CN107141101A - The fertilizers of repairing heavy metal in soil - Google Patents

The fertilizers of repairing heavy metal in soil Download PDF

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Publication number
CN107141101A
CN107141101A CN201710417769.7A CN201710417769A CN107141101A CN 107141101 A CN107141101 A CN 107141101A CN 201710417769 A CN201710417769 A CN 201710417769A CN 107141101 A CN107141101 A CN 107141101A
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fertilizer
heavy metal
fertilizers
soil
organic
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CN107141101B (en
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严历
陈裕新
向铁军
易百科
卢小伸
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HUNAN GOLD LEAF PUBLIC EXPECTATION TECHNOLOGY Co Ltd
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HUNAN GOLD LEAF PUBLIC EXPECTATION TECHNOLOGY Co Ltd
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    • 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
    • C05BPHOSPHATIC FERTILISERS
    • C05B7/00Fertilisers based essentially on alkali or ammonium orthophosphates
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05DINORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D9/00Other inorganic fertilisers
    • 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

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Pest Control & Pesticides (AREA)
  • Soil Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a kind of fertilizers of repairing heavy metal in soil, mainly it is mixed with and is formed with heavy metal absorbent by fertilizer, the heavy metal absorbent is porous ceramic film material, and the aperture of the porous ceramic film material is 5 35nm, and specific surface area is 240 300m2/g.The present invention is by heavy metal absorbent and Fertilizer combination, and the two is mutually cooperateed with, and significantly improves the adsorption capacity of heavy metal absorbent heavy metal, achieves unexpected technique effect.

Description

The fertilizers of repairing heavy metal in soil
Technical field
The invention belongs to the technical field of agricultural fertilizer, more particularly to a kind of functional fertilizer of energy repairing heavy metal in soil Material.
Background technology
With modern society and the quick and extensive development of industry, a large amount of waste water, waste gas, solid waste are produced therewith The modern industrialization pollutant such as thing, causes to have a strong impact on to human society and Global Ecological.And among these especially with soil pollution most For protrusion, because soil also brings up the mankind while carry the mankind.Heavy metal pollution of soil is the one of modern industrial society Big disastrous effect, first contaminated soil, and then polluted source;Secondly by biological chain, it is enriched with plant, animal and the mankind.Plant, Special crops, are animal and the main food source of people, therefore plant is the initial victim of heavy metal pollution of soil, by It is also the main undertaker that heavy metal pollution of soil is caused harm in the presence of bioconcentration.Heavy metal pollution of soil is caused harm plant The principle of thing is that root system of plant is absorbed can produce toxic action after the heavy metal in soil to the eubolism of itself, Such as absorption of the activity of influence metabolic enzyme, the transhipment of the other mineral elements of interference and the necessary element of influence etc..Due to plant Eubolism is interfered, and can not obtain from soil must nutrient, directly result in root system and be damaged, yield and Quality is affected, and plant life cycle shortens, or even premature death.Due to there is the weight in biological chain, soil in nature Metal can be enriched in animal and human body with food chain transport, in turn resulted in and caused harm.If the heavy metal in soil can not Remove effectively and in time, eventually seriously endanger the development of human society.In consideration of it, heavy metal pollution of soil just increasingly by To the concern of people, the Significant Problems of Eco-environment faced as the whole society, research of the associated restoration with administering field is also existing The emphasis paid close attention to for scientific worker.For the sustainable development of modern agriculture, ensure food safety, heavy metal pollution of soil is repaiied Multiple and improvement is the unavoidable reality of modern society.
It is currently applied to heavy metal-polluted soil reparation and the measure administered, from being divided into three kinds in nature:Physical method, chemistry side Method and biological method.Physical method, mainly by way of electromagnetism, the mode of elution, the mode of soil removal and replacement.Electromagnetism transfer is removed Heavy metal is to make heavy metal ion displacement either heavy metal is quickly volatilized using electric heating environment using electromagnetic environment, this To having certain restriction using scale, and there is certain damage to soil.The mode of elution is to be transferred to heavy metal from solid phase In liquid phase, the heavy metal in recycling liquid phase is relatively ripe, but the big consuming of quantities is more.The mode of soil removal and replacement is mainly Polluted Soil layer depth is turned over or changed, but quantities is big and cures the symptoms, not the disease.Chemical method, mainly adds one in soil The material of wherein heavy metal physicochemical property can be changed a bit so that heavy metal occur precipitation, absorption, redox etc. react or Effect, so reduces mobility, absorbed power and the degree that causes harm of heavy metal in soil.Chemical method is also can not be thorough Solution heavy metal pollution problem be only to change heavy metal because heavy metal is not separated exclusion by this method from soil Existence in soil, if improper measures are it is also possible to cause secondary pollution.Biological method, mainly utilizes plant absorption The characteristic of enriching heavy metal.Comparatively rehabilitation cost is relatively low for this method, is adapted to large-scale application, can produce good Ecological Effect Should, but this method is time-consuming that longer, efficiency is relatively low, specific mechanism of action is fuzzy, useful plant exploitation is urgently to be resolved hurrily.On The situation of heavy metal pollution of soil can be repaired and improve to a certain extent by stating several method mode, but shortcoming is also bright Aobvious.So, it is with low cost, repair efficiently, measure is simple, the method that has good ecological environment benefit is that heavy metal-polluted soil is dirty Dye is repaired and pursuing a goal for administering.
Soil is no longer suitably cultivated by after heavy metal pollution, unless heavy metal contaminants therein are eliminated, is otherwise Make to have harvested, also can be the agricultural product of heavy metals exceeding standard, it is impossible on the dining table for entering people.And as a reparation huge sum of money Category, individually progress soil remediation is no doubt feasible, but if rehabilitating soil be able to can be received while healthy food is harvested Ecological benefits and economic benefit bumper harvests, here it is being worth the problem of research.
The content of the invention
The technical problems to be solved by the invention are to overcome the shortcomings of to mention with defect that there is provided one in background above technology Plant the fertilizers of repairing heavy metal in soil.
In order to solve the above technical problems, technical scheme proposed by the present invention is:
A kind of fertilizers of repairing heavy metal in soil, are mainly mixed with heavy metal absorbent by fertilizer and formed, institute Heavy metal absorbent is stated for porous ceramic film material, the aperture of the porous ceramic film material is 5-35nm, specific surface area 240- 300m2/g.By porous ceramic film material in alkalescence itself, after the Fertilizer combination with generally showing acidity so that porous ceramic film material The energy-absorbing power of heavy metal is greatly improved, and the effective cadmium reduced rate of soil is single use more than 1.5 times during repair materials.
Heavy metal absorbent of the present invention be porous ceramic film material, by Ge Feng tech materials Co., Ltd research and development and Production, is a kind of new high self assembly, intensive function unimolecule, orderly controlled pore, nano composite material, and the material has height Selectivity, big adsorbance, extremely low energy consumption, long-life, the advantage of low cost;It is core by modified porous ceramic nanocomposites " three wastes " processing equipment of assembling has the characteristics of modularization, intellectuality, integrated, seriation, with the spy for removing removing heavy metals Determine function.The porous ceramic film material, mainly with six big characteristics:
(1) physics and mechanical stability:It is non-breakable, do not drifted about in the water after Adsorption of Heavy Metals;
(2) chemical stability:Pollutant will not be discharged again because of acid rain or soil acidity or alkalinity change;
(3) biological stability:5-35nm nano-pore structure, makes microorganism cannot be introduced into nanometer aperture and turns heavy metal Turn to toxicity and the bigger organic heavy metal of mobility (such as methyl mercury);
(4) geological stability:Porous ceramic film material after Adsorption of Heavy Metals is with passage (the 1-3 season crops of farming time Plantation), under gravity gradually downward migrate and finally leave arable layer, there is no may be absorbed to for the root of such plant These heavy metals being cured, and the porous ceramic film material solidification heavy metal-nano ceramics heavy metal carrier arable layer it Under be turned into heavy metallic mineral matter class material, heavy metal no longer migrates into biological chain, no longer causes heavy metal pollution to environment, Reach the final purpose being passivated on the spot;
(5) protectiveness of soil characteristic and structure:Porous ceramic film material does not absorb alkaline-earth metal, potassium, phosphorus and nutritional ingredient, Chemicals is not introduced, the function with the gas permeability that can improve soil.
Therefore, the present invention is applied in fertilizer, and soil can also be improved while plant growth nutrient supply is provided Physics, chemistry and biological character, be plant roots so as to reach rehabilitating soil colloid, soil enzyme system and soil granular structure System, which grows, to create a pleasant ecological environment.
Importantly, because porous ceramic film material is in itself in alkalescence, and fertilizer generally shows acidity, makes by carrier of fertilizer The aobvious acid and faintly acid of porous ceramic film material local environment is obtained, and is conducive to heavy metal to be converted into free state under acid state, from And it is easy to the absorption of porous ceramic film material heavy metal, therefore, porous ceramic film material is combined by the present invention with chemical fertilizer so that The adsorption capacity of porous ceramic film material heavy metal is significantly improved.
Above-mentioned fertilizers, it is preferred that in parts by weight, the fertilizers it is main by 90-99.7 part fertilizer and 0.3-10 parts of heavy metal absorbents are mixed with and formed.
Above-mentioned fertilizers, it is preferred that the fertilizer be selected from organic-inorganic complex fertilizer, inorganic compound (conjunction) fertilizer, One or more in organic fertilizer, bulk blended fertilizer.
Above-mentioned fertilizers, it is preferred that by weight/mass percentage composition, the total nutrient of the organic-inorganic complex fertilizer is 25%~35%, organic matter 15~25%, chlorion≤3.0%, moisture≤12%, fineness be 40~60 mesh, pH be 5.5~ 7.0。
Above-mentioned fertilizers, it is preferred that by weight/mass percentage composition, the total nutrient 6%~10% of the organic fertilizer has Machine matter content 45~80%, moisture≤30%, pH is 4.5~7.0;Living bacteria count in the organic fertilizer is 0.2 hundred million/g~1 Hundred million/g.
Above-mentioned fertilizers, it is preferred that the organic matter be with one kind in rapeseed meal, offal, offal, feces of livestock and poultry or Several is raw material, what the fermenting agent after fermentation that addition accounts for raw material weight 0.25%-1% was prepared.
Above-mentioned fertilizers, it is preferred that inorganic compound (conjunction) fertilizer is by urea, ammonium nitrate phosphorus, MAP, chlorination Several process compound techniques in ammonium, sulphur ammonium, potassium chloride and potassium sulfate are made.
An above-mentioned fertilizers, it is preferred that the bulk blended fertilizer is blended with using resin-bonded grinding wheel as primary raw material Grain urea, particle MAP, granular ammonium chloride, particle sulphur ammonium, granule potassium chloride, granular potassium sulfate, particle trace element It is one or more.
Above-mentioned fertilizers, it is preferred that by weight/mass percentage composition, total nutrient >=35% of the bulk blended fertilizer, chlorine from Son≤3.0%, moisture≤2%, granularity (particle diameter 1mm-4.75mm or 3.35mm-5.60mm) >=90%, moderate-element content >=2%, micronutrient levels >=0.02%.
Above-mentioned fertilizers, it is preferred that during fertilising, are uniformly spread fertilizer over the fields in soil table with every mu of 50-120kg consumption Face, then ploughs.
Compared with prior art, the advantage of the invention is that:
(1) present invention is by heavy metal absorbent and Fertilizer combination, and the two is mutually cooperateed with, and makes heavy metal absorbent heavy metal Adsorption capacity significantly improve, achieve unexpected technique effect.
(2) multi-Functional Fertilizers of repairing heavy metal in soil of the invention, contain a large amount of, the middle amount needed for crop growth And the product of the repairing heavy metal in soil is administered simultaneously there is provided different plantation products or the sufficient nutrient of crop in trace element, Effect of repairing polluted soil can be played while crops are harvested.
(3) multi-Functional Fertilizers of repairing heavy metal in soil of the invention can obtain ecological benefits and economic benefit simultaneously.
(4) multi-Functional Fertilizers of repairing heavy metal in soil of the invention, safety non-toxic will not produce secondary pollution, using side Just, without individually doing the operation of repairing heavy metal in soil, the ultrahigh in efficiency with Adsorption of Heavy Metals, amount are very big, and with pole Good selectivity.
Embodiment
For the ease of understanding the present invention, more comprehensively, meticulously retouched below in conjunction with preferred embodiment to inventing to do herein State, but protection scope of the present invention is not limited to specific examples below.
Unless otherwise defined, all technical terms used hereinafter are generally understood that implication phase with those skilled in the art Together.Technical term used herein is intended merely to describe the purpose of specific embodiment, is not intended to the limitation present invention's Protection domain.
Unless otherwise specified, various raw material, reagent, instrument and equipment used in the present invention etc. can be by city Field is commercially available or can prepared by existing method.
Embodiment 1:
A kind of fertilizers of repairing heavy metal in soil of the invention, mainly by the 95kg inorganic compounds of 24-10-12 (conjunction) Fertilizer is (by urea, ammonium nitrate phosphorus, MAP, ammonium chloride, sulphur ammonium, potassium chloride and potassium sulfate by the making of compound technique Into) and 5kg porous ceramic film material be mixed with and form, the aperture of the porous ceramic film material is 5-35nm, and specific surface area is 240-300m2/g。
1st, test site:Tongren district Guizhou Province.
2nd, test material:
Fertilizer variety:The fertilizers of the repairing heavy metal in soil of the present embodiment, inorganic compound (conjunction) fertilizer, inorganic compound (conjunction) fertilizer+porous ceramic film material is separately handled;
Crop varieties:Early rice, strain two excellent 1.
3rd, experimental design:
Processing 1:Using the fertilizers of the repairing heavy metal in soil of the present embodiment, mu applies 75kg;
Processing 2:Using the inorganic fertilizer for waiting nutrient content proportioning without porous ceramic film material, mu applies 75kg;
Processing 3:The inorganic fertilizer for waiting nutrient content proportioning without porous ceramic film material is first applied, is then applying porous Ceramic material, the two total consumption and processing 1 are identical.
Paddy rice is unified to transplant using unified nursery, unified production measure.Each processing sets 3 repetitions, each cell face Product is 133.3m2.Single receive singly is shone and claims dry weight, and Plant Height of Rice, Miho length, tiller number, mass of 1000 kernel and setting percentage etc. are collected before harvest Data.In addition, to rice grain, plant, and soil carries out content of beary metal and determines analysis.
4th, result and analysis:
In general, by the soil of heavy metal pollution, if being not reaching to certain pollution level, paddy rice still can give birth to Long harvest, will not even produce influence to yield.The rice only obtained in this case is heavy metals exceeding standard, people's food After harm can be produced to body.And if pollution is more serious, rice growth is affected, yield also it is corresponding by Influence.Test data shows that testing each cell, soil pollution not up to influences experiment Yield of Rice Varieties before treatment Among degree, table 1, contrasted between processing 1, processing 2 and processing 3 and this point can be explained.
The different disposal of table 1 and rice yield
Table 2 is the paddy rice economic conditions of different disposal, is shown by the test data in table 2, the regional heavy metal-polluted soil of experiment The paddy rice normal growth and development that pollution effect is arrived, but lesser extent.Heavy metal contaminants enter after soil, and what is influenceed first is Soil environment and structure, such as soil enzyme system, P in soil H, soil granular structure etc..Into after plant, start to disturb plant Normal Physiological and Biochemical Metabolism process.It is affected as a result, plant absorbs nutrient from the external world, therefore effective point Tiller, plant height, full seed degree etc. are influenced to different extents.
The different disposal of table 2 and Economic Character of Rice
Generally, the soil horizon of the suitable farming of soil is 0-20cm scope, is also most of system of fibrous root crops The soil horizon that root system is primarily present.The soil of deeper has crop root or other field biologicals are present, but relatively It is few.Test data shows and (is shown in Table 3), after it application of the fertilizers of repairing heavy metal in soil of the present invention, a huge sum of money in soil Category content significantly declines, and content of beary metal is no longer exceeded in crop product.
The different disposal of table 3 influences on heavy metal content in soil
Embodiment 2:
A kind of fertilizers of repairing heavy metal in soil of the invention, mainly by 95kg bulk blended fertilizer (26-10-12, always Nutrient >=48%, chlorion≤3.0%, moisture≤2%, granularity (particle diameter 1mm-4.75mm) >=90%, moderate-element content >=2%, micronutrient levels >=0.02%) and 5kg porous ceramic film material, which are mixed with, to be formed, the hole of the porous ceramic film material Footpath is 5-35nm, specific surface area 240-300m2/g。
1st, test site:Changsha, Zhuzhou, Xiang Tan
2nd, test material:
Fertilizer variety:The fertilizers of the repairing heavy metal in soil of the present embodiment, Slow release bulk blend fertilizer, Slow release bulk blend fertilizer + porous ceramic film material is separately handled
Crop varieties:Late rice, strain two excellent 1
3rd, experimental design:
Processing 1:Using the fertilizers of the repairing heavy metal in soil of the present embodiment, mu applies 65kg;
Processing 2:Using the Slow release bulk blend fertilizer for waiting nutrient content proportioning without porous ceramic film material, mu applies 65kg;
Processing 3:The Slow release bulk blend fertilizer for waiting nutrient content proportioning without porous ceramic film material is first applied, is then applied again Porous ceramic film material, the two total consumption and processing 1 are identical.
Paddy rice is unified to transplant using unified nursery, unified production measure.Each processing sets 3 repetitions, each cell face Product is 133.3m2.Single receive singly is shone and claims dry weight, and Plant Height of Rice, Miho length, tiller number, mass of 1000 kernel and setting percentage etc. are collected before harvest Data.In addition, to rice grain, plant, and soil carries out content of beary metal and determines analysis.
4th, result and analysis:
Test data shows that testing each cell, soil pollution not up to influences experiment Yield of Rice Varieties before treatment Degree, among table 4, contrasted between processing 1, processing 2, processing 3 and this point can be explained.So that is not reaching experimental field To certain pollution level, paddy rice still can grow harvest, and yield is not produced and had a strong impact on.But, using fertilizers Yield is improved to a certain extent.
The different disposal of table 4 and rice yield
The different disposal of table 5 and rice cadmium content
Such as test data of table 5, in the case where applying repairing heavy metal in soil fertilizers, if heavy metal in soil content It is low, heavy metal in rice quickly can be reduced to level of security.
The different disposal of table 6 and soil cadmium content (arable layer)
As shown in Table 6, heavy metal in soil content reduction level has much relations with heavy metal in soil content, if contained The high absolute magnitude then reduced of amount is also high, and the low absolute magnitude of content sinking is also low.
Embodiment 3:
A kind of fertilizers of repairing heavy metal in soil of the invention, mainly by 95kg organic-inorganic complex fertilizer (13-5-8) and 5kg porous ceramic film material, which are mixed with, to be formed, and the aperture of the porous ceramic film material is 5-35nm, specific surface area 240-300m2/g;Total nutrient >=26% of the organic-inorganic complex fertilizer, organic matter >=20%, chlorion≤3.0%, moisture ≤ 12%, fineness is 40~60 mesh, and pH is 5.5~7.0.
1st, test site:Hunan Changning
2nd, test material
Fertilizer variety:The fertilizers of repairing heavy metal in soil, compound organic and inorganic fertilizer type fertilizer, compound organic and inorganic fertilizer Type fertilizer+porous ceramic film material
Crop varieties:Late rice, strain two excellent 1
3rd, experimental design
Processing 1:Using the fertilizers of the repairing heavy metal in soil of the present embodiment, mu applies 70kg
Processing 2:Using the fertilizer for waiting nutrient content proportioning without porous ceramic film material, mu applies 70kg
Processing 3:The compound organic and inorganic fertilizer type fertilizer for waiting nutrient content proportioning without porous ceramic film material is first applied, so Porous ceramic film material is being applied afterwards, the two total consumption and processing 1 are identical.
Paddy rice is unified to transplant using unified nursery, unified production measure.Each processing sets 3 repetitions, each cell face Product is 133.3m2.Single receive singly is shone and claims dry weight, and Plant Height of Rice, Miho length, tiller number, mass of 1000 kernel and setting percentage etc. are collected before harvest Data.In addition, to rice grain, plant, and soil carries out content of beary metal and determines analysis.
4th, result and analysis
Test data shows that testing each cell, soil pollution not up to influences experiment Yield of Rice Varieties before treatment Degree, among table 7, contrasted respectively between 1 three testing sites of processing and processing 2 and this point can be explained.Do not have experimental field Certain pollution level is reached, paddy rice still can grow harvest, yield is not produced and had a strong impact on.Multispots trial also illustrates, Yield is improved to a certain extent using the fertilizers of the repairing heavy metal in soil of the present invention.
The different disposal of table 7 and rice yield
The different disposal of table 8 and rice cadmium content
As shown in table 8, using the fertilizers of repairing heavy metal in soil of the invention, the cadmium content in paddy rice is reduced 80%~90%, " cadmium rice " is become " the safe rice " of the requirement that is up to state standards.By 3 contrast tables of processing 1 and processing Bright, repairing heavy metal in soil multi-Functional Fertilizers of the invention are substantially better than to the drop cadmium effect of paddy rice is used separately fertilizer and a huge sum of money Belong to adsorbent.
The different disposal of table 9 and soil cadmium content (arable layer)
As shown in table 9, the fertilizers for the repairing heavy metal in soil that the present invention is applied in multispots trial display can effectively drop Low heavy metal in soil (cadmium) content.Shown by processing 1 and the contrast of processing 3, repairing heavy metal in soil functional fertilizer of the invention Expect to be substantially better than the drop cadmium effect of soil and be used separately fertilizer and heavy metal absorbent.
Embodiment 4:
A kind of fertilizers of repairing heavy metal in soil of the invention, mainly by 95kg organic-inorganic complex fertilizer (13-5-8) and 5kg porous ceramic film material, which are mixed with, to be formed, and the aperture of the porous ceramic film material is 5-35nm, specific surface area 240-300m2/g;Total nutrient >=26% of the organic-inorganic complex fertilizer, organic matter >=20%, chlorion≤3.0%, moisture ≤ 12%, fineness is 40~60 mesh, and pH is 5.5~7.0.
1st, test site:Zhuzhou,hunan.
2nd, test material:
Fertilizer variety:The fertilizers of repairing heavy metal in soil, organic-inorganic complex fertilizer (13-5-8), porous ceramics Material;
Crop varieties:Late rice, strain two excellent 1.
3:Experimental design:
Processing 1:Using the fertilizers of the repairing heavy metal in soil of the present embodiment, mu applies 70kg
Processing 2:Using the fertilizer with processing 1 grade nutrient content proportioning without porous ceramic film material, mu applies 70kg, in addition It is administered alone and 1 equivalent porous ceramic film material of processing (not with Fertilizer combination administration);
Processing 3:Using the fertilizer with processing 1 grade nutrient content proportioning without porous ceramic film material, mu applies 70kg.
Paddy rice is unified to transplant using unified nursery, unified production measure.Each processing sets 3 repetitions, each cell face Product is 133.3m2.Single receive singly is shone and claims dry weight, and Plant Height of Rice, Miho length, tiller number, mass of 1000 kernel and setting percentage etc. are collected before harvest Data.In addition, to rice grain, plant, and soil carries out content of beary metal and determines analysis.
4th, result and analysis
The different disposal of table 10 and rice yield
The different disposal of table 11 and rice cadmium content
The different disposal of table 12 and soil cadmium content (arable layer)
Test data shows that testing each cell, soil pollution not up to influences experiment Yield of Rice Varieties before treatment Degree, by the processing 1 of table 10, processing 2 respectively with processing 3 contrast can be explained this point.Experimental field it is not reaching to certain Pollution level, paddy rice still can grow harvest, and yield is not produced and had a strong impact on.Multispots trial also illustrates, is polluting not When reaching the degree of influence paddy growth, it can be carried to a certain extent using the fertilizers of the repairing heavy metal in soil of the present invention The high yield of paddy rice.
It can be confirmed from the result of the test of table 11 and table 12, fertilizer and porous material are used in mixed way by the present invention can Significantly improved with the adsorption capacity of heavy metal.

Claims (8)

1. a kind of fertilizers of repairing heavy metal in soil, it is characterised in that system is mainly mixed with heavy metal absorbent by fertilizer Standby to form, the heavy metal absorbent is porous ceramic film material, and the aperture of the porous ceramic film material is 5-35nm, specific surface area For 240-300m2/g。
2. fertilizers as claimed in claim 1, it is characterised in that in parts by weight, the fertilizers are main by 90- 99.7 parts of fertilizer are mixed with 0.3-10 parts of heavy metal absorbents and formed.
3. fertilizers as claimed in claim 1, it is characterised in that the fertilizer is selected from organic-inorganic complex fertilizer, inorganic One kind in complex fertilizer, organic fertilizer, bulk blended fertilizer.
4. fertilizers as claimed in claim 3, it is characterised in that by weight/mass percentage composition, the organic-inorganic compound mixed fertilizer The total nutrient of material is 25%~35%, organic matter 15~25%, chlorion≤3.0%, moisture≤12%, and fineness is 40~60 Mesh, pH is 5.5~7.0.
5. fertilizers as claimed in claim 3, it is characterised in that by weight/mass percentage composition, the total of the organic fertilizer supports It is divided into 6%~10%, the content of organic matter 45~80%, moisture≤30%, pH is 4.5~7.0;It is effective in the organic fertilizer Viable count is 0.2 hundred million/g~100,000,000/g.
6. the fertilizers as described in claim 4 or 5, it is characterised in that the organic matter is with rapeseed meal, offal, offal, poultry One or more in poultry manure are raw material, and the fermenting agent after fermentation that addition accounts for raw material weight 0.25%-1% is prepared 's.
7. fertilizers as claimed in claim 3, it is characterised in that the inorganic complex fertilizer is by urea, ammonium nitrate phosphorus, phosphoric acid Several process compound techniques in one ammonium, ammonium chloride, sulphur ammonium, potassium chloride and potassium sulfate are made.
8. fertilizers as claimed in claim 3, it is characterised in that total nutrient >=35% of the bulk blended fertilizer, chlorion ≤ 3.0%, moisture≤2%;The bulk blended fertilizer is blended with granular urea, particle using resin-bonded grinding wheel as primary raw material MAP, granular ammonium chloride, particle sulphur ammonium, granule potassium chloride, granular potassium sulfate, the one or more of particle trace element.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108971211A (en) * 2018-07-05 2018-12-11 安徽袁粮水稻产业有限公司 A kind of method for comprehensive repairing of nickel contamination rice soil
CN113087578A (en) * 2021-03-30 2021-07-09 中地宝联(北京)国土资源勘查技术开发集团有限公司 Chemical fertilizer with soil heavy metal restoration function and preparation method thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101117299A (en) * 2007-06-29 2008-02-06 东莞市大众农业科技有限公司 Process for producing compound fertilizer by tower granulation
CN103788960A (en) * 2014-03-05 2014-05-14 中国科学院合肥物质科学研究院 Functional fertilizer and repair agents for repairing soil heavy metal
CN104447038A (en) * 2014-12-15 2015-03-25 湖南金叶众望科技股份有限公司 Biological organic/inorganic compound fertilizer as well as preparation method and application of fertilizer
CN104525123A (en) * 2014-12-12 2015-04-22 格丰科技材料有限公司 Porous composite material for removing heavy metals in soil and preparation method thereof
CN106045553A (en) * 2016-05-26 2016-10-26 格丰环保科技有限公司 Method for preparing porous ceramic material for adsorbing heavy metals
CN106699338A (en) * 2016-11-21 2017-05-24 上海永通化工有限公司 Special slow-release bulk blending fertilizer for wheat and preparation method of fertilizer

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101117299A (en) * 2007-06-29 2008-02-06 东莞市大众农业科技有限公司 Process for producing compound fertilizer by tower granulation
CN103788960A (en) * 2014-03-05 2014-05-14 中国科学院合肥物质科学研究院 Functional fertilizer and repair agents for repairing soil heavy metal
CN104525123A (en) * 2014-12-12 2015-04-22 格丰科技材料有限公司 Porous composite material for removing heavy metals in soil and preparation method thereof
CN104447038A (en) * 2014-12-15 2015-03-25 湖南金叶众望科技股份有限公司 Biological organic/inorganic compound fertilizer as well as preparation method and application of fertilizer
CN106045553A (en) * 2016-05-26 2016-10-26 格丰环保科技有限公司 Method for preparing porous ceramic material for adsorbing heavy metals
CN106699338A (en) * 2016-11-21 2017-05-24 上海永通化工有限公司 Special slow-release bulk blending fertilizer for wheat and preparation method of fertilizer

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108971211A (en) * 2018-07-05 2018-12-11 安徽袁粮水稻产业有限公司 A kind of method for comprehensive repairing of nickel contamination rice soil
CN113087578A (en) * 2021-03-30 2021-07-09 中地宝联(北京)国土资源勘查技术开发集团有限公司 Chemical fertilizer with soil heavy metal restoration function and preparation method thereof

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