CN107244749A - It is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof - Google Patents
It is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof Download PDFInfo
- Publication number
- CN107244749A CN107244749A CN201710653856.2A CN201710653856A CN107244749A CN 107244749 A CN107244749 A CN 107244749A CN 201710653856 A CN201710653856 A CN 201710653856A CN 107244749 A CN107244749 A CN 107244749A
- Authority
- CN
- China
- Prior art keywords
- sludge
- biological
- portions
- sewage disposal
- biological sludge
- 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
- 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
- C02F11/00—Treatment of sludge; Devices 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
- C02F3/348—Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
-
- 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
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Biotechnology (AREA)
- Genetics & Genomics (AREA)
- Zoology (AREA)
- Wood Science & Technology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Virology (AREA)
- Biomedical Technology (AREA)
- Tropical Medicine & Parasitology (AREA)
- Medicinal Chemistry (AREA)
- Biochemistry (AREA)
- General Engineering & Computer Science (AREA)
- General Health & Medical Sciences (AREA)
- Treatment Of Sludge (AREA)
Abstract
The invention belongs to sewage disposal bio-synergistic technology and comprehensive utilization of resources field, and in particular to a kind of high-activity biological sludge and preparation method thereof.The biological sludge raw material is sewage disposal plant excess sludge and particular organisms strain, preparation technology cost is low, simple to operate, pollution-free, both solid waste resource reutilization had been realized, while reducing the cost of biological potentiating agent, the input of bioanalysis sewage disposal technology has been reduced.The beneficial effects of the invention are as follows in this kind of biological sludge containing polyP bacteria, except beneficial microbes such as carbon bacterium, nitrococcus, nitrifier, denitrifying bacteriums, with decompose sewage in organic substance, decompose phosphorus, except ammonia nitrogen, except total nitrogen, to reduce effect of COD in sewage, ammonia nitrogen, total nitrogen content.Handle sewage using it, it is possible to resolve the access of the special strain of sewage disposal, and the biological bacteria quantity that increases sharply purpose, and it is simple to operation to add technique, does not produce secondary pollution, promotes the further popularization and application of bioanalysis sewage disposal technology.
Description
Technical field
The present invention relates to technical field of sewage, and in particular to a kind of high-activity biological sludge suitable for sewage disposal
And preparation method thereof.
Background technology
Bio-synergistic technology is screened by directly being added into existing biochemical waste water processing system from nature
For the dominant bacteria of a certain or certain a class of pollutant, to improve the ability of former processing system, reach raising to a certain or
The dominant bacteria of certain a class of pollutant, to improve the ability of former processing system, reaches raising to a certain or a certain class nuisance
The purpose of the removal effect of matter.Biological potentiating agent be the current whole world generally acknowledge it is high in technological content, have a wide range of application, development potentiality is huge
Big sewage disposal preparation, is also to be assert and widelyd popularize by national environmental protection portion《Country encourages the environmental protection skill of development
Art》, it is a kind of green and environmentally friendly new water process preparation.However, biological potentiating agent in the market it is main according to
It is expensive by external import, and independently developed biological potentiating agent domestic in recent years, its price and using effect still can not
The degree that large-scale popularization is used is reached, popularization and application of the bio-synergistic technology in sewage disposal are greatly limit.Therefore design
A kind of new, inexpensive, high activity, the biological potentiating agent of easily domestication and cleaning easy to use are developed, with highly important existing
Sincere justice.
Biological sludge be exactly it is a kind of have cost it is low, it is easy domestication, the new bio synergist of obvious processing effect, its work
Principle is microbial population in the sewage that increases sharply after biological sludge is added in sewage, and having using each component
Machine biochemical reaction, strengthened by colloid chemistry process, chemical reaction process and the oxidizing process of microorganism microbial activity and
Capacity of decomposition, while the stabilization and balance of microbial population system can be kept, maintains sewage disposal system efficient stable and anti-impact
The ability hit.
The preparation process technique of biological sludge is simple to operation, and cost is low, pollution-free, and its primary raw material comes from sewage disposal
Factory's waste sludge, and content of beary metal, total phosphorus content, total nitrogen content, 550 degree and 900 degree burning decrements etc. are carried out to sludge
The measure of project, reaches to choose after standard and utilizes, the problem of to avoid secondary pollution.With biological bacteria after sludge is pre-processed
Kind compound, biological bacteria expands rapidly numerous and reaches certain amount, sludge is had a very high bioactivity, then after processed shaping into
For a kind of new bio synergist of efficient and cheap in sewage disposal system can be added to.
The content of the invention
It is an object of the invention to provide a kind of biological sludge, polyP bacteria is contained in this kind of biological sludge, except carbon bacterium, nitrosation
Both the special strain of sewage disposal had been solved in the beneficial microbes such as bacterium, nitrifier, denitrifying bacterium, the sewage disposal system of input
Access problem, while the dominant bacteria quantity that can increase sharply, lifting autochthonous microorganism flora to the capability of influence of technological fluctuation or
To the degradation capability of some compositions, and then reach the processing intent of improvement water quality.
A further object of the invention is to expand numerous strain method by a kind of sludge, reduces microbial inoculum consumption, when shortening domestication
Between and reduction use cost, with good economic benefit.
A further object of the invention is to realize that solid waste resource Efficient Cycle is utilized, and reduces the cost of biological sludge, finally
Realize low cost, high efficiency, the bioanalysis sewage disposal technology of environmental protection.The primary raw material sludge of this kind of biological sludge is chosen
The indices of sludge and are detected by the sludge of municipal sewage plant's discharge, do not contain heavy metal, total phosphorus content,
Total nitrogen content, 550 degree and 900 degree of burning decrements are determined and met the requirements.
In order to realize object of the present invention and other advantages, the technical solution adopted by the present invention is such.
A kind of high-activity biological sludge suitable for sewage disposal, the living bacteria count that it contains >=2,000,000,000/gram, miscellaneous bacteria rate
≤ 5%, easily domestication, the term of validity are not less than half a year.
A kind of preparation method for preparing described biological sludge, using sewage disposal excess sludge as matrix, expands numerous specific
Strain, comprises the following steps.
Step one:Dispensing.
40-95 parts of sludge, 0-20 portions of rice brans, 0-25 portions of wheat bran, 1-10 portions of careless carbon, 4-10 portions of nutritional agents are disappeared respectively
Poison sterilizing, is then uniformly mixed, and obtains cultivating mud.
Step 2:Inoculation.
Selected strain is added to the water and stirred, biological bacteria dilution is obtained, 1-30 parts of biological bacteria dilutions are sprayed
Spill in 60-95 parts of steps(1)On the culture mud of gained, it is thoroughly mixed uniformly, obtains the primary containing particular organisms bacterium dirty
Mud.
Step 3:Biological bacteria expands numerous.
By step(2)The preliminary sludge of middle gained banks up fermentation in fermentation tank, after fermentation temperature rises to steadily, enters
Row roller is overturned, and continues to bank up fermentation, after temperature rises to steadily again, obtains biological sludge finished product, fermentation time typically exists
12-48 hours.
Step 4:Discharge, dry.
Biological sludge is spread, stirred, is dried, airing.
Step 5:Packaging, storage.
Dried biological sludge, is packed by quantitative use laminating adhesive woven bag, is stored in health, shady and cool, dry, ventilation
Place.
Preferably, the step(1)In sludge refer in particular to municipal sewage plant discharge sludge, do not contain a huge sum of money
Category, total phosphorus content, total nitrogen content, 550 degree and 900 degree of burning decrements are determined and met the requirements.
Preferably, the step(1)In sterilization refer to utilize ultraviolet radioactive method, by sludge, rice bran, wheat bran,
The materials such as careless carbon, sterilize 2-4 hours, sterilization rate reaches 99% under ultraviolet lighting.
Preferably, the step(1)In the nutritional agents biological bacteria breeding needed for nutriment.
Preferably, the step(3)In strain include polyP bacteria, except carbon bacterium, nitrococcus, nitrifier, denitrification
The functional microbial strain such as bacterium.
Compared with prior art, beneficial effects of the present invention are as follows.
(1)Huge containing effective number of viable in this kind of biological sludge, they have the organic substance decomposed in sewage, decomposed
Phosphorus, except ammonia nitrogen, except total nitrogen, to reduce the content of COD in sewage, ammonia nitrogen, total nitrogen, using its handle sewage, the sewage after processing
Discharge quality complies fully with national standard, and this kind of biological sludge is easily tamed, biological strong, adds technique simple to operation.
(2)Biological sludge is compared with existing biological potentiating agent, and biological sludge can solve the access of the special strain of sewage disposal,
Largely add to supplement microorganism species quantity in sewage disposal system rapidly, and microbial ecosystem can be kept more permanent
Balance and stably, enhance the oxidative decomposition capacity to organic matter.
(3)According to sewage disposal demand, add after the biological sludge containing different strain, can be achieved to be directed in the short time
Property removal effect, improve the clearance of specific a certain pollutant.
(4)The speed of the microorganism in domestication biochemistry pool is greatly improved, strengthens its poison resistance, improving its decomposition oxidation has
The ability of malicious organic matter.
(5)Reduce the use cost of biological potentiating agent technology.The primary raw material of biological sludge is using sewage treatment plant
Waste sludge, by adding, a small amount of Spawn incubation goes out the biological flora containing comparatively high amts, drops the cost of biological potentiating agent
Low 60-80%.The solid waste for realizing sewage treatment plant's waste sludge simultaneously is recycled, and meets the development reason of national green environmental protection
Read.
(6)Technique is simple, cost is low, environmental protection, do not produce secondary pollution.
Brief description of the drawings
Fig. 1 is the preparation method process chart of the present invention.
Embodiment
Below in conjunction with accompanying drawing, the invention will be further described.
Process chart as shown in Fig. 1, a kind of high-activity biological sludge suitable for sewage disposal, what it contained has
Effect viable count >=2,000,000,000/gram, miscellaneous bacteria rate≤5%, easily domestication, the term of validity be not less than half a year.
Embodiment one.
A kind of preparation method for preparing described biological potentiating agent, comprises the following steps, and comes by production 1000Kg amount
Prepare biological sludge 1#.
(1)Dispensing.
700kg sludge, 100kg rice brans, the careless carbon of 50kg, 50kg nutritional agents are carried out disinfection sterilizing respectively, then stirring is mixed
Close uniform, obtain culture mud 1#.The method for disinfection and sterilization that each raw material is used is to use ultraviolet lighting method.
(2)Inoculation.
Selected denitrification strain is added to the water and stirred, denitrifying bacterium dilution is obtained, by 100kg denitrifying bacteriums
Dilution is sprayed on 900kg(1)On the culture mud 1# of gained, it is thoroughly mixed uniformly, obtains the primary containing denitrifying bacterium
Biological sludge 1#.
Sprinkling process need to uniformly be carried out in the state of stirring, accomplish that bacterium solution and culture mud 1# are fully merged.
(3)Biological bacteria expands numerous.
By step(2)The preliminary sludge 1# of middle gained banks up fermentation, heap thickness 30-50cm in fermentation tank(Summer can be thin, the winter
Ji Kehou), after fermentation temperature rises to steadily, roller overturning is carried out, continues to bank up fermentation, when temperature rises to steadily again
Afterwards, biological sludge 1# finished products are obtained, fermentation time is typically at 36 hours.
When temperature rise is very fast, need duty to stir, ripe biological sludge has a peat-reek, very loose, softness, it is tacky or
There is filiform to lump etc., if it find that stink, then by living contaminants, it is impossible to as being continuing with.
(4)Discharge, dry.
The biological sludge 1# of gained is spread, stirred, is dried, airing.Now favourable biological sludge is detected, surveys effective
Bacteria containing amount and miscellaneous bacteria rate, its product index is:Living bacteria count >=2,000,000,000/gram, miscellaneous bacteria rate≤5%.
(5)Packaging, storage.
Dried biological sludge 1#, is packed or barreled by quantitative use laminating adhesive woven bag, be stored in health, it is shady and cool,
Dry, ventilation, never exposes to the sun and rain.
Claims (4)
1. it is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof, it is characterised in that to comprise the following steps
:
Step one:Dispensing
40-95 parts of sludge, 0-20 portions of rice brans, 0-25 portions of wheat bran, 1-10 portions of careless carbon, 4-10 portions of nutritional agents are carried out disinfection go out respectively
Bacterium, is then uniformly mixed, and obtains cultivating mud;
Step 2:Inoculation
Selected strain is added to the water and stirred, biological bacteria dilution is obtained, 1-30 parts of biological bacteria dilutions are sprayed on
60-95 parts of steps(1)On the culture mud of gained, it is thoroughly mixed uniformly, obtains the preliminary sludge containing particular organisms bacterium;
Step 3:Biological bacteria expands numerous
By step(2)The preliminary sludge of middle gained banks up fermentation in fermentation tank, after fermentation temperature rises to steadily, is rolled
Dynamic formula is overturned, and continues to bank up fermentation, after temperature rises to steadily again, obtains biological sludge finished product, fermentation time is typically in 12-48
Hour;
Step 4:Discharge, dry
Biological sludge is spread, stirred, is dried, airing;
Step 5:Packaging, storage
Dried biological sludge, is packed by quantitative use laminating adhesive woven bag, is stored in health, shady and cool, dry, ventilation.
2. high-activity biological sludge as claimed in claim 1 and preparation method thereof, it is characterized in that, the raw material is by following weight
The composition of part is mixed:40-95 portions of sludge, 0-20 portions of rice brans, 0-25 portions of wheat bran, 1-10 portions of careless carbon, 4-10 portions of nutritional agents.
3. high-activity biological sludge as claimed in claim 1 and preparation method thereof, it is characterized in that, in the step 2, according to
1-30 parts of biological bacteria dilutions are sprayed on 60-95 parts of culture mud and stirred.
4. high-activity biological sludge as claimed in claim 1 and preparation method thereof, it is characterized in that, in the step 3, sludge
It is 12-48 hours that fermentation fermentation time is banked up in fermentation tank.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710653856.2A CN107244749A (en) | 2017-08-03 | 2017-08-03 | It is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710653856.2A CN107244749A (en) | 2017-08-03 | 2017-08-03 | It is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107244749A true CN107244749A (en) | 2017-10-13 |
Family
ID=60012217
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710653856.2A Pending CN107244749A (en) | 2017-08-03 | 2017-08-03 | It is a kind of suitable for high-activity biological sludge of sewage disposal and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107244749A (en) |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101538173A (en) * | 2009-05-08 | 2009-09-23 | 北京化工大学 | Method for producing microbial compound bacterial fertilizer |
CN105462880A (en) * | 2015-12-10 | 2016-04-06 | 南平正大欧瑞信生物科技开发有限公司 | Preparation method of sewage processing complex bacterium |
-
2017
- 2017-08-03 CN CN201710653856.2A patent/CN107244749A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101538173A (en) * | 2009-05-08 | 2009-09-23 | 北京化工大学 | Method for producing microbial compound bacterial fertilizer |
CN105462880A (en) * | 2015-12-10 | 2016-04-06 | 南平正大欧瑞信生物科技开发有限公司 | Preparation method of sewage processing complex bacterium |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Zhao et al. | Effect of enriched thermotolerant nitrifying bacteria inoculation on reducing nitrogen loss during sewage sludge composting | |
Chang et al. | Dynamics of microbial diversity during the composting of agricultural straw | |
CN101555169B (en) | Scale high-speed composting treatment method of organic wastes | |
CN100425690C (en) | Fast harmless biological treating process of animal excrement and manure water | |
Fan et al. | Effects of compost characteristics on nutrient retention and simultaneous pollutant immobilization and degradation during co-composting process | |
CN104370582B (en) | A kind of organic waste odorless aerobic compost method | |
Frąc et al. | Methane fermentation process for utilization of organic waste. | |
CN102010109A (en) | Application of bio-enzyme catalysis in residual sludge treatment | |
Manyi-Loh et al. | Microbial anaerobic digestion: process dynamics and implications from the renewable energy, environmental and agronomy perspectives | |
CN105000676B (en) | A kind of processing method of amylum wastewater | |
CN104150684A (en) | Aquaculture wastewater treatment process | |
Li et al. | Changes in microbial community and methanogenesis during high-solid anaerobic digestion of ensiled corn stover | |
CN101580412A (en) | Low-temperature aerobic composting method for organic solid waste | |
Iqbal et al. | Role of decomposers in agricultural waste management | |
Soo et al. | Recent advancements in the treatment of palm oil mill effluent (POME) using anaerobic biofilm reactors: challenges and future perspectives | |
CN103664255A (en) | Organic waste facultative aerobic fermentation composting treatment process | |
CN102344319A (en) | Microbial organic fertilizer produced by papermaking sludge and producing method thereof | |
CN102206105A (en) | Compost treatment method for food residues | |
CN108203165A (en) | A kind of complex enzyme biochemical water purification agent and preparation method thereof | |
CN101921709B (en) | Composite high-efficiency microorganism preparation for synergy of sewage treatment plant and synergistic process | |
CN103641593B (en) | Method for preparing garden media from biogas slurry | |
Chen et al. | Strategy to strengthen rural domestic waste composting at low temperature: choice of ventilation condition | |
CN104774057B (en) | For canopy formula fermentation organic fertilizer cycle deodorizing method | |
CN103553288B (en) | Method for preparing water treatment biological activity accelerant from winery wastewater treatment sludge | |
CN102964176B (en) | Biological organic fertilizer and preparation method thereof |
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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20171013 |