000010951 brass Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 239000010793 electronic waste Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 229910052935 jarosite Inorganic materials 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 239000011572 manganese Substances 0.000 description 1
- NUJOXMJBOLGQSY-UHFFFAOYSA-N manganese dioxide Inorganic materials O=[Mn]=O NUJOXMJBOLGQSY-UHFFFAOYSA-N 0.000 description 1
- 229940099596 manganese sulfate Drugs 0.000 description 1
- 239000011702 manganese sulphate Substances 0.000 description 1
- 235000007079 manganese sulphate Nutrition 0.000 description 1
- SQQMAOCOWKFBNP-UHFFFAOYSA-L manganese(II) sulfate Chemical compound [Mn+2].[O-]S([O-])(=O)=O SQQMAOCOWKFBNP-UHFFFAOYSA-L 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- 230000001699 photocatalysis Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 229910052709 silver Inorganic materials 0.000 description 1
- 239000004332 silver Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 229910052718 tin Inorganic materials 0.000 description 1
- 239000011135 tin Substances 0.000 description 1
- 229910052875 vesuvianite Inorganic materials 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
- C12N1/205—Bacterial isolates
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/20—Bacteria; Culture media therefor
-
- 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
- C22B15/00—Obtaining copper
- C22B15/0063—Hydrometallurgy
- C22B15/0065—Leaching or slurrying
-
- 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
- C22B23/00—Obtaining nickel or cobalt
- C22B23/04—Obtaining nickel or cobalt by wet processes
- C22B23/0407—Leaching processes
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12R—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES C12C - C12Q, RELATING TO MICROORGANISMS
- C12R2001/00—Microorganisms ; Processes using microorganisms
- C12R2001/01—Bacteria or Actinomycetales ; using bacteria or Actinomycetales
-
- 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
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Biotechnology (AREA)
- Genetics & Genomics (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Metallurgy (AREA)
- Biochemistry (AREA)
- Mechanical Engineering (AREA)
- Microbiology (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Tropical Medicine & Parasitology (AREA)
- Medicinal Chemistry (AREA)
- Virology (AREA)
- Biomedical Technology (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Geology (AREA)
- Geochemistry & Mineralogy (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Apparatus Associated With Microorganisms And Enzymes (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention relates to a thiobacillus ferrooxidans derived from volcanic ash and application thereof. The preservation number of the thiobacillus ferrooxidans is CCTCC NO: M20211183. The invention combines the thiobacillus ferrooxidans with the magnetic field strengthening immobilization technology, the electrochemical reaction promotion technology and the microorganism rapid propagation technology, perfectly integrates the thiobacillus ferrooxidans with the magneto-electric coupling leaching technology, and greatly improves the biological leaching efficiency. The invention can improve and accelerate the metal leaching rate, shorten the leaching period, and has the advantages of easy operation, low cost, green and no secondary pollution, etc.
Description
The invention is a divisional application, and the original Chinese invention patent application number is: 202111549020.0, filing date: 2021, 12 months and 17 days, patent name at the time of application is: a method for extracting metal from Thiobacillus ferrooxidans from volcanic ash.
Technical Field
The invention belongs to the technical field of bioleaching, and particularly relates to a strain of thiobacillus ferrooxidans derived from volcanic ash and application thereof, in particular to a strain of thiobacillus ferrooxidans derived from volcanic ash and magnetoelectric coupling for strengthening copper and nickel in a leached circuit board.
Background
The biological leaching method for recycling the noble metal in the electronic waste has the advantages of low cost, low energy consumption, no secondary pollution and the like, so that the method becomes one of the most promising technologies. The circuit board contains a large amount of noble metals such as copper, iron, nickel, tin, zinc, gold, silver, palladium, and the like. Taking copper as an example, the copper content of brass ore with the most abundant reserves is even lower than the copper content of each gram of communication circuit board, however, the components are complex, the crystal structure is compact, the requirements on the extraction process are severe, and the conventional high-temperature smelting method for refining copper ores has quite high cost, so that the economic value of the copper ores is difficult to realize. The bioleaching method for recovering metal becomes the optimal scheme for metal recovery. However, the problems of long leaching period, low efficiency and the like exist in the bioleaching process, and if the problem of short plates of bioleaching can be solved, great contribution is provided for wide application of bioleaching. Wang Jun et al (patent number CN 201910369442.6) propose a method for enhancing the biological leaching of a photocatalytic semiconductor sulphide mineral with jarosite, which is biosynthesized, makes the leaching process more cumbersome and increases the cost, and requires strong light conditions to enable acidophilic iron sulphide-oxidizing bacteria to leach the semiconductor sulphide mineral, as to whether other articles can leach the metal effect is unknown; chen Mengjun (patent number CN 201910906294.7) proposes a method for leaching manganese sulfate by combining a ball mill and an electric field to strengthen pyrolusite, wherein the method damages a crystal form in a ball milling and electric field application mode, so that metal manganese is more easy to leach, and the method improves leaching rate, but has complex process, needs to purchase special equipment such as ball milling and the like, has complicated pretreatment links and is difficult to popularize and apply practically.
Disclosure of Invention
In view of the problems existing in the prior art, the invention provides a strain of ferrous thiobacillus ferrooxidans derived from volcanic ash and application thereof, and the strain can be used for magnetically and electrically coupling and strengthening copper and nickel in a leaching circuit board. Based on the bioleaching method, the technology of combining magnetic field strengthening immobilization technology, microorganism rapid propagation technology, electrochemical technology, bioleaching technology and the like is used for recovering metals such as copper and the like from a circuit board, the technology can greatly improve bioleaching efficiency, shortens leaching period, is environment-friendly, and can recycle leaching liquid without waste liquid.
The technical scheme for solving the technical problems is as follows:
the invention provides a strain of thiobacillus ferrooxidans derived from volcanic ash, the preservation number of the strain is CCTCC NO: M20211183, the strain can be named acidophilic thiobacillus ferrooxidans MA-Y1 (Acidithiobacillus ferrooxidans MA-Y1), and the strain is preserved in China center for type culture collection (China center for type culture collection) at the year 09 of 2021, address: chinese university of Wuhan and Wuhan.
The strain is obtained by accidental separation of the volcanic ash of the saddle mountain in great Khingan of Heilongjiang province, enrichment and separation are carried out through a 9K culture medium, sequencing is carried out, and after NCBI comparison, the strain is determined to be acidophilic thiobacillus ferrooxidans and named as MA-Y1. Optimizing the culture conditions to obtain the optimal growth conditions: the growth temperature is 30-40 ℃, the pH value is 1.5-2.5, the concentration of Fe (II) is 20-40g/L, and the thiobacillus ferrooxidans MA-Y1 is sent to the China center for type culture collection of Wuhan, and the strain collection number is CCTCCNO: M20211183.
The beneficial effects of the technical scheme are that: the strain can be used for recovering metals such as copper and nickel from a circuit board, greatly improving the biological leaching efficiency, shortening the leaching period, simultaneously avoiding complex equipment, being environment-friendly, recycling the leaching solution and generating no waste liquid.
The invention provides a fermentation method of the thiobacillus ferrooxidans, which comprises the steps of inoculating the thiobacillus ferrooxidans into a culture medium and fermenting and culturing.
The culture conditions for fermentation include: the inoculation amount is 10% (v/v), the temperature is 30-40 ℃, the pH is 1.5-2.5, the aeration amount is controlled to be 0.5-0.8L/min, and the concentration of Fe (II) is 20-40g/L.
The beneficial effects of adopting the technical scheme include: the adoption of the conditions is beneficial to the fermentation culture of the thiobacillus ferrooxidans.
The invention provides a microbial inoculum comprising the thiobacillus ferrooxidans. The bacterial agent can also comprise other components besides the thiobacillus ferrooxidans.
The beneficial effects of adopting the technical scheme include: the microbial inoculum can be used for recovering metals such as copper, nickel and the like from the circuit board, so that the biological leaching efficiency can be greatly improved, and the leaching period can be shortened.
The invention provides application of the thiobacillus ferrooxidans or the microbial inoculum in metal leaching. The leached metal may be leached copper and/or nickel.
The invention provides application of the thiobacillus ferrooxidans or the microbial inoculum in improving the oxidation rate of Fe (II).
The beneficial effects of adopting the technical scheme include: the thiobacillus ferrooxidans or the microbial inoculum can be used for leaching copper and nickel in a circuit board, and has the advantages of high Fe (II) oxidation rate, high biological leaching efficiency, short leaching period and the like.
Further, the thiobacillus ferrooxidans or the microbial inoculum is utilized, and then the technology of magnetic field strengthening and fixing technology and the technology of electric field strengthening and leaching technology are combined.
The beneficial effects of adopting the technical scheme include: the combination of the thiobacillus ferrooxidans or the microbial inoculum, the magnetic field strengthening immobilization technology and the electric field strengthening leaching technology can further improve the metal leaching efficiency and shorten the leaching period. Compared with a non-magnetoelectric strengthening control group, the leaching period of the invention can be shortened by 7-10 days, and the leaching period of the same leaching mode is generally 15-20 days.
Further, the inoculation amount of the thiobacillus ferrooxidans or the microbial inoculum is 10%, the leaching temperature is 30-40 ℃, the pH is 1.5-2.5, the concentration of Fe (II) is 20-40g/L, the ventilation is controlled to be 0.5-0.8L/min, and the exchange amount is 0.2-3.6L/min; copper and nickel in the circuit board are leached out, 40-120g of the circuit board is obtained, and the grain size of the circuit board is 2-4cm.
Further, the conditions for the magnetic field strengthening fixation include: the magnetic field strength is 0-40mT, the volume of the immobilized carrier is 20-40% of the volume of the bioreactor, and the immobilization time is 5-10 days; the conditions for electric field enhanced leaching include: the current is 0-200mA.
The beneficial effects of adopting the technical scheme include: the adoption of the conditions is beneficial to further improving the metal leaching efficiency and shortening the leaching period.
Further, leaching the metal with a leaching system, the leaching system comprising: bioreactor, magnetic field generator, chemical reactor and electric field generator; the liquid in the bioreactor and the liquid in the chemical reactor are exchanged through a circulating pump; the bioreactor is internally provided with an immobilization carrier, the immobilization carrier is immobilized with the thiobacillus ferrooxidans or the microbial inoculum, the outer side of the bioreactor is provided with a magnetic field generator, and the bioreactor is provided with a heating device and a ventilation device; a circuit board is placed in the chemical reactor, two electrodes of the electric field generator are placed in the chemical reactor, and the chemical reactor is provided with a heating device.
Further, the method for leaching the metal by adopting the leaching system comprises a magnetic field enhanced immobilization process and an electric field enhanced leaching technology;
the magnetic field strengthening and fixing process comprises the following steps: (1) Filling 20-40% of non-immobilized carrier in a bioreactor, wherein the particle size of the carrier is 2-3cm; (2) Adding a culture medium, and inoculating the thiobacillus ferrooxidans or the microbial inoculum with 10% of inoculation amount; (3) Opening the ventilation device, and controlling the ventilation rate to be 0.5-0.8L/min; (4) heating by a heating device at 20-40 ℃; (5) Installing a magnetic field generator, setting the magnetic field strength to be 0-40mT and the immobilization time to be 5-10 days to obtain an immobilization carrier;
the electric field enhanced leaching technology comprises the following steps: (1) By adopting the leaching system, 40-120g of circuit board is added into a chemical reactor, the grain diameter of the circuit board is 2-4cm, an immobilized carrier is placed in the bioreactor, and the immobilized carrier is immobilized with the thiobacillus ferrooxidans or the microbial inoculum; (2) Respectively adding culture medium into the bioreactor and the chemical reactor, opening a circulating pump, a heating device and a ventilation device, wherein the circulating pump sets the liquid flow rate to be 0.2-3.6L/min, and the ventilation amount to be 0.5-0.8L/min; (3) When the Fe (II) in the bioreactor or the chemical reactor reaches 90%, the electrode of the electric field generator is placed, the direct current power supply is turned on, and the current is set to be 0-200mA.
The beneficial effects of adopting the technical scheme include: the magnetic field generator is used for strengthening the capability of the volcanic rock immobilized thiobacillus ferrooxidans. The circulation pump is used to facilitate liquid exchange between the bioreactor and the chemical reactor. The ventilation device is used for providing oxygen and carbon dioxide and promoting the rapid growth and reproduction of the thiobacillus ferrooxidans. The system and the method are beneficial to further improving the metal leaching efficiency and shortening the leaching period.
The invention provides a method for leaching metal, which comprises the following steps: leaching the metal by using the thiobacillus ferrooxidans or the microbial inoculum.
The beneficial effects of adopting the technical scheme include: the method has the advantages of high oxidation rate of Fe (II), high biological leaching efficiency, short leaching period and the like.
Further, the method comprises the following steps: the ferrous oxide thiobacillus or the microbial inoculum is used for leaching metals by combining a magnetic field strengthening and fixing technology and an electric field strengthening and leaching technology.
The beneficial effects of adopting the technical scheme include: the combination of the thiobacillus ferrooxidans or the microbial inoculum, the magnetic field strengthening immobilization technology and the electric field strengthening leaching technology can further improve the metal leaching efficiency and shorten the leaching period. Compared with a non-magnetoelectric strengthening control group, the leaching period of the invention can be shortened by 7-10 days, and the leaching period of the same leaching mode is generally 15-20 days.
Further, the inoculation amount of the thiobacillus ferrooxidans or the microbial inoculum is 10% (v/v), the leaching temperature is 30-40 ℃, the pH is 1.5-2.5, the concentration of Fe (II) is 20-40g/L, the ventilation amount is controlled to be 0.5-0.8L/min, and the exchange amount is 0.2-3.6L/min; copper and nickel in the circuit board are leached out, 40-120g of the circuit board is obtained, and the grain size of the circuit board is 2-4cm.
Further, the conditions for the magnetic field strengthening fixation include: the magnetic field strength is 0-40mT, the volume of the immobilized carrier is 20-40% of the volume of the bioreactor, and the immobilization time is 5-10 days; the conditions for electric field enhanced leaching include: the current is 0-200mA.
The beneficial effects of adopting the technical scheme include: the adoption of the conditions is beneficial to further improving the metal leaching efficiency and shortening the leaching period.
Further, leaching the metal with a leaching system, the leaching system comprising: bioreactor, magnetic field generator, chemical reactor and electric field generator; the liquid in the bioreactor and the liquid in the chemical reactor are exchanged through a circulating pump; the bioreactor is internally provided with an immobilized carrier, the immobilized carrier is immobilized with the thiobacillus ferrooxidans or the microbial inoculum, the outer side of the bioreactor is provided with a magnetic field generator, a magnetic field can be generated for the bioreactor through the magnetic field generator, and the bioreactor is provided with a heating device and a ventilation device; a circuit board is arranged in the chemical reactor, two electrodes of the electric field generator are arranged at the inner side of the chemical reactor, and the chemical reactor is provided with a heating device;
the method for leaching the metal by adopting the system comprises a magnetic field enhanced immobilization process and an electric field enhanced leaching technology;
the magnetic field strengthening and fixing process comprises the following steps: (1) Filling 20-40% of non-immobilized carrier in a bioreactor, wherein the particle size of the carrier is 2-3cm; (2) Adding a culture medium, and inoculating the thiobacillus ferrooxidans or the microbial inoculum according to 10% (v/v) inoculum size; (3) Opening the ventilation device, and controlling the ventilation rate to be 0.5-0.8L/min; (4) heating by a heating device at 20-40 ℃; (5) Installing a magnetic field generator, setting the magnetic field strength to be 0-40mT, and setting the immobilization time to be 5-10 days;
the electric field enhanced leaching technology comprises the following steps: (1) By adopting the leaching system, 40-120g of circuit board is added into a chemical reactor, the grain diameter of the circuit board is 2-4cm, an immobilized carrier is placed in the bioreactor, and the immobilized carrier is immobilized with the thiobacillus ferrooxidans or the microbial inoculum; (2) Respectively adding culture medium into the bioreactor and the chemical reactor, opening a circulating pump, a heating device and a ventilation device, wherein the circulating pump sets the liquid flow rate to be 0.2-3.6L/min, the ventilation amount to be 0.5-0.8L/min, and the temperature to be 20-40 ℃; (3) When the Fe (II) in the bioreactor or the chemical reactor reaches 90%, the electrode of the electric field generator is placed, the direct current power supply is turned on, and the current is set to be 0-200mA.
The beneficial effects of adopting the technical scheme include: the magnetic field generator is used for strengthening the capability of the volcanic rock immobilized thiobacillus ferrooxidans. The circulation pump is used to facilitate liquid exchange between the bioreactor and the chemical reactor. The ventilation device is used for providing oxygen and carbon dioxide and promoting the rapid growth and reproduction of the thiobacillus ferrooxidans. The system and the method are beneficial to further improving the metal leaching efficiency and shortening the leaching period.
Drawings
FIG. 1 is a schematic diagram of a leaching system of the present invention;
in the drawings, the numerals represent the following meanings: 1. the device comprises a bioreactor, 2, a magnetic field generator, 3, a chemical reactor, 4, an electric field generator, 5, a circulating pump, 6, an immobilization carrier, 7, a ventilation device, 8, a circuit board, 9 and a heating device.
Detailed Description
The principles and features of the present invention are described below with reference to the drawings, the examples are illustrated for the purpose of illustrating the invention and are not to be construed as limiting the scope of the invention.
The preservation number of the thiobacillus ferrooxidans derived from volcanic ash is CCTCC NO: M20211183, and the thiobacillus ferrooxidans can be named as acidophilic thiobacillus ferrooxidans MA-Y1 (Acidithiobacillus ferrooxidans MA-Y1); the preparation is deposited in China center for type culture Collection with the following addresses: the preservation date of the university of Wuhan, wuhan in China is 2021, 9 months and 15 days.
The microorganism is obtained by enrichment culture and separation from volcanic ash samples collected from Maacks mountain in great Khingan of Heilongjiang province. Preferably, the culturing conditions of the thiobacillus ferrooxidans MA-Y1 are as follows: the growth temperature is 30-40 ℃, the pH is 1.5-2.5, and the concentration of Fe (II) is 20-40g/L.
Preferably, the oxidation rate of Fe (II) is 98.47% after culturing for 100h at a growth temperature of 35 ℃ and a pH of 2.0 with a concentration of Fe (II) of 40g/L.
The adoption of the culture conditions is favorable for the quick propagation and growth of the thiobacillus ferrooxidans MA-Y1, shortens the culture time, and consumes Fe (II) to produce Fe (III).
In the specific implementation process, specific Fe can be configured according to the following proportion 2+ 9K liquid medium at a concentration such as: 0.3g (NH) 4 ) 2 SO 4 0.1g KCl,0.5g K 2 HPO 4 0.5g of MgSO 4 ·7H 2 O,0.01g of Ca (NO 3 ) 2 30g of FeSO 4 ·7H 2 O, and 1000mL of distilled water, finally with 0.5mol/L H 2 SO 4 The pH value is regulated to 1.5-2.0, and the 9K liquid culture medium is obtained. Agar (v/v 1.2%) was added to the formulation of 9K liquid medium to give 9K solid medium.
As shown in fig. 1, the present invention provides a leaching system comprising a biochemical two-stage reactor, which may specifically include: a bioreactor 1, a magnetic field generator 2, a chemical reactor 3 and an electric field generator 4; the liquid in the bioreactor 1 and the liquid in the chemical reactor 3 are exchanged by a circulating pump 5; the bioreactor 1 is internally provided with an immobilization carrier 6, the immobilization carrier 6 immobilizes the thiobacillus ferrooxidans or the bacterial agent, the outer side of the bioreactor 1 is provided with a magnetic field generator 2, the magnetic field generator 2 can generate a magnetic field for the bioreactor 1, and the bioreactor 1 is provided with a heating device 9 and a ventilation device 7; an object to be leached (for example, a circuit board 8) is placed in the chemical reactor 3, two electrodes of the electric field generator 4 are placed on the inner side of the chemical reactor 3, the electrode distance is 2-5cm, and the chemical reactor 3 is provided with a heating device 9; the heating device 9 can heat the bioreactor 1 and the chemical reactor 3, ensuring the required temperature conditions.
Specifically, the heating device 9 may be a thermostat water bath, and water in the thermostat water bath is pumped to the outer sides of the bioreactor 1 and the chemical reactor 3 through a three-phase brushless water pump, so as to keep the temperature in the bioreactor 1 and the chemical reactor 3 constant, and finally return the water to the thermostat water bath, thereby forming a closed water circulation path.
The immobilization carrier 6 is a vesuvianite immobilized with the thiobacillus ferrooxidans or the microbial inoculum. The magnetic field generator 2 is used for strengthening the capability of the volcanic rock immobilized thiobacillus ferrooxidans.
The circulation pump 5 is used to facilitate the exchange of liquids within the bioreactor 1 and the chemical reactor 3.
The ventilation device can be a ventilation pump which is connected to one side of the bioreactor 1 and used for providing oxygen and carbon dioxide to promote the rapid growth and reproduction of the thiobacillus ferrooxidans, and the ventilation pump is connected with the bioreactor 1 through a rubber tube.
The method for leaching the metal by adopting the system comprises a magnetic field enhanced immobilization process technology and an electric field enhanced leaching technology.
The magnetic field strengthening and fixing process comprises the following steps: (1) Filling 20-40% (v/v) volcanic stone (particle size 2-3 cm) column layer into bioreactor 1. (2) 800mL of 9K liquid medium was added and inoculated with Thiobacillus ferrooxidans MA-Y1 at an inoculum size of 10% (v/v). (3) Opening the air pump, and controlling the ventilation rate at 0.5-0.8L/min. (4) The constant-temperature water bath kettle and the three-phase brushless water pump are turned on, and the temperature of the constant-temperature water bath kettle is set to be 30 ℃. (5) The magnetic field generator 2 is installed and the magnetic field strength is set to be 0-40mT.
The electric field enhanced leaching technology comprises the following steps: (1) After immobilization is completed, the leaching system is adopted to leach, the bioreactor 1 and the chemical reactor 3 are connected through a circulating pump 5, 40-120g of circuit board 8 is added into the chemical reactor 3, and volcanic stones of immobilized thiobacillus ferrooxidans MA-Y1 are placed in the bioreactor 1. (2) The bioreactor 1 and the chemical reactor 3 are respectively added with 9K liquid culture medium, a circulating pump 5, a three-phase brushless water pump, a constant-temperature water bath kettle and a ventilation pump are started to operate, the circulating pump 5 sets the liquid flow rate to be 1.2-3.6L/min, and the ventilation rate is 0.5-0.8L/min. (3) When the Fe (II) in the bioreactor 1 and the chemical reactor 3 reaches 90%, the electrodes of the electric field generator 4 are placed, a direct current power supply is turned on, and the current is set to be 0-200mA.
The present invention will be described in further detail with reference to examples, but embodiments of the present invention are not limited thereto.
The experimental methods used in each example and each comparative example were conventional methods unless otherwise specified. The materials, reagents and apparatus used, unless otherwise specified, are conventional in the art and can be prepared or commercially available by conventional methods by those skilled in the art.
In each example and each comparative example, the formulation of the 9K liquid medium used included: 0.3g (NH) 4 ) 2 SO 4 0.1g KCl,0.5g K 2 HPO 4 0.5g of MgSO 4 ·7H 2 O,0.01g of Ca (NO 3 ) 2 30g of FeSO 4 ·7H 2 O, and 1000mL of distilled water, finally with 0.5mol/L H 2 SO 4 The pH value is regulated to 1.5-2.0, and the 9K liquid culture medium is obtained.
Example 1
In 2018, the method comprises the steps of collecting the saddle mountain volcanic ash of great Khingan in Heilongjiang province, enriching by using a 9K liquid culture medium to obtain microorganism enrichment, separating and purifying the strain by combining a 9K solid culture medium (agar is added in the 9K liquid culture medium, the agar volume ratio is 1.2%) with a dilution coating plate and a plate streaking method, extracting DNA, amplifying 16s rDNA of a pure culture by PCR, comparing by NCBI after sequencing, identifying the purified strain as acidophilic thiobacillus ferrooxidans (Acidithiobacillus ferrooxidans), and naming the purified strain as MA-Y1. The bacteria are in a red brown round dot shape on the bacterial grade agar typesetting, are in a long rod shape under an optical microscope, and the physicochemical conditions are optimized, so that the growth temperature is 30-40 ℃, the pH is 1.5-2.5, and the concentration of Fe (II) is 20-40g/L. It can fully optimize Fe (II) within 100h, and the oxidation rate is as high as 98.47%. The thiobacillus ferrooxidans MA-Y1 is sent to the China center for type culture collection of Wuhan to obtain a strain with a collection number of CCTCC NO: M20211183.
Example 2
Example 2.1 detection of the Effect of magnetic field intensity on the oxidation rate of immobilized cell Fe (II)
The magnetic field strengthening and fixing process comprises the following steps:
(1) A30% (v/v) volcanic rock (particle size 2-3 cm) column layer was packed in bioreactor 1.
(2) 800mL of 9K liquid medium was added and inoculated with Thiobacillus ferrooxidans MA-Y1 at an inoculum size of 10% (v/v).
(3) The air pump is turned on, and the ventilation rate is controlled to be 0.6L/min.
(4) The constant-temperature water bath kettle and the three-phase brushless water pump are turned on, and the temperature of the constant-temperature water bath kettle is set to be 35 ℃.
(5) The magnetic field generator 2 is installed, the magnetic field intensity is set to be 0-40mT, and the immobilization time is 9 days. After completion of immobilization, the Fe (II) oxidation rate of the immobilized cells was measured, and the results are shown in Table 1.
TABLE 1 influence of magnetic field strength on the oxidation rate (%) of Fe (II) of immobilized cells
Example 2.2 detection of the Effect of the ratio of the immobilized carrier on the oxidation rate of Fe (II) in immobilized cells
The proportion of immobilized carrier in the bioreactor is 20-40%, the immobilization time is 9 days, the temperature is 35 ℃, the magnetic field strength is 20mT, after immobilization is completed, the Fe (II) oxidation rate of immobilized cells is measured, and the other steps are the same as those of example 2.1, and the detection results are shown in Table 2.
TABLE 2 influence of the ratio of the immobilized carrier on the oxidation rate (%) of Fe (II) of the immobilized cells
Example 2.3 detection of the effect of the immobilization time ratio on the Fe (II) oxidation rate of immobilized cells
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 5-10 days, the temperature is 35 ℃, the magnetic field strength is 20mT, after immobilization is completed, the Fe (II) oxidation rate of immobilized cells is measured, and the other steps are the same as those of example 2.1, and the detection results are shown in Table 3.
TABLE 3 influence of immobilization time on the oxidation rate (%) of Fe (II) in immobilized cells
Example 2.4 detection of the influence of temperature on the oxidation rate of Fe (II) in immobilized cells
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 9 days, the temperature is 20-40 ℃, the magnetic field strength is 20mT, after immobilization is completed, the Fe (II) oxidation rate of immobilized cells is measured, and the other steps are the same as those of example 2.1, and the detection results are shown in Table 4.
TABLE 4 influence of temperature on the oxidation rate (%) of Fe (II) in immobilized cells
Example 3
The system shown in fig. 1 is used for leaching metal, and the leaching system comprises a magnetic field strengthening fixing technology and an electric field strengthening leaching technology.
The magnetic field strengthening and fixing process comprises the following steps: (1) A30% (v/v) volcanic rock (particle size 2-3 cm) column layer was packed in bioreactor 1. (2) 800mL of 9K liquid medium was added and inoculated with Thiobacillus ferrooxidans MA-Y1 at an inoculum size of 10% (v/v). (3) opening the air pump, and controlling the ventilation rate at 0.6L/min. (4) The constant-temperature water bath kettle and the three-phase brushless water pump are turned on, and the temperature of the constant-temperature water bath kettle is set to be 35 ℃. (5) mounting a magnetic field generator 2, and setting the magnetic field strength to 20mT. The immobilization time is 9 days, and the volcanic stone immobilized with the thiobacillus ferrooxidans MA-Y1 is obtained.
The electric field enhanced leaching technology comprises the following steps: (1) After immobilization is completed, the leaching system is adopted to leach, the bioreactor 1 and the chemical reactor 3 are connected through a circulating pump 5, 85g of circuit board 8 is added into the chemical reactor 3, the grain size is 3cm, and volcanic stones of immobilized thiobacillus ferrooxidans MA-Y1 are placed in the bioreactor 1. (2) The bioreactor 1 and the chemical reactor 3 are respectively added with 9K liquid culture medium, a circulating pump 5, a three-phase brushless water pump, a constant-temperature water bath kettle and a ventilation pump are started to operate, the circulating pump 5 sets the liquid exchange amount to be 0.2-3.6L/min, the ventilation amount to be 0.6L/min, and the temperature is 35 ℃. (3) When the Fe (II) in the bioreactor 1 and the chemical reactor 3 reaches 90%, the electrodes of the electric field generator 4 are placed, and a direct current power supply is turned on, so that the current intensity is 40mA. Leaching time is 7 days. The detection results are shown in Table 5.
TABLE 5 influence of liquid exchange on copper and Nickel leaching Rate in Circuit Board
| Liquid exchange amount (L/min) | 0.2 | 1.2 | 2.4 | 3.2 | 3.6 |
| Copper leaching Rate (%) | 60.12 | 63.08 | 77.67 | 74.45 | 69.25 |
| Nickel leaching rate (%) | 65.25 | 67.44 | 85.44 | 84.52 | 80.64 |
Example 4
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 9 days, the temperature is 35 ℃, and the magnetic field strength is 20mT. The liquid exchange amount between the chemical reactor and the bioreactor is 2.4L/min, the addition amount of the circuit board is 40-100g, the particle size of the circuit board is 3cm, the current intensity is 40mA, the leaching time is 7 days, and the results are shown in Table 6.
TABLE 6 influence of the addition amount of Circuit Board on the copper and Nickel leaching Rate in Circuit Board
Example 5
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 9 days, the temperature is 35 ℃, and the magnetic field strength is 20mT. The liquid exchange amount between the chemical reactor and the bioreactor is 2.4L/min, the addition amount of the circuit board is 85g, the particle size of the circuit board is 2-4cm, the current intensity is 40mA, the leaching time is 7 days, and the results are shown in Table 7 in the rest of example 3.
TABLE 7 influence of Circuit Board particle size on copper and Nickel leaching Rate in Circuit Board
| Circuit board grain size (cm) | 2 | 2.5 | 3 | 3.5 | 4 |
| Copper leaching Rate (%) | 64.45 | 68.11 | 77.67 | 72.13 | 69.65 |
| Nickel leaching rate (%) | 79.16 | 82.56 | 85.44 | 80.25 | 78.63 |
Example 6
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 9 days, the temperature is 35 ℃, and the magnetic field strength is 20mT. The liquid exchange amount between the chemical reactor and the bioreactor is 2.4L/min, the addition amount of the circuit board is 85g, the particle size of the circuit board is 3cm, the current intensity is 0-200mA, the leaching time is 7 days, and the results are shown in Table 8.
TABLE 8 influence of amperage on copper and Nickel leaching Rate in Circuit Board
| Amperage (mA) | 0 | 40 | 100 | 160 | 200 |
| Copper leaching Rate (%) | 29.98 | 77.67 | 75.26 | 69.51 | 40.26 |
| Nickel leaching rate (%) | 36.25 | 85.44 | 78.37 | 74.62 | 51.23 |
Comparative example 1
One side of the bioreactor is not provided with immobilized cells and a magnetic field strengthening device (NO volcanic stone is added and NO magnetic field is used, and 9K liquid culture medium is directly added into the reactor), and the culture is carried out until the logarithmic phase CCTCC NO: m20211183 bacterial liquid, the exchange amount of the chemical reactor and the bioreactor liquid is 2.4L/min, the addition amount of a circuit board is 85g, the particle size of the circuit board is 3cm, the current intensity is 40mA, the leaching time is 7 days, and the results are shown in Table 9.
TABLE 9 influence of bacterial liquid addition on copper and Nickel leaching rate in Circuit Board in magneto-electric enhancement Process
| Bacterial liquid addition (%) | 10 | 14 | 16 | 18 | 20 |
| Copper leaching Rate (%) | 52.45 | 53.17 | 55.12 | 57.43 | 57.56 |
| Nickel leaching rate (%) | 58.61 | 59.21 | 59.44 | 61.06 | 65.43 |
As can be seen in combination with examples 3-6 and comparative example 1, CCTCC NO: m20211183 leaches out the circuit board under the technology of non-magnetic field strengthening fixing technology, and the leaching rate of copper and nickel is lower than that of the circuit board obtained by the technology of magnetic field strengthening fixing technology and the technology of electric field strengthening leaching.
Comparative example 2
NO immobilized cells are added into the bioreactor, and the culture is carried out until the logarithmic phase CCTCC NO: m20211183 bacterial liquid, the liquid exchange amount of the chemical reactor and the bioreactor is 2.4L/min, the addition amount of the circuit board is 85g, the particle size of the circuit board is 3cm, the electric field enhanced leaching process is not added, the leaching time is 7 days, and the rest is the same as in example 3, and the results are shown in Table 10.
Table 10 influence of the addition amount of the bacterial liquid on the leaching rate of copper and nickel in the circuit board without strengthening the process
| Bacterial liquid addition (%) | 10 | 14 | 16 | 18 | 20 |
| Copper leaching Rate (%) | 29.98 | 30.34 | 33.21 | 35.15 | 36.23 |
| Nickel leaching rate (%) | 36.25 | 38.59 | 39.15 | 40.09 | 42.12 |
As can be seen in combination with examples 3-6 and comparative example 2, CCTCC NO: after the M20211183 is combined with the magnetic field strengthening immobilization and the electric field strengthening leaching process, the leaching capability of copper and nickel in the circuit board is improved.
Comparative example 3
The proportion of immobilized carrier in the bioreactor is 30%, the immobilization time is 9 days, the temperature is 35 ℃, and the magnetic field strength is 20mT. The bacterial liquid of the strain M2017687 (which was preserved in the China center for type culture collection of Wuhan) which was cultured to the logarithmic phase CCTCC NO: M was added in an amount of 10-20% (v/v), the liquid exchange amount between the chemical reactor and the bioreactor was 2.4L/min, the addition amount of the circuit board was 85g, the particle size of the circuit board was 3cm, the current intensity was 40mA, and the leaching time was 7 days, and the rest was the same as in example 3, and the results were shown in Table 11.
Table 11CCTCC NO:M 2017687 influence of the addition amount of bacterial liquid on the leaching rate of copper and nickel in a circuit board
| Bacterial liquid addition (%) | 10 | 14 | 16 | 18 | 20 |
| Copper leaching Rate (%) | 27.11 | 28.23 | 29.04 | 29.78 | 32.11 |
| Nickel leaching rate (%) | 35.44 | 37.25 | 38.11 | 10.22 | 41.17 |
As can be seen from the combination of examples 3-6 and comparative example 3, the magnetic field enhanced immobilization technology and the electric field enhanced leaching technology can effectively enhance CCTCC NO: m20211183 has poor leaching rate of copper and nickel in the circuit board and has poor lifting capacity on other microorganisms.
The foregoing description of the preferred embodiments of the invention is not intended to limit the invention to the precise form disclosed, and any such modifications, equivalents, and alternatives falling within the spirit and scope of the invention are intended to be included within the scope of the invention.
Claims (10)
1. The strain of the thiobacillus ferrooxidans derived from volcanic ash is characterized in that the preservation number of the thiobacillus ferrooxidans is CCTCC NO: M20211183.
2. The method for fermenting a thiobacillus ferrooxidans according to claim 1, wherein the thiobacillus ferrooxidans according to claim 1 is inoculated into a culture medium and cultured in a fermentation manner.
3. A microbial agent comprising the thiobacillus ferrooxidans of claim 1.
4. Use of the thiobacillus ferrooxidans of claim 1 or the microbial inoculum of claim 3 for leaching metals.
5. Use of the thiobacillus ferrooxidans of claim 1 or the microbial inoculum of claim 3 for increasing the oxidation rate of Fe (II).
6. The use according to claim 4 or 5, characterized in that the use of the bacterial agent according to claim 1 or the bacterial agent according to claim 3 is combined with a magnetic field enhanced immobilization process and an electric field enhanced leaching process.
7. The use according to claim 6, characterized in that the inoculum size of the thiobacillus ferrooxidans according to claim 1 or the microbial inoculum according to claim 3 is 10%, the leaching temperature is 30-40 ℃, the pH is 1.5-2.5, the fe (II) concentration is 20-40g/L, the aeration rate is controlled to be 0.5-0.8L/min, and the exchange size is 0.2-3.6L/min; copper and nickel in the circuit board are leached out, 40-120g of the circuit board is obtained, and the grain size of the circuit board is 2-4cm.
8. The use of claim 6, wherein the conditions for magnetic field enhanced immobilization include: the magnetic field intensity is 0-40mT, the volume of the immobilized carrier is 20-40% of the volume of the bioreactor, and the immobilization time is 5-10 days; the conditions for electric field enhanced leaching include: the current is 0-200mA.
9. The use according to claim 6, wherein the metal is leached by means of a leaching system comprising: bioreactor, magnetic field generator, chemical reactor and electric field generator; the liquid in the bioreactor and the liquid in the chemical reactor are exchanged through a circulating pump; an immobilization carrier is arranged in the bioreactor, the immobilization carrier is immobilized with the thiobacillus ferrooxidans according to claim 1 or the microbial inoculum according to claim 3, a magnetic field generator is arranged on the outer side of the bioreactor, and the bioreactor is provided with a heating device and a ventilation device; a circuit board is placed in the chemical reactor, two electrodes of the electric field generator are placed in the chemical reactor, and the chemical reactor is provided with a heating device.
10. The use according to claim 9, wherein the method of leaching metals using the leaching system of claim 9 comprises a magnetic field enhanced immobilization process and an electric field enhanced leaching technique;
the magnetic field strengthening and fixing process comprises the following steps: (1) Filling 20-40% of non-immobilized carrier in the bioreactor, wherein the particle size of the carrier is 2-3cm; (2) Adding a culture medium, and inoculating the thiobacillus ferrooxidans of claim 1 or the microbial inoculum of claim 3 in an inoculum size of 10%; (3) Opening the ventilation device, and controlling ventilation rate to be 0.5-0.8L/min; (4) heating by a heating device at 20-40 ℃; (5) Installing a magnetic field generator, setting the magnetic field strength to be 0-40mT and the immobilization time to be 5-10 days to obtain an immobilization carrier;
the electric field enhanced leaching technology comprises the following steps: (1) By adopting the leaching system, a 40-120g circuit board is added into a chemical reactor, the particle size of the circuit board is 2-4cm, an immobilized carrier is placed in the bioreactor, and the immobilized carrier is immobilized with the thiobacillus ferrooxidans according to claim 1 or the microbial inoculum according to claim 3; (2) Respectively adding culture medium into the bioreactor and chemical reactor, opening circulating pump, heating device and ventilating device, setting liquid flow rate of circulating pump to 0.2-3.6L/min and ventilating quantity to 0.5-0.8L/min, when Fe (II) in the bioreactor and chemical reactor is up to 90%, placing into electrode of electric field generator, turning on DC power supply, and setting current to 0-200mA.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202310667854.4A CN116694521B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and application thereof |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202310667854.4A CN116694521B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and application thereof |
| CN202111549020.0A CN114231453B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and method for leaching metals |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202111549020.0A Division CN114231453B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and method for leaching metals |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN116694521A true CN116694521A (en) | 2023-09-05 |
| CN116694521B CN116694521B (en) | 2023-10-20 |
Family
ID=80757822
Family Applications (2)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202310667854.4A Active CN116694521B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and application thereof |
| CN202111549020.0A Active CN114231453B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and method for leaching metals |
Family Applications After (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202111549020.0A Active CN114231453B (en) | 2021-12-17 | 2021-12-17 | Thiobacillus ferrooxidans derived from volcanic ash and method for leaching metals |
Country Status (1)
| Country | Link |
|---|---|
| CN (2) | CN116694521B (en) |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103232953A (en) * | 2013-03-26 | 2013-08-07 | 华南理工大学 | Acidithiobacillus ferrooxidans and applications thereof |
| CN109439586A (en) * | 2018-11-21 | 2019-03-08 | 黑龙江八农垦大学 | A kind of acidophilus iron oxidizing microorganisms, microbial inoculum and application thereof |
| CN109628357A (en) * | 2019-02-12 | 2019-04-16 | 黑龙江八农垦大学 | A kind of ferrous oxide complex microbial inoculum and its application |
| CN111808773A (en) * | 2020-07-22 | 2020-10-23 | 东华理工大学 | Acidithiobacillus ferrooxidans and application thereof and ore leaching method |
| CN113355519A (en) * | 2021-06-03 | 2021-09-07 | 上海第二工业大学 | Method for leaching copper in waste circuit board by using microwave-enhanced thiobacillus ferrooxidans |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| PE20060789A1 (en) * | 2004-10-22 | 2006-08-10 | Biosigma Sa | WENELEN BACTERIA STRAIN DSM 16786 AND LEACHING PROCESS BASED ON INOCULATION OF SAID STRAIN |
| JP2016054736A (en) * | 2014-09-05 | 2016-04-21 | 公立大学法人秋田県立大学 | Metal extraction method using acidophilic thiobacillus ferrooxidans |
-
2021
- 2021-12-17 CN CN202310667854.4A patent/CN116694521B/en active Active
- 2021-12-17 CN CN202111549020.0A patent/CN114231453B/en active Active
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103232953A (en) * | 2013-03-26 | 2013-08-07 | 华南理工大学 | Acidithiobacillus ferrooxidans and applications thereof |
| CN109439586A (en) * | 2018-11-21 | 2019-03-08 | 黑龙江八农垦大学 | A kind of acidophilus iron oxidizing microorganisms, microbial inoculum and application thereof |
| CN109628357A (en) * | 2019-02-12 | 2019-04-16 | 黑龙江八农垦大学 | A kind of ferrous oxide complex microbial inoculum and its application |
| CN111808773A (en) * | 2020-07-22 | 2020-10-23 | 东华理工大学 | Acidithiobacillus ferrooxidans and application thereof and ore leaching method |
| CN113355519A (en) * | 2021-06-03 | 2021-09-07 | 上海第二工业大学 | Method for leaching copper in waste circuit board by using microwave-enhanced thiobacillus ferrooxidans |
Also Published As
| Publication number | Publication date |
|---|---|
| CN114231453A (en) | 2022-03-25 |
| CN116694521B (en) | 2023-10-20 |
| CN114231453B (en) | 2023-06-27 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104862475B (en) | The method of copper in Thiobacillus ferrooxidans leaching discarded printed circuit boards | |
| CN103484680B (en) | Method for leaching copper in waste printed circuit boards (PCBs) by mixed bacteria | |
| CN112157119A (en) | Restoration method for controlling microorganisms to reduce heavy metals by iron-containing minerals | |
| Lee et al. | Leaching of Mn, Co, and Ni from manganese nodules using an anaerobic bioleaching method | |
| CN109628357A (en) | A kind of ferrous oxide complex microbial inoculum and its application | |
| CN103131650B (en) | Eosino-thiobacillus and application thereof to copper pyrites leaching | |
| CN107119194B (en) | A kind of the high-performance bio leaching method and device of waste and old circuit board noble metal | |
| CN1566377A (en) | Combined heap leaching process for copper ore | |
| CN102206751B (en) | Method for continuously recovering copper from printed circuit boards by microbial metabolites under action of micro electric field | |
| CN106966494A (en) | The method for removing nitrate nitrogen in water removal, electrode colonization method, electrode and device | |
| CN101457209B (en) | Low-temperature leaching-ore bacteria and application thereof in low-temperature biological heap leaching process for copper sulfide ore | |
| Dan et al. | Reductive leaching of manganese from manganese dioxide ores by bacterial-catalyzed two-ores method | |
| CN104561544A (en) | Light-intensified bioleaching method for semiconductor minerals | |
| CN103413958A (en) | Acidophilic microbe fuel cell and culture method of acidophilic microbes | |
| CN116694521B (en) | Thiobacillus ferrooxidans derived from volcanic ash and application thereof | |
| CN104332645B (en) | A kind of microbiological fuel cell for handling leaded sewage | |
| CN109439586B (en) | Acidophilic iron-oxidizing microorganism, microbial inoculum and application thereof | |
| CN103572048A (en) | Method of cobalt leaching with activated carbon catalysis bacteria | |
| CN113355519B (en) | Method for leaching copper in waste circuit board by using microwave-enhanced thiobacillus ferrooxidans | |
| CN113308605B (en) | Method for strengthening leaching of copper and gold in waste circuit board by phanerochaete chrysosporium by using micro-electric field | |
| CN110616329A (en) | Method for recovering tin from tin-containing waste | |
| CN108130424B (en) | A kind of method of pyrite cinder biological desulphurization upgrading collaboration recycling valuable metal | |
| CN212404218U (en) | Microorganism mineral leaching device | |
| CN104726714B (en) | A kind of method of copper in Mixed Microbes leaching discarded printed circuit boards | |
| CN103114209A (en) | Method for leaching cobalt and copper in cobalt-copper alloy through cooperation of thiobacillus ferrooxidans |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |