CN104232510A - Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation - Google Patents
Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation Download PDFInfo
- Publication number
- CN104232510A CN104232510A CN201410382505.9A CN201410382505A CN104232510A CN 104232510 A CN104232510 A CN 104232510A CN 201410382505 A CN201410382505 A CN 201410382505A CN 104232510 A CN104232510 A CN 104232510A
- Authority
- CN
- China
- Prior art keywords
- water body
- microbial preparation
- produce
- biomembranous
- gram
- 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
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Abstract
The invention relates to a microbial preparation capable of generating a biological membrane in a water body. The microbial preparation is prepared from the following components in percentage by weight: 90-92% of a compound microbial preparation, 5-8% of enzyme microorganism, 2-4% of brown sugar, wherein the compound microbial preparation comprises bacillus subtilis, actinomycete, saccharomycete and enzyme microorganism; the effective viable count of the bacillus subtilis is 1.9 billion/g, the effective viable count of the actinomycete is 6 million/g, and the effective viable count of the saccharomycete is 0.05 billion/g. The microbial preparation can be used for solving the problems that the lake pollution treatment method in the prior art is high in cost and unobvious in treatment effect and functions for a short time.
Description
Technical field
The present invention relates to microorganism field, be specifically related to one and water body can be made to produce biomembranous microbial preparation and using method thereof.
Background technology
In the pollutent of current Lake Water, total phosphorus and heavy metal ion account for very large proportion, improvement for lake pollution generally adopts the method for desilting or implantation methods waterplant, these two kinds of methods all need larger manpower and materials, pollute control expense high, dredging method can only short period of time decontamination; And plant cover cultivation methods may cause secondary pollution with the death of seasonal variations due to plant.
Although also there is the method by microbial treatment in prior art, applicant tests that its result of use of rear discovery is not obvious and effect duration is shorter.
Summary of the invention
In order to solve above technical problem, the invention provides one and water body can be made to produce biomembranous microbial preparation and using method thereof, solving the problem that in prior art, lake pollution administering method costly, regulation effect is not obvious, the time length is short.
One can make water body produce biomembranous microbial preparation, and the following composition comprised by weight percentage is made:
Complex microorganism preparations 90-92%, enzymatic microorganism 5-8%, brown sugar 2-4%;
Described complex microorganism preparations comprises subtilis, actinomycetes, yeast, enzymatic microorganism, described subtilis living bacteria count is 1,900,000,000/gram, described actinomycetes living bacteria count is 6,000,000/gram, described yeast living bacteria count is 0.5 hundred million/gram.
The above-described using method making water body produce biomembranous microbial preparation, the described complex microorganism preparations prepared is placed in container the water adding 1.5 times of weights, mix latter standing 2 hours thoroughly, after described complex microorganism preparations fully activates, be evenly sprinkled upon among water body.
In technique scheme, evenly splashed in complete for described microbial preparation pond, every mu uses 2.5-3 kilogram, and biofilm development removes microbial film to when will come off from bank or pool wall.
In technique scheme, add in the water body of required use described water body can be made to produce biomembranous microbial preparation after produce to microbial film before by oxygen delivery equipment to water body oxygenation.
The microbial strains preparation that the present invention does not produce antagonistic action mutually by reasonable selection can make water body produce biomembranous microbial preparation, water body bank is made to produce microbial film rapidly, microbial film can fix the microorganism that enriched has degradation function on unit space, be conducive to the removal of the pollutent such as organism, ammonia nitrogen, heavy metal ion in flowing water environment, can purifying water body, and use procedure is easy and simple to handle, secondary pollution can not be caused.
Embodiment
Below in conjunction with embodiment, technical scheme of the present invention is described in detail.
Embodiment one
One can make water body produce biomembranous microbial preparation, and the following composition comprised by weight percentage is made: complex microorganism preparations 90%, enzymatic microorganism 8%, brown sugar 2%;
Described complex microorganism preparations comprises subtilis, actinomycetes, yeast, enzymatic microorganism (buying from Japanese Pan Ya Co., Ltd.), described subtilis living bacteria count is 1,900,000,000/gram, described actinomycetes living bacteria count is 6,000,000/gram, described yeast living bacteria count is 0.5 hundred million/gram.
Embodiment two
One can make water body produce biomembranous microbial preparation, and the following composition comprised by weight percentage is made: complex microorganism preparations 91%, enzymatic microorganism 7%, brown sugar 3%;
Described complex microorganism preparations comprises subtilis, actinomycetes, yeast, enzymatic microorganism (buying from Japanese Pan Ya Co., Ltd.), described subtilis living bacteria count is 1,900,000,000/gram, described actinomycetes living bacteria count is 6,000,000/gram, described yeast living bacteria count is 0.5 hundred million/gram.
Embodiment three
Made water body in embodiment two being produced biomembranous microbial preparation drops in the Lake Water Body of Ziyang, wuchang, wuhan, and every mu uses 2.5 kilograms, evenly splashes; Use on the cliff of loke shore after 2 months and start to generate microbial film, within every five days, measure its total phosphorus concentration and concentration of heavy metal ion to the water sampling in lake water after producing microbial film, measuring result is in table 1 and table 2.
Total phosphorus concentration contrast (unit: mg/L) in table 1 each sky water intaking water sample
In the water body in lake of the microbial preparation process of embodiment of the present invention process, total phosphorous can decline gradually as seen from Table 1, and the total phosphorus standard processed after 50 days in water body reaches two class levels (method and standard detection according to GB 3838-2002 " water environment quality standard ") from three class levels.
Part concentration of heavy metal ion contrast (unit: mg/L) in table 2 each sky water intaking water sample
In the water body in lake of the microbial preparation process of embodiment of the present invention process, heavy metal content can decline gradually as seen from Table 2, and the heavy metal standard after 50 days in water body of processing reaches two class levels or close to a class level (method and standard detection according to " water environment quality standard " GB 3838-2002) from three classes or four class levels.
The made water body that the present invention uses produces subtilis in biomembranous microbial preparation, actinomycetes, enzymatic microorganism are aerobic bacteria, yeast is facultative aerobe, therefore preferably take oxygenating machine to be water body oxygenation in use simultaneously, biofilm development can be promoted like this and play a role.
Multiple enzyme and the microbiotic such as the subtilis energy extracellular proteinase that the present invention uses, abundant residues bait, excrete wastes, plant and animal residues and the obnoxious flavour (ammonia, hydrogen sulfide etc.) accumulated in water body is made first to be decomposed into small molecules (polypeptide, higher fatty acid etc.), after be decomposed into more micromolecular organism (amino acid, lower fatty acid, monose, disaccharides etc.), finally be decomposed into carbonic acid gas, nitrate and vitriol etc., effectively reduce COD, the BOD in water, make the amino nitrogen (NH in water body
3-N), nitroso-group nitrogen (NO
2-N) and sulfide concentration reduction, thus effectively improve water quality.
Actinomycetes can produce microbiotic and enzyme material, go back decomposable asymmetric choice net protein, Mierocrystalline cellulose and organism, and the taste offseted except water body also has certain effect.
It is fast that yeast had both had bacterial growth reproduction speed, has again that fungal metabolite is vigorous, acidproof, a feature such as osmophilic strain and high density organic substrates, effectively decomposes gas chromatography and grease etc., can remove COD and BOD in water, improve water quality.
It should be noted last that, above embodiment is only in order to illustrate the technology implementation scheme of this material but not to limit, although with reference to preferred embodiment to invention has been detailed description, those of ordinary skill in the art is to be understood that, can modify to technical scheme of the present invention or equivalent replacement, and not departing from the spirit and scope of technical solution of the present invention, it all should be encompassed in the middle of right of the present invention.
Claims (4)
1. water body can be made to produce a biomembranous microbial preparation, it is characterized in that, the following composition comprised by weight percentage is made:
Complex microorganism preparations 90-92%, enzymatic microorganism 5-8%, brown sugar 2-4%;
Described complex microorganism preparations comprises subtilis, actinomycetes, yeast, enzymatic microorganism, described subtilis living bacteria count is 1,900,000,000/gram, described actinomycetes living bacteria count is 6,000,000/gram, described yeast living bacteria count is 0.5 hundred million/gram.
2. water body can be made as claimed in claim 1 to produce the using method of biomembranous microbial preparation, it is characterized in that, the described complex microorganism preparations prepared is placed in container the water adding 1.5 times of weights, mix latter standing 2 hours thoroughly, after described complex microorganism preparations fully activates, be evenly sprinkled upon among water body.
3. water body can be made as claimed in claim 2 to produce the using method of biomembranous microbial preparation, it is characterized in that, evenly splashed in the water body of required use by described microbial preparation, every mu uses 2.5-3 kilogram, and biofilm development removes microbial film to when will come off from bank or pool wall.
4. water body can be made as claimed in claim 3 to produce the using method of biomembranous microbial preparation, it is characterized in that, add in the water body of required use described water body can be made to produce biomembranous microbial preparation after produce to microbial film before by oxygen delivery equipment to water body oxygenation.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201410382505.9A CN104232510A (en) | 2014-08-06 | 2014-08-06 | Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201410382505.9A CN104232510A (en) | 2014-08-06 | 2014-08-06 | Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation |
Publications (1)
Publication Number | Publication Date |
---|---|
CN104232510A true CN104232510A (en) | 2014-12-24 |
Family
ID=52221420
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201410382505.9A Pending CN104232510A (en) | 2014-08-06 | 2014-08-06 | Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104232510A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US10336636B2 (en) * | 2015-11-02 | 2019-07-02 | BiOWiSH Technologies, Inc. | Methods for reducing evaporative loss from swimming pools |
US10988728B2 (en) | 2013-05-20 | 2021-04-27 | BiOWiSH Technologies, Inc. | Microbial-based waste water treatment compositions and methods of use thereof |
US11116240B2 (en) | 2018-05-29 | 2021-09-14 | BiOWiSH Technologies, Inc. | Compositions and methods for improving survivability of aquatic animals |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101082029A (en) * | 2006-06-01 | 2007-12-05 | 上海泓宝绿色水产科技发展有限公司 | Preparation of water purification bacterium and method for restoring aquaculture environment |
CN101402934A (en) * | 2008-10-30 | 2009-04-08 | 河南省龙腾高科实业有限公司 | Water quality purification bacterium agent from mix fermentation production with multiple bacterials and production method thereof |
CN101544523A (en) * | 2009-04-30 | 2009-09-30 | 谢群英 | Fertilizer with biological ferment and preparation method and use method thereof |
CN101607762A (en) * | 2009-07-09 | 2009-12-23 | 东莞圣源环保科技有限公司 | Ecological restoring method of river water body |
CN101643280A (en) * | 2009-09-02 | 2010-02-10 | 张培举 | Microbial water-purifying agent and preparation method thereof |
CN101993829A (en) * | 2009-08-25 | 2011-03-30 | 吉林师范大学 | Composite microbial agent |
CN103214320A (en) * | 2013-04-18 | 2013-07-24 | 淮安柴米河农业科技发展有限公司 | Soil improvement matrix for alleviating soil continuous cropping obstacles and preparation method thereof |
-
2014
- 2014-08-06 CN CN201410382505.9A patent/CN104232510A/en active Pending
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101082029A (en) * | 2006-06-01 | 2007-12-05 | 上海泓宝绿色水产科技发展有限公司 | Preparation of water purification bacterium and method for restoring aquaculture environment |
CN101402934A (en) * | 2008-10-30 | 2009-04-08 | 河南省龙腾高科实业有限公司 | Water quality purification bacterium agent from mix fermentation production with multiple bacterials and production method thereof |
CN101544523A (en) * | 2009-04-30 | 2009-09-30 | 谢群英 | Fertilizer with biological ferment and preparation method and use method thereof |
CN101607762A (en) * | 2009-07-09 | 2009-12-23 | 东莞圣源环保科技有限公司 | Ecological restoring method of river water body |
CN101993829A (en) * | 2009-08-25 | 2011-03-30 | 吉林师范大学 | Composite microbial agent |
CN101643280A (en) * | 2009-09-02 | 2010-02-10 | 张培举 | Microbial water-purifying agent and preparation method thereof |
CN103214320A (en) * | 2013-04-18 | 2013-07-24 | 淮安柴米河农业科技发展有限公司 | Soil improvement matrix for alleviating soil continuous cropping obstacles and preparation method thereof |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US10988728B2 (en) | 2013-05-20 | 2021-04-27 | BiOWiSH Technologies, Inc. | Microbial-based waste water treatment compositions and methods of use thereof |
US10336636B2 (en) * | 2015-11-02 | 2019-07-02 | BiOWiSH Technologies, Inc. | Methods for reducing evaporative loss from swimming pools |
US11116240B2 (en) | 2018-05-29 | 2021-09-14 | BiOWiSH Technologies, Inc. | Compositions and methods for improving survivability of aquatic animals |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP3095855B1 (en) | Efficient bottom treatment bacillus, composite bottom treatment inoculant prepared using same and applications thereof | |
Lananan et al. | Symbiotic bioremediation of aquaculture wastewater in reducing ammonia and phosphorus utilizing Effective Microorganism (EM-1) and microalgae (Chlorella sp.) | |
Yusoff et al. | Phytoplankton succession in intensive marine shrimp culture ponds treated with a commercial bacterial product | |
Nielsen et al. | Cultivation of Ulva lactuca with manure for simultaneous bioremediation and biomass production | |
Wetzel | Factors influencing photosynthesis and excretion of dissolved organic matter by aquatic macrophytes in hard-water lakes: With 8 figures and 10 tables in the text | |
CN106396112B (en) | A kind of helotisn purifies the composite system of high ammonia nitrogen pig raising biogas slurry in conjunction with biological floating bed technology | |
CN102649936A (en) | Compound microorganism fungicide for improving water quality of culturing water body and preparation method | |
CN103773722B (en) | Salt tolerant also has subtilis and the application thereof of low-temperature biological deamination function | |
CN103205382A (en) | Microbial agent for purifying river wastewater and preparation method of microbial agent | |
CN101723521B (en) | Method for preparing water purification agent for degrading nitrite and ammoniacal nitrogen in aquaculture water body | |
CN105540870B (en) | A kind of lake river regulation composition | |
CN109607818A (en) | A kind of microorganism improver of water quality and preparation method thereof | |
CN104326551B (en) | A kind of Compound Water quality improving agent for aquaculture and preparation method thereof | |
CN105274029B (en) | A kind of Nitrobacter winogradskyi and nitrobacteria-denitrifying bacteria composite bacteria agent and production method and application | |
CN116640702A (en) | Preparation method and application of microbial agent for treating aquaculture wastewater | |
Sorokin | Microbiological aspects of the productivity of coral reefs | |
CN112273218A (en) | Method for indoor culture of composite algae by using nutrient salts | |
CN104232510A (en) | Microbial preparation capable of generating biological membrane in water body and using method of microbial preparation | |
Kong et al. | Control of the harmful alga Microcystis aeruginosa and absorption of nitrogen and phosphorus by Candida utilis | |
CN105481102B (en) | A kind of remodeling method of promoting to a higher rank with microbial cleaning skill upgrading sewage effluents water quality | |
CN104232512A (en) | Compound microorganism preparation for repairing water boy as well as preparation method and application thereof | |
CN110835170A (en) | Compound for degrading pesticide residues in water body and preparation method and application thereof | |
CN108423838B (en) | Microbial preparation for ecological safety water system and preparation method thereof | |
Okomoda et al. | Rearing water quality and zootechnical parameters of Litopenaeus vannamei in rapid Biofloc® and conventional intensive culture system | |
CN109266573B (en) | Fermentation agent and microbial inoculum for treating landfill leachate and reverse osmosis concentrated solution and treatment method |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20141224 |