CN110313374A - A kind of processing method of biological soil - Google Patents
A kind of processing method of biological soil Download PDFInfo
- Publication number
- CN110313374A CN110313374A CN201910655896.XA CN201910655896A CN110313374A CN 110313374 A CN110313374 A CN 110313374A CN 201910655896 A CN201910655896 A CN 201910655896A CN 110313374 A CN110313374 A CN 110313374A
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- Prior art keywords
- soil
- processing method
- matrix
- filter residue
- mass ratio
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Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/10—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
- A01G24/22—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing plant material
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
- A01G24/28—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing peat, moss or sphagnum
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05C—NITROGENOUS FERTILISERS
- C05C3/00—Fertilisers containing other salts of ammonia or ammonia itself, e.g. gas liquor
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/80—Soil conditioners
Abstract
A kind of processing method of biological soil, comprising the following steps: S1, ammoniate water immersion after crushing matrix, filter out liquid, obtain filter residue, matrix includes at least one of peat, lignite and weathered coal;Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;The mass ratio of filter residue, amonifying bacteria and photosynthetic bacteria group is 1000:(20~30): (1~3) obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%~10%, obtains soil;S3, the soil in step S2 is cured for 24 hours at normal temperature.Processing method of the present invention rationally utilizes the humic acid in matrix, and the humic acid after ammonification is transported in the soil using water, and realization is uniformly distributed, and facilitates the growth of crop.
Description
Technical field
The invention belongs to plant to use soil technology field, and in particular to the processing method of biological soil.
Background technique
Soil refers to one layer of loose substance of earth surface, by various granular matrix matter, organic substance, moisture, sky
The composition such as gas, microorganism, can growing plant.Soil matrix matter, animals and plants as made of rock weathering, microorganism residuum decomposition produce
Raw organic matter, geobiont (solid matter) and moisture (liquid phase substance), air (gaseous substance), the humus etc. of oxidation
Composition.In recent years, biological soil generally is processed by the way that the organic matter of corresponding microorganism and corruption is added in particulate substrates
Earth, fertilizer degree with higher facilitate the fast-growth of crop, and specific microorganism selects according to the floristics to be planted
It selects.Humic acid is the larger molecular organics being widely present in nature, is that the remains of animals and plants pass through the decomposition of microorganism, conversion
And the type organic that a series of geochemical processes are caused and accumulated, it is widely present in nature, in rivers lake
Sea, soil coal mine and most of earth's surface largely exist.Humic acid is resourceful, and reserves are big, as Organic Ingredients, is often used as
Fertilizer, such as application No. is 201711214017.7 Chinese invention patents, disclose a kind of multifunctional microbial soil-repairing agent
And its preparation method and application, by the way that Nano chitosan, humic acid, nano biological charcoal and complex micro organism fungicide are mixed with
It is added in soil after renovation agent, but due to humic acid poorly water-soluble itself, makes an addition in soil soil generally using microorganism
Decomposition is absorbed by crops, and the decomposition of humic acid fully relies on contact, decomposition with microorganism, is difficult to ensure microorganism in soil
It is uniformly distributed, and corrosive acid is difficult to be uniformly distributed in the soil as a kind of large biological molecule not soluble in water, decomposition efficiency is slow
Slowly, it is unfavorable for the absorption of crop.Therefore, it needs a kind of to efficiently use the high life of humic acid in matrix, humic acid decomposition efficiency
The processing method of object soil.
Summary of the invention
It is an object of the invention to: in view of the deficiencies of the prior art, providing a kind of can efficiently use humic acid in matrix, corruption
Grow the processing method of the high biological soil of sour decomposition efficiency.
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat, lignite and weathering
At least one of coal;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:(20~30): (1~3) obtains just mixed object, addition account for just mixed amount of substance 5%~
10% water, obtains soil;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
In one of specific embodiment of the invention, step S1 matrix is peat and weathered coal.
Content of humic acid in peat and weathered coal is higher, and hardness is small, density is small, and convenient for broken, the residue of formation is dredged
Pine, can effectively contact with air and water moisture self restraint.
In one of specific embodiment of the invention, the mass ratio of peat and weathered coal is 1:3.
The present invention test discovery, when the mass ratio of peat and weathered coal be 1:3 when, relative to the peat matched by other,
In the matrix of lignite and weathered coal composition, plant growth is very fast.
It further include stalk in matrix in one of specific embodiment of the invention, stalk accounts for the 5% of matrix quality
~10%.
Stalk curing rots that the element and organic matter of nitrogenous, phosphorus, potassium, calcium, magnesium can be generated, and can be suitably used for a variety of different plants
Growth, increase soil fertility.
In one of specific embodiment of the invention, the same of amonifying bacteria and photosynthetic bacteria group is additionally added in step S2
When, it is additionally added aspergillus oryzae, the mass ratio of aspergillus oryzae and filter residue is (1~3): 1000.
Nutrition needed for the organic matter that aspergillus oryzae can accelerate to convert in stalk becomes plant growth, improves organic matter, improves
Soil texture, due to the amonifying bacteria being limited in filter residue and photosynthetic bacteria group, it is (1 that the mass ratio of aspergillus oryzae and filter residue, which is controlled,
~3): 1000, aspergillus oryzae is higher to the transfer efficiency of organic matter.
In one of specific embodiment of the invention, amonifying bacteria includes hay bacillus and bacillus.Withered grass
Bacillus and bacillus other than the nitrogenous compound in soil can be decomposed into crop and be easy the small molecule absorbed and ammonia,
Hay bacillus can enhance the resistance of crop, and bacillus can degrade organic phosphorus in soil, release the micro of plant growth
Element promotes the growth of crop root.
In one of specific embodiment of the invention, the mass ratio of hay bacillus and bacillus is 1:3.
In terms of existing technologies, the invention has the following advantages:
Matrix is impregnated by ammonium hydroxide, makes the humic acid ammonification in matrix, the humic acid after ammonification is soluble easily in water, passes through soil
In moisture transmission transport ammonification after humic acid, humic acid comes into full contact in amonifying bacteria in transportational process, is broken down into work
The nutriment and ammonia that object easily absorbs, ammonia is soluble in water, forms ammonium hydroxide, carries out ammonia to the humic acid of ammonification non-in matrix
Change, by rationally utilizing the humic acid in matrix, the humic acid after ammonification is transported in the soil using water, is realized and is uniformly divided
Cloth facilitates the growth of crop.
Specific embodiment
In order to be more clear the purpose of the present invention, technical solution and technical effect, with reference to embodiments, to the present invention
It is described in detail.It should be understood that embodiment described in this specification is not intended to just for the sake of explaining the present invention
Limit the present invention, parameter, ratio of embodiment etc. can adaptation to local conditions make a choice and substantial effect had no to result.
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat, lignite and weathering
At least one of coal;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:(20~30): (1~3) obtains just mixed object, addition account for just mixed amount of substance 5%~
10% water, obtains soil;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
In one of specific embodiment of the invention, step S1 matrix is peat and weathered coal.
In one of specific embodiment of the invention, the mass ratio of peat and weathered coal is 1:3.
It further include stalk in matrix in one of specific embodiment of the invention, stalk accounts for the 5% of matrix quality
~10%.
In one of specific embodiment of the invention, the same of amonifying bacteria and photosynthetic bacteria group is additionally added in step S2
When, it is additionally added aspergillus oryzae, the mass ratio of aspergillus oryzae and filter residue is (1~3): 1000.
In one of specific embodiment of the invention, amonifying bacteria includes hay bacillus and bacillus.Withered grass
Bacillus and bacillus other than the nitrogenous compound in soil can be decomposed into crop and be easy the small molecule absorbed and ammonia,
Hay bacillus can enhance the resistance of crop, and bacillus can degrade organic phosphorus in soil, release the micro of plant growth
Element promotes the growth of crop root.
In one of specific embodiment of the invention, the mass ratio of hay bacillus and bacillus is 1:3.
Embodiment 1
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and weathered coal, mud
The mass ratio of charcoal and weathered coal is 1:3;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 5% of matrix quality.
While being additionally added amonifying bacteria and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the matter of aspergillus oryzae and filter residue
Amount is than being 1:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 77.3cm.
Embodiment 2
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and weathered coal, mud
The mass ratio of charcoal and weathered coal is 1:3;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:30:3, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 10% of matrix quality.
While being additionally added amonifying bacteria and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the matter of aspergillus oryzae and filter residue
Amount is than being 3:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 82.6cm.
Embodiment 3
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and weathered coal, mud
The mass ratio of charcoal and weathered coal is 1:3;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 65.8cm, the branches and leaves of cinnamomum camphora seedling relative to
The branches and leaves of the cinnamomum camphora seedling of embodiment 1 are sparse.
Comparative example 1
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and lignite, peat
Mass ratio with lignite is 1:3;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 5% of matrix quality.
While being additionally added amonifying bacteria and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the matter of aspergillus oryzae and filter residue
Amount is than being 1:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 69.5cm, the branches and leaves of cinnamomum camphora seedling relative to
The branches and leaves of the cinnamomum camphora seedling of embodiment 1 are sparse.
Comparative example 2
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and weathered coal, mud
The mass ratio of charcoal and weathered coal is 1:4;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 5% of matrix quality.
While being additionally added amonifying bacteria and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the matter of aspergillus oryzae and filter residue
Amount is than being 1:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 72.7cm.
Comparative example 3
A kind of processing method of biological soil, comprising the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, matrix includes peat and weathered coal, mud
The mass ratio of charcoal and weathered coal is 1:3;
Nitrifier and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;Filter residue, nitrifier and
The mass ratio of photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 5% of matrix quality.
While being additionally added nitrifier and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the quality of aspergillus oryzae and filter residue
Than for 1:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, and average plant height is 42.8cm, and branches and leaves are rare, and part branch
Leaf is withered.
Comparative example 4
A kind of processing method of biological soil, comprising the following steps:
S1, loam is crushed;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the loam obtained in the step S1, stirs evenly;Filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:20:1, obtains just mixed object, and addition accounts for the water of just mixed amount of substance 5%, obtains soil,
Amonifying bacteria includes hay bacillus and bacillus, and the mass ratio of hay bacillus and bacillus is 1:3;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
It further include stalk in matrix, stalk accounts for the 5% of matrix quality.
While being additionally added amonifying bacteria and photosynthetic bacteria group in step S2, it is additionally added aspergillus oryzae, the matter of aspergillus oryzae and filter residue
Amount is than being 1:1000.
The cinnamomum camphora seedling for being 25cm by ten plants of plant heights is planted 30 days, wherein seven plants are withered, remaining three plants of average plant heights
The branches and leaves of 37.9cm, cinnamomum camphora seedling are rare.
Only several embodiments of the present invention are expressed for above embodiments, and the description thereof is more specific and detailed, but can not
Therefore it is construed as limiting the scope of the patent.It should be pointed out that for those of ordinary skill in the art,
Under the premise of not departing from present inventive concept, various modifications and improvements can be made, and these are all within the scope of protection of the present invention.
Therefore, the scope of protection of the patent of the invention shall be subject to the appended claims.
Claims (7)
1. a kind of processing method of biological soil, which comprises the following steps:
S1, water immersion is ammoniated after crushing matrix, filter out liquid, obtain filter residue, the matrix includes peat, lignite and weathering
At least one of coal;
Amonifying bacteria and photosynthetic bacteria group is added in S2, the filter residue obtained in the step S1, stirs evenly;The filter residue, ammonification are thin
The mass ratio of bacterium and photosynthetic bacteria group is 1000:(20~30): (1~3) obtains just mixed object, addition account for just mixed amount of substance 5%~
10% water, obtains soil;
S3, the soil in step S2 is cured for 24 hours at normal temperature.
2. the processing method of biological soil according to claim 1, which is characterized in that matrix described in step S1 is peat and wind
Change coal.
3. the processing method of biological soil according to claim 2, which is characterized in that the mass ratio of the peat and weathered coal
For 1:3.
4. the processing method of biological soil described in -3 any one claims according to claim 1, which is characterized in that the base
It further include stalk in matter, the stalk accounts for the 5%~10% of the matrix quality.
5. the processing method of biological soil according to claim 4, which is characterized in that it is thin to be additionally added the ammonification in step S2
While bacterium and photosynthetic bacteria group, it is additionally added aspergillus oryzae, the mass ratio of the aspergillus oryzae and the filter residue is (1~3): 1000.
6. the processing method of biological soil according to claim 1, which is characterized in that the amonifying bacteria includes hay bacillus
And bacillus.
7. the processing method of biological soil according to claim 6, which is characterized in that the hay bacillus and bacillus
Mass ratio is 1:3.
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112970558A (en) * | 2021-02-03 | 2021-06-18 | 广东东华生态科技有限公司 | Nursery stock cultivating device and cultivating method |
Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1648107A (en) * | 2005-01-10 | 2005-08-03 | 左淑珍 | Biological organic fertilizer and its preparing method |
CN1765844A (en) * | 2004-10-26 | 2006-05-03 | 刘甫名 | Humic acid biological fertilizer and its production method |
CN102924133A (en) * | 2012-11-19 | 2013-02-13 | 王天喜 | Method for producing microbial agent by using filter mud of sugar mills through fermentation |
CN102942393A (en) * | 2012-12-16 | 2013-02-27 | 王天喜 | Method for fermenting and producing microbial agent by utilizing cassava alcohol residues |
CN103058772A (en) * | 2013-01-15 | 2013-04-24 | 内蒙古永业生物技术有限责任公司 | Preparation method for high-activity humic acid biofertilizer |
CN106565382A (en) * | 2016-11-15 | 2017-04-19 | 郑州智拓生物科技有限公司 | Microbial carbon fertilizer and preparation method thereof |
CN106631540A (en) * | 2015-07-26 | 2017-05-10 | 魏忠 | Compound microbial fertilizer |
CN107759253A (en) * | 2017-11-01 | 2018-03-06 | 泸天化(集团)有限责任公司 | A kind of preparation method of high-activity humic acid sludge |
CN108383621A (en) * | 2018-05-08 | 2018-08-10 | 侯淑璐 | A kind of compound biological enzyme fertilizer |
CN108456104A (en) * | 2018-02-11 | 2018-08-28 | 赵光 | Potato devil liquor recovery utilizes method, humic acid biological organic fertilizer and preparation method thereof |
CN109627106A (en) * | 2019-02-18 | 2019-04-16 | 黑龙江金合康肥业有限公司 | A kind of high-activity humic acid ecology compound fertilizer |
-
2019
- 2019-07-19 CN CN201910655896.XA patent/CN110313374A/en active Pending
Patent Citations (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1765844A (en) * | 2004-10-26 | 2006-05-03 | 刘甫名 | Humic acid biological fertilizer and its production method |
CN1648107A (en) * | 2005-01-10 | 2005-08-03 | 左淑珍 | Biological organic fertilizer and its preparing method |
CN102924133A (en) * | 2012-11-19 | 2013-02-13 | 王天喜 | Method for producing microbial agent by using filter mud of sugar mills through fermentation |
CN102942393A (en) * | 2012-12-16 | 2013-02-27 | 王天喜 | Method for fermenting and producing microbial agent by utilizing cassava alcohol residues |
CN103058772A (en) * | 2013-01-15 | 2013-04-24 | 内蒙古永业生物技术有限责任公司 | Preparation method for high-activity humic acid biofertilizer |
CN106631540A (en) * | 2015-07-26 | 2017-05-10 | 魏忠 | Compound microbial fertilizer |
CN106565382A (en) * | 2016-11-15 | 2017-04-19 | 郑州智拓生物科技有限公司 | Microbial carbon fertilizer and preparation method thereof |
CN107759253A (en) * | 2017-11-01 | 2018-03-06 | 泸天化(集团)有限责任公司 | A kind of preparation method of high-activity humic acid sludge |
CN108456104A (en) * | 2018-02-11 | 2018-08-28 | 赵光 | Potato devil liquor recovery utilizes method, humic acid biological organic fertilizer and preparation method thereof |
CN108383621A (en) * | 2018-05-08 | 2018-08-10 | 侯淑璐 | A kind of compound biological enzyme fertilizer |
CN109627106A (en) * | 2019-02-18 | 2019-04-16 | 黑龙江金合康肥业有限公司 | A kind of high-activity humic acid ecology compound fertilizer |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN112970558A (en) * | 2021-02-03 | 2021-06-18 | 广东东华生态科技有限公司 | Nursery stock cultivating device and cultivating method |
CN112970558B (en) * | 2021-02-03 | 2023-03-10 | 广东东华生态科技有限公司 | Nursery stock cultivating device and cultivating method |
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