CN107805502A - A kind of utilize loses the standby soil conditioner of wine lees pickling and its application - Google Patents
A kind of utilize loses the standby soil conditioner of wine lees pickling and its application Download PDFInfo
- Publication number
- CN107805502A CN107805502A CN201711051318.2A CN201711051318A CN107805502A CN 107805502 A CN107805502 A CN 107805502A CN 201711051318 A CN201711051318 A CN 201711051318A CN 107805502 A CN107805502 A CN 107805502A
- Authority
- CN
- China
- Prior art keywords
- soil
- parts
- wine lees
- soil conditioner
- standby
- 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.)
- Withdrawn
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K17/00—Soil-conditioning materials or soil-stabilising materials
- C09K17/40—Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
-
- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K2109/00—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE pH regulation
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Soil Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Mycology (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Biotechnology (AREA)
- Biomedical Technology (AREA)
- Inorganic Chemistry (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Distillation Of Fermentation Liquor, Processing Of Alcohols, Vinegar And Beer (AREA)
Abstract
The invention discloses a kind of using the standby soil conditioner of wine lees pickling and its application is lost, it is related to technical field of land improvement.The raw material that the standby soil conditioner of wine lees pickling is lost in the utilization of the present invention includes losing 18 22 parts of grain, 12 parts of composite bacteria agent, 12 14 parts of stalk, 24 28 parts of flue gas desulfurization waste of fire coal, 58 parts of pyroligneous liquor, 46 parts of polyacrylamide in terms of mass fraction.The present invention realizes the recycling waste for losing the industry such as grain, stalk, flue gas desulfurization waste of fire coal or agricultural production, reduces resource consumption, reduces production cost, increases economic efficiency；Improve the microorganism system of soil, the microcirculqtory system of rehabilitating soil using composite bacteria agent；Improve the property and structure of soil with pyroligneous liquor, polyacrylamide, meanwhile, polyacrylamide can also reduce the absorption of plant heavy metal ion.
Description
Technical field
The present invention relates to technical field of land improvement, especially a kind of utilize to lose the standby soil conditioner of wine lees pickling and its answer
With.
Background technology
Saline-alkali soil is salinization or a kind of soil formed that alkalizes, including solonchak, alkaline earth and various salinized soils.In arid
And semiarid zone, contained salinity in underearth and underground water, because evaporation from land acts on, as soil capillarity makes
The waterborne of contained salinity is raised to surface layer, after moisture evaporation, salinity is stayed in upper soll layer, builds up and form salt-soda soil.China
The formation of alkaline earth and alkali-affected soil, most of industrial pollution and it is unreasonable fertilising it is relevant, cause Carbonates In Soil and metal from
The accumulation of son, salinization and basicity are universal higher, and serious salt affected soil regional plant can hardly survive.
Ameliorative measure to salt-soda soil at present mainly has following three kinds：(1) physical method improvement salt-soda soil；It is physically improved just
It is that transformation saline-alkali soil is carried out using the method for some physics, such as uses irrigation and drainage system, rinses desalination, Song Geng, pressure Sha Dengfang
Method, reach the purpose of modified utilization, but there is the amount of labour used is big, input cost is high, it is limited to hold time or is limited to water resource
A series of problems, such as nervous, and can not fundamentally reduce soil salt, it is necessary to carried out with reference to other measures.(2) chemical method
Improvement salt-soda soil chemical modifying is exactly to improve the property in salt-soda soil using some acid salts substances, reduces the soda acid of soil
Degree, increase the cation replacement ability of soil, reduce the salt content of soil, strengthen the activity of Soil Microorganism and enzyme, promote
Plant root growth.Improve the physical property of soil, increase soil granular structure, coordinate soil water fat gas heat, increase soil fertilizer
Power.But many chemical reagent easily cause secondary pollution to soil, limit its application.(3) biological method improvement salt-soda soil.
Traditional biological control measure improves salt-soda soil, i.e., with plant improvement salt-soda soil, easy to implement the method, remarkable in economical benefits.But
These present methods are all with a large amount of consumption of natural resource, absorb natural material or have passed through what nature processing and manufacturing formed,
Environmental protection and the requirement of recycling economy can not be met, therefore find one kind and changed using discarded object or Resource recovery progress salt-soda soil
Good technical method is the key point that the field is badly in need of breaking through.
The content of the invention
The first goal of the invention of the present invention is：For above-mentioned problem, there is provided a kind of utilize loses the standby soil of wine lees pickling
Earth modifying agent, it belongs to microbe soil conditioner, good to the improved effect of soil；And its raw material comes from industry or agriculture more
The discarded object of industry production, promotes recycling for resource, cost-effective.
The second goal of the invention of the present invention is：Above-mentioned utilize is provided and loses the standby soil conditioner of wine lees pickling in improved soil
Application.
The technical solution adopted by the present invention is as follows：
A kind of utilize loses the standby soil conditioner of wine lees pickling, and its raw material includes poor 18-22 parts of losing in terms of mass fraction, compound
Microbial inoculum 1-2 parts, stalk 12-14 parts, flue gas desulfurization waste of fire coal 24-28 parts, pyroligneous liquor 5-8 parts, polyacrylamide 4-6 parts.
Spirit distiller grain is using residue of the cereal as raw material after solid state fermentation, distillation extraction alcohol.China's white wine is made
That makes industry about 25,000,000 tons of generation every year loses grain.Spirit distiller grain in acidity, easily corruption and be not easy to store, if arbitrarily abandon or
Burn, environment can be caused seriously to pollute；On the other hand, in spirit distiller grain remaining fail full utilization starch, enrichment
The nutrients such as protein, metabolite amino acid, vitamin, mineral element, cellulose, NFE and microorganism residuum
Matter.Flue gas desulfurization waste of fire coal is the byproduct of coal-fired plant flue gas desulfurization method of limestone-gypsum technique, its main component
(70%-90% of content) is calcium sulphate dihydrate CaSO4·2H2O。
By adopting the above-described technical solution, losing grain and flue gas desulfurization waste of fire coal is effectively recycled.
Nutrient can be provided for the growth metabolism of composite bacteria agent by losing the nutrition of rich content in grain.In flue gas desulfurization waste of fire coal
Replaceability sodium ion on calcium ion-exchanged soil colloid, makes sodium ion enter the soil liquid from soil colloid, and replacement turns into
Na2SO4, sodium ion, so as to reduce the basicity of soil, can improve soil with oozing under irrigation water or draining via drainage ditch
The crumb structure of physical behavior and soil, calcium and element sulphur are important plant nutrient ingredient, appropriate supplement both support
The growth of plant can be promoted by dividing.Composite bacteria agent is used for the microorganism system for improving soil, the microcirculation system of rehabilitating soil.Wood
Jealous woman liquid is the condensate recovery liquid of the thermal decomposition of wood composition during charcoal is fired, in acidity, for adjusting soil pH, also, wood
Jealous woman liquid contains auximone, gibberellin, the basic element of cell division, trace element, vitamins and other nutritious components, effectively facilitates plant life
It is long.Polyacrylamide can effectively improve soil texture, increase macro aggregate number, reduce the soil weight, improve permeability, increase
Add the water content of soil, improve soil resistance to corrosion.I.e. the standby soil conditioner of wine lees pickling is lost in the utilization can effectively improve soil
Salinization of soil property, increase soil granular, keep soil from packing together.
The present invention's is a kind of using losing the standby soil conditioner of wine lees pickling, composite bacteria agent by colloid bacillus cereus, hay bacillus,
Bacillus licheniformis and nitrogen-fixing bacteria are according to mass ratio 1：0.6-0.8:0.3-0.5：0.1-0.2 ratio composition.
The present invention's is a kind of using losing the standby soil conditioner of wine lees pickling, and the polyacrylamide is anionic, its ion
Change degree is 20%-30%, degree of polymerization 1000-2000.
By adopting the above-described technical solution, anion-polyacrylamide is combined with the metal ion in soil, metal
Cation can be combined with soil particle again, so as to form cation bridge, i.e. polyacrylamide-cation-soil particle structure,
On the one hand form crumb structure and resist hardened, the absorption of another invention reduction plant heavy metal ion.
The present invention's is a kind of using the standby soil conditioner of wine lees pickling is lost, and it is prepared by the following method：
Step 1：Crushed to obtain waste spent grains powder end after poor drying will be lost；
Step 2：Normal temperature is naturally cooled to after the moist heat sterilization of waste spent grains powder end；
Step 3：Composite bacteria agent is seeded in the waste spent grains powder end through cooling and carries out Spawn incubation and obtains decomposed losing grain；
Step 4：Stalk, flue gas desulfurization waste of fire coal, pyroligneous liquor, polyacrylamide are uniformly mixed with decomposed grain of losing
Both.
By adopting the above-described technical solution, one side composite bacteria agent is activated in grain in pretreated lose, it is raw
Long acting height, another invention, composite bacteria agent further decompose the macromolecular nutritional ingredient lost in grain, are easy to plant directly to absorb
Utilize.
A kind of utilize of the present invention loses the standby soil conditioner of wine lees pickling, and in step 1,40-80 mesh is crossed at broken waste spent grains powder end
Sieve.
A kind of utilize of the present invention loses the standby soil conditioner of wine lees pickling, and in step 3, the Spawn incubation time is 3-7 days.
A kind of utilize of the present invention loses the standby soil conditioner of wine lees pickling, and in step 4, the particle diameter of stalk is 1-2mm, aqueous
Measure as 12-20%；Flue gas desulfurization waste of fire coal crosses 30-60 mesh sieves through crushing.
By adopting the above-described technical solution, after waste spent grains powder is broken, it is easy to decomposition of the microorganism to it；Coal-fired flue gas desulfurization gives up
Gurry promotes the exchange process of calcium ion and sodium ion after crushed.
Application of the standby soil conditioner of wine lees pickling in improved soil is lost in above-mentioned utilization.
Application of the standby soil conditioner of wine lees pickling in improved soil is lost in the utilization of the present invention, preferably in improvement salinization of soil
Application in soil.
Due to losing the aobvious acidity of grain, pyroligneous liquor, and the exchange process of calcium ion and sodium ion, so provided by the invention
It is particularly suitable for improvement to salinized soil using the standby soil conditioner of wine lees pickling is lost.
Application of the standby soil conditioner of wine lees pickling in improved soil is lost in the utilization of the present invention, and the standby soil of wine lees pickling is lost in the utilization
The application depth of earth modifying agent is the 15-20cm of farming layer depth, is applied once per the 1-2 months, amount of application 0.5-2kg/m2。
By adopting the above-described technical solution, easily survival and growth, polyacrylamide decomposition rate reduce microorganism, soil
Earth improved effect is good.
In summary, by adopting the above-described technical solution, the beneficial effects of the invention are as follows：
1. the recycling waste of the industry such as grain, stalk, flue gas desulfurization waste of fire coal or agricultural production will be lost, reduce
Resource consumption, production cost is reduced, is increased economic efficiency.
2. improve the microorganism system of soil, the microcirculqtory system of rehabilitating soil using composite bacteria agent.
3. improve the property and structure of soil with pyroligneous liquor, polyacrylamide, meanwhile, polyacrylamide can also reduce plant
The absorption of heavy metal ion.
Embodiment
All features disclosed in this specification, or disclosed all methods or during the step of, except mutually exclusive
Feature and/or step beyond, can combine in any way.
Any feature disclosed in this specification (including any accessory claim, summary), unless specifically stated otherwise,
Replaced by other equivalent or with similar purpose alternative features.I.e., unless specifically stated otherwise, each feature is a series of
An example in equivalent or similar characteristics.
Embodiment 1
The present embodiment provides a kind of utilize and loses the standby soil conditioner of wine lees pickling, and the soil conditioner belongs to microbe soil and changed
It is good dose, good to the improved effect of soil；And its raw material comes from the discarded object of industry or agricultural production more, promotes following for resource
Ring utilizes, cost-effective.
A kind of utilize loses the standby modifying agent of wine lees pickling, and its raw material includes losing 18 parts of grain, composite bacteria agent 1 in terms of mass fraction
Part, 12 parts of stalk, 24 parts of flue gas desulfurization waste of fire coal, 5 parts of pyroligneous liquor, 4 parts of polyacrylamide.Wherein, composite bacteria agent is by glue
Matter bacillus, hay bacillus, bacillus licheniformis and nitrogen-fixing bacteria are according to mass ratio 1:0.6:0.3:0.1 ratio composition, gathers
Acrylamide is anionic, and its ionization degree is 20%, the degree of polymerization 1000.
The utilization that the present embodiment provides is lost the standby soil conditioner of wine lees pickling and is prepared by the following method：
Step 1：Take it is fresh go out rice steamer lose grain, first forced air drying to water content is under conditions of wind speed is 6m/s
40%, it is 30% then to be dried under the conditions of 80 DEG C to water content, is finally dried under the conditions of 60 DEG C not high to water content
In 20%.40 mesh will be broken to through dry waste spent grains powder, obtain waste spent grains powder end.Waste spent grains powder end dimension is placed at 121 DEG C and sterilized
30min, naturally cool to normal temperature and obtain sterile powder.
Step 2：Colloid bacillus cereus, hay bacillus, bacillus licheniformis and the strain of nitrogen-fixing bacteria are taken in proportion, are disperseed
30min is incubated in 37 DEG C of sterile warm water and obtains solution placed in the middle.By strain solution inoculum in sterile powder, fermentation obtains for 3 days
Grain is lost to decomposed.
Step 3：It is 12% by stalk drying to water content, it is 1mm to be then crushed to particle diameter, and coal-fired flue gas desulfurization is discarded
Thing through being crushed to 30 mesh, and the two is added with pyroligneous liquor and polyacrylamide it is decomposed lose grain, stir and produce.
Embodiment 2
The present embodiment provides a kind of utilize and loses the standby soil conditioner of wine lees pickling, and the soil conditioner belongs to microbe soil and changed
It is good dose, good to the improved effect of soil；And its raw material comes from the discarded object of industry or agricultural production more, promotes following for resource
Ring utilizes, cost-effective.
A kind of utilize loses the standby soil conditioner of wine lees pickling, and its raw material includes losing 20 parts of grain, compound bacteria in terms of mass fraction
2 parts of agent, 12 parts of stalk, 25 parts of flue gas desulfurization waste of fire coal, 6 parts of pyroligneous liquor, 5 parts of polyacrylamide.Wherein, composite bacteria agent by
Colloid bacillus cereus, hay bacillus, bacillus licheniformis and nitrogen-fixing bacteria are according to mass ratio 1:0.7:0.4:0.2 ratio composition,
Polyacrylamide is anionic, and its ionization degree is 25%, the degree of polymerization 1800.
The utilization that the present embodiment provides is lost the standby soil conditioner of wine lees pickling and is prepared by the following method：
Step 1：Take it is fresh go out rice steamer lose grain, first forced air drying to water content is under conditions of wind speed is 8m/s
35%, it is 25% then to be dried under the conditions of 60 DEG C to water content, is finally dried under the conditions of 40 DEG C not high to water content
In 20%.60 mesh will be broken to through dry waste spent grains powder, obtain waste spent grains powder end.
Step 2：Colloid bacillus cereus, hay bacillus, bacillus licheniformis and the strain of nitrogen-fixing bacteria are taken in proportion, are disperseed
30min is incubated in 37 DEG C of sterile warm water and obtains solution placed in the middle.By strain solution inoculum in sterile powder, fermentation obtains for 5 days
Grain is lost to decomposed.
Step 3：It is 15% by stalk drying to water content, it is 2mm to be then crushed to particle diameter, and coal-fired flue gas desulfurization is discarded
Thing through being crushed to 40 mesh, and the two is added with pyroligneous liquor and polyacrylamide it is decomposed lose grain, stir and produce.
Embodiment 3
The present embodiment provides a kind of utilize and loses the standby soil conditioner of wine lees pickling, and the soil conditioner belongs to microbe soil and changed
It is good dose, good to the improved effect of soil；And its raw material comes from the discarded object of industry or agricultural production more, promotes following for resource
Ring utilizes, cost-effective.
A kind of utilize loses the standby soil conditioner of wine lees pickling, and its raw material includes losing 22 parts of grain, compound bacteria in terms of mass fraction
2 parts of agent, 14 parts of stalk, 28 parts of flue gas desulfurization waste of fire coal, 8 parts of pyroligneous liquor, 6 parts of polyacrylamide.Wherein, composite bacteria agent by
Colloid bacillus cereus, hay bacillus, bacillus licheniformis and nitrogen-fixing bacteria are according to mass ratio 1:0.8:0.5:0.2 ratio composition,
Polyacrylamide is anionic, and its ionization degree is 30%, the degree of polymerization 2000.
The utilization that the present embodiment provides is lost the standby soil conditioner of wine lees pickling and is prepared by the following method：
Step 1：Take it is fresh go out rice steamer lose grain, first forced air drying to water content is under conditions of wind speed is 8m/s
35%, it is 25% then to be dried under the conditions of 60 DEG C to water content, is finally dried under the conditions of 40 DEG C not high to water content
In 20%.80 mesh will be broken to through dry waste spent grains powder, obtain waste spent grains powder end.
Step 2：Colloid bacillus cereus, hay bacillus, bacillus licheniformis and the strain of nitrogen-fixing bacteria are taken in proportion, are disperseed
30min is incubated in 37 DEG C of sterile warm water and obtains solution placed in the middle.By strain solution inoculum in sterile powder, fermentation obtains for 7 days
Grain is lost to decomposed.
Step 3：It is 20% by stalk drying to water content, it is 2mm to be then crushed to particle diameter, and coal-fired flue gas desulfurization is discarded
Thing through being crushed to 80 mesh, and the two is added with pyroligneous liquor and polyacrylamide it is decomposed lose grain, stir and produce.
Embodiment 4
Application of the standby soil conditioner of wine lees pickling in improved soil is lost in the utilization that the present embodiment is provided in embodiment 2, its
Specifically application process is：
The soil of one piece of salinization of soil is selected, detects its pH value and soil clump count.Then the utilization provided in embodiment 2 is lost
The standby soil conditioner of wine lees pickling apply with the 15-20cm of farming layer depth, first time amount of application is 2kg/m2, then cover soil
Earth, soil pH value and clump count are detected after one month, then according to the application process, carry out second and apply, amount of application is
1kg/m2Repetitive administration once, after two months, detects soil pH value and clump count, then according to the application process, carries out the 3rd
Secondary administration, amount of application 0.5kg/m2Repetitive administration once, detects soil pH value and clump count after one month.Soil pH value and bacterium
It is as shown in table 1 to fall several results：
Soil pH and clump count contrast before and after the standby soil conditioner of wine lees pickling are lost in the administration utilization of table 1
As shown in Table 1, the standby soil conditioner of wine lees pickling is lost in utilization of the invention can be effectively improved the pH in salt-soda soil, make it
Neutrality is returned back to, and the micro organism quantity in soil can be increased, improves the microcirculqtory system of soil, realizes to degenerated soil
Improvement.
The invention is not limited in foregoing embodiment.The present invention, which expands to, any in this manual to be disclosed
New feature or any new combination, and disclose any new method or process the step of or any new combination.
Claims (10)
1. a kind of utilize loses the standby soil conditioner of wine lees pickling, it is characterised in that its raw material includes losing poor 18- in terms of mass fraction
22 parts, composite bacteria agent 1-2 parts, stalk 12-14 parts, flue gas desulfurization waste of fire coal 24-28 parts, pyroligneous liquor 5-8 parts, polyacrylamide
Amine 4-6 parts.
2. according to claim 1 utilize loses the standby soil conditioner of wine lees pickling, it is characterised in that composite bacteria agent is by colloid bud
Spore bacillus, hay bacillus, bacillus licheniformis and nitrogen-fixing bacteria are according to mass ratio 1:0.6-0.8:0.3-0.5：0.1-0.2 ratio
Composition.
It is 3. according to claim 2 using losing the standby soil conditioner of wine lees pickling, it is characterised in that the polyacrylamide is
Anionic, its ionization degree are 20%-30%, degree of polymerization 1000-2000.
4. the standby soil conditioner of wine lees pickling is lost in the utilization according to any one of claim 1-3, it is characterised in that it is by such as
Lower section method is prepared：
Step 1：Crushed to obtain waste spent grains powder end after poor drying will be lost；
Step 2：Normal temperature is naturally cooled to after the moist heat sterilization of waste spent grains powder end；
Step 3：Composite bacteria agent is seeded in the waste spent grains powder end through cooling and carries out Spawn incubation and obtains decomposed losing grain；
Step 4：By stalk, flue gas desulfurization waste of fire coal, pyroligneous liquor, polyacrylamide loses poor uniformly mix and both must with decomposed.
5. according to claim 4 utilize loses the standby soil conditioner of wine lees pickling, it is characterised in that broken in step 1
40-80 mesh sieves are crossed at waste spent grains powder end.
6. according to claim 5 utilize loses the standby soil conditioner of wine lees pickling, it is characterised in that in step 3, strain training
It is 3-7 days to support the time.
7. according to claim 6 utilize loses the standby soil conditioner of wine lees pickling, it is characterised in that in step 4, stalk
Particle diameter is 1-2mm, water content 12-20%；Flue gas desulfurization waste of fire coal crosses 30-60 mesh sieves through crushing.
8. application of the standby soil conditioner of wine lees pickling in improved soil is lost in the utilization any one of claim 1-7.
9. application according to claim 8, it is characterised in that the application in salinized soil is improved.
10. application according to claim 9, it is characterised in that the application that the standby soil conditioner of wine lees pickling is lost in the utilization is deep
Spend and applied once for the 15-20cm of farming layer depth, every 1-2 months, amount of application 0.5-2kg/m2。
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711051318.2A CN107805502A (en) | 2017-10-31 | 2017-10-31 | A kind of utilize loses the standby soil conditioner of wine lees pickling and its application |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711051318.2A CN107805502A (en) | 2017-10-31 | 2017-10-31 | A kind of utilize loses the standby soil conditioner of wine lees pickling and its application |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107805502A true CN107805502A (en) | 2018-03-16 |
Family
ID=61582754
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711051318.2A Withdrawn CN107805502A (en) | 2017-10-31 | 2017-10-31 | A kind of utilize loses the standby soil conditioner of wine lees pickling and its application |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN107805502A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109913234A (en) * | 2019-04-30 | 2019-06-21 | 曲阜师范大学 | A kind of soil conditioner and its application |
| CN110643371A (en) * | 2019-10-22 | 2020-01-03 | 时科生物科技（上海）有限公司 | Soil conditioner and preparation method thereof |
| CN114014721A (en) * | 2021-12-15 | 2022-02-08 | 中农新科(苏州)有机循环研究院有限公司 | Preparation method and application of alkaline soil conditioner based on kitchen waste |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105038801A (en) * | 2015-06-19 | 2015-11-11 | 成都普天泽科技有限公司 | Compound type soil improvement agent for saline alkali soil |
| CN106380345A (en) * | 2016-08-30 | 2017-02-08 | 山东胜伟园林科技有限公司 | Humus fertile soil for conditioning secondary saline-alkali soil and production method thereof |
-
2017
- 2017-10-31 CN CN201711051318.2A patent/CN107805502A/en not_active Withdrawn
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105038801A (en) * | 2015-06-19 | 2015-11-11 | 成都普天泽科技有限公司 | Compound type soil improvement agent for saline alkali soil |
| CN106380345A (en) * | 2016-08-30 | 2017-02-08 | 山东胜伟园林科技有限公司 | Humus fertile soil for conditioning secondary saline-alkali soil and production method thereof |
Non-Patent Citations (1)
| Title |
|---|
| 张德荣等: "丢糟综合优化利用研究", 《四川理工学院学报( 自然科学版)》 * |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109913234A (en) * | 2019-04-30 | 2019-06-21 | 曲阜师范大学 | A kind of soil conditioner and its application |
| CN110643371A (en) * | 2019-10-22 | 2020-01-03 | 时科生物科技（上海）有限公司 | Soil conditioner and preparation method thereof |
| CN114014721A (en) * | 2021-12-15 | 2022-02-08 | 中农新科(苏州)有机循环研究院有限公司 | Preparation method and application of alkaline soil conditioner based on kitchen waste |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104761416B (en) | A kind of biochemical conditioner that can improve saline-alkali soil and preparation method thereof | |
| CN104261981B (en) | The preparation method of seaweed organic fertilizer material and the organic fertilizer being made of the method | |
| CN101234919B (en) | High-activity biological water-keeping slow release composite fertilizer and preparation method thereof | |
| CN102775250B (en) | Saline-alkali soil fertilizer | |
| CN110156516A (en) | A kind of saline-alkali land soil conditioner, preparation method and applications | |
| CN105439775A (en) | Specific fertilizer for saline-alkali soil and preparation method thereof | |
| CN108410470B (en) | Microbial soil conditioner for saline-alkali soil and preparation method thereof | |
| CN104262046A (en) | Fertilizer for saline-alkali soil and preparation method of fertilizer | |
| CN106590671B (en) | Soil conditioner and preparation method and application thereof | |
| CN103739411A (en) | Preparation method of functional organic fertilizer for soil restoration | |
| CN1854245A (en) | Improvement of vegetative salt alkaline land soil | |
| CN103787763A (en) | Dung fermentation slow release fertilizer and preparation method thereof | |
| CN108002918A (en) | A kind of special poultry manure biological organic fertilizer in salt-soda soil | |
| CN102344324B (en) | Modified fertilizer dealkalized by wet desulfurization waste and preparation method thereof | |
| CN105237185A (en) | 38-40% nitrogen-phosphorus-potassium-containing high-concentration compound fertilizer and production method thereof | |
| CN102276368A (en) | Fermentation composite fertilizer suitable for greenhouse vegetable planting and preparation method thereof | |
| CN106883075A (en) | A kind of compound fertilizer of adjustable soil ph | |
| CN107805502A (en) | A kind of utilize loses the standby soil conditioner of wine lees pickling and its application | |
| CN106631596A (en) | Mixed fertilizer for improving hardened soil and manufacturing method thereof | |
| CN105906386A (en) | Saline-alkali soil conditioner prepared from corn straw and preparation method thereof | |
| CN104193534B (en) | Biological salt-relieving activator and agricultural application thereof | |
| CN103265386B (en) | Organic fertilizer containing furfural residues and trace elements and preparation method thereof | |
| CN103304322A (en) | Seaweed compound fertilizer and preparation method thereof | |
| CN107935767A (en) | A kind of alkaline land improving fertilizer | |
| CN108276213A (en) | A kind of composite microbiological fertilizer and preparation method thereof of high nutrient content |
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 | ||
| WW01 | Invention patent application withdrawn after publication | ||
| WW01 | Invention patent application withdrawn after publication |
Application publication date: 20180316 |