CN108993130A - A kind of method of pig manure stink degradation - Google Patents
A kind of method of pig manure stink degradation Download PDFInfo
- Publication number
- CN108993130A CN108993130A CN201810972266.0A CN201810972266A CN108993130A CN 108993130 A CN108993130 A CN 108993130A CN 201810972266 A CN201810972266 A CN 201810972266A CN 108993130 A CN108993130 A CN 108993130A
- Authority
- CN
- China
- Prior art keywords
- parts
- pig manure
- degradation
- lactic acid
- powder
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/84—Biological processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
- B01D53/58—Ammonia
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0266—Other waste gases from animal farms
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Molecular Biology (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention discloses a kind of methods of pig manure stink degradation, and method is: periodically spraying a kind of deodorization degradation reagent containing microbial bacterial and adsorbent according to demand.The composition of reagent are as follows: 0.1-6 parts of Rhodopseudomonas palustris, 0.1-5 parts of thiobacillus denitrificans, 0.1-3 parts of lactobacillus acidophilus, 0.1-10 parts of lactic acid bacteria, 0.1-2 parts of Bacillus pasteurii, 0.1-3 parts of streptomyces microflavus, 1-40 parts of glucose, 1-10 parts of agar powder, 0.1-5 parts of ferric sulfate, 0.1-3 parts of potassium nitrate, 10-60 parts of water, 0.01-1 parts of bergamot oil, 1-20 parts of activated carbon powder, 0.1-10 parts of talcum powder.This microbial deodorant degradation reagent can be adsorbed effectively and decompose odorous gas, the air qualities of purifying pig-raising field such as sulfide and nitride that pig manure fermentation generates and improve the economic value on pig farm.
Description
Technical field
The invention belongs to a kind of methods that livestock and poultry cultivation method and technology field more particularly to pig manure stink are degraded.
Background technique
With the fast development of pig industry, how to handle pig manure is the main bugbear that numerous pig farms face, especially
The most important thing that the bad-smell problem that a large amount of pig manure generates even more needs to solve.Often contain some harmful objects in stink
Matter, to influence the healthy growth of pig and the health of people.Such as, pig manure can produce more NH in the case where aerobic3、
H2S, the pernicious gases such as methyl mercaptan and dimethyl disulfide (methyl mercaptan oxide), while under the conditions of certain high temperature anaerobic, H2S
Yield can significantly improve, these gases not only negative unhealthy, but also taste is pungent, seriously affects the air on pig farm
Quality.Meanwhile NH3A large amount of volatilizations, will lead to the loss of nitrogenous fertilizer in pig manure, reduce the economic value of pig manure.
The method of current main deodorization has: physical method, chemical method or bioanalysis etc..Physical method be by masking,
The method of dilution or absorption reduces smell to the susceptibility of gas, chemistry of this method without fundamentally change stink
Property, process range and capacity are limited.Chemical method is by adding certain chemical reagent to be allowed to that chemistry occurs with odorant
Reaction changes its chemical structure to destroy it and cause smelly group, is allowed to be changed into odorless or the lower substance of stink.This side
Method, although stink substances can effectively be gone out, cumbersome, energy consumption is high, involves great expense, is not suitable for large-scale application.
Bioanalysis needs the stink substances that will volatilize out to be dissolved in water, then by abilities such as the absorption of microorganism and degradations, effectively
Decomposition smell substance achievees the purpose that deodorization is degraded.This deodorizing methods has strong applicability, and use scope is extensive, deodorization effect
The strong advantage of fruit persistence, but the periodicity of its bacterial fermentation is long, therefore effect is slower.
In conclusion problem of the existing technology is: pig manure is easy to produce vulcanization during windrow or fermentation
The volatile malodors gas such as object or nitride, seriously affects the air quality on pig farm, thus influence pig healthy growth and
There is very big environmental security in the health of people.The a large amount of NH volatilized in pig manure simultaneously3It will cause a large amount of of nitrogenous fertilizer
It is lost, influences the economic value of pig manure.Existing a variety of deodorization technologies respectively have advantage and disadvantage, realize the ability and effect of deodorization degradation
It is limited.
Summary of the invention
(1) the technical issues of solving
In view of the deficiencies of the prior art, it the present invention provides a kind of method of pig manure stink degradation, can effectively adsorb
And pig manure of degrading is easy to produce the volatile malodors gas such as sulfide or nitride during windrow or fermentation.This hair
The pig manure stink biodegrading process of bright offer, effect is lasting, and use scope is wide and economic and environment-friendly, can be high-efficient, effectively reduces pig manure
The problems such as what loss of nitrogenous fertilizer of the air pollution of generation, the economic value on pig farm can be greatly improved.
(2) technical solution
In order to achieve the above object, the present invention is achieved by the following technical programs: a kind of method of pig manure stink degradation,
A kind of deodorization degradation reagent containing microbial bacterial and adsorbent, the composition of reagent are as follows: natural pond are periodically sprayed according to demand
Damp red pseudomonas 0.1-6 parts, 0.1-5 parts of thiobacillus denitrificans, 0.1-3 parts of lactobacillus acidophilus, 0.1-10 parts of lactic acid bacteria, Ba Shiya
0.1-2 parts of spore bacillus, 0.1-3 parts of streptomyces microflavus, 1-40 parts of glucose, 1-10 parts of agar powder, 0.1-5 parts of ferric sulfate, nitric acid
0.1-3 parts of potassium, 30-100 parts of water, 0.01-1 parts of bergamot oil, 1-20 parts of activated carbon powder, 0.1-10 parts of talcum powder.
Preferably, the reagent set becomes: 0.1 part of Rhodopseudomonas palustris, 0.1 part of thiobacillus denitrificans, acidophilus cream bar
0.1 part of bacterium, 0.1 part of lactic acid bacteria, 0.1 part of Bacillus pasteurii, 0.1 part of streptomyces microflavus, 1 part of glucose, 1 part of agar powder, sulphur
0.1 part of sour iron, 0.1 part of potassium nitrate, 30 parts of water, 0.01 part of bergamot oil, 1 part of activated carbon powder, 0.1 part of talcum powder.
Preferably, the reagent set becomes: 3 parts of Rhodopseudomonas palustris, 2.5 parts of thiobacillus denitrificans, lactobacillus acidophilus
1.5 parts, 5 parts of lactic acid bacteria, 1 part of Bacillus pasteurii, 1.5 parts of streptomyces microflavus, 20 parts of glucose, 5 parts of agar powder, ferric sulfate
2.5 parts, 1.5 parts of potassium nitrate, 65 parts of water, 0.5 part of bergamot oil, 10 parts of activated carbon powder, 5 parts of talcum powder.
Preferably, the reagent set becomes: 6 parts of Rhodopseudomonas palustris, 5 parts of thiobacillus denitrificans, lactobacillus acidophilus 3
Part, 10 parts of lactic acid bacteria, 2 parts of Bacillus pasteurii, 3 parts of streptomyces microflavus, 40 parts of glucose, 10 parts of agar powder, 5 parts of ferric sulfate,
3 parts of potassium nitrate, 100 parts of water, 1 part of bergamot oil, 20 parts of activated carbon powder, 10 parts of talcum powder.
Further, the Rhodopseudomonas palustris, thiobacillus denitrificans, lactobacillus acidophilus, lactic acid bacteria, Pasteur's gemma bar
Bacterium, streptomyces microflavus are microorganism stoste, effective viable bacteria number in stoste be respectively Rhodopseudomonas palustris 1-10 hundred million/
Ml, hundred million/ml of thiobacillus denitrificans 0.1-5, hundred million/ml of lactobacillus acidophilus 1-6, hundred million/ml of lactic acid bacteria 1-10, Bacillus pasteurii
Hundred million 0.1-3, streptomyces microflavus 0.1-5/ml.
Further, the sprinkling period is 4-12 times/day, and each fountain height is 0.5-5L/m2。
Preferably, the sprinkling period is 4 times/day, and each fountain height is 0.5L/m2。
Preferably, the sprinkling period is 8 times/day, and each fountain height is 2.5L/m2。
Preferably, the sprinkling period is 12 times/day, and each fountain height is 5L/m2。
(3) beneficial effect
The present invention provides a kind of pig manure stink degradation method, have it is following the utility model has the advantages that
The present invention first passes through the mode of sprinkling, stink substances efficient liquefaction in the pig manure that will volatilize out, and utilizes active carbon
Powder and talcum powder reduce the volatilization of stink substances effectively by stink substances adsorption and sedimentation；Then, pass through micro- life of multiple functions
Object bacterium colony effectively absorbs and decomposes the stink substances of its pig manure generation；Pig manure stink biodegrading process provided by the invention, effect
Persistently, use scope is wide and economic and environment-friendly, can efficiently and rapidly remove the stink substances volatilized in pig manure, reduces pig manure and produces
Raw air pollution substantially increases the economic value on pig farm.
Specific embodiment
In order to make the objectives, technical solutions, and advantages of the present invention clearer, with reference to embodiments, to the present invention
It is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, it is not used to
Limit the present invention.
The present invention provides a kind of technical solution: a kind of method of pig manure stink degradation periodically sprays one according to demand
Deodorization degradation reagent of the kind containing microbial bacterial and adsorbent, the composition of reagent are as follows: 0.1-6 parts of Rhodopseudomonas palustris takes off
0.1-5 parts of nitrogen Thiobacillus, 0.1-3 parts of lactobacillus acidophilus, 0.1-10 parts of lactic acid bacteria, 0.1-2 parts of Bacillus pasteurii, thin yellow strepto-
0.1-3 parts of bacterium, 1-40 parts of glucose, 1-10 parts of agar powder, 0.1-5 parts of ferric sulfate, 0.1-3 parts of potassium nitrate, 30-100 parts of water, perfume
0.01-1 parts of lemon oil, 1-20 parts of activated carbon powder, 0.1-10 parts of talcum powder.
Preferably, the reagent set becomes: 0.1 part of Rhodopseudomonas palustris, 0.1 part of thiobacillus denitrificans, acidophilus cream bar
0.1 part of bacterium, 0.1 part of lactic acid bacteria, 0.1 part of Bacillus pasteurii, 0.1 part of streptomyces microflavus, 1 part of glucose, 1 part of agar powder, sulphur
0.1 part of sour iron, 0.1 part of potassium nitrate, 30 parts of water, 0.01 part of bergamot oil, 1 part of activated carbon powder, 0.1 part of talcum powder.
Preferably, the reagent set becomes: 3 parts of Rhodopseudomonas palustris, 2.5 parts of thiobacillus denitrificans, lactobacillus acidophilus
1.5 parts, 5 parts of lactic acid bacteria, 1 part of Bacillus pasteurii, 1.5 parts of streptomyces microflavus, 20 parts of glucose, 5 parts of agar powder, ferric sulfate
2.5 parts, 1.5 parts of potassium nitrate, 65 parts of water, 0.5 part of bergamot oil, 10 parts of activated carbon powder, 5 parts of talcum powder.
Preferably, the reagent set becomes: 6 parts of Rhodopseudomonas palustris, 5 parts of thiobacillus denitrificans, lactobacillus acidophilus 3
Part, 10 parts of lactic acid bacteria, 2 parts of Bacillus pasteurii, 3 parts of streptomyces microflavus, 40 parts of glucose, 10 parts of agar powder, 5 parts of ferric sulfate,
3 parts of potassium nitrate, 100 parts of water, 1 part of bergamot oil, 20 parts of activated carbon powder, 10 parts of talcum powder.
Further, the Rhodopseudomonas palustris, thiobacillus denitrificans, lactobacillus acidophilus, lactic acid bacteria, Pasteur's gemma bar
Bacterium, streptomyces microflavus are microorganism stoste, effective viable bacteria number in stoste be respectively Rhodopseudomonas palustris 1-10 hundred million/
Ml, hundred million/ml of thiobacillus denitrificans 0.1-5, hundred million/ml of lactobacillus acidophilus 1-6, hundred million/ml of lactic acid bacteria 1-10, Bacillus pasteurii
Hundred million 0.1-3, streptomyces microflavus 0.1-5/ml.
Further, the sprinkling period is 4-12 times/day, and each fountain height is 0.5-5L/m2。
Technical method of the invention is further described below.
Embodiment 1
The composition of reagent are as follows: 3 parts of Rhodopseudomonas palustris, 2 parts of thiobacillus denitrificans, 1 part of lactobacillus acidophilus, 4 parts of lactic acid bacteria,
0.3 part of Bacillus pasteurii, 0.1 part of streptomyces microflavus, 10 parts of glucose, 5 parts of agar powder, 0.1 part of ferric sulfate, potassium nitrate 0.3
Part, 70 parts of water, 0.05 part of bergamot oil, 10 parts of activated carbon powder, 3 parts of talcum powder.
Wherein, effective viable bacteria number in stoste is respectively 300,000,000/ml of Rhodopseudomonas palustris, thiobacillus denitrificans 100,000,000
300,000,000 a/ml, 300,000,000/ml of lactobacillus acidophilus, 400,000,000/ml of lactic acid bacteria, Bacillus pasteurii 1, streptomyces microflavus/ml.
Spraying the period is 8 times/day, and each fountain height is 1L/m2。
Embodiment 2
The composition of reagent are as follows: 4 parts of Rhodopseudomonas palustris, 3 parts of thiobacillus denitrificans, 2 parts of lactobacillus acidophilus, 5 parts of lactic acid bacteria,
0.7 part of Bacillus pasteurii, 0.2 part of streptomyces microflavus, 10 parts of glucose, 5 parts of agar powder, 0.1 part of ferric sulfate, potassium nitrate 0.3
Part, 70 parts of water, 0.05 part of bergamot oil, 10 parts of activated carbon powder, 3 parts of talcum powder.
Wherein, effective viable bacteria number in stoste is respectively 300,000,000/ml of Rhodopseudomonas palustris, thiobacillus denitrificans 100,000,000
300,000,000 a/ml, 300,000,000/ml of lactobacillus acidophilus, 400,000,000/ml of lactic acid bacteria, Bacillus pasteurii 1, streptomyces microflavus/ml.
Spraying the period is 10 times/day, and each fountain height is 1L/m2。
Embodiment 3
The composition of reagent are as follows: 4 parts of Rhodopseudomonas palustris, 3 parts of thiobacillus denitrificans, 2 parts of lactobacillus acidophilus, 5 parts of lactic acid bacteria,
0.7 part of Bacillus pasteurii, 0.2 part of streptomyces microflavus, 20 parts of glucose, 5 parts of agar powder, 0.5 part of ferric sulfate, potassium nitrate 0.3
Part, 100 parts of water, 0.09 part of bergamot oil, 15 parts of activated carbon powder, 2 parts of talcum powder.
Wherein, effective viable bacteria number in stoste is respectively 300,000,000/ml of Rhodopseudomonas palustris, thiobacillus denitrificans 100,000,000
300,000,000 a/ml, 300,000,000/ml of lactobacillus acidophilus, 500,000,000/ml of lactic acid bacteria, Bacillus pasteurii 1, streptomyces microflavus/ml.
Spraying the period is 5 times/day, and each fountain height is 2L/m2。
Embodiment 4
The composition of reagent are as follows: 4 parts of Rhodopseudomonas palustris, 3 parts of thiobacillus denitrificans, 2 parts of lactobacillus acidophilus, 5 parts of lactic acid bacteria,
0.7 part of Bacillus pasteurii, 0.2 part of streptomyces microflavus, 20 parts of glucose, 5 parts of agar powder, 0.5 part of ferric sulfate, potassium nitrate 0.3
Part, 100 parts of water, 0.09 part of bergamot oil, 15 parts of activated carbon powder, 2 parts of talcum powder.
Wherein, effective viable bacteria number in stoste is respectively 300,000,000/ml of Rhodopseudomonas palustris, thiobacillus denitrificans 100,000,000
300,000,000 a/ml, 100,000,000/ml of lactobacillus acidophilus, 500,000,000/ml of lactic acid bacteria, Bacillus pasteurii 1, streptomyces microflavus/ml.
Spraying the period is 12 times/day, and each fountain height is 0.5L/m2。
In summary: the present invention first passes through the mode of sprinkling, stink substances efficient liquefaction in the pig manure that will volatilize out, and benefit
With active powdered carbon and talcum powder effectively by stink substances adsorption and sedimentation, the volatilization of stink substances is reduced；Then, pass through a variety of function
The microbe colony of energy effectively absorbs and decomposes the stink substances of its pig manure generation；Pig manure stink degradation provided by the invention
Method, effect is lasting, and use scope is wide and economic and environment-friendly, can efficiently and rapidly remove the stink substances volatilized in pig manure,
The air pollution that pig manure generates is reduced, the economic value on pig farm is substantially increased.
The foregoing is merely illustrative of the preferred embodiments of the present invention, is not intended to limit the invention, all in essence of the invention
Made any modifications, equivalent replacements, and improvements etc., should all be included in the protection scope of the present invention within mind and principle.
Claims (6)
1. a kind of method of pig manure stink degradation, which is characterized in that periodically spray according to demand a kind of thin containing microorganism
The deodorization degradation reagent of bacterium and adsorbent, the composition of reagent are as follows: 0.1-6 parts of Rhodopseudomonas palustris, thiobacillus denitrificans 0.1-5
Part, 0.1-3 parts of lactobacillus acidophilus, 0.1-10 parts of lactic acid bacteria, 0.1-2 parts of Bacillus pasteurii, 0.1-3 parts of streptomyces microflavus, Portugal
1-40 parts of grape sugar, 1-10 parts of agar powder, 0.1-5 parts of ferric sulfate, 0.1-3 parts of potassium nitrate, 30-100 parts of water, bergamot oil 0.01-1
Part, 1-20 parts of activated carbon powder, 0.1-10 parts of talcum powder.
2. a kind of method of pig manure stink degradation according to claim 1, it is characterised in that: the reagent set becomes:
0.1 part of Rhodopseudomonas palustris, 0.1 part of thiobacillus denitrificans, 0.1 part of lactobacillus acidophilus, 0.1 part of lactic acid bacteria, Bacillus pasteurii
0.1 part, 0.1 part of streptomyces microflavus, 1 part of glucose, 1 part of agar powder, 0.1 part of ferric sulfate, 0.1 part of potassium nitrate, 30 parts of water, fragrant lemon
Lemon oil 0.01 part, 1 part of activated carbon powder, 0.1 part of talcum powder.
3. a kind of method of pig manure stink degradation according to claim 1, it is characterised in that: the reagent set becomes:
3 parts of Rhodopseudomonas palustris, 2.5 parts of thiobacillus denitrificans, 1.5 parts of lactobacillus acidophilus, 5 parts of lactic acid bacteria, 1 part of Bacillus pasteurii,
1.5 parts of streptomyces microflavus, 20 parts of glucose, 5 parts of agar powder, 2.5 parts of ferric sulfate, 1.5 parts of potassium nitrate, 65 parts of water, bergamot oil
0.5 part, 10 parts of activated carbon powder, 5 parts of talcum powder.
4. a kind of method of pig manure stink degradation according to claim 1, it is characterised in that: the reagent set becomes:
6 parts of Rhodopseudomonas palustris, 5 parts of thiobacillus denitrificans, 3 parts of lactobacillus acidophilus, 10 parts of lactic acid bacteria, 2 parts of Bacillus pasteurii, thin Huang
3 parts of streptomycete, 40 parts of glucose, 10 parts of agar powder, 5 parts of ferric sulfate, 3 parts of potassium nitrate, 100 parts of water, 1 part of bergamot oil, activity
20 parts of carbon dust, 10 parts of talcum powder.
5. a kind of method of pig manure stink degradation according to any one of claims 1-4, it is characterised in that: the natural pond
Damp red pseudomonas, thiobacillus denitrificans, lactobacillus acidophilus, lactic acid bacteria, Bacillus pasteurii, streptomyces microflavus are that microorganism is former
Liquid, effective viable bacteria number in stoste be respectively hundred million/ml of Rhodopseudomonas palustris 1-10, thiobacillus denitrificans 0.1-5 hundred million/
Ml, hundred million/ml of lactobacillus acidophilus 1-6, hundred million/ml of lactic acid bacteria 1-10, Bacillus pasteurii 0.1-3, streptomyces microflavus 0.1-5 hundred million
A/ml.
6. a kind of method of pig manure stink degradation according to claim 1, it is characterised in that: the sprinkling period is 4-
12 times/day, each fountain height is 0.5-5L/m2。
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810972266.0A CN108993130A (en) | 2018-08-24 | 2018-08-24 | A kind of method of pig manure stink degradation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810972266.0A CN108993130A (en) | 2018-08-24 | 2018-08-24 | A kind of method of pig manure stink degradation |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108993130A true CN108993130A (en) | 2018-12-14 |
Family
ID=64592204
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810972266.0A Pending CN108993130A (en) | 2018-08-24 | 2018-08-24 | A kind of method of pig manure stink degradation |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108993130A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109364737A (en) * | 2018-12-27 | 2019-02-22 | 黄河三角洲京博化工研究院有限公司 | A kind of compound deodorizer |
| CN109897808A (en) * | 2019-04-23 | 2019-06-18 | 周宁县生隆科技养殖有限公司 | A kind of fermentation bed for pig raising fermenting agent |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102247611A (en) * | 2011-07-07 | 2011-11-23 | 贵州大学 | Microorganism deodorant and preparation method thereof |
| CN103540539A (en) * | 2013-09-27 | 2014-01-29 | 中国科学院成都生物研究所 | Microbial deodorizing microbial inoculum as well as preparation method and application thereof |
| CN105174491A (en) * | 2015-09-25 | 2015-12-23 | 南京润中生物技术有限公司 | Microbial preparation for water deodorization and preparation method and application thereof |
-
2018
- 2018-08-24 CN CN201810972266.0A patent/CN108993130A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102247611A (en) * | 2011-07-07 | 2011-11-23 | 贵州大学 | Microorganism deodorant and preparation method thereof |
| CN103540539A (en) * | 2013-09-27 | 2014-01-29 | 中国科学院成都生物研究所 | Microbial deodorizing microbial inoculum as well as preparation method and application thereof |
| CN105174491A (en) * | 2015-09-25 | 2015-12-23 | 南京润中生物技术有限公司 | Microbial preparation for water deodorization and preparation method and application thereof |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109364737A (en) * | 2018-12-27 | 2019-02-22 | 黄河三角洲京博化工研究院有限公司 | A kind of compound deodorizer |
| CN109897808A (en) * | 2019-04-23 | 2019-06-18 | 周宁县生隆科技养殖有限公司 | A kind of fermentation bed for pig raising fermenting agent |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| Gutarowska et al. | Removal of odorous compounds from poultry manure by microorganisms on perlite–bentonite carrier | |
| CN102258796A (en) | Microbial deodorant and preparation method thereof | |
| CN105536509A (en) | Plant extract and microbe composite deodorant | |
| Matusiak et al. | The use of Yucca schidigera and microbial preparation for poultry manure deodorization and hygienization | |
| CN110643535B (en) | Composite microbial deodorant, preparation method and application | |
| CN103468619B (en) | A kind of microorganism formulation purifying air | |
| CN107164284A (en) | A kind of deodorizing microorganism microbial inoculum and preparation method thereof | |
| CN103463654B (en) | A method of producing deodorant microbial agent | |
| CN101954105A (en) | Method for removing odor of feces and urine of animals and poultry through oxidation | |
| CN110358699A (en) | A kind of complex microorganism deodorizing microorganism and the preparation method and application thereof | |
| CN108993130A (en) | A kind of method of pig manure stink degradation | |
| CN109876644A (en) | A kind of biological deodorant and the preparation method and application thereof | |
| CN101352578A (en) | High-efficient deodorant solution for malodorous gas of consumer waste and preparation method thereof | |
| CN104353352B (en) | A kind of vegetative microorganism liquid for deodorization and production method | |
| CN109364737A (en) | A kind of compound deodorizer | |
| CN107243251A (en) | Microbial deoderizer containing saccharomycete | |
| CN109092048A (en) | Microbiocidal deodorant | |
| CN113736686B (en) | Microbial deodorant for desulfurizing and deaminizing and preparation method thereof | |
| CN108611301B (en) | Composite biological deodorant and preparation method thereof | |
| CN110102177A (en) | A kind of technique purifying slurry-spraying pelletizing flue gas | |
| CN109971650A (en) | It is a kind of for removing the biological agent of slurry-spraying pelletizing tail gas peculiar smell | |
| CN111909865A (en) | Compound microbial preparation for air deodorization and application thereof | |
| CN112675694A (en) | Efficient biological deodorant | |
| CN112522159A (en) | Microbial compound microbial inoculum for treating peculiar smell of garbage throwing point | |
| CN102836454A (en) | Compound biological deodorant solution used in refuse landfills and refuse transfer stations |
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: 20181214 |