CN106068739A - The sterilization of a kind of total straw also field soil and the method for acid-base value regulation - Google Patents
The sterilization of a kind of total straw also field soil and the method for acid-base value regulation Download PDFInfo
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- CN106068739A CN106068739A CN201610388906.4A CN201610388906A CN106068739A CN 106068739 A CN106068739 A CN 106068739A CN 201610388906 A CN201610388906 A CN 201610388906A CN 106068739 A CN106068739 A CN 106068739A
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- 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
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
- A01N59/00—Biocides, pest repellants or attractants, or plant growth regulators containing elements or inorganic compounds
- A01N59/06—Aluminium; Calcium; Magnesium; Compounds thereof
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
- A01N59/00—Biocides, pest repellants or attractants, or plant growth regulators containing elements or inorganic compounds
- A01N59/24—Cyanogen or compounds thereof, e.g. hydrogen cyanide, cyanic acid, cyanamide, thiocyanic acid
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F11/00—Other organic fertilisers
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
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- Organic Chemistry (AREA)
- Plant Pathology (AREA)
- Inorganic Chemistry (AREA)
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- Wood Science & Technology (AREA)
- Agronomy & Crop Science (AREA)
- Pest Control & Pesticides (AREA)
- Biochemistry (AREA)
- Toxicology (AREA)
- Biotechnology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Mechanical Engineering (AREA)
- Soil Sciences (AREA)
- Agricultural Chemicals And Associated Chemicals (AREA)
- Fertilizers (AREA)
Abstract
The invention discloses sterilization and the method for acid-base value regulation of a kind of total straw also field soil, the method for the sterilization of described total straw also field soil and acid-base value regulation comprises the following steps: crushed stalk.After Oryza sativa L. maturation, united reaper is utilized to carry out rice harvesting and straw chopping and returning；Join and execute decomposing agent, then turn over；Shed quick lime and lime nitrogen.The present invention can be effectively improved the pH value of straw incorporation soil, accelerates the decomposition speed of straw, effectively kills soil poisonous and harmful microorganism and harmful bacteria, increases Soil nitrogen content, the beneficially healthy growth of succession crop (late rice) simultaneously.
Description
Technical field
The invention belongs to straw-returning technical field, particularly relate to sterilization and the acid-base value of a kind of total straw also field soil
The method of regulation.
Background technology
Countryside tax system to have about 50% and be eventually converted into agricultural crop straw.The waste of stalk resource, substantially plough,
Water resource and the waste of countryside tax system.Strengthen the research and development of the agricultural waste utilization new techniques such as straw, scientific and efficient land productivity
With stalk resource, forbid crop straw burning, on the one hand can turn waste into wealth, improve resource utilization, improve farmers' income, by straw
Resources advantage is converted into visible economic advantages.On the other hand can protect environment, protect people's health, keep traffic,
The unimpeded operation of civil aviaton, is the Important Action built a resource-conserving and environment-friendly society.Crop straw burning is very harmful, and leads
Endangering is atmospheric pollution.Crop straw burning adds the particulate matter in air and Hydrocarbon, NO2Will increase, impact is strong
Health；Crop straw burning also causes atmospheric visibility to reduce, and brings the biggest hidden danger to the operation on airport, highway；Crop straw burning is also
Reduce soil fertility, cause arable land impoverishment.The elements such as the nitrogen that contains in straw, sulfur be largely converted into volatile material or
Grain and enter air, nutrient loss is serious, is highly detrimental to improvement of soil fertility.Rice mechanization harvesting provides for straw-returning
Basis of reality, straw-returning can be effectively increased the content of soil with organic matter, improves soil fertility, improves farmland raw
State environmental quality, the generation of particularly the most serious to minimizing haze weather, and alleviate China nitrogen, phosphorus, potash fertilizer ratio
The contradiction of example imbalance is of great significance.Straw-returning can be effectively increased the content of soil with organic matter, improves soil
Fertility state, improves farmland ecological environment quality, the generation of particularly the most serious to minimizing haze weather, Yi Jihuan
The contradiction solving China's nitrogen, phosphorus, potash fertilizer out of proportion is of great significance.
But straw-returning soil there is also some shortcomings: (1) Caulis et Folium Oryzae decomposition speed is slow, affects plant growth.Straw is also
Tian Hou, because Caulis et Folium Oryzae quantity is relatively big, decomposes slowly in soil, and the energy abruptly increase of soil microorganism vital movement hydrolyzes in soil
Nitrogen reduces, and causes late rice nitrogenous fertilizer in early days not enough.Meanwhile because in soil a large amount of Caulis et Folium Oryzaes exist, under the influence of season Oryza sativa L. plant or
Other crop seeding qualities.Further, since a large amount of anaerobes are movable, make soil meta-acid, be unfavorable for the growth of succession crop.
(2) straw-returning adds pest and disease damage risk.After straw incorporation, soil moisture increases, ground temperature rise, is providing for plant growth
While good condition, also the generation for some pest and disease damage creates suitable environmental condition with popular.And, in Caulis et Folium Oryzae some
Pathogenic bacteria is difficult to remove land for growing field crops, thus adds the quantity of pathogenic bacteria, makes rice disease rate increase.
Summary of the invention
It is an object of the invention to provide sterilization and the method for acid-base value regulation of a kind of total straw also field soil, it is intended to
Solve straw-returning soil and there is Caulis et Folium Oryzae decomposition speed slowly, affect plant growth；The problem adding pest and disease damage risk.
The present invention is achieved in that sterilization and the method for acid-base value regulation of a kind of total straw also field soil, described
The method of the sterilization of total straw also field soil and acid-base value regulation comprises the following steps:
Step one, crushed stalk, after Oryza sativa L. maturation, utilize united reaper to carry out rice harvesting and straw chopping and returning；
Step 2, joins and executes decomposing agent, pour water soaked field 3～5 days at once；
Step 3, sheds quick lime and lime nitrogen, then turns over.
Further, toothing 15cm during described combine operation, the straw a length of 5～10cm of pulverizing.
Further, described in join and execute decomposing agent, after total straw also field, select anaerobic straw decomposing inoculant 2kg for every mu
～3kg, to mix soil and spread fertilizer over the fields, soaked field of at once pouring water, water irrigating depth is advisable just flooding straw, retting time 3～5 days.
Further, shed quick lime described in specifically include with lime nitrogen:
The first step, sheds quick lime, behind decomposing agent soaked field 3～5 days, and every mu of quick lime executing 50～75kg, shed life
Calx is carried out with liming nitrogen simultaneously；
Second step, liming nitrogen, prevent and treat bacterial wilt, damping-off, root rot, rust, white mould.
Further, described decomposing agent soaked field 3～after 5 days, with lime nitrogen 50～100kg, shed before Soil tillage for every mu.
Further, described quick lime is 3～5 days with the soil disinfection time of lime nitrogen.
The sterilization of the total straw also field soil that the present invention provides and the method for acid-base value regulation, can be effectively improved Caulis et Folium Oryzae
The also pH value of field soil, accelerates the decomposition speed of straw, effectively kills soil poisonous and harmful microorganism and harmful bacteria, increase simultaneously
Soil nitrogen content, the beneficially healthy growth of succession crop (late rice).
2015, the present invention carried out the test of total straw also field in China Paddy Rice Inst base, and rice material is the spring
River 119, result see table.
Accompanying drawing explanation
Fig. 1 is sterilization and the method flow of acid-base value regulation of the total straw also field soil that the embodiment of the present invention provides
Figure.
Detailed description of the invention
In order to make the purpose of the present invention, technical scheme and advantage clearer, below in conjunction with embodiment, to the present invention
It is further elaborated.Should be appreciated that specific embodiment described herein, only in order to explain the present invention, is not used to
Limit the present invention.
Below in conjunction with the accompanying drawings the application principle of the present invention is explained in detail.
As it is shown in figure 1, the method for the sterilization of the total straw of the embodiment of the present invention also field soil and acid-base value regulation includes
Following steps:
S101: crushed stalk.After Oryza sativa L. maturation, utilize united reaper to carry out rice harvesting and straw chopping and returning, make
General toothing about 15cm during industry, the straw length suggestion of pulverizing is 5～10cm；
S102: join and execute decomposing agent, pour water soaked field 3～5 days at once；
S103: shed quick lime and lime nitrogen, then carry out Soil tillage.
In step S102, join and execute decomposing agent.After total straw also field, select anaerobic straw decomposing inoculant (rotten for every mu
Agent, market products) 2kg～3kg, mix soil and spread fertilizer over the fields, soaked field of at once pouring water, water irrigating depth is advisable just flooding straw,
Retting (soaked field) time 3～5 days.Decomposing agent processes the decomposition speed not only contributing to accelerate Caulis et Folium Oryzae, moreover it is possible to reduce noxious substance
Murder by poisoning to rice root.
Step S103 specifically includes:
(1) quick lime is shed.Behind decomposing agent soaked field 3～5 days, every mu of quick lime executing 50～75kg, it is possible not only to add
Speed Caulis et Folium Oryzae rots, and also acts as the effect heightening soil pH value and diseases prevention.Shed quick lime to carry out with liming nitrogen simultaneously.
(2) liming nitrogen.Lime nitrogen main component is nitrolim, calcium oxide, is a kind of alkaline fertilizer.Lime nitrogen is met
Intermediate product cyanamide in water splitting processes and dicyandiamide all have the effect of sterilization, deinsectization, diseases prevention, can effectively prevent and treat blue or green withered
The diseases such as disease, damping-off, root rot, rust, white mould, effectively prevent subterranean pest-insect and kill root-knot nematode, can be used as weeding
Agent, antibacterial, insecticide.
Behind decomposing agent soaked field 3～5 days, with lime nitrogen 50～100kg, shed before Soil tillage for every mu, can be effective
Kill soil pests, and have the effect heightening soil pH value concurrently, also correspond to application of to succession crop once harrow leaven simultaneously.
Shed quick lime can carry out with liming nitrogen simultaneously.
(3) shed quick lime and carry out Soil tillage after lime nitrogen.
The soil disinfection time of quick lime and lime nitrogen is generally 3～5 days, and the time is the shortest can affect turning green of succession crop
Speed or survival rate.Shed quick lime and liming nitrogen 3～rice transplanting or lower stubble operation after 5 days, can be carried out.
The foregoing is only presently preferred embodiments of the present invention, not in order to limit the present invention, all essences in the present invention
Any amendment, equivalent and the improvement etc. made within god and principle, should be included within the scope of the present invention.
Claims (6)
1. the sterilization of a total straw also field soil and the method for acid-base value regulation, it is characterised in that described total straw is also
The method of the sterilization of field soil and acid-base value regulation comprises the following steps:
Step one, crushed stalk, after Oryza sativa L. maturation, utilize united reaper to carry out rice harvesting and straw chopping and returning；
Step 2, joins and executes decomposing agent, pour water soaked field 3～5 days；
Step 3, sheds quick lime and lime nitrogen, then turns over.
2. the sterilization of total straw also field soil as claimed in claim 1 and the method for acid-base value regulation, it is characterised in that institute
Toothing 15cm when stating combine operation, the straw a length of 5～10cm of pulverizing.
3. the sterilization of total straw also field soil as claimed in claim 1 and the method for acid-base value regulation, it is characterised in that institute
State to join and execute decomposing agent, after total straw also field, select anaerobic straw decomposing inoculant 2kg～3kg, mix soil and spread fertilizer over the fields for every mu, horse
On pour water soaked field, water irrigating depth is advisable just flooding straw, retting time 3～5 days.
4. the sterilization of total straw also field soil as claimed in claim 1 and the method for acid-base value regulation, it is characterised in that institute
State and shed quick lime and lime nitrogen, then carry out Soil tillage, specifically include:
The first step, sheds quick lime, behind decomposing agent soaked field 3～5 days, and every mu of quick lime executing 50～75kg, shed quick lime
Carry out with liming nitrogen simultaneously；
Second step, liming nitrogen, prevent and treat bacterial wilt, damping-off, root rot, rust, white mould.
5. the sterilization of total straw also field soil as claimed in claim 4 and the method for acid-base value regulation, it is characterised in that institute
State decomposing agent soaked field 3～after 5 days, with lime nitrogen 50～100kg, shed before Soil tillage for every mu.
6. the sterilization of total straw also field soil as claimed in claim 4 and the method for acid-base value regulation, it is characterised in that institute
The soil disinfection time stating quick lime and lime nitrogen is 3～5 days.
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| CN201610388906.4A CN106068739A (en) | 2016-06-02 | 2016-06-02 | The sterilization of a kind of total straw also field soil and the method for acid-base value regulation |
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| CN201610388906.4A CN106068739A (en) | 2016-06-02 | 2016-06-02 | The sterilization of a kind of total straw also field soil and the method for acid-base value regulation |
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Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106973574A (en) * | 2017-03-31 | 2017-07-25 | 广东省农业科学院农业资源与环境研究所 | The modification method in sour regurgitation field |
| CN107148823A (en) * | 2017-07-10 | 2017-09-12 | 江西农业大学 | It is a kind of to alleviate the method that early rice straw incorporation grows adverse effect to double cropping late rice |
| CN107439284A (en) * | 2017-07-26 | 2017-12-08 | 安徽省福宁米业有限公司 | A kind of rice straw turns over the implantation methods of returning to the field |
| CN107455036A (en) * | 2017-08-16 | 2017-12-12 | 巨野德福生态农业开发有限公司 | A kind of plastic shed soil modification method |
| CN108059508A (en) * | 2017-12-27 | 2018-05-22 | 西南科技大学 | A kind of new rice field dedicated fertilizer and its method of administration |
| CN108718962A (en) * | 2018-04-26 | 2018-11-02 | 湖南玖恪土壤与环境科技有限公司 | A method of reducing paddy fields in south china rice cadmium content |
| CN108811576A (en) * | 2018-07-02 | 2018-11-16 | 中国农业科学院烟草研究所 | A kind of method of vega soil improvement |
| CN111034407A (en) * | 2019-12-17 | 2020-04-21 | 石家庄亚特生物科技有限公司 | Microbial utilization technology for returning rice straws to field in northeast region |
| CN112272987A (en) * | 2020-09-22 | 2021-01-29 | 阜南县美林蓝莓科技发展有限公司 | Soil improvement method for blueberry planting |
| CN112806138A (en) * | 2020-10-16 | 2021-05-18 | 吉林省农业科学院 | Method for improving cold resistance of rice based on complete decomposition and returning of rice straw to field |
| CN113896262A (en) * | 2021-11-03 | 2022-01-07 | 河海大学 | Water pollution control treatment system for field soaking |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0411689A (en) * | 1990-01-30 | 1992-01-16 | Masanori Shinozaki | Soil conditioner and method of utilizing it |
| CN1732773A (en) * | 2005-07-15 | 2006-02-15 | 中国农业科学院蔬菜花卉研究所 | A kind of soil disinfection method of facility for prevention and control soil-borne diseases of vegetable |
| CN1759646A (en) * | 2005-10-25 | 2006-04-19 | 刘建 | Planting tandem plowing type culturing method for returning full stalk to farmland suitable to zonal rice or wheat form |
| CN103477849A (en) * | 2013-09-29 | 2014-01-01 | 四川省农业科学院作物研究所 | Method for straw full-amount returning and rice-wheat planted seedling in rice-wheat double cropping area |
| CN104488397A (en) * | 2014-12-16 | 2015-04-08 | 安徽省农业科学院土壤肥料研究所 | Simplified straw-returning-to-field method applicable to clay paddy fields |
| CN104770096A (en) * | 2015-04-15 | 2015-07-15 | 滨海随耕生态农业有限公司 | Continuous cropping obstacle removal method for facility culturing soil |
-
2016
- 2016-06-02 CN CN201610388906.4A patent/CN106068739A/en active Pending
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0411689A (en) * | 1990-01-30 | 1992-01-16 | Masanori Shinozaki | Soil conditioner and method of utilizing it |
| CN1732773A (en) * | 2005-07-15 | 2006-02-15 | 中国农业科学院蔬菜花卉研究所 | A kind of soil disinfection method of facility for prevention and control soil-borne diseases of vegetable |
| CN1759646A (en) * | 2005-10-25 | 2006-04-19 | 刘建 | Planting tandem plowing type culturing method for returning full stalk to farmland suitable to zonal rice or wheat form |
| CN103477849A (en) * | 2013-09-29 | 2014-01-01 | 四川省农业科学院作物研究所 | Method for straw full-amount returning and rice-wheat planted seedling in rice-wheat double cropping area |
| CN104488397A (en) * | 2014-12-16 | 2015-04-08 | 安徽省农业科学院土壤肥料研究所 | Simplified straw-returning-to-field method applicable to clay paddy fields |
| CN104770096A (en) * | 2015-04-15 | 2015-07-15 | 滨海随耕生态农业有限公司 | Continuous cropping obstacle removal method for facility culturing soil |
Cited By (11)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106973574A (en) * | 2017-03-31 | 2017-07-25 | 广东省农业科学院农业资源与环境研究所 | The modification method in sour regurgitation field |
| CN107148823A (en) * | 2017-07-10 | 2017-09-12 | 江西农业大学 | It is a kind of to alleviate the method that early rice straw incorporation grows adverse effect to double cropping late rice |
| CN107439284A (en) * | 2017-07-26 | 2017-12-08 | 安徽省福宁米业有限公司 | A kind of rice straw turns over the implantation methods of returning to the field |
| CN107455036A (en) * | 2017-08-16 | 2017-12-12 | 巨野德福生态农业开发有限公司 | A kind of plastic shed soil modification method |
| CN108059508A (en) * | 2017-12-27 | 2018-05-22 | 西南科技大学 | A kind of new rice field dedicated fertilizer and its method of administration |
| CN108718962A (en) * | 2018-04-26 | 2018-11-02 | 湖南玖恪土壤与环境科技有限公司 | A method of reducing paddy fields in south china rice cadmium content |
| CN108811576A (en) * | 2018-07-02 | 2018-11-16 | 中国农业科学院烟草研究所 | A kind of method of vega soil improvement |
| CN111034407A (en) * | 2019-12-17 | 2020-04-21 | 石家庄亚特生物科技有限公司 | Microbial utilization technology for returning rice straws to field in northeast region |
| CN112272987A (en) * | 2020-09-22 | 2021-01-29 | 阜南县美林蓝莓科技发展有限公司 | Soil improvement method for blueberry planting |
| CN112806138A (en) * | 2020-10-16 | 2021-05-18 | 吉林省农业科学院 | Method for improving cold resistance of rice based on complete decomposition and returning of rice straw to field |
| CN113896262A (en) * | 2021-11-03 | 2022-01-07 | 河海大学 | Water pollution control treatment system for field soaking |
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