CN106495949A - Soil desertification biological modification agent and preparation method thereof, using method - Google Patents
Soil desertification biological modification agent and preparation method thereof, using method Download PDFInfo
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- CN106495949A CN106495949A CN201610952493.8A CN201610952493A CN106495949A CN 106495949 A CN106495949 A CN 106495949A CN 201610952493 A CN201610952493 A CN 201610952493A CN 106495949 A CN106495949 A CN 106495949A
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- 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
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01B—SOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
- A01B79/00—Methods for working soil
- A01B79/02—Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
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- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Soil Sciences (AREA)
- Organic Chemistry (AREA)
- Pest Control & Pesticides (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Environmental Sciences (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
Abstract
The invention discloses a kind of soil desertification biological modification agent, the soil desertification biological modification agent includes following weight portion material：1,000 2000 parts of diatomite, 400 800 parts of SANWET, 200 600 parts of cinder, 600 800 parts of liver moss, 100 400 parts of bamboo charcoal ash, 300 500 parts of cocoanut shell, 200 300 parts of tea grounds, 150 250 parts of marine alga, 100 200 parts of silkworm excrement, 400 800 parts of fowl and animal excrement, 300 600 parts of biogas residue, 10 50 parts of microbial inoculum；The present invention is combined with the soil for desertifying by materials such as diatomite, SANWET, marine algas, play a part of notable water conservation, prevent erosion, retain the nutrient content of soil to greatest extent, and the material after bacteria fermentation contains beneficial bacterium and can provide enough nutrient sources to the soil for desertifying, so as to improve soil texture, improved soil desertifies.
Description
Technical field
The present invention relates to soil improvement field, and in particular to a kind of soil desertification biological modification agent and preparation method thereof, make
Use method.
Background technology
Soil desertification refers to good soil or available soil becomes containing husky a lot of soil or soil or even becomes
The process in desert.Soil desertification main process is wind erosion and wind deposit process.In desert surrounding area, due to vegetation deterioration or
Overgrazing or to open up wasteland be farmland, soil becomes drying because of dehydration, and grogs disperses, and is lost by wind, and fine particle content drops
Low.And after wind-force or the location weakened, dust storm particle gradual builds up upper soll layer and makes soil desertification.Therefore, soil
Desertifying includes the wind erosion process and the aeolian sediments process in location farther out of grassland soil.At present, the soil desertification situation of China
Day by day serious, if improving not in time, it will cause the result that environment rapidly deteriorates, but improving the Main Means for desertifying at present is
Planting trees and grass, is difficult to grow yet with soil desertification planting trees and grass, so improving soil desertification, first has to improved soil.
Content of the invention
It is an object of the invention to be directed to the problems referred to above, there is provided a kind of soil desertification biological modification agent, by diatomite,
The materials such as SANWET, marine alga are combined with the soil for desertifying, and are played a part of notable water conservation, are prevented water and soil stream
Lose, the nutrient content of reservation soil, and the material after bacteria fermentation to greatest extent contains beneficial bacterium can be to the soil for desertifying
Earth provides enough nutrient sources, and so as to improve soil texture, improved soil desertifies.
The present invention provide technical scheme be：
A kind of soil desertification biological modification agent, the soil desertification biological modification agent include following weight portion material：Diatom
Native 1000-2000 parts, SANWET 400-800 parts, cinder 200-600 parts, liver moss 600-800 parts, bamboo charcoal ash
100-400 parts, cocoanut shell 300-500 parts, tea grounds 200-300 parts, marine alga 150-250 parts, silkworm excrement 100-200 parts, fowl and animal excrement
400-800 parts, biogas residue 300-600 part, microbial inoculum 10-50 parts, the microbial inoculum are bacillus subtilis, actinomyces, saccharomycete, lactic acid
One or more in bacterium.
Preferably, the soil desertification biological modification agent also includes following weight portion material：Feather meal 100-200 parts,
Edible fungi residues 100-200 parts, bean dregs 200-300 parts, vinasse 150-200 parts, peat soil 400-600 parts.
Preferably, the soil desertification biological modification agent also includes：Raw earthworm, it is biological that the raw earthworm accounts for soil desertification
The 0.05-0.5% of modifying agent weight.
Preferably, the microbial inoculum is bacillus subtilis, the mixture of saccharomycete by weight 1: 2.
Preferably, the soil desertification biological modification agent is made up of following weight portion material：1500 parts of diatomite, starch
600 parts of grafted polyacrylic acid sodium, 300 parts of cinder, 700 parts of liver moss, 250 parts of bamboo charcoal ash, 450 parts of cocoanut shell, 220 parts of tea grounds, sea
190 parts of algae, 180 parts of silkworm excrement, 650 parts of fowl and animal excrement, 500 parts of biogas residue, 30 parts of bacillus subtilis, 150 parts of feather meal, edible mushroom
120 parts of slag, 250 parts of bean dregs, 180 parts of vinasse, 500 parts of peat soil, 230 parts of raw earthworm.
The present invention also provides a kind of preparation method of described soil desertification biological modification agent, the preparation method include with
Lower step：
1) by bamboo charcoal ash, cocoanut shell, tea grounds, marine alga, silkworm excrement, fowl and animal excrement, biogas residue, feather meal, edible fungi residues, bean dregs,
PH is adjusted to 3.5-5 by vinasse mechanical crushing, is added microbial inoculum, is stirred, after fermentation 2-3 days, by fermentation after material dry
Arrive fermentation material；
2) diatomite, cinder, SANWET, peat soil are crushed, crosses 50 mesh sieve, to powder；
3) powder, fermentation material are well mixed with raw earthworm, obtain final product the soil desertification biological modification agent.
Preferably, step 1) in be additionally included in sweat, every 2 hours, toward on fermented material spray 50 DEG C of water,
After stirring, wrapped with preservative film and then fermented, every time the water of sprinkling for fermented material gross weight 10%.
The present invention also provides a kind of using method of described soil desertification biological modification agent, the using method include with
Lower step：
1) the soil desertification biological modification agent is mixed with the soil that need to be improved, is flattened, pouring into water and contain soil moisture
Amount 40-50%, encloses layer of plastic film in upper soll layer, adds soil desertification biological modification agent 100- describedly per mu
1000kg, the present invention can add in the range of this according to the situation of substantive soil desertification when using；
2) plastic sheeting watering pours water being opened once every 2 days, continuing 1 month, soil improvement is finished.
Beneficial effects of the present invention are as follows：
There is water conservation of the high-hydroscopicity as prone soil using diatomite, SANWET in the present invention
Agent, for the soil for desertifying plays water conservation, the effect for preventing erosion, and good permeability, retain soil to greatest extent
Nutrient content；Wherein bamboo charcoal ash, cocoanut shell, tea grounds, marine alga, silkworm excrement, fowl and animal excrement, biogas residue, feather meal, edible fungi residues, bean dregs,
Vinasse belong to organic matter, by fermentation after provide enough nutrients can to the soil for desertifying, persistently improve soil texture, bamboo charcoal ash,
Cocoanut shell, marine alga can equally play a part of water-absorbing-retaining, and good permeability is suitable for plant growth；The present invention also added raw earthworm
Earthworm, improves soil texture as biology, as organic matter gradually can be expanded by the effect of earthworm.
Specific embodiment
With reference to specific embodiment, the present invention is described in further detail, to make those skilled in the art's reference say
Bright book word can be implemented according to this.
Embodiment 1
A kind of soil desertification biological modification agent, including following weight portion material：1000 parts of diatomite, starch-grafted polypropylene
400 parts of sour sodium, 200 parts of cinder, 600 parts of liver moss, 100 parts of bamboo charcoal ash, 300 parts of cocoanut shell, 200 parts of tea grounds, 150 parts of marine alga, silkworm
Husky 100 parts, 400 parts of fowl and animal excrement, 300 parts of biogas residue, 10 parts of actinomyces.
Embodiment 2
A kind of soil desertification biological modification agent, including following weight portion material：2000 parts of diatomite, starch-grafted polypropylene
800 parts of sour sodium, 600 parts of cinder, 800 parts of liver moss, 400 parts of bamboo charcoal ash, 500 parts of cocoanut shell, 300 parts of tea grounds, 250 parts of marine alga, silkworm
Husky 200 parts, 800 parts of fowl and animal excrement, 600 parts of biogas residue, 50 parts of lactic acid bacteria.
Embodiment 3
A kind of soil desertification biological modification agent, including following weight portion material：1500 parts of diatomite, starch-grafted polypropylene
500 parts of sour sodium, 300 parts of cinder, 650 parts of liver moss, 200 parts of bamboo charcoal ash, 350 parts of cocoanut shell, 210 parts of tea grounds, 220 parts of marine alga, silkworm
Husky 180 parts, 600 parts of fowl and animal excrement, 350 parts of biogas residue, 10 parts of bacillus subtilis, 10 parts of actinomyces, 10 parts of lactic acid bacteria, feather meal
130 parts, 150 parts of edible fungi residues, 250 parts of bean dregs, 180 parts of vinasse, 550 parts of peat soil.
Embodiment 4
A kind of soil desertification biological modification agent, including following weight portion material：1000 parts of diatomite, starch-grafted polypropylene
400 parts of sour sodium, 200 parts of cinder, 600 parts of liver moss, 100 parts of bamboo charcoal ash, 300 parts of cocoanut shell, 200 parts of tea grounds, 150 parts of marine alga, silkworm
Husky 100 parts, 400 parts of fowl and animal excrement, 300 parts of biogas residue, 15 parts of bacillus subtilis, 30 parts of saccharomycete, 100 parts of feather meal, edible
100 parts of bacteria residue, 200 parts of bean dregs, 150 parts of vinasse, 400 parts of peat soil,
Soil desertification biological modification agent also includes：Raw earthworm, accounts for the 0.05% of soil desertification biological modification agent weight.
Embodiment 5
A kind of soil desertification biological modification agent, is made up of following weight portion material：1500 parts of diatomite, starch-grafted poly- third
600 parts of olefin(e) acid sodium, 300 parts of cinder, 700 parts of liver moss, bamboo charcoal ash 250 parts, 450 parts of cocoanut shell, 220 parts of tea grounds, 190 parts of marine alga,
180 parts of silkworm excrement, 650 parts of fowl and animal excrement, 500 parts of biogas residue, 30 parts of bacillus subtilis, 150 parts of feather meal, 120 parts of edible fungi residues,
250 parts of bean dregs, 180 parts of vinasse, 500 parts of peat soil, 230 parts of raw earthworm.
Embodiment 6
Embodiment 1-5 is made using following methods
The preparation method of described soil desertification biological modification agent, comprises the following steps：
1) by bamboo charcoal ash, cocoanut shell, tea grounds, marine alga, silkworm excrement, fowl and animal excrement, biogas residue, feather meal, edible fungi residues, bean dregs,
PH is adjusted to 3.5-5 by vinasse mechanical crushing, is added microbial inoculum, is stirred, after fermentation 2-3 days, by fermentation after material dry
Arrive fermentation material；
2) diatomite, cinder, SANWET, peat soil are crushed, crosses 50 mesh sieve, to powder；
3) powder, fermentation material are well mixed with raw earthworm, obtain final product the soil desertification biological modification agent.
Another program of the preparation method of the present invention：Step 1) in be additionally included in sweat, every 2 hours, toward send out
50 DEG C of water being sprayed on ferment material, after stirring, being wrapped with preservative film and then fermented, the water of sprinkling is fermented material gross weight every time
10%.
Embodiment 7
Certain prone soil is improved using soil desertification biological modification agent of the present invention, soil desertification biological modification of the present invention
The using method of agent is comprised the following steps：
1) will be mixed with the soil that need to be improved using 500kg/ mu soil desertification biological modification agents according to soil regime, whole
Put down, pour into water and make soil water content 40%, layer of plastic film is enclosed in upper soll layer；
2) plastic sheeting watering pours water being opened once every 2 days, continuing 1 month, soil improvement is finished.
After soil improvement is finished, Turf Culture, turf energy Rapid Rooting are colonized, and are colonized about 7 days.
Using modifying agent improving sandy soil success rate more than 98% of the present invention.
Although embodiment of the present invention is disclosed as above, which is not restricted in specification and embodiment listed
With, it can be applied to various suitable the field of the invention completely, for those skilled in the art, can be easily
Other modification is realized, therefore under the universal limited without departing substantially from claim and equivalency range, the present invention is not limited
In specific details and shown here as the embodiment with description.
Claims (8)
1. a kind of soil desertification biological modification agent, it is characterised in that the soil desertification biological modification agent includes following weight portion
Material：Diatomite 1000-2000 parts, SANWET 400-800 parts, cinder 200-600 parts, liver moss 600-800
Part, bamboo charcoal ash 100-400 parts, cocoanut shell 300-500 parts, tea grounds 200-300 parts, marine alga 150-250 parts, silkworm excrement 100-200 parts,
Fowl and animal excrement 400-800 parts, biogas residue 300-600 part, microbial inoculum 10-50 parts, the microbial inoculum are bacillus subtilis, actinomyces, ferment
One or more in female bacterium, lactic acid bacteria.
2. soil desertification biological modification agent as claimed in claim 1, it is characterised in that the soil desertification biological modification agent is also
Including following weight portion material：Feather meal 100-200 parts, edible fungi residues 100-200 parts, bean dregs 200-300 parts, vinasse 150-
200 parts, peat soil 400-600 parts.
3. soil desertification biological modification agent as claimed in claim 2, it is characterised in that the soil desertification biological modification agent is also
Including：Raw earthworm, the raw earthworm account for the 0.05-0.5% of soil desertification biological modification agent weight.
4. soil desertification biological modification agent as claimed in claim 1, it is characterised in that the microbial inoculum be bacillus subtilis,
The mixture of saccharomycete by weight 1: 2.
5. soil desertification biological modification agent as claimed in claim 3, it is characterised in that the soil desertification biological modification agent by
Following weight portion material is made：1500 parts of diatomite, 600 parts of SANWET, 300 parts of cinder, 700 parts of liver moss,
250 parts of bamboo charcoal ash, 450 parts of cocoanut shell, 220 parts of tea grounds, 190 parts of marine alga, 180 parts of silkworm excrement, 650 parts of fowl and animal excrement, biogas residue 500
Part, 30 parts of bacillus subtilis, 150 parts of feather meal, 120 parts of edible fungi residues, 250 parts of bean dregs, 180 parts of vinasse, peat soil 500
Part, 230 parts of raw earthworm.
6. the preparation method of soil desertification biological modification agent as claimed in claim 5, it is characterised in that the preparation method bag
Include following steps：
1) by bamboo charcoal ash, cocoanut shell, tea grounds, marine alga, silkworm excrement, fowl and animal excrement, biogas residue, feather meal, edible fungi residues, bean dregs, vinasse
PH is adjusted to 3.5-5 by mechanical crushing, is added microbial inoculum, is stirred, after fermentation 2-3 days, by fermentation after material be dried to obtain and send out
Ferment material；
2) diatomite, cinder, SANWET, peat soil are crushed, crosses 50 mesh sieve, to powder；
3) powder, fermentation material are well mixed with raw earthworm, obtain final product the soil desertification biological modification agent.
7. the preparation method of soil desertification biological modification agent as claimed in claim 6, it is characterised in that step 1) in also include
During the fermentation, every 2 hours, 50 DEG C of water are sprayed toward on fermented material, after stirring, wrapped with preservative film and then sent out
Ferment, the water of sprinkling is the 10% of fermented material gross weight every time.
8. the using method of the soil desertification biological modification agent as described in claim 1-7 is arbitrary, it is characterised in that the use
Method is comprised the following steps：
1) the soil desertification biological modification agent is mixed with the soil that need to be improved, is flattened, pouring into water and make soil water content 40-
50%, layer of plastic film is enclosed in upper soll layer；Add soil desertification biological modification agent 100- describedly per mu
1000kg；
2) plastic sheeting watering pours water being opened once every 2 days, continuing 1 month, soil improvement is finished.
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Cited By (16)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107041251A (en) * | 2017-04-26 | 2017-08-15 | 扬州大学 | The high fertility loam and its synthetic method of a kind of barren sand synthesis of utilization biogas residue |
| CN107124928A (en) * | 2017-04-21 | 2017-09-05 | 雷笑天 | It is a kind of to exempt from the hardened method of rehabilitating soil of deep ploughing |
| CN107286944A (en) * | 2017-07-31 | 2017-10-24 | 钟春明 | Sandy land soil conditioner |
| CN107371434A (en) * | 2017-06-07 | 2017-11-24 | 常州兆威不锈钢有限公司 | A kind of administering method of arid desert soil |
| CN107439077A (en) * | 2017-06-23 | 2017-12-08 | 福建省春天生态科技股份有限公司 | A kind of method of cell salt-soda soil comprehensive improvement |
| CN107473883A (en) * | 2017-07-31 | 2017-12-15 | 钟春明 | Prone soil fertilizer special for organic |
| CN107556126A (en) * | 2017-08-01 | 2018-01-09 | 浙江海洋大学 | A kind of soil improvement material for being used to improve coastal soil |
| CN108949183A (en) * | 2017-08-24 | 2018-12-07 | 中国科学院寒区旱区环境与工程研究所 | Desert greening method |
| CN108949184A (en) * | 2017-08-24 | 2018-12-07 | 中国科学院寒区旱区环境与工程研究所 | Soil conditioner for desert and desert soil conditioning method thereof |
| CN109089454A (en) * | 2018-09-21 | 2018-12-28 | 佛山市森昂生物科技有限公司 | A kind of desertification land control method |
| CN109220280A (en) * | 2017-08-24 | 2019-01-18 | 中国科学院寒区旱区环境与工程研究所 | Grafting method for promoting asexual propagation of populus euphratica |
| CN109233867A (en) * | 2018-09-20 | 2019-01-18 | 中国林业科学研究院森林生态环境与保护研究所 | A kind of conditioner and preparation method thereof improving south subtropics Eroded timbered soil carbon sequestration capacity |
| CN109417980A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Plant planting method for reducing water evaporation of desert |
| CN109425700A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Method for testing relation between populus diversifolia seed germination capacity and medium salt content |
| CN109425701A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Method for testing relation between populus diversifolia seed germination capacity and substrate moisture content |
| CN111247896A (en) * | 2020-03-17 | 2020-06-09 | 浙江省农业科学院 | Rapid ecological restoration method for continuous cropping obstacles of herbal traditional Chinese medicinal materials and organic restoration agent thereof |
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| CN107124928A (en) * | 2017-04-21 | 2017-09-05 | 雷笑天 | It is a kind of to exempt from the hardened method of rehabilitating soil of deep ploughing |
| CN107041251A (en) * | 2017-04-26 | 2017-08-15 | 扬州大学 | The high fertility loam and its synthetic method of a kind of barren sand synthesis of utilization biogas residue |
| CN107371434A (en) * | 2017-06-07 | 2017-11-24 | 常州兆威不锈钢有限公司 | A kind of administering method of arid desert soil |
| CN107439077A (en) * | 2017-06-23 | 2017-12-08 | 福建省春天生态科技股份有限公司 | A kind of method of cell salt-soda soil comprehensive improvement |
| CN107286944A (en) * | 2017-07-31 | 2017-10-24 | 钟春明 | Sandy land soil conditioner |
| CN107473883A (en) * | 2017-07-31 | 2017-12-15 | 钟春明 | Prone soil fertilizer special for organic |
| CN107556126A (en) * | 2017-08-01 | 2018-01-09 | 浙江海洋大学 | A kind of soil improvement material for being used to improve coastal soil |
| CN108949184A (en) * | 2017-08-24 | 2018-12-07 | 中国科学院寒区旱区环境与工程研究所 | Soil conditioner for desert and desert soil conditioning method thereof |
| CN108949183A (en) * | 2017-08-24 | 2018-12-07 | 中国科学院寒区旱区环境与工程研究所 | Desert greening method |
| CN109220280A (en) * | 2017-08-24 | 2019-01-18 | 中国科学院寒区旱区环境与工程研究所 | Grafting method for promoting asexual propagation of populus euphratica |
| CN109417980A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Plant planting method for reducing water evaporation of desert |
| CN109425700A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Method for testing relation between populus diversifolia seed germination capacity and medium salt content |
| CN109425701A (en) * | 2017-08-24 | 2019-03-05 | 中国科学院寒区旱区环境与工程研究所 | Method for testing relation between populus diversifolia seed germination capacity and substrate moisture content |
| CN109425700B (en) * | 2017-08-24 | 2020-08-14 | 中国科学院西北生态环境资源研究院 | Method for testing relation between populus diversifolia seed germination capacity and medium salt content |
| CN109425701B (en) * | 2017-08-24 | 2020-08-21 | 中国科学院西北生态环境资源研究院 | Method for testing relation between populus diversifolia seed germination capacity and substrate moisture content |
| CN109417980B (en) * | 2017-08-24 | 2023-11-24 | 中国科学院西北生态环境资源研究院 | A plant planting method that reduces water evaporation in deserts |
| CN109233867A (en) * | 2018-09-20 | 2019-01-18 | 中国林业科学研究院森林生态环境与保护研究所 | A kind of conditioner and preparation method thereof improving south subtropics Eroded timbered soil carbon sequestration capacity |
| CN109089454A (en) * | 2018-09-21 | 2018-12-28 | 佛山市森昂生物科技有限公司 | A kind of desertification land control method |
| CN111247896A (en) * | 2020-03-17 | 2020-06-09 | 浙江省农业科学院 | Rapid ecological restoration method for continuous cropping obstacles of herbal traditional Chinese medicinal materials and organic restoration agent thereof |
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Application publication date: 20170315 |