CN106966780A - A kind of soil conditioner and preparation method thereof - Google Patents

A kind of soil conditioner and preparation method thereof Download PDF

Info

Publication number
CN106966780A
CN106966780A CN201710113853.XA CN201710113853A CN106966780A CN 106966780 A CN106966780 A CN 106966780A CN 201710113853 A CN201710113853 A CN 201710113853A CN 106966780 A CN106966780 A CN 106966780A
Authority
CN
China
Prior art keywords
parts
soil conditioner
soil
temperature
preparation
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
CN201710113853.XA
Other languages
Chinese (zh)
Inventor
施春华
张美芬
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.)
Shengzhou City Paitepu Technology Development Co Ltd
Original Assignee
Shengzhou City Paitepu Technology 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 Shengzhou City Paitepu Technology Development Co Ltd filed Critical Shengzhou City Paitepu Technology Development Co Ltd
Priority to CN201710113853.XA priority Critical patent/CN106966780A/en
Publication of CN106966780A publication Critical patent/CN106966780A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B5/00Thomas phosphate; Other slag phosphates
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/60Biocides or preservatives, e.g. disinfectants, pesticides or herbicides; Pest repellants or attractants
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES 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
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/80Soil conditioners
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/40Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2101/00Agricultural use
    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K2109/00MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE pH regulation

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Organic Chemistry (AREA)
  • Pest Control & Pesticides (AREA)
  • Soil Sciences (AREA)
  • Plant Pathology (AREA)
  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Fertilizers (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

The invention provides a kind of soil conditioner and preparation method thereof, composition and its parts by weight are:12 ~ 20 parts of plant ash, 5 ~ 10 parts of phosphorus ore slags, 5 ~ 9 parts of quick limes, 2 ~ 5 parts of zeolites, 2 ~ 5 parts of attapulgites, 1 ~ 3 Fen Yi Longhai City algal gel, 2 ~ 5 parts of fruit of Chinese magnoliavine dregs of a decoction, 2 ~ 5 parts of the radix scutellariae dregs of a decoction, 20 ~ 30 parts of stalks, 8 ~ 13 parts of hickory nut shells, 0.02 ~ 0.04 part of rotenone, 10 ~ 15 parts of mangosteen shells, 3 ~ 5 parts of EM bacteria agents, 7 ~ 20 parts of urea phosphates, 8 ~ 14 parts of urea, 10 ~ 15 parts of biochemical fulvic acid potassiums, 9 ~ 12 parts of γ polyglutamic acids.Have the beneficial effect that:Soil conditioner porosity is high, and heavy metal ion has specific adsorption;Soil pH is adjusted, micronutrient levels enriches, while supplementing tri- kinds of elements of N, P, K;The gas porosity that soil conservation can be made higher, the fertility retention time is long, and retentiveness is good.

Description

A kind of soil conditioner and preparation method thereof
Technical field
The present invention relates to technical field of land improvement, specifically a kind of soil conditioner and preparation method thereof.
Background technology
With the propulsion and the raising of people's living standard of increase, the urbanization of China human mortality, industrial and mineral is looked forward to The various product demand of industry processing also increases at a high speed, and negative effect is so that industrial and mining enterprises lead in production management process Cross the harmful heavy metal (such as Cr, Cd, Pb, As) that various approach are discharged into ambient soil to be continuously increased, heavy damage nature Ecological environment and threaten people's health, therefore contaminated soil administers extremely urgent.
It is raw that the heavy metal of contaminated soil mainly includes mercury (Hg), cadmium (Cd), lead (Pb), chromium (Cr) and metalloid arsenic (As) etc. The significant element of thing toxicity, and have the elements such as the zinc (Zn), copper (Cu), nickel (Ni) of certain toxicity;Essentially from agricultural chemicals, give up Water, sludge and atmospheric sedimentation etc., such as mercury are essentially from mercury-containing waste water, and cadmium, lead contamination are essentially from smelting discharge and automobile exhaust gas Sedimentation, arsenic is then widely used as insecticide, bactericide, rat poison and herbicide.Excessive heavy metal can cause physiological function of plants Disorderly, trophic disturbance, element concentration coefficient in crop grain such as cadmium, mercury is higher, even more than food hygienic standard, also not shadow Plant growth, development and yield are rung, mercury, arsenic can weaken and suppress nitrification in soil, amonifying bacteria activity in addition, influence nitrogen is supplied Should.Heavy metal contaminants mobility very little in soil, is difficult, with water leaching, to be not microbial degradation, by food chain enter After human body, potential hazard is very big, it should be specifically noted that preventing heavy metal to soil pollution.
At present, restoration of soil polluted by heavy metal mainly passes through two kinds of approach:One is the presence for changing heavy metal in soil State, reduces its migration and bioavailability in the environment, and main recovery technique has agronomy and chemical method;Two be to utilize Engineering techniques remove removing heavy metals from soil, and main recovery technique mainly has Physical, bioanalysis.
Phytoremediation is generally acknowledged ideal original position soil Treatment process, but there is obvious shortcoming:Ultraproduct is tired to plant Often plant is short and small, biomass is relatively low, the speed of growth is slow for thing, growth cycle is long;Most of hyperaccumulative plants can only accumulate certain Heavy metal, is not suitable for compound heavy-metal contaminated soil reparation;Phytoremediation is by soil types, temperature, humidity and nutrition etc. Environmental condition is limited.
Chemical method is exactly to add soil conditioner to change the physics of soil, chemical property, by the adsorbing of heavy metal, is sunk Form sediment or co-precipitation, existence of the heavy metal in soil is changed, so as to reduce its biological effectiveness and migration.
Physical engineering measure is to utilize physics (machinery), a class method of physical and chemical principle pollution administration soil, including Heavy metal pollution of soil, elution method, heat treating process, electrolysis etc..Heavy metal pollution of soil will destroy the character of natural soils, while can also affect on to ground Lower water security;Elution method require soil must have compared with Thief zone ability, while residual eluent can produce secondary pollution Problem;Heat treating process remediation efficiency is relatively low and economic input is high, also there is the discharge of toxic gas and changing for soil Elemental characters Become;Electrolysis is limited to the characteristic of soil, is not suitable for good penetrability, the soil of conductibility difference.All in all, although Physical The heavy metal of contaminated soil can more thoroughly be removed, but exist with high costs, not be suitable for the larger soil of contaminated area, And soil texture and soil fertility are easily destroyed, and cause secondary pollution.
Prior art such as Authorization Notice No. is CN104046361B Chinese invention patent, discloses an a kind of compound huge sum of money Belong to contaminated soil conditioner and its application and application process, it includes following component:Plant ash, calcium magnesium phosphate, quick lime, zeolite And organic fertilizer, the proportioning of its weight is:Plant ash:Calcium magnesium phosphate:Quick lime:Zeolite:Hydroxyapatite:Organic fertilizer=(0.3- 1.1):(0.1-1.2):(0.4-2.1):(0.1-0.6):(0.008-0.06):(0.4-1.2).It passes through quick lime, calcium and magnesium phosphorus Heavy metal in the inorganic component fixed-contamination soil such as fertilizer, the phosphate in hydroxyapatite, potassium carbonate in plant ash, and tie Closing the organic fertilizer such as plant ash, organic fertilizer mutually improves the fertility of contaminated soil, persistently strengthens the reparation of polluted soil.The soil The ability that modifying agent fixes heavy metal is weaker, and soil fertility conservation degree and water retention property are undesirable.
The content of the invention
It is an object of the invention to provide a kind of energy Adsorption of Heavy Metals ion, its biological effectiveness and migration are reduced, is adjusted Soil pH is saved, increases soil fertility, and the retention time is long, increases soil water retention;N, P, K are supplemented simultaneously, comprehensive nutrition Soil conditioner.
The present invention is directed to the problem of being mentioned in background technology, and the technical scheme taken is:
A kind of soil conditioner, composition and its parts by weight are:12 ~ 20 parts of plant ash, 5 ~ 10 parts of phosphorus ore slags, 5 ~ 9 parts of quick lime, 2 ~ 5 parts of zeolites, 2 ~ 5 parts of attapulgites, 1 ~ 3 Fen Yi Longhai City algal gel, 2 ~ 5 parts of fruit of Chinese magnoliavine dregs of a decoction, 2 ~ 5 parts of the radix scutellariae dregs of a decoction, 20 ~ 30 parts of straw Stalk, 8 ~ 13 parts of hickory nut shells, 0.02 ~ 0.04 part of rotenone, 10 ~ 15 parts of mangosteen shells, 3 ~ 5 parts of EM bacteria agents, 7 ~ 20 parts of phosphoric acid Urea, 8 ~ 14 parts of urea, 10 ~ 15 parts of biochemical fulvic acid potassiums, 9 ~ 12 parts of gamma-polyglutamic acids.Above-mentioned soil conditioner porosity is high, Heavy metal ion has specific adsorption, can effectively reduce its biological effectiveness and migration, reduces bioaccumulation;Different Longhai City Algal gel and rotenone promote the reduction of biological effectiveness and migration by urea phosphate, adjust soil pH, improve basic soil, make It is adapted to plant growth;Micronutrient levels enriches, while tri- kinds of elements of N, P, K are supplemented, and organic fertilizer and inorganic fertilizer are combined, Fertility is sufficient, accelerates plant growth;The gas porosity that soil conservation can be made higher, the fertility retention time is long, and retentiveness is good.
A kind of preparation method of soil conditioner, is concretely comprised the following steps:
1)One time fermentation:The fruit of Chinese magnoliavine dregs of a decoction, the radix scutellariae dregs of a decoction, stalk, hickory nut shell, mangosteen shell are crushed, EM bacteria agent is added And water, material:The mass volume ratio of water is 1g:(0.5~1.1)mL.It is sufficiently mixed, places 4 ~ 6 days, heating, temperature is after heating 50 ~ 58 DEG C, the oxygen content and water content of material are detected during fermentation, it is 8 ~ 15% to control oxygen content, water content is 25 ~ 39%, hair The ferment time is 5 ~ 6 days.Strain carries out aerobic respiration, by the cellulose of material, hemicellulose, lignin, pectin Cheng little Fen Bacterium can be broken down into inorganic matter in sub- material, soil, be utilized for plant absorption;
2)Secondary fermentation:Parabolic stockpile is turned over, is fermented, temperature reaches turns over throwing again after 45 ~ 50 DEG C, continues to ferment, temperature reaches 65 ~ 78 After DEG C, spread material out drying, dry, pulverize, sieve.Step fermentation, makes the more abundant of material fermentation;
3)Calcining:By zeolite, attapulgite and phosphorus ore slag calcining, calcine by steps, temperature be 100 ~ 200 DEG C when calcining 12 ~ 15min;20 ~ 25min is calcined when temperature is 500 ~ 600 DEG C;10 ~ 15min is calcined when temperature is 1000 ~ 1200 DEG C;Temperature is 300 10 ~ 15min is calcined at ~ 400 DEG C, every section of temperature changes to be completed in 2 ~ 3min.Calcining cools after terminating, grinding.By zeolite, recessed After convex rod soil and the calcining of phosphorus ore slag, the increase of its porosity, absorption property enhancing;
4)The preparation of soil conditioner:The material mixing that step 2,3 are obtained, add plant ash, quick lime, different Longhai City's algal gel, Rotenone, urea phosphate, urea, biochemical fulvic acid potassium and gamma-polyglutamic acid, are well mixed, granulation, obtain particle diameter for 1.5 ~ 3.0mm soil conditioner.
Compared with prior art, the advantage of the invention is that:Take stepwise fermentation, and ensure the oxygen content of material and aqueous Amount, strain carries out aerobic respiration, by the cellulose of material, hemicellulose, lignin, pectin into small-molecule substance, soil Middle bacterium can be broken down into inorganic matter, be utilized for plant absorption;After zeolite, attapulgite and phosphorus ore slag are calcined, its hole Rate increase, absorption property enhancing;The soil conditioner porosity finally obtained is high, and heavy metal ion has specific adsorption, Its biological effectiveness and migration can be effectively reduced, bioaccumulation is reduced;Adjust soil pH, improvement basic soil so as to fit Plant growth;Micronutrient levels enriches, while tri- kinds of elements of N, P, K are supplemented, and organic fertilizer and inorganic fertilizer are combined, and fertility is filled Foot, accelerates plant growth;The gas porosity that soil conservation can be made higher, the fertility retention time is long, and retentiveness is good;Operating procedure letter Single, low raw-material cost, is adapted to the serious soil of heavy metal pollution and saline-alkali soil is used.
Specific embodiment
The present invention program is described further below by embodiment:
Embodiment 1:
A kind of soil conditioner, composition and its parts by weight are:12 ~ 20 parts of plant ash, 5 ~ 10 parts of phosphorus ore slags, 5 ~ 9 parts of quick lime, 2 ~ 5 parts of zeolites, 2 ~ 5 parts of attapulgites, 1 ~ 3 Fen Yi Longhai City algal gel, 2 ~ 5 parts of fruit of Chinese magnoliavine dregs of a decoction, 2 ~ 5 parts of the radix scutellariae dregs of a decoction, 20 ~ 30 parts of straw Stalk, 8 ~ 13 parts of hickory nut shells, 0.02 ~ 0.04 part of rotenone, 10 ~ 15 parts of mangosteen shells, 3 ~ 5 parts of EM bacteria agents, 7 ~ 20 parts of phosphoric acid Urea, 8 ~ 14 parts of urea, 10 ~ 15 parts of biochemical fulvic acid potassiums, 9 ~ 12 parts of gamma-polyglutamic acids.Above-mentioned soil conditioner porosity is high, Heavy metal ion has specific adsorption, can effectively reduce its biological effectiveness and migration, reduces bioaccumulation;Regulation soil Earth pH, improvement basic soil is so as to fit plant growth;Micronutrient levels enriches, while tri- kinds of elements of N, P, K are supplemented, and And organic fertilizer and inorganic fertilizer are combined, fertility is sufficient, accelerates plant growth;The gas porosity that soil conservation can be made higher, fertility is kept Time is long, and retentiveness is good.
A kind of preparation method of soil conditioner, is concretely comprised the following steps:
1)One time fermentation:The fruit of Chinese magnoliavine dregs of a decoction, the radix scutellariae dregs of a decoction, stalk, hickory nut shell, mangosteen shell are crushed, EM bacteria agent is added And water, material:The mass volume ratio of water is 1g:(0.5~1.1)mL.It is sufficiently mixed, places 4 ~ 6 days, heating, temperature is after heating 50 ~ 58 DEG C, the oxygen content and water content of material are detected during fermentation, it is 8 ~ 15% to control oxygen content, water content is 25 ~ 39%, hair The ferment time is 5 ~ 6 days.Strain carries out aerobic respiration, by the cellulose of material, hemicellulose, lignin, pectin Cheng little Fen Bacterium can be broken down into inorganic matter in sub- material, soil, be utilized for plant absorption;
2)Secondary fermentation:Stop heating, turn over parabolic stockpile, ferment, temperature reaches turns over throwing again after 45 ~ 50 DEG C, continue to ferment, temperature Reach after 65 ~ 78 DEG C, spread material out drying, dry, pulverize, sieve.Step fermentation, makes the more abundant of material fermentation;
3)Calcining:By zeolite, attapulgite and phosphorus ore slag calcining, calcine by steps, temperature be 100 ~ 200 DEG C when calcining 12 ~ 15min;20 ~ 25min is calcined when temperature is 500 ~ 600 DEG C;10 ~ 15min is calcined when temperature is 1000 ~ 1200 DEG C;Temperature is 300 10 ~ 15min is calcined at ~ 400 DEG C, every section of temperature changes to be completed in 2 ~ 3min.Calcining cools after terminating, grinding.By zeolite, recessed After convex rod soil and the calcining of phosphorus ore slag, the increase of its porosity, absorption property enhancing;
4)The preparation of soil conditioner:The material mixing that step 2,3 are obtained, add plant ash, quick lime, different Longhai City's algal gel, Rotenone, urea phosphate, urea, biochemical fulvic acid potassium and gamma-polyglutamic acid, are well mixed, granulation, obtain particle diameter for 1.5 ~ 3.0mm soil conditioner.
Embodiment 2:
A kind of soil conditioner, composition and its most preferably parts by weight are:18 parts of plant ash, 7 parts of phosphorus ore slags, 8 parts of quick lime, 4 parts Zeolite, 3 portions of attapulgites, 2 Fen Yi Longhai City algal gels, 5 portions of fruit of Chinese magnoliavine dregs of a decoction, 2 portions of the radix scutellariae dregs of a decoction, 27 portions of stalks, 10 portions of hickory nuts Shell, 0.03 part of rotenone, 13 parts of mangosteen shells, 4 parts of EM bacteria agents, 13 parts of urea phosphates, 10 parts of urea, 12 parts of biochemical fulvic acids Potassium, 10 parts of gamma-polyglutamic acids.Above-mentioned soil conditioner porosity is high, and heavy metal ion has specific adsorption, can effectively dropped Low its biological effectiveness and migration, reduce bioaccumulation;Soil pH is adjusted, improvement basic soil is so as to fit plant growth; Micronutrient levels enriches, while tri- kinds of elements of N, P, K are supplemented, and organic fertilizer and inorganic fertilizer are combined, and fertility is sufficient, accelerates to plant Thing grows;The gas porosity that soil conservation can be made higher, the fertility retention time is long, and retentiveness is good.
A kind of preparation method of soil conditioner, most preferably step is:
1)One time fermentation:The fruit of Chinese magnoliavine dregs of a decoction, the radix scutellariae dregs of a decoction, stalk, hickory nut shell, mangosteen shell are crushed, EM bacteria agent is added And water, material:The mass volume ratio of water is 1g:1mL.It is sufficiently mixed, places 5 days, heating, temperature is 55 DEG C after heating, fermentation Period detects the oxygen content and water content of material, and it is 12% to control oxygen content, and water content is 31%, and fermentation time is 6 days.Fermentation cabin In oxygen supply mainly completed by the device of aerating system, pass through the automatic test probe of temperature, humidity instrument probe, dissolved oxygen amount Probe, the temperature in straw compost, moisture, oxygen content etc. are transferred in central control computer, and central control computer again will Information transfer realizes that batch (-type) ventilation exposes the purpose of oxygen and supplement water to oxygen blower fan and moisture spray motor is exposed;Strain is had Oxygen is breathed, by the cellulose of material, hemicellulose, lignin, pectin into small-molecule substance, and bacterium can be by its point in soil Solution is utilized into inorganic matter for plant absorption;
2)Secondary fermentation:Stop heating, turn over parabolic stockpile, ferment, temperature is recorded daily, temperature reaches turns over throwing again after 48 DEG C, after Supervention ferment, temperature is reached after 72 DEG C, is spread material out drying, be dry, pulverize, sieving.Step fermentation, makes more filling for material fermentation Point, decomposition dissolution a great number of elements and trace element;
3)Calcining:By the calcining of zeolite, attapulgite and phosphorus ore slag, calcine by steps, temperature calcines 15min when being 100 ~ 200 DEG C;Temperature Spend for 500 ~ 600 DEG C when calcine 25min;Temperature calcines 15min when being 1000 ~ 1200 DEG C;Temperature is calcined when being 300 ~ 400 DEG C 15min, every section of temperature changes to be completed in 2 ~ 3min.Calcining cools after terminating, grinding.By zeolite, attapulgite and phosphorus ore slag After calcining, the increase of its porosity, absorption property enhancing;
4)The preparation of soil conditioner:The material mixing that step 2,3 are obtained, add plant ash, quick lime, different Longhai City's algal gel, Rotenone, urea phosphate, urea, biochemical fulvic acid potassium and gamma-polyglutamic acid, are well mixed, granulation, obtain particle diameter for 1.5 ~ 3.0mm soil conditioner.
Routine operation in the operating procedure of the present invention is well known to those skilled in the art, herein without repeating.
Technical scheme is described in detail embodiment described above, it should be understood that it is described above only For the specific embodiment of the present invention, it is not intended to limit the invention, all any modifications made in the spirit of the present invention, Supplement or similar fashion replacement etc., should be included in the scope of the protection.

Claims (8)

1. a kind of soil conditioner, it is characterised in that composition and its parts by weight are:12 ~ 20 parts of plant ash, 5 ~ 10 parts of phosphorus ore slags, 5 ~ 9 parts of quick limes, 2 ~ 5 parts of zeolites, 2 ~ 5 parts of attapulgites, 1 ~ 3 Fen Yi Longhai City algal gel, 2 ~ 5 parts of fruit of Chinese magnoliavine dregs of a decoction, 2 ~ 5 parts of radix scutellariae medicines Slag, 20 ~ 30 parts of stalks, 8 ~ 13 parts of hickory nut shells, 0.02 ~ 0.04 part of rotenone, 10 ~ 15 parts of mangosteen shells, 3 ~ 5 parts of EM bacterium Agent, 7 ~ 20 parts of urea phosphates, 8 ~ 14 parts of urea, 10 ~ 15 parts of biochemical fulvic acid potassiums, 9 ~ 12 parts of gamma-polyglutamic acids.
2. a kind of preparation method of soil conditioner, it is characterised in that following steps:
1)One time fermentation:The fruit of Chinese magnoliavine dregs of a decoction, the radix scutellariae dregs of a decoction, stalk, hickory nut shell, mangosteen shell are crushed, EM bacteria agent is added And water, it is sufficiently mixed, places, heats up, fermentation;
2)Secondary fermentation:Parabolic stockpile is turned over, is fermented, then turns over throwing, continues to ferment, after the completion of fermentation, spreads material out drying, do It is dry, crush, sieving;
3)Calcining:By the calcining of zeolite, attapulgite and phosphorus ore slag, calcining cools after terminating, grinding;
4)The preparation of soil conditioner:The material mixing that step 2,3 are obtained, add plant ash, quick lime, different Longhai City's algal gel, Rotenone, urea phosphate, urea, biochemical fulvic acid potassium and gamma-polyglutamic acid, are well mixed, and granulation obtains soil conditioner.
3. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:Thing in described step 1 Material:The mass volume ratio of water is 1g:(0.5~1.1)mL.
4. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:Put in described step 1 The time is put for 4 ~ 6 days.
5. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:Risen in described step 1 Temperature is 50 ~ 58 DEG C after temperature, and the oxygen content and water content of material are detected during fermentation, and it is 8 ~ 15% to control oxygen content, and water content is 25 ~ 39%, fermentation time is 5 ~ 6 days.
6. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:In described step 2 Once turn over temperature after throwing and reach 45 ~ 50 DEG C, then carry out turning over throwing, temperature is reached after 65 ~ 78 DEG C, spreads material out drying.
7. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:Divide in described step 3 Section calcining, calcines 12 ~ 15min when temperature is 100 ~ 200 DEG C;20 ~ 25min is calcined when temperature is 500 ~ 600 DEG C;Temperature is 1000 10 ~ 15min is calcined at ~ 1200 DEG C;10 ~ 15min is calcined when temperature is 300 ~ 400 DEG C, every section of temperature changes complete in 2 ~ 3min Into.
8. a kind of preparation method of soil conditioner according to claim 2, it is characterised in that:It is native in described step 4 Earth modifying agent particle diameter is 1.5 ~ 3.0mm.
CN201710113853.XA 2017-02-28 2017-02-28 A kind of soil conditioner and preparation method thereof Pending CN106966780A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710113853.XA CN106966780A (en) 2017-02-28 2017-02-28 A kind of soil conditioner and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710113853.XA CN106966780A (en) 2017-02-28 2017-02-28 A kind of soil conditioner and preparation method thereof

Publications (1)

Publication Number Publication Date
CN106966780A true CN106966780A (en) 2017-07-21

Family

ID=59329291

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710113853.XA Pending CN106966780A (en) 2017-02-28 2017-02-28 A kind of soil conditioner and preparation method thereof

Country Status (1)

Country Link
CN (1) CN106966780A (en)

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107384435A (en) * 2017-09-07 2017-11-24 李满旺 A kind of soil conditioner for heavy metal of degrading
CN107935693A (en) * 2017-11-30 2018-04-20 浦江县美泽生物科技有限公司 The preparation method of pot flowers organic fertilizer
CN108130088A (en) * 2018-01-17 2018-06-08 深圳市晟祥知识产权有限公司 A kind of saline-alkali land soil conditioner and its preparation method and application
CN108424272A (en) * 2018-05-28 2018-08-21 四川国康农业科技有限公司 A kind of long acting multifunction composite microbe fertilizer and its production technology
CN110330982A (en) * 2019-02-11 2019-10-15 权冉(银川)科技有限公司 A kind of material of the soil sanitation reparation of adjustable function
CN110423624A (en) * 2019-09-03 2019-11-08 森特士兴集团股份有限公司 A kind of stabilization renovation agent of soil pollution and preparation and application
CN111875439A (en) * 2020-08-14 2020-11-03 内蒙古呼日呼惜美土生物科技有限公司 Method for preparing bio-organic fertilizer by adding niuxin grass
CN112250503A (en) * 2020-10-26 2021-01-22 沈阳瑞元德生物科技有限公司 Natural adsorption material compounded bio-organic fertilizer and preparation method thereof
CN112624857A (en) * 2021-02-24 2021-04-09 云南省生态环境科学研究院 Ecological restoration base material for restoring mine wasteland and preparation method thereof
CN112840787A (en) * 2021-02-24 2021-05-28 云南省生态环境科学研究院 Method for repairing mine wasteland
CN113136209A (en) * 2020-01-20 2021-07-20 成都新朝阳作物科学股份有限公司 Soil remediation agent and application thereof
CN114262245A (en) * 2020-09-16 2022-04-01 通海县金元有机肥有限公司 Organic fertilizer capable of preventing soil hardening damage and production method thereof
CN115012386A (en) * 2022-06-23 2022-09-06 中化地质河南局集团有限公司 Improvement method for weakening foundation loess collapsibility
CN115404083A (en) * 2022-08-24 2022-11-29 雨木林风(云南)科技有限公司 Soil heavy metal modifier and preparation and use methods thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103524247A (en) * 2013-10-25 2014-01-22 安徽环绿生态农业投资发展有限公司 Method for producing organic fertilizer by utilizing poultry and livestock excrement
CN104788263A (en) * 2015-04-16 2015-07-22 王龙潮 Composite soil conditioner
CN105964672A (en) * 2016-03-17 2016-09-28 凤阳徽亨商贸有限公司 Environmental friendly soil heavy metal restoration agent
CN106008113A (en) * 2016-07-20 2016-10-12 安徽三星化工有限责任公司 Organic fertilizer for improving dry farmland soil
CN106008112A (en) * 2016-07-20 2016-10-12 安徽三星化工有限责任公司 Organic and inorganic compound fertilizer
CN106699388A (en) * 2016-12-28 2017-05-24 贵州省贵福生态肥业有限公司 Heavy metal catching fertilizer

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103524247A (en) * 2013-10-25 2014-01-22 安徽环绿生态农业投资发展有限公司 Method for producing organic fertilizer by utilizing poultry and livestock excrement
CN104788263A (en) * 2015-04-16 2015-07-22 王龙潮 Composite soil conditioner
CN105964672A (en) * 2016-03-17 2016-09-28 凤阳徽亨商贸有限公司 Environmental friendly soil heavy metal restoration agent
CN106008113A (en) * 2016-07-20 2016-10-12 安徽三星化工有限责任公司 Organic fertilizer for improving dry farmland soil
CN106008112A (en) * 2016-07-20 2016-10-12 安徽三星化工有限责任公司 Organic and inorganic compound fertilizer
CN106699388A (en) * 2016-12-28 2017-05-24 贵州省贵福生态肥业有限公司 Heavy metal catching fertilizer

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
揭益寿等: "《中国农业发展模式创新与农业现代化 第2版》", 31 January 2013, 中国矿业大学出版社 *

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107384435A (en) * 2017-09-07 2017-11-24 李满旺 A kind of soil conditioner for heavy metal of degrading
CN107935693A (en) * 2017-11-30 2018-04-20 浦江县美泽生物科技有限公司 The preparation method of pot flowers organic fertilizer
CN108130088A (en) * 2018-01-17 2018-06-08 深圳市晟祥知识产权有限公司 A kind of saline-alkali land soil conditioner and its preparation method and application
CN108424272A (en) * 2018-05-28 2018-08-21 四川国康农业科技有限公司 A kind of long acting multifunction composite microbe fertilizer and its production technology
CN110330982A (en) * 2019-02-11 2019-10-15 权冉(银川)科技有限公司 A kind of material of the soil sanitation reparation of adjustable function
CN110423624A (en) * 2019-09-03 2019-11-08 森特士兴集团股份有限公司 A kind of stabilization renovation agent of soil pollution and preparation and application
CN113136209A (en) * 2020-01-20 2021-07-20 成都新朝阳作物科学股份有限公司 Soil remediation agent and application thereof
CN111875439A (en) * 2020-08-14 2020-11-03 内蒙古呼日呼惜美土生物科技有限公司 Method for preparing bio-organic fertilizer by adding niuxin grass
CN114262245A (en) * 2020-09-16 2022-04-01 通海县金元有机肥有限公司 Organic fertilizer capable of preventing soil hardening damage and production method thereof
CN112250503A (en) * 2020-10-26 2021-01-22 沈阳瑞元德生物科技有限公司 Natural adsorption material compounded bio-organic fertilizer and preparation method thereof
CN112624857A (en) * 2021-02-24 2021-04-09 云南省生态环境科学研究院 Ecological restoration base material for restoring mine wasteland and preparation method thereof
CN112840787A (en) * 2021-02-24 2021-05-28 云南省生态环境科学研究院 Method for repairing mine wasteland
CN115012386A (en) * 2022-06-23 2022-09-06 中化地质河南局集团有限公司 Improvement method for weakening foundation loess collapsibility
CN115404083A (en) * 2022-08-24 2022-11-29 雨木林风(云南)科技有限公司 Soil heavy metal modifier and preparation and use methods thereof

Similar Documents

Publication Publication Date Title
CN106966780A (en) A kind of soil conditioner and preparation method thereof
Zhang et al. Immobilization and bioavailability of heavy metals in greenhouse soils amended with rice straw-derived biochar
Choudhary et al. Impact of fluoride on agriculture: A review on it’s sources, toxicity in plants and mitigation strategies
CN104056852B (en) The chemistry of compound heavy-metal contaminated soil and microbial association restorative procedure and application
CN105713619B (en) Method for preparing iron silicon sulfur multi-element composite biochar soil heavy metal conditioner
Liu et al. Immobilization and phytotoxicity of Cd in contaminated soil amended with chicken manure compost
Chen et al. Synergistic effects of plant growth-promoting Neorhizobium huautlense T1-17 and immobilizers on the growth and heavy metal accumulation of edible tissues of hot pepper
WO2017020536A1 (en) Particle for treatment and repairing of soil contamination and repairing method
CN104046361A (en) Composite heavy metal polluted soil conditioner as well as application and application method thereof
CN106734161A (en) A kind of APP combined remediation methods for heavy metal pollution reparation of ploughing
CN105170621A (en) Method for restoring heavy metal contaminated soil through activating agent and microorganism reinforced plants
CN106905980A (en) A kind of heavy metal sewage sludge soil-repairing agent, preparation method and its application in sludge is dissolved
CN101928179A (en) Slow release fertilizer having soil remediation function and soil contamination remediation method
CN104338741A (en) Heavy metal polluted soil repairing agent with high content of biocarbon and humus and application method thereof
CN108856282B (en) Composite remediation method for heavy metal contaminated farmland soil
CN110724012A (en) Conditioner for repairing south alkaline cadmium-polluted soil and preparation and use methods thereof
CN105170619B (en) A method of repairing and improve heavy-metal contaminated soil
CN105885855A (en) Efficient soil remediation agent and preparing method thereof
CN110407649A (en) A kind of multiple-effect renovation agent of heavy-metal contaminated soil and preparation method thereof
CN106699443A (en) Conditioner for promoting selenium activation in selenium-containing dry land soil
CN106914484A (en) The ecological restoring method of rural area noxious waste pollution soil
CN104178178A (en) Organic amendment capable of passivating Cu, Zn and Pb in soil of vegetable field
Bashir et al. The role of different organic amendments to improve maize growth in wastewater irrigated soil
CN108817069A (en) A kind of heavy metallic activation agent and its application in soil joint is repaired
CN107879850A (en) A kind of acid heavy metal polluted soil of farmland conditioner and its preparation method and application

Legal Events

Date Code Title Description
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20170721

RJ01 Rejection of invention patent application after publication