CN108329082A - A kind of environmental protection heavy metal-polluted soil stabilizer - Google Patents
A kind of environmental protection heavy metal-polluted soil stabilizer Download PDFInfo
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- CN108329082A CN108329082A CN201711309614.8A CN201711309614A CN108329082A CN 108329082 A CN108329082 A CN 108329082A CN 201711309614 A CN201711309614 A CN 201711309614A CN 108329082 A CN108329082 A CN 108329082A
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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
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B1/00—Superphosphates, i.e. fertilisers produced by reacting rock or bone phosphates with sulfuric or phosphoric acid in such amounts and concentrations as to yield solid products directly
- C05B1/02—Superphosphates
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- 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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- 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
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- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K17/00—Soil-conditioning materials or soil-stabilising materials
- C09K17/40—Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
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- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
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- C09K2101/00—Agricultural use
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- 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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Abstract
The present invention discloses a kind of environmentally friendly heavy metal-polluted soil stabilizer, the material matched by following parts by weight is made, 15 33 parts of sodium dihydrogen phosphate, 20 31 parts of bentonite, 14 31 parts of potassium chloride, 11 21 parts of polyvinyl alcohol, 14 31 parts of diethylene triamine pentacetic acid (DTPA), 8 40 parts of carbide slag, 25 40 parts of mushroom dreg, 15 28 parts of carboxymethyl chitosan, 17 31 parts of polyacrylamide, 7 11 parts of calcium magnesium phosphate, 28 33 parts of calcium superphosphate, 13 23 parts of boric acid, 28 37 parts of zinc sulfate, 1 21 parts of amino acid 1, 9 14 parts of humic acid, 13 18 parts of complex enzyme formulation, 46 parts of Needle of Slash Pine, 46 parts of Pseudomonas fluorescens bacterium powder;The heavy metal-polluted soil stabilizer provided through the invention cooperatively forms crosslinking net chelate with contents of many kinds of heavy metal ion, various heavy passivation in soil can be stablized, reduce soil aciditiy, culture fertility, reach fertile soil, improvement soil property, the purpose for preventing soil to be passivated, reaches the stabilization and environmental-friendlyization of heavy-metal composite pollution object.
Description
Technical field
Present invention relates particularly to heavy-metal contaminated soils to administer and recovery technique field, and in particular to a kind of environmental protection soil weight
Metallic stabilizer.
Background technology
China's Heavy Metals In Environment is more serious and universal, Heavy Metals In Environment not only influence crops and
The yield and quality of aquatic products, and it is related to air and quality of water environment, and the life of the mankind can be endangered by food chain and be good for
Health.It is between heavy metal different shape, different heavy metals and mutual with other pollutants in environment due to sources of heavy metal complexity
Effect, the complexity for generating various combined pollutions increases the difficulty studied heavy metal, and heavy metal is to animals and plants and human body
Harm have chronicity, potentiality and irreversibility.
Therefore, Heavy Metal Pollution Control technology will become in one period from now in the hot spot in heavy metal pollution field
Hold.In view of the above problems, China has carried out this respect research, in the hope of solving the problems, such as.Application publication number is:
1. heavy metal-polluted soil heavy metal-polluted soil renovation agent and its application-to combining contaminated soil
CN201310677528.8 can be used to improve yield of the plants such as capsicum on heavy metal joint contaminated soil, Wu Fayou
Effect ground, which adsorbs the free heavy metal ion in soil, to be fixed, the acidity of sweetening of the soil.
2. heavy metal-polluted soil heavy metal-polluted soil renovation agent and its application-CN201310677304.7 to high pollution soil,
It can be used to improve the growing states and/or quality of the plants on heavy metal high pollution soil such as balsam pear, it equally can not be effective
Ground, which adsorbs the free heavy metal ion in soil, to be fixed, the acidity of sweetening of the soil.
3. heavy metal-polluted soil renovation agent and its application-CN201310200934.5, can chromium and/or cadmium in rehabilitating soil (and/
Or lead) pollution, improve the chromium and/or cadmium (and/or lead) residual of planted plant, and have the function of synergy, but
It is the acidity for being equally unable to sweetening of the soil, heavy metal or absorption in soil can not be made or be chelated or be degraded.
4. use in conjunction-the CN201310668985.0 of Agrotechnical formulation containing selenium and heavy metal-polluted soil renovation agent, can enhance
The effect of heavy metal-polluted soil renovation agent significantly reduces the content of the heavy metals such as the cadmium in plant (especially vegetable seeds), but not
Heavy metal in soil ion releasing can be prevented with the acidity of sweetening of the soil, while supplement the nutrition of crop needs, activating soil is anti-
Only it is passivated.
5. use in conjunction-the CN201310677949.0 of zinc selenium Agrotechnical formulation and heavy metal-polluted soil renovation agent, in addition to improving
Except plant products, additionally it is possible to enhance the effect of heavy metal-polluted soil renovation agent, significantly reduce in plant (especially vegetable seeds)
The heavy metals such as cadmium content, can not sweetening of the soil acidity, heavy metal or absorption in soil can not be made or be chelated or by
Degradation.
Various heavy passivation in soil can be stablized for this purpose, the present inventor provides one kind for soil of lying fallow, is reduced
Soil aciditiy, culture fertility, the heavy metal soil stabilizer for achieving the purpose that fertile soil, improveing soil property.
Invention content
The technical problem to be solved in the present invention is to provide a kind of environmentally friendly heavy metal-polluted soil stabilizers.
To solve the above problems, the present invention adopts the following technical scheme that:
A kind of environmental protection heavy metal-polluted soil stabilizer, the material matched by following parts by weight are made, sodium dihydrogen phosphate 15-33
Part, 20-31 parts of bentonite, 14-31 parts of potassium chloride, 11-21 parts of polyvinyl alcohol, 14-31 parts of diethylene triamine pentacetic acid (DTPA), carbide slag
8-40 parts, 25-40 parts of mushroom dreg, 15-28 parts of carboxymethyl chitosan, 17-31 parts of polyacrylamide, 7-11 parts of calcium magnesium phosphate,
28-33 parts of calcium superphosphate, 13-23 parts of boric acid, 28-37 parts of zinc sulfate, 1-21 parts of amino acid 1,9-14 parts of humic acid, complex enzyme
13-18 parts of preparation, 4-6 parts of Needle of Slash Pine, 4-6 parts of Pseudomonas fluorescens bacterium powder.
A kind of preparation method of environmental protection heavy metal-polluted soil stabilizer, it is characterised in that:Include the following steps:
1) take 20-31 parts of bentonite, 14-31 parts of potassium chloride, 8-40 parts of carbide slag, 25-40 parts of mushroom dreg through pulverizer
40 mesh sieve is crushed, it is spare that powder is made;
2) by powder made from step 1) and 15-33 parts of sodium dihydrogen phosphate, 11-21 parts of polyvinyl alcohol, diethylenetriamine five
14-31 parts of acetic acid, 15-28 parts of carboxymethyl chitosan, 17-31 parts of polyacrylamide, 7-11 parts of calcium magnesium phosphate, calcium superphosphate 28-
33 parts of mixing are put into reaction kettle, at a temperature of 120 DEG C, are stirred 1 hour, and glue is made, spare;
3) by glue made from step 2) and deionized water in proportion 1:3 addition mixing, keep glue thinning, pour into fermentation vat
In, it is spare;
4) by 13-23 parts of boric acid, 28-37 parts of zinc sulfate, 1-21 parts of amino acid 1,9-14 parts of humic acid, complex enzyme formulation
13-18 parts mix in glues obtained by input steps 3), ferment 1 week, during which constantly add water to keep fermentation heap water content 86%, send out
To fermentation materials squeeze and filter after the completion of ferment, fermentation solid residue and zymotic fluid are obtained;
5) by 4-6 parts of Needle of Slash Pine and water by weight 1:It is beaten after 3 mixing, is used in combination filtered through gauze to obtain slurries, will starch
Liquid is mixed and added into 4-6 parts of Pseudomonas fluorescens bacterium powder with the zymotic fluid obtained by step 4), stirs evenly and is heated to 120 DEG C of guarantors
Temperature is after 3 hours, and cooling, it is heavy metal-polluted soil stabilizer to obtain suspension.
Further, the carbide slag is that calcium carbide hydrolysis obtains the waste residue after acetylene gas, and main component is calcium hydroxide,
It is spare that 20 mesh sieve is crossed after the air-dried grinding of the waste residue.
Further, the bacteria residue is the culture medium after edible fungus culturing harvest, dry after 85 DEG C of compost maturities,
It is spare that 50 mesh sieve is crushed through pulverizer.
The beneficial effects of the invention are as follows:Environmental protection heavy metal-polluted soil stabilizer of the present invention utilizes composite phosphate mineral
Long-time stability, the features such as influence that change of external conditions generates phosphoric acid salt minerals is smaller, using phosphate, swelling
Soil is equal to form composite drug according to a certain percentage, under normal temperature and pressure conditions can self-induction generate heavy metal phosphoric acid minerals, certain
A little metal cations can occur ion-exchange reactions with the calcium ion in hydroxyapatite lattice and enter lattice, energy and heavy metal
Ion forms stable chelate, effectively adsorbs the free heavy metal ion in soil and fixes, and reduces heavy metal activity, and
Heavy metal in soil ion releasing can be prevented with the acidity of sweetening of the soil;Humic acid has fertilizer synergistic, improvement soil, stimulation
Plant growth improves the functions such as agricultural product quality, while supplementing the nutrition of crop needs, and activating soil prevents from being passivated;It ties simultaneously
Synthase and microorganism collective effect make heavy metal or absorption in soil or are chelated or are dropped in contaminated by heavy metals soil
Solution achievees the purpose that administer heavy-metal contaminated soil, reaches the stabilization and environmental-friendlyization of heavy-metal composite pollution object.
Description of the drawings
Fig. 1 is the content of beary metal test result of the soil in 3 areas in the embodiment of the present invention 1.
Specific implementation mode
Embodiment 1:
A kind of environmental protection heavy metal-polluted soil stabilizer, the material matched by following parts by weight are made, 15 parts of sodium dihydrogen phosphate,
20 parts of bentonite, 14 parts of potassium chloride, 11 parts of polyvinyl alcohol, 14 parts of diethylene triamine pentacetic acid (DTPA), 8 parts of carbide slag, mushroom dreg 25
Part, 15 parts of carboxymethyl chitosan, 17 parts of polyacrylamide, 7 parts of calcium magnesium phosphate, 28 parts of calcium superphosphate, 13 parts of boric acid, zinc sulfate 28
Part, 1 part of amino acid 1,9 parts of humic acid, 13 parts of complex enzyme formulation, 4 parts of Needle of Slash Pine, 4 parts of Pseudomonas fluorescens bacterium powder.
A kind of preparation method of environmental protection heavy metal-polluted soil stabilizer, it is characterised in that:Include the following steps:
1) 20 parts of bentonite, 14 parts of potassium chloride, 8 parts of carbide slag, 25 parts of mushroom dreg is taken to crushed 40 mesh sieve through pulverizer,
It is spare that powder is made;
2) by powder made from step 1) and 15 parts of sodium dihydrogen phosphate, 11 parts of polyvinyl alcohol, diethylene triamine pentacetic acid (DTPA) 14
28 parts of part, 15 parts of carboxymethyl chitosan, 17 parts of polyacrylamide, 7 parts of calcium magnesium phosphate, calcium superphosphate mixing are put into reaction kettle,
It at a temperature of 120 DEG C, stirs 1 hour, glue is made, it is spare;
3) by glue made from step 2) and deionized water in proportion 1:3 addition mixing, keep glue thinning, pour into fermentation vat
In, it is spare;
4) by 13 parts of 13 parts of boric acid, 28 parts of zinc sulfate, 1 part of amino acid 1,9 parts of humic acid, complex enzyme formulation mixing input steps
In rapid 3) gained glue, ferments 1 week, during which constantly add water to keep fermentation heap water content 86%, after fermentation to fermentate
Expect squeeze and filter, obtains fermentation solid residue and zymotic fluid;
5) by 4 parts of Needle of Slash Pine and water by weight 1:It is beaten after 3 mixing, is used in combination filtered through gauze to obtain slurries, by slurries
It is mixed and added into 4 parts of Pseudomonas fluorescens bacterium powder with the zymotic fluid obtained by step 4), stir evenly and is heated to 120 DEG C of heat preservations 3
After hour, cooling, it is heavy metal-polluted soil stabilizer to obtain suspension.
The carbide slag is that calcium carbide hydrolysis obtains the waste residue after acetylene gas, and main component is calcium hydroxide, the waste residue
It is spare that 20 mesh sieve is crossed after air-dried grinding.
The bacteria residue is the culture medium after edible fungus culturing harvest, dry after 85 DEG C of compost maturities, through pulverizer powder
50 mesh of broken mistake sieve is spare.
Embodiment 2:
A kind of environmental protection heavy metal-polluted soil stabilizer, the material matched by following parts by weight are made, 33 parts of sodium dihydrogen phosphate,
31 parts of bentonite, 31 parts of potassium chloride, 21 parts of polyvinyl alcohol, 31 parts of diethylene triamine pentacetic acid (DTPA), 40 parts of carbide slag, mushroom dreg
40 parts, 28 parts of carboxymethyl chitosan, 31 parts of polyacrylamide, 11 parts of calcium magnesium phosphate, 33 parts of calcium superphosphate, 23 parts of boric acid, sulfuric acid
37 parts of zinc, 21 parts of amino acid, 14 parts of humic acid, 18 parts of complex enzyme formulation, 6 parts of Needle of Slash Pine, Pseudomonas fluorescens bacterium powder 6
Part.
A kind of preparation method of environmental protection heavy metal-polluted soil stabilizer, it is characterised in that:Include the following steps:
1) 31 parts of bentonite, 31 parts of potassium chloride, 40 parts of carbide slag, 40 parts of mushroom dreg is taken to crushed 40 mesh through pulverizer
Sieve, it is spare to be made powder;
2) by powder made from step 1) and 33 parts of sodium dihydrogen phosphate, 21 parts of polyvinyl alcohol, diethylene triamine pentacetic acid (DTPA) 31
33 parts of part, 28 parts of carboxymethyl chitosan, 31 parts of polyacrylamide, 11 parts of calcium magnesium phosphate, calcium superphosphate mixing are put into reaction kettle,
It at a temperature of 120 DEG C, stirs 1 hour, glue is made, it is spare;
3) by glue made from step 2) and deionized water in proportion 1:3 addition mixing, keep glue thinning, pour into fermentation vat
In, it is spare;
4) by 18 parts of 23 parts of boric acid, 37 parts of zinc sulfate, 21 parts of amino acid, 14 parts of humic acid, complex enzyme formulation mixing inputs
It in glue obtained by step 3), ferments 1 week, water is during which constantly added to keep fermentation heap water content 86%, after fermentation to fermentation
Material squeeze and filter obtains fermentation solid residue and zymotic fluid;
5) by 6 parts of Needle of Slash Pine and water by weight 1:It is beaten after 3 mixing, is used in combination filtered through gauze to obtain slurries, by slurries
It is mixed and added into 6 parts of Pseudomonas fluorescens bacterium powder with the zymotic fluid obtained by step 4), stir evenly and is heated to 120 DEG C of heat preservations 3
After hour, cooling, it is heavy metal-polluted soil stabilizer to obtain suspension.
The carbide slag is that calcium carbide hydrolysis obtains the waste residue after acetylene gas, and main component is calcium hydroxide, the waste residue
It is spare that 20 mesh sieve is crossed after air-dried grinding.
The bacteria residue is the culture medium after edible fungus culturing harvest, dry after 85 DEG C of compost maturities, through pulverizer powder
50 mesh of broken mistake sieve is spare.
Embodiment 3:
A kind of environmental protection heavy metal-polluted soil stabilizer, the material matched by following parts by weight are made, 20 parts of sodium dihydrogen phosphate,
25 parts of bentonite, 25 parts of potassium chloride, 16 parts of polyvinyl alcohol, 25 parts of diethylene triamine pentacetic acid (DTPA), 24 parts of carbide slag, mushroom dreg
30 parts, 22 parts of carboxymethyl chitosan, 22 parts of polyacrylamide, 9 parts of calcium magnesium phosphate, 30 parts of calcium superphosphate, 18 parts of boric acid, zinc sulfate
33 parts, 6 parts of amino acid 1,12 parts of humic acid, 15 parts of complex enzyme formulation, 5 parts of Needle of Slash Pine, 5 parts of Pseudomonas fluorescens bacterium powder.
A kind of preparation method of environmental protection heavy metal-polluted soil stabilizer, it is characterised in that:Include the following steps:
1) 25 parts of bentonite, 25 parts of potassium chloride, 24 parts of carbide slag, 30 parts of mushroom dreg is taken to crushed 40 mesh through pulverizer
Sieve, it is spare to be made powder;
2) by powder made from step 1) and 20 parts of sodium dihydrogen phosphate, 16 parts of polyvinyl alcohol, diethylene triamine pentacetic acid (DTPA) 25
30 parts of part, 22 parts of carboxymethyl chitosan, 22 parts of polyacrylamide, 9 parts of calcium magnesium phosphate, calcium superphosphate mixing are put into reaction kettle,
It at a temperature of 120 DEG C, stirs 1 hour, glue is made, it is spare;
3) by glue made from step 2) and deionized water in proportion 1:3 addition mixing, keep glue thinning, pour into fermentation vat
In, it is spare;
4) by 15 parts of 18 parts of boric acid, 33 parts of zinc sulfate, 6 parts of amino acid 1,12 parts of humic acid, complex enzyme formulation mixing inputs
It in glue obtained by step 3), ferments 1 week, water is during which constantly added to keep fermentation heap water content 86%, after fermentation to fermentation
Material squeeze and filter obtains fermentation solid residue and zymotic fluid;
5) by 5 parts of Needle of Slash Pine and water by weight 1:It is beaten after 3 mixing, is used in combination filtered through gauze to obtain slurries, by slurries
It is mixed and added into 5 parts of Pseudomonas fluorescens bacterium powder with the zymotic fluid obtained by step 4), stir evenly and is heated to 120 DEG C of heat preservations 3
After hour, cooling, it is heavy metal-polluted soil stabilizer to obtain suspension.
The carbide slag is that calcium carbide hydrolysis obtains the waste residue after acetylene gas, and main component is calcium hydroxide, the waste residue
It is spare that 20 mesh sieve is crossed after air-dried grinding.
The bacteria residue is the culture medium after edible fungus culturing harvest, dry after 85 DEG C of compost maturities, through pulverizer powder
50 mesh of broken mistake sieve is spare.
Experimental example 1:
Experimental subjects:The soil of 1 piece of heavy metal pollution, randomized are divided into 3rd area:Check plot one, check plot two and test block.
Test method:It pours daily and once coats heavy metal-polluted soil stabilizer high-end on the market, check plot two in check plot one
Primary heavy metal-polluted soil stabilizer general on the market is poured daily, and the primary environmentally friendly soil weight for coating the present invention is poured in test block daily
Metallic stabilizer, according to GB 15618-1995 standard of soil environment quality, measures each area after the 30th day completes passivation
Content of beary metal in liquid soil.
The content of beary metal test result of the soil in 3 areas is shown in Fig. 1:
It was tested by three months, the significant difference of content of beary metal in three areas.
By the above experimental result it is found that a kind of heavy metal-polluted soil stabilizer of the present invention can be effectively to the heavy metal in soil
It is passivated stabilization.
Experimental example 2:
Experimental subjects:The soil of 1 piece of heavy metal pollution, randomized are divided into 3rd area:Check plot one, check plot two and test block,
Wheat is planted respectively on the soil in 3 areas.
Test method:Check plot one, which is poured weekly, once coats heavy metal-polluted soil stabilizer high-end on the market, check plot two
Primary heavy metal-polluted soil stabilizer general on the market is poured weekly, and the primary environmentally friendly soil weight for coating the present invention is poured weekly in test block
Metallic stabilizer counts the wheat yield in each area after wheat maturation.
As a result it see the table below:
Difference | Wheat yield |
Check plot one | 400 kilograms per acre |
Check plot two | 750 kilograms per acre |
Test block | 900 kilograms per acre |
By the above experimental result it is found that the environmentally friendly heavy metal-polluted soil stabilizer of the present invention effectively improves soil physical chemistry
Shape reduces soil aciditiy, soil of having increased fertilizer.
Advantageous effect of the invention is:Environmental protection heavy metal-polluted soil stabilizer of the present invention utilizes composite phosphate mineral
The features such as long-time stability, the influence that change of external conditions generates phosphoric acid salt minerals is smaller, using phosphate, bentonite
Deng forming composite drug according to a certain percentage, under normal temperature and pressure conditions can self-induction generate heavy metal phosphoric acid minerals, it is certain
Metal cation can with the calcium ion in hydroxyapatite lattice occur ion-exchange reactions and enter lattice, can with heavy metal from
Son forms stable chelate, effectively adsorbs the free heavy metal ion in soil and fixes, reduces heavy metal activity, and can
With the acidity of sweetening of the soil, heavy metal in soil ion releasing is prevented;There is humic acid fertilizer synergistic, improvement soil, stimulation to make
Object growth improves the functions such as agricultural product quality, while supplementing the nutrition of crop needs, and activating soil prevents from being passivated;In combination with
Enzyme and microorganism collective effect make heavy metal or absorption in soil or are chelated or are dropped in contaminated by heavy metals soil
Solution achievees the purpose that administer heavy-metal contaminated soil, reaches the stabilization and environmental-friendlyization of heavy-metal composite pollution object.
The above description is merely a specific embodiment, but scope of protection of the present invention is not limited thereto, any
The change or replacement expected without creative work should all be covered within the scope of the present invention.
Claims (4)
1. a kind of environmental protection heavy metal-polluted soil stabilizer, it is characterised in that:The material matched by following parts by weight is made, di(2-ethylhexyl)phosphate
15-33 parts of hydrogen sodium, 20-31 parts of bentonite, 14-31 parts of potassium chloride, 11-21 parts of polyvinyl alcohol, diethylene triamine pentacetic acid (DTPA) 14-31
Part, 8-40 parts of carbide slag, 25-40 parts of mushroom dreg, 15-28 parts of carboxymethyl chitosan, 17-31 parts of polyacrylamide, calcium and magnesium phosphorus
7-11 parts fertile, 28-33 parts of calcium superphosphate, 13-23 parts of boric acid, 28-37 parts of zinc sulfate, 1-21 parts of amino acid 1, humic acid 9-14
Part, 13-18 parts of complex enzyme formulation, 4-6 parts of Needle of Slash Pine, 4-6 parts of Pseudomonas fluorescens bacterium powder.
2. a kind of preparation method of environmentally friendly heavy metal-polluted soil stabilizer as described in claim 1, it is characterised in that:Including following
Step:
1) 20-31 parts of bentonite, 14-31 parts of potassium chloride, 8-40 parts of carbide slag, 25-40 parts of mushroom dreg is taken to be crushed through pulverizer
40 mesh sieve is crossed, it is spare that powder is made;
2) by powder made from step 1) and 15-33 parts of sodium dihydrogen phosphate, 11-21 parts of polyvinyl alcohol, diethylene triamine pentacetic acid (DTPA)
14-31 parts, 15-28 parts of carboxymethyl chitosan, 17-31 parts of polyacrylamide, 7-11 parts of calcium magnesium phosphate, 28-33 parts of calcium superphosphate
Mixing is put into reaction kettle, at a temperature of 120 DEG C, is stirred 1 hour, and glue is made, spare;
3) by glue made from step 2) and deionized water in proportion 1:3 addition mixing, keep glue thinning, pour into fermentation vat,
It is spare;
4) by 13-23 parts of boric acid, 28-37 parts of zinc sulfate, 1-21 parts of amino acid 1,9-14 parts of humic acid, complex enzyme formulation 13-18
It in glue obtained by part mixing input step 3), ferments 1 week, during which constantly adds water holding fermentation heap water content 86%, fermented
At rear to fermentation materials squeeze and filter, fermentation solid residue and zymotic fluid are obtained;
5) by 4-6 parts of Needle of Slash Pine and water by weight 1:3 mixing after be beaten, be used in combination filtered through gauze to obtain slurries, by slurries with
Zymotic fluid obtained by step 4) is mixed and added into 4-6 parts of Pseudomonas fluorescens bacterium powder, stirs evenly and is heated to 120 DEG C of heat preservations 3
After hour, cooling, it is heavy metal-polluted soil stabilizer to obtain suspension.
3. a kind of heavy metal-polluted soil stabilizer as described in claim 1, it is characterised in that:The carbide slag is that calcium carbide hydrolysis obtains
It is calcium hydroxide to take the waste residue after acetylene gas, main component, and it is spare to cross 20 mesh sieve after the air-dried grinding of the waste residue.
4. a kind of heavy metal-polluted soil stabilizer as described in claim 1, it is characterised in that:The bacteria residue is received for edible fungus culturing
Culture medium after obtaining, it is dry after 85 DEG C of compost maturities, it is spare to crushed 50 mesh sieve through pulverizer.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
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CN111072430A (en) * | 2018-10-18 | 2020-04-28 | 南京化学工业园环保产业协同创新有限公司 | Heavy metal stabilizer for soil acidity and alkalinity improvement and use method |
CN114774133A (en) * | 2022-04-09 | 2022-07-22 | 山东大学 | Microbial soil conditioner and preparation and application thereof |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103710029A (en) * | 2013-12-20 | 2014-04-09 | 中节能六合天融环保科技有限公司 | Targeted stabilizer for repairing heavy metal contaminated soil and preparation method thereof |
CN104327858A (en) * | 2014-09-22 | 2015-02-04 | 广西大学 | Soil heavy metal compound stabilizer and method using soil heavy metal compound stabilizer for passivation of soil heavy metals |
CN105985778A (en) * | 2016-02-24 | 2016-10-05 | 凤阳徽亨商贸有限公司 | Organic soil heavy metal restoration agent |
CN106085450A (en) * | 2016-06-17 | 2016-11-09 | 战锡林 | Heavy-metal contaminated soil repair materials |
-
2017
- 2017-12-11 CN CN201711309614.8A patent/CN108329082A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103710029A (en) * | 2013-12-20 | 2014-04-09 | 中节能六合天融环保科技有限公司 | Targeted stabilizer for repairing heavy metal contaminated soil and preparation method thereof |
CN104327858A (en) * | 2014-09-22 | 2015-02-04 | 广西大学 | Soil heavy metal compound stabilizer and method using soil heavy metal compound stabilizer for passivation of soil heavy metals |
CN105985778A (en) * | 2016-02-24 | 2016-10-05 | 凤阳徽亨商贸有限公司 | Organic soil heavy metal restoration agent |
CN106085450A (en) * | 2016-06-17 | 2016-11-09 | 战锡林 | Heavy-metal contaminated soil repair materials |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111072430A (en) * | 2018-10-18 | 2020-04-28 | 南京化学工业园环保产业协同创新有限公司 | Heavy metal stabilizer for soil acidity and alkalinity improvement and use method |
CN114774133A (en) * | 2022-04-09 | 2022-07-22 | 山东大学 | Microbial soil conditioner and preparation and application thereof |
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