CN105462903A - Efficient sewage treatment microbial agent - Google Patents
Efficient sewage treatment microbial agent Download PDFInfo
- Publication number
- CN105462903A CN105462903A CN201610032517.8A CN201610032517A CN105462903A CN 105462903 A CN105462903 A CN 105462903A CN 201610032517 A CN201610032517 A CN 201610032517A CN 105462903 A CN105462903 A CN 105462903A
- Authority
- CN
- China
- Prior art keywords
- parts
- sewage treatment
- treatment microbial
- efficient sewage
- microbial inoculant
- 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.)
- Pending
Links
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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
- C02F3/347—Use of yeasts or fungi
-
- 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
- C12N1/14—Fungi; Culture media therefor
-
- 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
- C12N1/14—Fungi; Culture media therefor
- C12N1/16—Yeasts; Culture media therefor
-
- 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
- C12N1/14—Fungi; Culture media therefor
- C12N1/16—Yeasts; Culture media therefor
- C12N1/18—Baker's yeast; Brewer's yeast
Abstract
The invention discloses an efficient sewage treatment microbial agent. The efficient sewage treatment microbial agent is prepared from, by weight, 2-4 parts of nitrosobacteria, 10-20 parts of bacillus subtilis, 8-15 parts of alcaligenes faecalis, 5-10 parts of bacillus megatherium, 2-8 parts of pseudomonas aeruginosa, 2-10 parts of candida lipolytica, 2-8 parts of deoxidized paracoccus, 2-6 parts of pseudomonas stutzeri, 2-10 parts of saccharomyces cerevisiae, 1-4 parts of aspergillus niger, 0.1-0.6 part of yeast extract, 2-6 parts of peptone, 0.1-0.5 part of glucose, 8-15 parts of kaolin, 2-5 parts of aluminum polychlorid, 0.1-0.5 part of FMEE and a proper amount of water. The efficient sewage treatment microbial agent is suitable for treating industrial waste water, breeding waste water and the like, all strains are in cooperation, symbiotic coordination is achieved, high activity is achieved, and reproduction is fast. The efficient sewage treatment microbial agent is put in the waste water to be treated, the degradation effect can be effectively accelerated, the treatment water quality can be greatly improved, operating cost can be reduced, the treated water reaches the standard to be drained, and damage to environment is reduced.
Description
Technical field
The present invention relates to technical field of water treatment chemical, particularly relate to a kind of sewage treatment microbial inoculant efficiently.
Background technology
At present, industry, incomparable effect is played in the process of cultivation and sanitary wastewater in protection of the environment, but inside sewage treatment area, still there is a lot of problem, such as industrial sewage is unstable when water quality treatment effect, and operation cost is higher, water after purification needs through passing into the disinfections such as chlorine, causing is the microorganism generation mortality carrying the inside originally, thus allow water body lose the ability of self-purification originally, there is higher phenomenon in the chemical composition in sewage-treating agent, easily secondary pollution etc. is caused to water body, the COD of aquaculture wastewater and ammonia nitrogen superelevation, traditional biogas and active sludge cannot reach the requirement of more and more tighter environmental protection index, and produce a large amount of mud, difficult treatment.And for sewage disposal, simple passes through microbiological deterioration, and speed is slow, is not easy to take effect very soon.For this reason, we propose a kind of sewage treatment microbial inoculant efficiently.
Summary of the invention
Based on the technical problem that background technology exists, the present invention proposes a kind of sewage treatment microbial inoculant efficiently.
The present invention proposes a kind of sewage treatment microbial inoculant efficiently, its raw material comprises by weight: nitrococcus 2-4 part, subtilis 10-20 part, Bacillus foecalis alkaligenes 8-15 part, bacillus megaterium 5-10 part, Pseudomonas aeruginosa 2-8 part, Candida lipolytica 2-10 part, deoxidation secondary coccus 2-8 part, Pseudomonas stutzeri 2-6 part, yeast saccharomyces cerevisiae 2-10 part, aspergillus niger 1-4 part, yeast extract paste 0.1-0.6 part, peptone 2-6 part, glucose 0.1-0.5 part, kaolin 8-15 part, polymerize aluminum chloride 2-5 part, aliphatic acid polyethenoxy methyl ether 0.1-0.5 part, suitable quantity of water.
Preferably, the weight ratio of subtilis, Bacillus foecalis alkaligenes, bacillus megaterium is 15-17:11-13:6-8.
Preferably, the weight ratio of Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae is 5-7:6-8:5-7:3-4:6-8.
Preferably, aspergillus niger, yeast extract paste, peptone, the weight ratio of glucose is 2-3:0.3-0.5:3-5:0.3-0.5.
Preferably, the efficient sewage treatment microbial inoculant of described one, its raw material comprises by weight: nitrococcus 2.5-3.2 part, subtilis 17-19 part, Bacillus foecalis alkaligenes 10-13 part, bacillus megaterium 6-8 part, Pseudomonas aeruginosa 3-6 part, Candida lipolytica 5-8 part, deoxidation secondary coccus 5-6 part, Pseudomonas stutzeri 4-5 part, yeast saccharomyces cerevisiae 5-7 part, aspergillus niger 2.5-3.5 part, yeast extract paste 0.3-0.5 part, peptone 3.5-5 part, glucose 0.3-0.45 part, kaolin 10-12 part, polymerize aluminum chloride 3-4 part, aliphatic acid polyethenoxy methyl ether 0.3-0.4 part.
Preferably, the efficient sewage treatment microbial inoculant of described one, its raw material comprises by weight: nitrococcus 3 parts, subtilis 16 parts, Bacillus foecalis alkaligenes 12 parts, bacillus megaterium 7 parts, Pseudomonas aeruginosa 5.5 parts, Candida lipolytica 7.5 parts, secondary 6 parts, the coccus of deoxidation, Pseudomonas stutzeri 5 parts, yeast saccharomyces cerevisiae 6.5 parts, aspergillus niger 3 parts, yeast extract paste 0.35 part, peptone 4.5 parts, glucose 0.4 part, kaolin 11 parts, polymerize aluminum chloride 3.5 parts, aliphatic acid polyethenoxy methyl ether 0.35 part.
Disclosed in the present invention also, a kind of preparation method of efficient sewage treatment microbial inoculant, comprises the steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring 5-10 minute and obtain mixed strains according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 25-35 DEG C, and incubation time is 30-45 hour, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
In the present invention, each bacterial classification wherein in nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae can accelerate the degraded of microorganism to sewage, to improve the bioavailability of whole Waste Water Treatment, thus accelerate the operation at waste water place, the foreign material accelerated in sewage decompose, cooperatively interact between each bacterial classification, symbiosis is coordinated, active high, and breeding is fast, be dropped in waste water to be dealt with, effectively can be accelerated degradation effect; Multiple harmful ion in the kaolin energy planar water added, further by sewage purification, it is wide that the polymerize aluminum chloride wherein added adapts to waters, and hydrolysis rate is fast, high adsorption capacity, forms alumen ustum large, and the close precipitation of matter is fast, the advantages such as delivery turbidity is low, and dewatering is good; The aliphatic acid polyethenoxy methyl ether added has fast, strong to the grease solubilising feature of cheap, the low bubble of raw material, water-soluble speed.The present invention is applicable to the process of the waste water such as industry and cultivation, can improve water quality treatment in a large number, reduces running cost, allows and processes water qualified discharge, reduce the destruction to environment.
Embodiment
Below in conjunction with specific embodiment, the present invention will be further described.
Embodiment 1
A kind of sewage treatment microbial inoculant efficiently, its raw material comprises by weight: nitrococcus 2 parts, subtilis 11 parts, Bacillus foecalis alkaligenes 8.5 parts, bacillus megaterium 5.5 parts, Pseudomonas aeruginosa 3 parts, Candida lipolytica 3 parts, secondary 2 parts, the coccus of deoxidation, Pseudomonas stutzeri 2 parts, yeast saccharomyces cerevisiae 3 parts, aspergillus niger 2 parts, yeast extract paste 0.15 part, peptone 2 parts, glucose 0.15 part, kaolin 8 parts, polymerize aluminum chloride 2 parts, aliphatic acid polyethenoxy methyl ether 0.1 part, suitable quantity of water.
Its preparation method comprises the following steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring and obtain mixed strains in 5 minutes according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 26 DEG C, and incubation time is 30 hours, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
Embodiment 2
A kind of sewage treatment microbial inoculant efficiently, its raw material comprises by weight: nitrococcus 2.5 parts, subtilis 14 parts, Bacillus foecalis alkaligenes 10 parts, bacillus megaterium 6.5 parts, Pseudomonas aeruginosa 4 parts, Candida lipolytica 5 parts, secondary 4.5 parts, the coccus of deoxidation, Pseudomonas stutzeri 3.5 parts, yeast saccharomyces cerevisiae 4.5 parts, aspergillus niger 3.2 parts, yeast extract paste 0.35 part, peptone 3 parts, glucose 0.25 part, kaolin 10 parts, polymerize aluminum chloride 2.8 parts, aliphatic acid polyethenoxy methyl ether 0.25 part, suitable quantity of water.
Its preparation method comprises the following steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring and obtain mixed strains in 6 minutes according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 28 DEG C, and incubation time is 35 hours, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
Embodiment 3
A kind of sewage treatment microbial inoculant efficiently, its raw material comprises by weight: nitrococcus 3 parts, subtilis 16 parts, Bacillus foecalis alkaligenes 12 parts, bacillus megaterium 7 parts, Pseudomonas aeruginosa 5.5 parts, Candida lipolytica 7.5 parts, secondary 6 parts, the coccus of deoxidation, Pseudomonas stutzeri 5 parts, yeast saccharomyces cerevisiae 6.5 parts, aspergillus niger 3 parts, yeast extract paste 0.35 part, peptone 4.5 parts, glucose 0.4 part, kaolin 11 parts, polymerize aluminum chloride 3.5 parts, aliphatic acid polyethenoxy methyl ether 0.35 part, suitable quantity of water.
Its preparation method comprises the following steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring and obtain mixed strains in 7 minutes according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 30 DEG C, and incubation time is 38 hours, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
Embodiment 4
A kind of sewage treatment microbial inoculant efficiently, its raw material comprises by weight: nitrococcus 4 parts, subtilis 18 parts, Bacillus foecalis alkaligenes 14 parts, bacillus megaterium 9 parts, Pseudomonas aeruginosa 7.5 parts, Candida lipolytica 8.5 parts, secondary 7.5 parts, the coccus of deoxidation, Pseudomonas stutzeri 5.5 parts, yeast saccharomyces cerevisiae 9 parts, aspergillus niger 3.5 parts, yeast extract paste 0.5 part, peptone 5 parts, glucose 0.45 part, kaolin 14 parts, polymerize aluminum chloride 4.5 parts, aliphatic acid polyethenoxy methyl ether 0.45 part, suitable quantity of water.
Its preparation method comprises the following steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring and obtain mixed strains in 9 minutes according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 33 DEG C, and incubation time is 43 hours, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
The above; be only the present invention's preferably embodiment; but protection scope of the present invention is not limited thereto; anyly be familiar with those skilled in the art in the technical scope that the present invention discloses; be equal to according to technical scheme of the present invention and inventive concept thereof and replace or change, all should be encompassed within protection scope of the present invention.
Claims (7)
1. an efficient sewage treatment microbial inoculant, it is characterized in that, its raw material comprises by weight: nitrococcus 2-4 part, subtilis 10-20 part, Bacillus foecalis alkaligenes 8-15 part, bacillus megaterium 5-10 part, Pseudomonas aeruginosa 2-8 part, Candida lipolytica 2-10 part, deoxidation secondary coccus 2-8 part, Pseudomonas stutzeri 2-6 part, yeast saccharomyces cerevisiae 2-10 part, aspergillus niger 1-4 part, yeast extract paste 0.1-0.6 part, peptone 2-6 part, glucose 0.1-0.5 part, kaolin 8-15 part, polymerize aluminum chloride 2-5 part, aliphatic acid polyethenoxy methyl ether 0.1-0.5 part, suitable quantity of water.
2. the efficient sewage treatment microbial inoculant of one according to claim 1, is characterized in that, the weight ratio of subtilis, Bacillus foecalis alkaligenes, bacillus megaterium is 15-17:11-13:6-8.
3. the efficient sewage treatment microbial inoculant of one according to claim 1, is characterized in that, the weight ratio of Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae is 5-7:6-8:5-7:3-4:6-8.
4. the efficient sewage treatment microbial inoculant of one according to claim 1, is characterized in that, aspergillus niger, yeast extract paste, peptone, and the weight ratio of glucose is 2-3:0.3-0.5:3-5:0.3-0.5.
5. the efficient sewage treatment microbial inoculant of one according to claim 1, it is characterized in that, its raw material comprises by weight: nitrococcus 2.5-3.2 part, subtilis 17-19 part, Bacillus foecalis alkaligenes 10-13 part, bacillus megaterium 6-8 part, Pseudomonas aeruginosa 3-6 part, Candida lipolytica 5-8 part, deoxidation secondary coccus 5-6 part, Pseudomonas stutzeri 4-5 part, yeast saccharomyces cerevisiae 5-7 part, aspergillus niger 2.5-3.5 part, yeast extract paste 0.3-0.5 part, peptone 3.5-5 part, glucose 0.3-0.45 part, kaolin 10-12 part, polymerize aluminum chloride 3-4 part, aliphatic acid polyethenoxy methyl ether 0.3-0.4 part.
6. a kind of sewage treatment microbial inoculant efficiently according to claim 1 or 5, it is characterized in that, its raw material comprises by weight: nitrococcus 3 parts, subtilis 16 parts, Bacillus foecalis alkaligenes 12 parts, bacillus megaterium 7 parts, Pseudomonas aeruginosa 5.5 parts, Candida lipolytica 7.5 parts, secondary 6 parts, the coccus of deoxidation, Pseudomonas stutzeri 5 parts, yeast saccharomyces cerevisiae 6.5 parts, aspergillus niger 3 parts, yeast extract paste 0.35 part, peptone 4.5 parts, glucose 0.4 part, kaolin 11 parts, polymerize aluminum chloride 3.5 parts, aliphatic acid polyethenoxy methyl ether 0.35 part.
7. a preparation method for a kind of efficient sewage treatment microbial inoculant according to any one of claim 1-6, is characterized in that, comprise the steps:
S1, provide mixed strains substratum, this mixed strains substratum is put in this mixed strains substratum the peptone, glucose, yeast extract paste and the water that take according to deal proportioning through high-temperature sterilization process;
S2, to take nitrococcus, subtilis, Bacillus foecalis alkaligenes, bacillus megaterium, Pseudomonas aeruginosa, Candida lipolytica, the secondary coccus of deoxidation, Pseudomonas stutzeri, yeast saccharomyces cerevisiae, aspergillus niger pour stirrer into and carry out stirring 5-10 minute and obtain mixed strains according to deal proportioning;
S3, to be placed in mixed strains substratum by gained mixed strains in S2 and to cultivate, culture temperature is 25-35 DEG C, and incubation time is 30-45 hour, can obtain complex microorganism after incubation time;
S4, by complex microorganism through centrifugal drying process, kaolin, polymerize aluminum chloride and aliphatic acid polyethenoxy methyl ether is taken again according to deal proportioning, and be placed in stirrer to stir and obtain mixture, then by mixture with dried complex microorganism heated and stirred machine is stirred just can obtain efficient sewage treatment microbial inoculant.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610032517.8A CN105462903A (en) | 2016-01-18 | 2016-01-18 | Efficient sewage treatment microbial agent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610032517.8A CN105462903A (en) | 2016-01-18 | 2016-01-18 | Efficient sewage treatment microbial agent |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN105462903A true CN105462903A (en) | 2016-04-06 |
Family
ID=55601065
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201610032517.8A Pending CN105462903A (en) | 2016-01-18 | 2016-01-18 | Efficient sewage treatment microbial agent |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105462903A (en) |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105907673A (en) * | 2016-04-29 | 2016-08-31 | 广州市佳境水处理技术工程有限公司 | Method for strengthening biochemical water treatment effects by microbial preparation |
| CN105948277A (en) * | 2016-07-06 | 2016-09-21 | 苏州市相城区阳澄湖镇东枪塘水产养殖专业合作社 | Aerobic microbial preparation for aquaculture |
| CN108795815A (en) * | 2018-06-28 | 2018-11-13 | 绍兴市海清环保科技有限公司 | A kind of denitrification mix bacterium agent for chemical industry garden Industrial Waste Water Treatments |
| CN109576184A (en) * | 2018-12-25 | 2019-04-05 | 重庆融极环保工程有限公司 | A kind of complex microbial inoculum for waste water of basic printing and dyeing processing |
| CN112740865A (en) * | 2020-12-25 | 2021-05-04 | 安徽理工大学 | Method and device for repairing mine post-explosion environment by adopting biological bacteria and moss |
| CN112939355A (en) * | 2021-02-04 | 2021-06-11 | 中水北方勘测设计研究有限责任公司 | Artificial filler with nitrogen and phosphorus removal functions and preparation method thereof |
| US11085016B1 (en) | 2020-01-20 | 2021-08-10 | Chio Kang Medical, Inc. | Method for screening bacteria capable of degrading ethylene oxide |
| US11124438B2 (en) * | 2020-01-20 | 2021-09-21 | Chio Kang Medical, Inc. | Alcaligenes faecalis for degrading ethylene oxide |
| US11130939B2 (en) | 2020-01-20 | 2021-09-28 | Chio Kang Medical, Inc. | Bacteria for degrading ethylene oxide and uses thereof |
| US11220667B2 (en) | 2020-01-20 | 2022-01-11 | Chio Kang Medical, Inc. | Bacteria for degrading ethylene oxide and applications thereof |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102864109A (en) * | 2012-09-26 | 2013-01-09 | 李丽萍 | Preparation for trinitrotoluene-contained sewage treatment and using method of preparation |
| CN102888345A (en) * | 2012-09-26 | 2013-01-23 | 何颖霞 | Biological agent for processing industrial sewage and preparation method and application |
| CN102888374A (en) * | 2012-09-26 | 2013-01-23 | 闫家怡 | Biological agent for processing industrial sewage and preparation method and application |
| CN103667141A (en) * | 2013-12-11 | 2014-03-26 | 山东华亚环保科技有限公司 | Industrial sewage treatment agent |
| CN103667144A (en) * | 2013-12-11 | 2014-03-26 | 山东华亚环保科技有限公司 | Domestic sewage treatment microbial inoculant |
-
2016
- 2016-01-18 CN CN201610032517.8A patent/CN105462903A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102864109A (en) * | 2012-09-26 | 2013-01-09 | 李丽萍 | Preparation for trinitrotoluene-contained sewage treatment and using method of preparation |
| CN102888345A (en) * | 2012-09-26 | 2013-01-23 | 何颖霞 | Biological agent for processing industrial sewage and preparation method and application |
| CN102888374A (en) * | 2012-09-26 | 2013-01-23 | 闫家怡 | Biological agent for processing industrial sewage and preparation method and application |
| CN103667141A (en) * | 2013-12-11 | 2014-03-26 | 山东华亚环保科技有限公司 | Industrial sewage treatment agent |
| CN103667144A (en) * | 2013-12-11 | 2014-03-26 | 山东华亚环保科技有限公司 | Domestic sewage treatment microbial inoculant |
Non-Patent Citations (12)
| Title |
|---|
| PJ WILLIAMS 等: "Microbial community study of the process- and groundwater of the Sishen Iron-Ore Mine, South Africa", 《WATER SA》 * |
| 伦世仪 主编: "《环境生物工程》", 30 September 2002 * |
| 张兰河 等: "微生物菌剂的构建及其在城市污水处理中的应用", 《化工进展》 * |
| 李元高 主编: "《物理化学》", 31 July 2013 * |
| 李祥高 等编著: "《精细化学品化学》", 30 April 2013 * |
| 李铁民 等编著: "《环境生物资源》", 31 May 2003 * |
| 杨润昌 主编: "《水污染控制工程》", 31 January 2006 * |
| 林鹿 等主编: "《制浆漂白生物技术与原理（第二版）》", 31 January 2012 * |
| 王建平 主编: "《REACH法规与生态纺织品》", 31 August 2009 * |
| 罗志腾 主编: "《水污染控制工程微生物学》", 31 May 1988 * |
| 蒋克彬 等编: "《污水处理技术问答》", 31 January 2013 * |
| 郭静波 等: "微生物菌剂的构建及其在污水处理中的应用", 《中国给水排水》 * |
Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105907673A (en) * | 2016-04-29 | 2016-08-31 | 广州市佳境水处理技术工程有限公司 | Method for strengthening biochemical water treatment effects by microbial preparation |
| CN105907673B (en) * | 2016-04-29 | 2018-02-06 | 广州市佳境水处理技术工程有限公司 | A kind of method using microorganism formulation enhanced water treatment biochemical effects |
| CN105948277A (en) * | 2016-07-06 | 2016-09-21 | 苏州市相城区阳澄湖镇东枪塘水产养殖专业合作社 | Aerobic microbial preparation for aquaculture |
| CN108795815A (en) * | 2018-06-28 | 2018-11-13 | 绍兴市海清环保科技有限公司 | A kind of denitrification mix bacterium agent for chemical industry garden Industrial Waste Water Treatments |
| CN109576184A (en) * | 2018-12-25 | 2019-04-05 | 重庆融极环保工程有限公司 | A kind of complex microbial inoculum for waste water of basic printing and dyeing processing |
| US11085016B1 (en) | 2020-01-20 | 2021-08-10 | Chio Kang Medical, Inc. | Method for screening bacteria capable of degrading ethylene oxide |
| US11124438B2 (en) * | 2020-01-20 | 2021-09-21 | Chio Kang Medical, Inc. | Alcaligenes faecalis for degrading ethylene oxide |
| US11130939B2 (en) | 2020-01-20 | 2021-09-28 | Chio Kang Medical, Inc. | Bacteria for degrading ethylene oxide and uses thereof |
| US11220667B2 (en) | 2020-01-20 | 2022-01-11 | Chio Kang Medical, Inc. | Bacteria for degrading ethylene oxide and applications thereof |
| CN112740865A (en) * | 2020-12-25 | 2021-05-04 | 安徽理工大学 | Method and device for repairing mine post-explosion environment by adopting biological bacteria and moss |
| CN112939355A (en) * | 2021-02-04 | 2021-06-11 | 中水北方勘测设计研究有限责任公司 | Artificial filler with nitrogen and phosphorus removal functions and preparation method thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN105462903A (en) | Efficient sewage treatment microbial agent | |
| Huo et al. | Co-culture of Chlorella and wastewater-borne bacteria in vinegar production wastewater: enhancement of nutrients removal and influence of algal biomass generation | |
| CN102858695B (en) | Wastewater processing method, system, and method for measuring pollutant-decomposition activity | |
| CN105645710B (en) | A kind of method that mud decrement is carried out using complex microorganism preparations | |
| CN110066082B (en) | Sludge anaerobic fermentation treatment method for synchronously strengthening acid production and phosphorus removal | |
| Alexandre et al. | Performance of anaerobic bioreactor treating fish-processing plant wastewater pre-hydrolyzed with a solid enzyme pool | |
| Sun et al. | Performance and microbial community analysis of an algal-activated sludge symbiotic system: Effect of activated sludge concentration | |
| Murugesan et al. | Flocculation and dewaterability of chemically enhanced primary treatment sludge by bioaugmentation with filamentous fungi | |
| CN103025668A (en) | A method for rapid treatment of waste water and a composition thereof | |
| Handous et al. | Two-stage anaerobic digestion of meat processing solid wastes: methane potential improvement with wastewater addition and solid substrate fermentation | |
| Rincón-Llorente et al. | Table olive wastewater: Problem, treatments and future strategy. A review | |
| Alberton et al. | Production of a fermented solid containing lipases of Rhizopus microsporus and its application in the pre-hydrolysis of a high-fat dairy wastewater | |
| CN104694443A (en) | Improved biological microbial agent for disposing industrial sewage and preparation method and application thereof | |
| CN103396947A (en) | Micro nutrient additive for microbial water treatment | |
| KR20120130167A (en) | Improved digestion of biosolods in wastewater | |
| Yan et al. | Investigation of microbial community structure in an advanced activated sludge side-stream reactor process with alkaline treatment | |
| CN108585224A (en) | A method of using complex micro organism fungicide treated sewage and being reduced sludge generation | |
| Fadile et al. | Aerobic treatment of lipid-rich wastewater by a bacterial consortium | |
| CN109081447B (en) | Method for removing nitrogen and phosphorus in culture wastewater by combining chlorella, acinetobacter and pseudomonas | |
| CN105152478B (en) | Treatment method of industrial wastewater produced during preparation of sodium glutamate through concentration isoelectric process | |
| CN109019874B (en) | Biological growth promoter for papermaking wastewater and preparation method thereof | |
| WO2016103949A1 (en) | Treatment method and treatment device for fat and/or oil-containing waste water | |
| CN109679865A (en) | A kind of microorganism blender and its preparation preparation and application | |
| CN108911160A (en) | A kind of sewage treatment biological growth promoter and preparation method thereof | |
| CN105132326B (en) | A kind of biological prosthetic preparation for concentrating isoelectric point technology and preparing industrial wastewater caused by sodium glutamate |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20160406 |
|
| RJ01 | Rejection of invention patent application after publication |