CN102649603A - High-activity and high-efficiency solid biological substrate-improving granule - Google Patents
High-activity and high-efficiency solid biological substrate-improving granule Download PDFInfo
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- CN102649603A CN102649603A CN2011100441994A CN201110044199A CN102649603A CN 102649603 A CN102649603 A CN 102649603A CN 2011100441994 A CN2011100441994 A CN 2011100441994A CN 201110044199 A CN201110044199 A CN 201110044199A CN 102649603 A CN102649603 A CN 102649603A
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- subtilis
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- denitrifying bacterium
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Abstract
The invention discloses a high-activity and high-efficiency solid biological substrate-improving granule which comprises bacillus subtilis, denitrifying bacteria, clay, synergistic agents and wheat bran, and is characterized in that according to proportion by weight, 85 to 88 percent of clay, 1 to 2 percent of molasses, 1 to 2 percent of wheat bran, and 8 to 10 percent of bacillus subtilis and denitrifying bacteria are mixed to prepare a granular medicament. The high-activity and high-efficiency solid biological substrate-improving granule is a new composite microbial preparation design for excessive organic matters and high-content toxic substances such as nitrite, ammonia nitrogen, hydrogen sulfide and the like in aquaculture water, strains are domesticated and modified, an advanced production technology is adopted, and the activity is high and the marked effects are quick; and the product is made into a granule form through a special formula, and is rapidly dispersed within 5 minutes in the water, and can ensure that the product rapidly reaches the water bottom, so that the problem of worsening of water quality is basically solved. The invention provides a reliable guarantee for green ecological culture.
Description
Technical field
The present invention relates to the solid particulate that a kind of biology changes end preparation, the solid-state biology of particularly a kind of high-activity high-efficiency rate changes end particle.
Background technology
The mariculture industry can be divided into sea farming and freshwater aquiculture.The water body of these two kinds of breed is in long-time the breed; Contact for a long time with the movement of marine products class, residual bait, plant and animal residues and the nutritive substance of water body itself at the bottom of the mud; Especially contacting of organism and mikrobe formed toxic substances such as too much organism, nitrite, ammonia nitrogen, hydrogen sulfide.
Especially in fresh-water fish-culture; Mostly its occupation of land is pond and batch production; Owing to itself be dead front type; Water body is in a kind of state of Static Water for a long time, is to help last production so remove toxic substances such as organism in the water body, nitrite, ammonia nitrogen, hydrogen sulfide, enhances productivity, the assurance of product health and green environment.
People have arrived a very sophisticated stage to the research of aquaculture water, thus to various water bodys to change end preparation also very abundant.But no matter be sea farming or freshwater aquiculture, different according to the degree of depth of its water body, content of harmful also is different.In the dark position of the 1-2 of aquaculture water rice, mainly being the chemical substance of ammonia and nitrogen for example, mainly is some hydrogen sulfide and chemical suspended substance in the dark position of 3-5 rice; In darker water body, have a large amount of mikrobe unwanted bacterias, be unfavorable for to edible breed.So change the slow-release function that substrate matter should be carried out different steps to different depths, to reach the purpose that changes the end.And mostly the existing substrate matter that changes is preparation, and liquid pouring is gone into aquaculture water, and it is general to change end effect, and mikrobe possibly bubbled through the water column or the shoaling water, does not really reach the effect that changes the end.
Summary of the invention
According to above-mentioned technical problem; The present invention provides the solid-state biology of a kind of high-activity high-efficiency rate to change end particle, and strict controlling microbial content produces particulate state; Guarantee certain medicament structure from inside to outside; Having slow releasing function, fundamentally solve the water quality deterioration problem, is the reliable guarantee that green ecological is cultured.
The present invention realizes through following technical scheme:
The solid-state biology of a kind of high-activity high-efficiency rate changes end particle; Comprise subtilis, denitrifying bacterium, clay, synergistic agent and wheat bran; According to the quality proportioning is clay 85%~88%, synergistic agent 1%~2%, wheat bran 1%~2%; Subtilis and denitrifying bacterium 8%~10% mix totally, are prepared into the particulate state medicament.
Said particulate state medicament is prepared into the particle with geometrical shape, and subtilis and denitrifying bacterium are in particulate innermost layer part.
Said subtilis is no less than 6% according to the quality proportioning.
The effective microbe content of said subtilis and denitrifying bacterium is that subtilis is more than or equal to 1 * 10
9CFU/g, denitrifying bacterium is more than or equal to 1 * 10
8CFU/g.
Said synergistic agent is molasses.
The invention also discloses the solid-state biology of a kind of high-activity high-efficiency rate and change end particulate preparation method: will shine the quality proportioning is clay 85%~88%; Synergistic agent 1%~2%, wheat bran 1%~2%, subtilis and denitrifying bacterium totally 8%~10% mix 10~20min; Change tablets press after mixing over to and carry out granulation; Oven dry is sieved, and processes finished product.
Said subtilis is no less than 6% according to the quality proportioning.
The effective microbe content of said subtilis and denitrifying bacterium is that subtilis is more than or equal to 1 * 10
9CFU/g, denitrifying bacterium is more than or equal to 1 * 10
8CFU/g.
Said synergistic agent is molasses.
Beneficial effect of the present invention is:
1, useful microbe and synergistic agent can fully decompose various objectionable impurities (NH
4 +-N, NO
2 --N, H
2S etc.), stablize water body pH, thereby reduce nitrite and ammonia-nitrogen content in the water body rapidly;
2, mikrobe is fully decomposed residual bait, animal residue and movement in the bed mud, changes into the available nitrogen of useful algae, sulphur nutrition source, fundamentally controls ammonia nitrogen, nitrite, H
2Substrate is improved in the source of toxic substances such as S, forms the high-quality bed mud;
3, useful microbe suppresses the harmful bacterium of bottom, forms the optimum ecological circulation of water body, reduces disease.
4, effectively improve stench substrate of culturing the middle and later periods and the bed mud that wears out the pond, stablize water colour.
Embodiment
Below in conjunction with embodiment, the present invention is further specified.
Embodiment 1
Product prepn:
According to mass ratio is clay 88%, molasses 1%, and wheat bran 1%, subtilis and denitrifying bacterium totally 10%, wherein the bacillus subtilis bacterial content is 7.5% to mix, wherein the content of microorganisms of subtilis is more than or equal to 1 * 10
9CFU/g, the content of microorganisms of denitrifying bacterium is more than or equal to 1 * 10
8CFU/g, 10~20min changes tablets press over to after mixing, and carries out granulation, and oven dry is sieved, and processes finished product.
Handle water body: 10 mu of waters surface, ammonia nitrogen 2.3mg/L, nitrous acid nitrogen 0.5mg/L, hydrogen sulfide 0.4mg/L.
Treatment time be every first quarter moon once, the treatment time is half a year.
Processing finishes water sample and tests: ammonia nitrogen is less than 0.01mg/L, and nitrous acid nitrogen is less than 0.05mg/L, and hydrogen sulfide is less than 0.05mg/L.Processing efficiency reaches 97.6%.
Embodiment 2
Product prepn:
According to mass ratio is clay 86%, molasses 2%, and wheat bran 2%, subtilis and denitrifying bacterium totally 10%, wherein the bacillus subtilis bacterial content is 6% to mix, wherein the content of microorganisms of subtilis is more than or equal to 1 * 10
9CFU/g, the content of microorganisms of denitrifying bacterium is more than or equal to 1 * 10
8CFU/g, 10~20min changes tablets press over to after mixing, and carries out granulation, and oven dry is sieved, and processes finished product.
Handle water body: 5 mu of waters surface, ammonia nitrogen 1.8mg/L, nitrous acid nitrogen 0.6mg/L, hydrogen sulfide 0.3mg/L.
Treatment time be every first quarter moon once, the treatment time is half a year.
Processing finishes water sample and tests: ammonia nitrogen is less than 0.02mg/L, nitrous acid nitrogen 0.05mg/L, hydrogen sulfide 0.05mg/L.Processing finishes, and the water sample processing efficiency reaches 96.6%.
Embodiment 3
Product prepn:
According to mass ratio is clay 88%, molasses 2%, and wheat bran 2%, subtilis and denitrifying bacterium totally 8%, wherein the bacillus subtilis bacterial content is 6% to mix, wherein the content of microorganisms of subtilis is more than or equal to 1 * 10
9CFU/g, the content of microorganisms of denitrifying bacterium is more than or equal to 1 * 10
8CFU/g, 10~20min changes tablets press over to after mixing, and carries out granulation, and oven dry is sieved, and processes finished product.
Handle water body: 8 mu of waters surface, ammonia nitrogen 0.4mg/L, nitrous acid nitrogen 1.5mg/L, hydrogen sulfide 0.25mg/L.
Treatment time be every first quarter moon once, the treatment time is half a year.
Processing finishes water sample and tests: ammonia nitrogen is less than 0.01mg/L, and nitrous acid nitrogen is less than 0.01mg/L, and hydrogen sulfide is less than 0.01mg/L.Processing efficiency reaches 98.6%.
Can find out that by the foregoing description the processing efficiency of this product all is higher than 96%, owing to be solid particulate; Has superpower slow releasing function; Can handle to different objectionable impuritiess at different water depths, so just can reach efficient effect, treatment effect is good.
Claims (9)
1. the solid-state biology of high-activity high-efficiency rate changes end particle; Comprise subtilis, denitrifying bacterium, clay, synergistic agent and wheat bran; It is characterized in that according to the quality proportioning be clay 85%~88%, synergistic agent 1%~2%, wheat bran 1%~2%; Subtilis and denitrifying bacterium 8%~10% mix totally, are prepared into the particle formulation.
2. the solid-state biology of high-activity high-efficiency rate as claimed in claim 1 changes end particle, it is characterized in that said particulate state medicament is prepared into the particle with geometrical shape, and subtilis and denitrifying bacterium are in particulate innermost layer part.
3. the solid-state biology of high-activity high-efficiency rate as claimed in claim 1 changes end particle, it is characterized in that said subtilis is no less than 6% according to the quality proportioning.
4. the solid-state biology of high-activity high-efficiency rate as claimed in claim 1 changes end particle, and the effective microbe content that it is characterized in that said subtilis and denitrifying bacterium is that subtilis is more than or equal to 1 * 10
9CFU/g, denitrifying bacterium is more than or equal to 1 * 10
8CFU/g.
5. the solid-state biology of high-activity high-efficiency rate as claimed in claim 1 changes end particle, it is characterized in that said synergistic agent is molasses.
6. the solid-state biology of high-activity high-efficiency rate changes end particulate preparation method: it is characterized in that with photograph quality proportioning be clay 85%~88%; Synergistic agent 1%~2%, wheat bran 1%~2%, subtilis and denitrifying bacterium totally 8%~10% mix 10~20min; Change tablets press after mixing over to and carry out granulation; Oven dry is sieved, and processes finished product.
7. the solid-state biology of high-activity high-efficiency rate as claimed in claim 6 changes end particulate preparation method, it is characterized in that said subtilis is no less than 6% according to the quality proportioning.
8. the solid-state biology of high-activity high-efficiency rate as claimed in claim 6 changes end particulate preparation method, and the effective microbe content that it is characterized in that said subtilis and denitrifying bacterium is that subtilis is more than or equal to 1 * 10
9CFU/g, denitrifying bacterium is more than or equal to 1 * 10
8CFU/g.
9. the solid-state biology of high-activity high-efficiency rate as claimed in claim 6 changes end particulate preparation method, it is characterized in that said synergistic agent is molasses.
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102992481A (en) * | 2012-12-24 | 2013-03-27 | 韦秋平 | Efficient microbial nutrition enhancer |
CN103951035A (en) * | 2014-05-17 | 2014-07-30 | 李品 | Granular material for water area governance as well as preparation method and application method thereof |
CN104071902A (en) * | 2014-07-10 | 2014-10-01 | 杨晴雅 | Method for treating household wastewater |
CN109775866A (en) * | 2019-03-13 | 2019-05-21 | 南京工业大学 | Handle the preparation method of the composite slow release microcapsule formulation of breeding water body ammonia nitrogen |
CN114212957A (en) * | 2021-11-23 | 2022-03-22 | 重庆誉康欣生物技术有限公司 | Formula and production process for decomposing bottom modification |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5884094A (en) * | 1981-10-29 | 1983-05-20 | U S C Internatl Co:Kk | Purifying agent for fresh water |
US20070262018A1 (en) * | 2006-05-09 | 2007-11-15 | Michael Richter | Method and product for protecting the residential and commercial aquatic environment |
CN101157892A (en) * | 2007-03-06 | 2008-04-09 | 扬州市绿科生物技术有限公司 | Production method of solid preparation for degradation of ammonia nitrogen and nitrite |
CN101269884A (en) * | 2008-05-08 | 2008-09-24 | 储卫华 | Microorganism renovation agent of water environment and preparation method thereof |
CN101367581A (en) * | 2008-09-24 | 2009-02-18 | 武汉合缘绿色生物工程有限公司 | Composite microorganism formulation for controlling excessive multiplication of blue-green algae and preparation method thereof |
CN101376877A (en) * | 2007-08-31 | 2009-03-04 | 天津中敖生物科技有限公司 | Compound microecological preparation for purifying cultivation water, preparation formulation thereof and preparation processes of the preparation and the preparation formulation |
CN101698539A (en) * | 2009-10-13 | 2010-04-28 | 王颖 | Microecological agent for purifying water and preparation method thereof |
CN101962229A (en) * | 2010-06-23 | 2011-02-02 | 天津生机集团股份有限公司 | Water purifying agent for pond culture |
-
2011
- 2011-02-24 CN CN2011100441994A patent/CN102649603A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5884094A (en) * | 1981-10-29 | 1983-05-20 | U S C Internatl Co:Kk | Purifying agent for fresh water |
US20070262018A1 (en) * | 2006-05-09 | 2007-11-15 | Michael Richter | Method and product for protecting the residential and commercial aquatic environment |
CN101157892A (en) * | 2007-03-06 | 2008-04-09 | 扬州市绿科生物技术有限公司 | Production method of solid preparation for degradation of ammonia nitrogen and nitrite |
CN101376877A (en) * | 2007-08-31 | 2009-03-04 | 天津中敖生物科技有限公司 | Compound microecological preparation for purifying cultivation water, preparation formulation thereof and preparation processes of the preparation and the preparation formulation |
CN101269884A (en) * | 2008-05-08 | 2008-09-24 | 储卫华 | Microorganism renovation agent of water environment and preparation method thereof |
CN101367581A (en) * | 2008-09-24 | 2009-02-18 | 武汉合缘绿色生物工程有限公司 | Composite microorganism formulation for controlling excessive multiplication of blue-green algae and preparation method thereof |
CN101698539A (en) * | 2009-10-13 | 2010-04-28 | 王颖 | Microecological agent for purifying water and preparation method thereof |
CN101962229A (en) * | 2010-06-23 | 2011-02-02 | 天津生机集团股份有限公司 | Water purifying agent for pond culture |
Non-Patent Citations (1)
Title |
---|
崔华平等: "固定化微生物在水产养殖中的应用", 《水产科学》 * |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102992481A (en) * | 2012-12-24 | 2013-03-27 | 韦秋平 | Efficient microbial nutrition enhancer |
CN103951035A (en) * | 2014-05-17 | 2014-07-30 | 李品 | Granular material for water area governance as well as preparation method and application method thereof |
CN103951035B (en) * | 2014-05-17 | 2015-09-23 | 李品 | A kind of waters improvement particulate material and preparation and application thereof |
CN104071902A (en) * | 2014-07-10 | 2014-10-01 | 杨晴雅 | Method for treating household wastewater |
CN109775866A (en) * | 2019-03-13 | 2019-05-21 | 南京工业大学 | Handle the preparation method of the composite slow release microcapsule formulation of breeding water body ammonia nitrogen |
CN114212957A (en) * | 2021-11-23 | 2022-03-22 | 重庆誉康欣生物技术有限公司 | Formula and production process for decomposing bottom modification |
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Application publication date: 20120829 |