CN106612702A - Protected area vegetable soil ecological remediation method - Google Patents

Protected area vegetable soil ecological remediation method Download PDF

Info

Publication number
CN106612702A
CN106612702A CN201611270571.2A CN201611270571A CN106612702A CN 106612702 A CN106612702 A CN 106612702A CN 201611270571 A CN201611270571 A CN 201611270571A CN 106612702 A CN106612702 A CN 106612702A
Authority
CN
China
Prior art keywords
soil
vegetable
restorative procedure
protected field
beneficial
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.)
Pending
Application number
CN201611270571.2A
Other languages
Chinese (zh)
Inventor
白京波
燕增文
于强
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shandong Siyuan Agricultural Development Co Ltd
Original Assignee
Shandong Siyuan Agricultural Development Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Shandong Siyuan Agricultural Development Co Ltd filed Critical Shandong Siyuan Agricultural Development Co Ltd
Priority to CN201611270571.2A priority Critical patent/CN106612702A/en
Publication of CN106612702A publication Critical patent/CN106612702A/en
Pending legal-status Critical Current

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B79/00Methods for working soil
    • A01B79/02Methods for working soil combined with other agricultural processing, e.g. fertilising, planting

Abstract

The invention discloses a protected area vegetable soil ecological remediation method. The method is characterized by comprising the steps of removing hazardous organisms in soil; removing hazardous substance in the soil; supplementing soil beneficial microorganisms; supplementing microelements in the soil. Due to adopting the technical scheme, according to the protected area vegetable soil ecological remediation method, by soil close plastic shed disinfection, relevant technologies of soil conditioning, hazardous organism conditioning in the soil, hazardous substance removing in the soil, the soil beneficial microorganism (actinomycetes, saccharomycetes, bacillus and the like) supplementing, microelement supplementing in the soil and the like are begun with, the problem of deficient organic matter and microelements in the soil is solved completely, and the soil granular structure, buffer ability and pH value are recovered; soil beneficial microorganism bacterial flora is balanced, soil-borne diseases and insect pests are inhibited, and the purposes of greenness of protected area vegetable, sustainability, ecological controllability and friendly environment are achieved.

Description

Vegetable at protected field soil ecology restorative procedure
Technical field
The present invention relates to agricultural technology field, more particularly to a kind of vegetable at protected field soil ecology restorative procedure.
Background technology
Protecting field plastic shed soil ecological environment abuses fertilizer and pesticide and control measures are improper and destroyed, soil due to abuse The problems such as earth acidifying, salination, continuous cropping obstacle, soil-borne disease insect pest, starts generation and with cultivation in the continuous cropping booth of more than 3 years The prolongation of time is increasingly weighed, it has also become the restriction problem that vegetable at protected field is sustainable, Green Development is urgently to be resolved hurrily.
The content of the invention
The technical problem to be solved in the present invention is to overcome drawbacks described above, there is provided one kind efficiently solves current booth vegetable life Soil issues present in product, have effectively recovered the ecological balance and health of protecting field soil, it is ensured that the sustainable development in soil Exhibition, realizes green, the efficient and safe vegetable at protected field soil ecology restorative procedure of growing vegetables industry.
To solve the above problems, the technical solution adopted in the present invention is:
Vegetable at protected field soil ecology restorative procedure, it is characterised in that:Comprise the following steps:
Remove the harmful organism in soil;
Remove the harmful substance in soil;
Supplement soil beneficial microbe;
Supplement Trace Elements in Soil.
As a kind of improvement:In removing the harmful substance step in the harmful organism and removing soil in soil, by soil Disinfectant is applied with water punching, the closed vexed canopy of booth 15 to 20 days, mat shelter 15 to 20 days.
As a kind of improvement:The soil sterilants includes 1,3- dichloropropylenes, cyanamide, cyanogas and water, and mass ratio is 75∶3∶2∶20。
As a kind of improvement:In soil beneficial microbe step is supplemented, peptide element living protein, the peptide element living protein are added Including organic matter >=30%, beneficial bacterium >=200,000,000/g.
As a kind of improvement:In soil beneficial microbe step is supplemented, bio-bacterial manure, bio-bacterial manure is added to include unwrapping wire Bacterium, Trichoderma, bacillus subtilis bacterial content >=2,000,000,000/gram.
As a kind of improvement:In Trace Elements in Soil step is supplemented, trace element fertilizer, the trace element fertilizer are added Including silicon 20%, calcium 30%, potassium 10%, iron 3%, sulphur 8%, chitin 0.05%, boron, zinc, manganese, copper, magnesium total content >=10%.
As a kind of improvement:Also include raw manure fermentation.
As a kind of improvement:In raw manure fermentation step, organic zymophyte, organic zymophyte is added to have in raw excrement Beneficial viable bacteria total amount >=200,000,000/g.
As a result of above-mentioned technical proposal, the present invention from conditioning soil, is removed in soil by the vexed canopy sterilization of soil Harmful organism (nematode, insect, germ etc.), harmful substance (nitrite, salt ion, the root exudates removed in soil Deng), supplement soil beneficial microbe (actinomyces, saccharomycete, bacillus etc.), supplement Trace Elements in Soil (boron, silicon, calcium, Zinc, iron, molybdenum, copper etc.) etc. correlation technique start with, thoroughly solve the soil organism, trace element scarcity problem, recover soil granular Structure, buffer capacity and P in soil H value;Balanced soil beneficial microbe colony, suppresses the generation of soil-borne disease insect pest, realizes protection Ground vegetables production green, sustainable and ecology is controllable, eco-friendly target.
Specific embodiment
Embodiment:
Vegetable at protected field soil ecology restorative procedure, comprises the following steps:
Selection 7, August part temperature is high, illumination is strong has a rest a batch phase, removes in canopy after all invalid bodies, weeds, discarded object, soil Earth carries out rotary tillage, leveling, ridging, overlay film.
Remove the harmful organism in soil;Soil sterilants is applied with water punching, the closed vexed canopy of booth 15 to 20 days, mat shelter 15 By 20 days.The soil sterilants includes 1,3- dichloropropylenes, cyanamide, cyanogas and water, and mass ratio is 75: 3: 2: 20.Pass through Fumigation action, effectively kills germ, worm's ovum and the weed seed of soil, thorough cleaning soil.
Nitrolim also known as lime nitrogen, with lime nitrogen as raw material, with effect of sulfuric acid and be obtained cyanamide solution.In a kettle. Input water, with cryosel water cooling, puts into lime nitrogen, maintains the temperature between 0~15 DEG C, and 5% sulfuric acid solution is added dropwise, and adjusts pH= 6,20min is kept, filter, wash, in returning again to reactor, lime nitrogen is added, repeat aforesaid operations 2 times, by the mistake for obtaining Filtrate carries out film concentration, keeps certain temperature, and cyanamide solution is obtained after concentration.
Remove the harmful substance in soil;In vexed canopy, Sui Shuichong applies soil sterilants, and under the dilution of water Eh is reduced Value, when being down to 160mv, many heavy metals all can generate the sulfide of slightly solubility and reduce its toxicity.
For the soil of heavy metal slight pollution, acid ground liming, soil pH value can be improved, make cadmium, zinc, copper, Mercury etc. forms hydroxide precipitation, so as to reduce their concentration in soil, reduces the harm to plant.
Supplement soil beneficial microbe;Add peptide element living protein, peptide element living protein includes organic matter >=30%, beneficial Bacterium >=200,000,000/g.Add bio-bacterial manure, bio-bacterial manure include actinomyces, Trichoderma, bacillus subtilis bacterial content >=2,000,000,000/gram. Crop rhizosphere forms large-scale superior microorganism flora, other pathogens of antagonism and root-knot nematode.
Supplement Trace Elements in Soil.Trace element fertilizer, the trace element fertilizer is added to include silicon 20%, calcium 30%, potassium 10%, iron 3%, sulphur 8%, chitin 0.05%, boron, zinc, manganese, copper, magnesium total content >=10%.Science is micro- in supplementing, Reduce physiological disturbance.
Peptide element living protein, microbial-bacterial fertilizer and trace element fertilizer are sprinkled into furrow varus and enter soil leveling.
Also include raw manure fermentation.Add organic zymophyte in raw excrement, beneficial viable bacteria total amount >=2 of the organic zymophyte Hundred million/g.Using the raw excrement of organic fermenting bacterial preparation fermentation, pathogen, the worm's ovum in the middle of the raw excrement of removing etc., from Sources controlling, while rotten Ripe, activation and the nutrient content and utilization rate of the raw excrement of raising.
Also include addition chemical fertilizer.Determine chemical fertilizer reasonable employment amount, reduce soil salt.
By above-mentioned measure, the soil organism and nutrient content can be increased, soil physico-chemical property can be improved and be particularly soil Earth colloidal nature, can increase volume weight of soils again, improve purification capacity of soil.By heavy metal and the soil of pollution by pesticides, enrich Organic fertilizer can increase adsorption capacity of the soil colloid to it, while agron can be complexed polluter, significantly improve soil Earth is passivated the ability of pollutant, so as to weaken its murder by poisoning to plant.Increase beneficial bacterium, some harmful substances in soil may be used also With by biodegradable.
By using peptide element living protein, increase organic matter and protein content, reduce fertilizer application amount, suitable earthworm can be created The prolific environment of earthworm.Earthworm is a kind of biology that can improve soil self purification activity, using it can also process municipal refuse and The harmful substance such as trade waste and agricultural chemicals, heavy metal.Therefore, earthworm is described as " ecological strong man " and " net by people Change device " etc..Expand numerous earthworm and can reach removing harmful substance this purpose.
For the improvement of heavy-metal contaminated soil, mainly by it is biological prosthetic, using lime, applying organic manure, tune of pouring water The measures such as section Soil Eh, reduce or eliminate pollution.For the preventing and treating of organic pollution, by applying organic manure material, using micro- Biodegradable microbial inoculum, the regulation and control measure such as soil pH and Eh, accelerate the degraded of pollutant, so as to eliminate pollution.
By Experimental Comparison, the present invention to the average prevention effect of nematodiasis up to more than 98%, imitate by the preventing and treating to root rot Fruit reaches more than 97%, can effectively kill harmful organism and the root exudates such as pathogenic bacteria, weeds, insect, nematode in soil Etc. harmful substance.From the sterilization effect to soil, the control effect to disease, mend the growth of microbial total quantity and flora after bacterium The comprehensive analysis such as structure optimization and cost benefit, this soil ecological reestablishment is simple to operate, and consumption is few, effect is high, to vegetable Dish safety, the soil texture is had no adverse effects.Low cost, high efficiency, it is suitable for large area applications.
Proved by the test in the domestic main vegetable at protected field place of production, using technical scheme after, equal mu saving 78.0 yuan of agricultural chemicals expense, saves 300 yuan of recruitment, saves chemical fertilizer and puts into 268.5 yuan, and meter mu is cost-effective 646.5 yuan.Average mu volume increase 1026 kilograms, it is 1378.6 yuan that mu increases benefit, and the newly-increased net earnings of mu newly-increased 2025.1 yuan of net earnings, i.e. unit scale is 2025.1 yuan.
One embodiment of the present of invention has been described in detail above, but the content is only the preferable enforcement of the present invention Example, it is impossible to be considered as the practical range for limiting the present invention.All impartial changes made according to the present patent application scope and improvement Deng, all should belong to the present invention patent covering scope within.

Claims (8)

1. vegetable at protected field soil ecology restorative procedure, it is characterised in that:Comprise the following steps:
Remove the harmful organism in soil;
Remove the harmful substance in soil;
Supplement soil beneficial microbe;
Supplement Trace Elements in Soil.
2. vegetable at protected field soil ecology restorative procedure according to claim 1, it is characterised in that:Remove having in soil In harmful substance step in the biological soil with removing of evil, soil sterilants is applied with water punching, the closed vexed canopy of booth 15 to 20 days, Mat shelter 15 to 20 days.
3. vegetable at protected field soil ecology restorative procedure according to claim 1, it is characterised in that:The soil sterilants Including 1,3- dichloropropylenes, cyanamide, cyanogas and water, mass ratio is 75: 3: 2: 20.
4. vegetable at protected field soil ecology restorative procedure according to claim 1, it is characterised in that:Supplementing, soil is beneficial In microbial step, peptide element living protein, the peptide element living protein is added to include organic matter >=30%, beneficial bacterium >=200,000,000/g.
5. vegetable at protected field soil ecology restorative procedure according to claim 4, it is characterised in that:Supplementing, soil is beneficial In microbial step, add bio-bacterial manure, bio-bacterial manure include actinomyces, Trichoderma, bacillus subtilis bacterial content >=2,000,000,000/ Gram.
6. vegetable at protected field soil ecology restorative procedure according to claim 1, it is characterised in that:It is micro- in soil is supplemented In secondary element step, trace element fertilizer, the trace element fertilizer is added to include silicon 20%, calcium 30%, potassium 10%, iron 3%, sulphur 8%, chitin 0.05%, boron, zinc, manganese, copper, magnesium total content >=10%.
7. according to one of them described vegetable at protected field soil ecology restorative procedure of claim 1 to 6, it is characterised in that:Also Including raw manure fermentation.
8. vegetable at protected field soil ecology restorative procedure according to claim 7, it is characterised in that:In raw manure fermentation step In, add organic zymophyte in raw excrement, the beneficial viable bacteria total amount >=200,000,000/g of the organic zymophyte.
CN201611270571.2A 2016-12-24 2016-12-24 Protected area vegetable soil ecological remediation method Pending CN106612702A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611270571.2A CN106612702A (en) 2016-12-24 2016-12-24 Protected area vegetable soil ecological remediation method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611270571.2A CN106612702A (en) 2016-12-24 2016-12-24 Protected area vegetable soil ecological remediation method

Publications (1)

Publication Number Publication Date
CN106612702A true CN106612702A (en) 2017-05-10

Family

ID=58838424

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611270571.2A Pending CN106612702A (en) 2016-12-24 2016-12-24 Protected area vegetable soil ecological remediation method

Country Status (1)

Country Link
CN (1) CN106612702A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110073861A (en) * 2019-06-11 2019-08-02 山东思远农业开发有限公司 A kind of bilayer composite type greenhouse
CN110622645A (en) * 2019-10-23 2019-12-31 北京嘉博文生物科技有限公司 Soil improvement method

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1868274A (en) * 2006-06-06 2006-11-29 郑建秋 Method for killing various kinds of harmfull bioses in soil
CN1868255A (en) * 2006-06-06 2006-11-29 郑建秋 Method for killing various kinds of harmful bioses in soil of green-house
CN104186057A (en) * 2014-08-21 2014-12-10 辽宁省农业科学院微生物工程中心 Method for preventing and treating plant soil-borne diseases and cultivating anti-bacteria cultivation soil
CN104429211A (en) * 2013-11-07 2015-03-25 济南兆龙科技发展有限公司 Soil fumigation and activation method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1868274A (en) * 2006-06-06 2006-11-29 郑建秋 Method for killing various kinds of harmfull bioses in soil
CN1868255A (en) * 2006-06-06 2006-11-29 郑建秋 Method for killing various kinds of harmful bioses in soil of green-house
CN100455183C (en) * 2006-06-06 2009-01-28 郑建秋 Method for killing various kinds of harmful bioses in soil of green-house
CN104429211A (en) * 2013-11-07 2015-03-25 济南兆龙科技发展有限公司 Soil fumigation and activation method
CN104186057A (en) * 2014-08-21 2014-12-10 辽宁省农业科学院微生物工程中心 Method for preventing and treating plant soil-borne diseases and cultivating anti-bacteria cultivation soil

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110073861A (en) * 2019-06-11 2019-08-02 山东思远农业开发有限公司 A kind of bilayer composite type greenhouse
CN110622645A (en) * 2019-10-23 2019-12-31 北京嘉博文生物科技有限公司 Soil improvement method
CN110622645B (en) * 2019-10-23 2022-07-15 北京嘉博文生物科技有限公司 Soil improvement method

Similar Documents

Publication Publication Date Title
Bonanomi et al. Repeated applications of organic amendments promote beneficial microbiota, improve soil fertility and increase crop yield
Baweja et al. Fertilizers and pesticides: Their impact on soil health and environment
Abdel-Raouf et al. Agricultural importance of algae
CN104056852B (en) The chemistry of compound heavy-metal contaminated soil and microbial association restorative procedure and application
Brevik Soil health and productivity
Renuka et al. Wastewater grown microalgal biomass as inoculants for improving micronutrient availability in wheat
Lopez-Mondejar et al. Utilisation of citrus compost-based growing media amended with Trichoderma harzianum T-78 in Cucumis melo L. seedling production
CN106478288A (en) A kind of soil conditioner of utilization microbial degradation Pesticide Residue in Soil
CN104311335B (en) Have soil-repairing agent and the preparation technology of process heavy metal contamination and getting fat effect concurrently
CN104311334B (en) Composite modifying agent and preparation technology for restoration of soil polluted by heavy metal
Kamal et al. Improving hybrid Pennisetum growth and cadmium phytoremediation potential by using Bacillus megaterium BM18-2 spores as biofertilizer
RU2437864C1 (en) Method of microbiological processing of bird droppings
CN109220035A (en) A kind of control method of muskmelon continuous cropping obstacle
CN105859338A (en) Functional microbial soil conditioner and preparation method thereof
Jaybhaye et al. Influence of Vermiwash on Germination and Growth Parameters of Seedlings of Green gram (Vigna radiata L.) and Black gram (Vigna mungo L.)
CN102284475B (en) Soil micro-ecological environment restoration method for preventing and treating soil-borne diseases
Sethi et al. Bringing Lab to Our Home: Bio-Enzyme and its Multiutility in Everyday Life
CN103739410A (en) Preparation method of organic watermelon continuous cropping high-yield composite bacterial fertilizer
CN105541513A (en) Compound multifunctional soil remediation agent and preparation method thereof
CN104591815B (en) A kind of efficient method for killing pathogen in vegetables residuum compost
Younas et al. A comprehensive review on impact of microorganisms on soil and plant
CN106612702A (en) Protected area vegetable soil ecological remediation method
CN108424182A (en) A kind of application of biogas slurry concentrate in prevention tomato root-knot eelworm disease
Ansari Soil profile studies during bioremediation of sodic soils through the application of organic amendments (vermiwash, tillage, green manure, mulch, earthworms and vermicompost)
CN111229807A (en) Soil remediation method

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