CN106831266A - Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay - Google Patents

Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay Download PDF

Info

Publication number
CN106831266A
CN106831266A CN201710205940.8A CN201710205940A CN106831266A CN 106831266 A CN106831266 A CN 106831266A CN 201710205940 A CN201710205940 A CN 201710205940A CN 106831266 A CN106831266 A CN 106831266A
Authority
CN
China
Prior art keywords
heavy metal
modifying agent
metal pollution
bleaching clay
spent bleaching
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
CN201710205940.8A
Other languages
Chinese (zh)
Inventor
许海
高素萍
谢爱军
常立
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.)
Gansu Tiannongyihe Agriculture Co ltd
Original Assignee
SHANGHAI LICHANG ENVIRONMENTAL ENGINEERING 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 SHANGHAI LICHANG ENVIRONMENTAL ENGINEERING Co Ltd filed Critical SHANGHAI LICHANG ENVIRONMENTAL ENGINEERING Co Ltd
Priority to CN201710205940.8A priority Critical patent/CN106831266A/en
Publication of CN106831266A publication Critical patent/CN106831266A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01BSOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
    • A01B79/00Methods for working soil
    • A01B79/02Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B3/00Fertilisers based essentially on di-calcium phosphate

Abstract

The invention provides a kind of heavy metal pollution alkaline land modifying agent and modification method based on spent bleaching clay, the composition of raw materials of modifying agent includes spent bleaching clay 45 80%, complex micro organism fungicide 0.5 2%, humic acid 5 15%, calcium dihydrogen phosphate 3 10%, calcium carbonate 2 5%, citric acid 1 6% and polyaluminium sulfate 2 19.5%, described complex micro organism fungicide are that bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, bacillusmusilaginosiengineering are 1 by nutrient solution volume ratio:1.2‑1.6:0.5‑0.7:1.2‑1.5:The mixture of 0.6 0.9 compositions.The improvement in salt-soda soil particularly heavy metal pollution salt-soda soil can be effectively realized using modifying agent of the present invention and with reference to modification method of the present invention, the improvement requirement in salt-soda soil is fundamentally solved, while low cost of the present invention, is capable of achieving resource reutilization, environmental pollution is reduced.

Description

Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay
Technical field
The invention belongs to soil improvement field, and in particular to a kind of heavy metal pollution alkaline land modifying agent and modification method.
Background technology
The salinization of soil is destroyed than larger to soil physico-chemical property, and pole is unfavorable for the growth of many crops, easily causes work Thing is short of seedling or dead, so as to hinder the development of agricultural economy.Salt-soda soil is more due to salt content, and organic quality is few, and acid-base value is high, makes Agron suffers leaching loss, and soil texture is destroyed, and is sticked when showing as wet, and hard when doing, native table often has white salinity accumulation, Ventilation, it is permeable bad, serious meeting cause plant wilt, poisoning and rotten death.In addition, surface soil alkalinity is too big, soil is had influence on The validity of the nutrients such as phosphorus, iron, manganese, boron, zinc in earth, easily causes a large amount of nitrogen, phosphorus, potassium essential element and iron, calcium, boron Deng the shortage of trace element.According to statistics, Chinese saline-alkali soil area there are about more than 20 ten thousand square kilometres, constitute about China's territory total area 2.1%.Up to the present China about also have 80% or so saline-alkali soil not to be developed.It is increasingly tight in land resource The today opened, the exploitation of large area saline-alkali wasteland and the preventing and treating of the salinization of soil have become influence China's economy and society The major issue of sustainable development.
Existing conventional modification method has chemical modifying, physically improved, organic fertilizer improvement and biological modification etc..Soil The kind of modifying agent has such as mineral substance, organic matter, artificial synthesized macromolecular compound, effective microorganism preparation, sulphur-bentonite Deng.These modifying agents are generally common liquid body fertilizer material ﹑ farm manures or organic matter, and nutrient content is than relatively low, though can be supplemented for soil Certain nutrient, but the improvement of soil physico-chemical property is have ignored, nutrient is difficult release, neither takes stopgap measures nor effects a permanent cure.Beneficial micro- life Thing type of preparation is various, and the improved effect of most of microbial bacterial agents reported or produced is general, mainly microbial bacterial agent Be difficult to survive and breed under alkaline land soil environment and played so as to limit its effect, although some microbial bacterial agent effects compared with It is good, but it is expensive.
CN106278705A discloses a kind of alkaline land improving fertilizer special for organic and its preparation method and application, organic fertilizer by Following components in percentage by weight is constituted:Edible oil and fat decolouring spent bleaching clay 90%~92%, middle micro- 1%~6%, it is saline and alkaline Ground improved materials 2%~9%;Middle trace element is consisted of the following components in percentage by weight:Potassium sulfate 35~65%, ammonium sulfate 30~60%, zinc sulfate 1~4%, borax 0.5~2%;Alkaline land improving material is consisted of the following components in percentage by weight: Desulfurization gypsum powder 70~100%, sofril 0~30%.The preparation method of organic fertilizer is:By edible oil and fat decolourize spent bleaching clay, in , according to described percentage by weight mixing and stirring, the pH of dilution is passed through in then addition for trace element and alkaline land improving material The acid conditioner of value, is uniformly mixed, and the pH value for adjusting mixture is 3~4, obtains alkaline land improving fertilizer special for organic, pH value Acid conditioner is consisted of the following components in percentage by weight:Gustatory production wastewater 60~80%, steel and iron industry H2SO4Pickling is given up Liquid 10~20%, steel and iron industry HCL pickle liquors 10~20%, the consumption of pH value acidity conditioner is the 5- of total weight of the mixture 20%.The organic fertilizer of the patent uses edible oil and fat decolouring spent bleaching clay in alkaline land improving first, but it is not to edible The content of grease is illustrated in grease-decolor spent bleaching clay.Meanwhile, it uses steel and iron industry hydrochloric acid and sulphur pickle liquor regulation pH, Because Cr is contained in iron and steel pickling waste liquid the inside, this can cause substantial amounts of Cr to enter soil, cause the secondary pollution of soil, and past Hydrochloric acid and sulfuric acid waste are added in spent bleaching clay, the microorganism in spent bleaching clay are all killed, destroy the environment of the growth of microorganism, Unnecessary grease in spent bleaching clay can not be decomposed by the microorganisms, while the nutrients that plant easily absorbs can not be converted it into Matter, the macronutrient in spent bleaching clay can not be absorbed and used by plants.Additionally, spent bleaching clay addition is up to more than 90%, and , without consumption, containing substantial amounts of nutrient, single fertilization is excessive, can cause the excessive growth of plant, hinders flower_bud formation for grease With bloom, be formulated be unfavorable on the whole that soil granular is formed in addition.For summary, although the organic fertilizer of the patent is using spent bleaching clay It is raw material, but but spent bleaching clay is not utilized well, it is impossible to fundamentally solves the improvement requirement in salt-soda soil.
CN103320137B discloses a kind of composite microbiological bacteriocin saline-alkali soil improver, and described modifying agent includes micro- life Thing, organic liquor and matrix.Described microorganism includes bacillus subtilis (Bacillussubtilis) and bacillus megaterium (Bacillusmegaterium), the ratio of weight and number of described bacillus subtilis and bacillus megaterium is:Withered grass gemma Bacillus 60~80;Bacillus megaterium 20~40, the bacillus subtilis is that the bacillus subtilis is bacillus subtilis Bacterium CGMCC7296, bacillus subtilis CGMCC7297, the mixture of bacillus subtilis CGMCC7298;The huge gemma Bacillus is CGMCC 7337.Described organic liquor includes the protease that described microbial bacterial agent fermentation is produced, lipase, α- Amylase, amino acid.Described matrix includes chicken manure or cow dung, lignite, ground phosphate rock, medical stone.Described chicken manure or cow dung pass through Cross 200~400 DEG C of high-temperature sterilizations;Described lignite is containing 20% humic acid;The ground phosphate rock, medical stone are more than 300 mesh. The patent formulation is complicated, production inconvenience, with the addition of the nutriment that a large amount of growth of microorganism need, relatively costly, and salt-soda soil Hardened environment under, growth of microorganism and breeding are limited, and regulation effect is not good.
Compared to general salt-soda soil, the improvement in the salt-soda soil of heavy metal pollution administers increasingly difficult, and one is pollutant in soil Poor mobility in earth, the holdup time is long, be unable to natural degradation, dilution, flowing, extension that can over time in salt-soda soil all the more Enrichment, the plant planted in harm salt-soda soil;Two is, because salt content is high and in alkalescence, plant survival rate is very low, to improve naturally It is extremely slow.A kind of low cost is provided and modifying agent and the improvement side of heavy metal pollution Saline-alkali Field Control requirement can be fundamentally solved Method is significant.
The content of the invention
An object of the present invention is to provide a kind of improved heavy metal pollution alkaline land modifying agent based on spent bleaching clay, should Modifying agent can effectively realize heavy metal pollution alkaline land improving, and the improvement for fundamentally solving heavy metal pollution salt-soda soil will Ask, while low cost of the present invention.
The present invention also provides a kind of modification method in heavy metal pollution salt-soda soil simultaneously, and the method is easy to operate and can be effective Realize heavy metal pollution alkaline land improving.
To achieve the above object, a kind of technical scheme that the present invention takes is as follows for the present invention:
A kind of heavy metal pollution alkaline land modifying agent based on spent bleaching clay, by weight percentage, its composition of raw materials includes Spent bleaching clay 45-80%, complex micro organism fungicide 0.5-2%, humic acid 5-15%, calcium dihydrogen phosphate 3-10%, calcium carbonate 2- 5%th, citric acid 1-6% and polyaluminium sulfate 2-19.5%, described complex micro organism fungicide is bacillus subtilis, lichens Bacillus, bacillus laterosporus, Streptomyces jingyangensis, bacillusmusilaginosiengineering are 1 by nutrient solution volume ratio:1.2-1.6:0.5- 0.7:1.2-1.5:The mixture of 0.6-0.9 compositions.
Preferably, complex micro organism fungicide is bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Jingyang chain Mould, the volume ratio of bacillusmusilaginosiengineering nutrient solution are 1:1.4-1.5:0.5-0.6:1.2-1.3:It is mixed that 0.8-0.9 is constituted Compound.Most preferably, bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, gel-shaped gemma bar The volume ratio of bacteria culture fluid is 1:1.5:0.6:1.3:0.8.
According to the present invention, the spent bleaching clay is useless white grease-decolor treatment.In oil and fat refining process, typically add atlapulgite Decolourized, the oil that the carclazyte being separated after grease-decolor treatment contains 20-30%.Contain 20-30%'s for these The carclazyte of oil, some producers can carry out secondary deep squeezing, obtain the oil-containing spent bleaching clay of miscella and oil-containing 5-8%.The present invention Can be using the spent bleaching clay of these spent bleaching clays or oil-containing 5-8% containing 20-30% oil.However, as preferred scheme of the invention, It is preferred that it is the spent bleaching clay of 12wt%-15wt% to use oil content, on the one hand, show by inventor's lot of experiments, oil-containing Rate provides good growing environment for the breeding that the spent bleaching clay of 10wt%-18wt% can be good at described complex microorganism, Mixed with microorganism with the spent bleaching clay that oil content is 5-8%, not enough support the growth of long-term microorganism, it is necessary to additionally add battalion again The normal growth that material just can guarantee that microorganism is supported, is such as mixed with microorganism with the spent bleaching clay without after-treatment, applied To in alkaline land soil, microbes have little time to decompose, and cause substantial amounts of grease to be full of in soil, can so cause substantial amounts of Air can not come in, and cause microorganism and be unable to normal growth.On the other hand, inventor is had found by by containing after decolouring The spent bleaching clay of 20-30% can obtain the spent bleaching clay that oil content is 12-15% by normal temperature physical squeezing.It is therefore especially preferred that 12- 15% spent bleaching clay is used as raw material of the invention, it is possible to achieve minimization of cost is (in oil and fat refining process, usually using oil weight 2- 5% carclazyte is decolourized, by the general grease for being adsorbed with 20-50% in the spent bleaching clay after decolouring, then again to decolouring after Spent bleaching clay carry out after-treatment, reduce the content of the inside grease, the handling process of existing market mainly has solvent extraction, height The treated spent bleaching clay of warm physical squeezing method, wherein solvent extraction, oil content inside it than relatively low, substantially grease all by Extract, but using and wasting for substantial amounts of solvent can be caused, simultaneously because using a large amount of solvents, increasing substantial amounts of being processed into This, causes treatment spent bleaching clay economic benefit not high;Spent bleaching clay is processed by high-temperature physics milling process, the oil content inside it is general In 5-8% or so, this method needs to use heated by natural gas, can also increase processing cost, can be big using normal temperature physical squeezing Width reduces cost) while obtain optimal effect.
Preferably, the composition of raw materials of heavy metal pollution alkaline land modifying agent of the invention includes spent bleaching clay 55-70%, is combined Microbial bacterial agent 0.5-2%, humic acid 6-12%, calcium dihydrogen phosphate 3-10%, calcium carbonate 2-5%, citric acid 2-5% and poly- Close aluminum sulfate 8-15%.
According to the present invention, each component for constituting above-mentioned raw materials formula is individually packed.
The present invention also provides a kind of heavy metal pollution saline and alkali land improvement method, and it uses the present invention above-mentioned based on spent bleaching clay Heavy metal pollution alkaline land modifying agent, and comprise the following steps:
(1) complex micro organism fungicide is added in spent bleaching clay, controls temperature to be kept for 3-5 weeks for 28-35 DEG C, make microorganism Breeding, obtains modifying agent component A;
(2) using citric acid as modifying agent B component, it is uniformly sprinkling upon saline and alkaline the earth's surface, is then turned over and spread Water, is kept for 5-15 days;
(3) uniformly are sprinkling upon for it as modifying agent C components by humic acid, calcium dihydrogen phosphate, calcium carbonate, polyaluminium sulfate Saline and alkaline the earth's surface, is then turned over, and is kept for 3-5 days;
(4) modifying agent component A is uniformly sprinkling upon the saline and alkaline the earth's surface processed by step (3), and is turned over, make to mix Close uniform, kept for 5-10 days.
Be added to citric acid in soil first by the inventive method, is mainly to activate and activate the heavy metal in soil, Then humic acid, calcium dihydrogen phosphate, calcium carbonate, polyaluminium sulfate are added in soil carries out the solidification stabilization of heavy metal-polluted soil Change, finally again add component A, further the heavy metal ion in absorption and curing soil such that it is able to process to greatest extent Heavy metal ion in soil, reaches improvement purpose.
Further, the preparation method of the complex micro organism fungicide is:By bacillus subtilis, bacillus licheniformis, Bacillus laterosporus, Streptomyces jingyangensis, the bacterium powder of bacillusmusilaginosiengineering are made each after being cultivated respectively through activation and domestication Nutrient solution, then obtain final product nutrient solution is well mixed.Bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Jingyang Streptomycete, the bacterium powder of bacillusmusilaginosiengineering have learned that, can by commercially available, activation and domestication and culture method according to And known program or the mode of producer's suggestion are carried out.
Preferably, in every gram of modifying agent component A, bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, the viable count of bacillusmusilaginosiengineering are respectively greater than 3.5x108、2.7x108、3.5x107、3.0x108With 2.0x108
Further, in step (1), during holding, 3-4 ventilation is stirred weekly.And preferably kept for 3 weeks.
Further, in step (2), ploughed depth is 18-25cm, preferably from about 20cm.Water is spread so that soil layer of turning over is wet Profit.Preferably, kept for 5-10 days in the step.
Further, in step (3), ploughed depth is 18-25cm, preferably from about 20cm.
Further, in step (3), ploughed depth is 18-25cm, preferably from about 20cm.
According to the present invention, the dosage of modifying agent can accordingly be added according to the saline and alkaline of soil and heavy metal pollution situation. General, the dosage of modifying agent is 150-200kg/ mus.
Compared with prior art, beneficial effects of the present invention are as follows:
(1) spent bleaching clay can be neutralized in acidity with the salt-soda soil in alkalescence, coordinate the use of microorganism, can be effective Reduce the pH value of alkaline land soil, at the same spent bleaching clay can be microorganism in the soil provide nutrient required for breeding and Do not result in excessive fertilization and cause plant excessive growth simultaneously.
(2) present invention pass through experimental studies have found that, by bacillus subtilis, bacillus licheniformis, bacillus laterosporus, river rising in Ningxia and flowing into central Shaanxi After positive streptomycete, bacillusmusilaginosiengineering mix in specific proportions, can be reached in the environment in salt-soda soil in the presence of spent bleaching clay To symplastic growth and breeding, if lacking jelly bacillus, bacillus licheniformis, bacillus laterosporus and Jingyang in microbial inoculum Streptomycete cannot survive discovery substantially, if removing bacillus licheniformis, be had when mix bacterium agent is mixed substantial amounts of miscellaneous Bacterium produces, so as to suppress the growth of beneficial bacterium in microbial inoculum, causes the quality of microbial inoculum between a batch unstable, causes to saline and alkaline Ground repairing effect does not reach requirement, the compounding of this several microbial inoculum, it is possible to increase its collaboration resistance alkali ability, can be in salt-soda soil soil Fermented well in earth, support the growth in saline and alkaline aerial plant.
(3) humic acid is added in inventive formulation, the pH of alkaline land soil on the one hand can be reduced, on the other hand can be changed It is apt to living environment of the microorganism in salt-soda soil, while substantial amounts of growth elements can also be provided for the growth of plant.In formula Calcium ion can chemically react with carbanion in salt-soda soil and bicarbonate ion in calcium salt and spent bleaching clay, generate carbonic acid Calcium and calcium bicarbonate, wherein calcium carbonate are water insoluble, and calcium bicarbonate is slightly soluble in water, and the property of calcium carbonate and calcium bicarbonate can promote Zinc fractions spherulitic texture, spherulitic texture, while reducing the unit weight of soil, the logical of soil can be increased with wrapping portion sodium ion It is aqueous.The heavy metal and OH that cause in soil are changed by ion simultaneously-、PO4 3-、CO3 2-、SO4 2-Etc. precipitation is combined into, so as to have Heavy metal in the rehabilitating soil of effect.The polyaluminium sulfate added in formula, by the substantial amounts of AL of ion exchange3+Into soil In, colloid is formed with the water in soil, the formation of the crumb structure of soil is promoted, increased the gas permeability of soil and permeable Property, so that the microorganism in soil substantial amounts of can breed, heavy metal that can effectively in rehabilitating soil.Lemon in formula On the one hand lemon acid can adjust the pH in salt-soda soil, on the other hand can activate and activate the heavy metal ion in soil, contribute to Heavy metal ion and OH-、PO4 3-、CO3 2-、SO4 2-Etc. being combined into precipitation.Whole recipe ingredient synergies, effectively improve saline and alkaline Ground and removes removing heavy metals at soil.
(4) raw material used is finally converted to plant growth and can absorb the element for utilizing in being formulated, and does not result in soil Secondary pollution, and wherein realize the resource reutilization of spent bleaching clay, help to reduce environmental pollution.
Specific embodiment
Below in conjunction with specific embodiment, the present invention will be further described in detail, and unreceipted condition is in embodiment The conventional condition in this area.When the consumption or dosage or content of material is addressed, unless stated otherwise, weight is referred both to.Below The complex micro organism fungicide used in embodiment, preparation method is as follows:Microbial bacteria by commercially available, and using it is preceding according to Known program or producer suggestion mode enter line activating and domestication cultivate, then by bacillus subtilis, bacillus licheniformis, Bacillus laterosporus, Streptomyces jingyangensis, bacillusmusilaginosiengineering nutrient solution are according to volume ratio 1:1.5:0.6:1.3:0.8 compounding exists Together, control temperature is at 28-32 DEG C.
Embodiment 1
This example provides a kind of heavy metal pollution alkaline land modifying agent, and by weight percentage, its composition of raw materials includes useless white Soil 65%, complex micro organism fungicide 1%, humic acid 8%, calcium dihydrogen phosphate 6%, calcium carbonate 5%, citric acid 5% and polymerization Aluminum sulfate 10%.Wherein spent bleaching clay oil content is for about 13-14%.Each component independent packaging.
Embodiment 2
This example provides a kind of heavy metal pollution alkaline land modifying agent, and by weight percentage, its raw material includes spent bleaching clay 55%, complex micro organism fungicide 1.5%, humic acid 10%, calcium dihydrogen phosphate 5%, calcium carbonate 4%, citric acid 5% and polymerization Aluminum sulfate 19.5%.Wherein spent bleaching clay oil content is for about 12-13%.Each component independent packaging.
Embodiment 3
This example provides a kind of heavy metal pollution alkaline land modifying agent, its substantially with embodiment 1, unlike, wherein useless white Native oil content is for about 6-8%.
Embodiment 4
This example provides a kind of heavy metal pollution alkaline land modifying agent, its substantially with embodiment 1, unlike, wherein useless white Native oil content is for about 20-22%.
Comparative example 1
This example provides a kind of heavy metal pollution alkaline land modifying agent, its substantially with embodiment 1, unlike, wherein compound Microbial bacterial agent is bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis in proportion 1:1.5:0.6: 1.3 mixing compositions.
Comparative example 2
This example provides a kind of heavy metal pollution alkaline land modifying agent, its substantially with embodiment 1, unlike, wherein compound Microbial bacterial agent is bacillus subtilis, bacillus laterosporus, Streptomyces jingyangensis, jelly bacillus in proportion 1:0.6:1.3: 0.8 mixing composition.
Comparative example 3
This example provides a kind of heavy metal pollution alkaline land modifying agent, and by weight percentage, its composition of raw materials includes useless white Soil 65%, complex micro organism fungicide 1%, humic acid 8%, calcium dihydrogen phosphate 11%, citric acid 5% and polyaluminium sulfate 10%, wherein spent bleaching clay oil content is for about 13-14%.Each component independent packaging.
Embodiment 5
Alkaline land improving experiment is carried out using the modifying agent of embodiment 1-4 and comparative example 1-3, it is specific as follows:
1. salt-soda soil situation is tested:Central arid belt in Ningxia Yinchuan City Xingqing District moderate salt affected soil, its pH value 8.65 or so, Salt-soda soil is divided into 8 homalographic regions, 0.05 mu of each region.
2. for studying thing:Paddy rice, in late April, 2016 sowing, late August harvests.
3. modifying agent consumption:180kg/ mus.
4. method for testing is supplied:First salt-soda soil is improved, then long-term cropping on the soil after improvement, wherein improvement side Method is as follows:Complex micro organism fungicide in each formula is added in spent bleaching clay, control temperature is for about 30-32 DEG C and is kept for 3 weeks, obtains To modifying agent component A, wherein viable count is surveyed, as a result referring to table 1;Using citric acid as modifying agent B component, it is uniformly sprinkling upon salt Alkali the earth's surface, then carries out turning over 20cm and spreads water (wetting), is kept for 7 days, by humic acid, calcium dihydrogen phosphate, carbonic acid Calcium and polyaluminium sulfate are uniformly sprinkling upon saline and alkaline the earth's surface as modifying agent C components, then carry out turning over 20cm and spread water (wetting ), kept for 5 days, modifying agent component A is uniformly sprinkling upon saline and alkaline the earth's surface, and the 20cm that turns over is carried out, and make to be well mixed, protect Hold 7 days, the betterment of land is to complete.Detection soil indices, as a result referring to table 2, wherein heavy metal index is shown in Table 3.
Table 1
Table 2
Table 3
Sequence number Cadmium (mg/kg) Chromium (mg/kg) Lead (mg/kg) Mercury (mg/kg) Copper (mg/kg)
Blank soil 2.4089 462.3 108.6 2.3963 135.6
Embodiment 1 0.8868 246.3 63.22 0.7689 66.36
Embodiment 2 0.8812 249.9 66.01 0.7584 64.98
Embodiment 3 1.3245 359.6 91.12 1.324 109.1
Embodiment 4 1.3589 355.3 92.19 1.341 105.2
Comparative example 1 2.3598 361.3 94.21 1.311 105.8
Comparative example 2 2.3345 360.1 92.46 1.321 113.8
Comparative example 3 1.3201 357.4 94.99 1.309 111.2
General planting and fertilizing management further are carried out according to conventional crop to the soil after the completion of improvement, is inserted in paddy rice Before seedling, with reference to site preparation, regular job is pressed in field management and water management.Indices to crop detect, as a result referring to Table 4.Further, it was observed that, the corresponding paddy rice of comparative example 1 and 2, every fringe overhead grain number and flat grain number (averagely about 79/fringe) are substantially More than other examples (averagely about 40-60/fringe), bear fruit grains (averagely about 65-70) are significantly lower than other examples (averagely about 80-90).
Table 4
Sequence number Plant height (cm) Spike length (cm) Yield (kg/ mus)
Embodiment 1 88.6 30 498 18.3 705.9
Embodiment 2 87.9 30 502 18.2 700.6
Embodiment 3 84.2 30 445 14.4 546.3
Embodiment 4 85.6 30 446 15.6 578.2
Comparative example 1 84.6 30 423 16.9 622.6
Comparative example 2 82.9 30 438 16.2 590.1
Comparative example 3 86.3 30 466 17.6 638.4
Above result of the test shows, can successfully realize that heavy metal is dirty using the modifying agent and modification method of inventive formulation The improvement in salt-soda soil is contaminated, improved effect is notable.

Claims (10)

1. a kind of heavy metal pollution alkaline land modifying agent based on spent bleaching clay, it is characterised in that:By weight percentage, it is described heavy The composition of raw materials of metallic pollution alkaline land modifying agent includes spent bleaching clay 45-80%, complex micro organism fungicide 0.5-2%, humic acid 5-15%, calcium dihydrogen phosphate 3-10%, calcium carbonate 2-5%, citric acid 1-6% and polyaluminium sulfate 2-19.5%, it is described Complex micro organism fungicide is bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, gel-shaped gemma Bacillus is 1 by nutrient solution volume ratio:1.2-1.6:0.5-0.7:1.2-1.5:The mixture of 0.6-0.9 compositions.
2. the heavy metal pollution alkaline land modifying agent based on spent bleaching clay according to claim 1, it is characterised in that:Described Complex micro organism fungicide is bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, gel-shaped gemma The volume ratio of bacillus nutrient solution is 1:1.4-1.5:0.5-0.6:1.2-1.3:The mixture of 0.8-0.9 compositions.
3. the heavy metal pollution alkaline land modifying agent based on spent bleaching clay according to claim 1, it is characterised in that:It is described useless Carclazyte is that grease-decolor processes spent bleaching clay, and its oil content is 12wt%-15wt%.
4. the heavy metal pollution alkaline land improving based on spent bleaching clay according to any one of claims 1 to 3 claim Agent, it is characterised in that:The each component of the composition above-mentioned raw materials is individually packed.
5. a kind of heavy metal pollution saline and alkali land improvement method, it is characterised in that:The method is using any in such as Claims 1-4 The heavy metal pollution alkaline land modifying agent based on spent bleaching clay described in item claim, and comprise the following steps:
(1) complex micro organism fungicide is added in spent bleaching clay, controls temperature to be kept for 3-5 weeks for 28-35 DEG C, make microorganism numerous Grow, obtain modifying agent component A;
(2) using citric acid as modifying agent B component, it is uniformly sprinkling upon saline and alkaline the earth's surface, is then turned over and spread water, protected Hold 5-15 days;
(3) uniformly are sprinkling upon for it saline and alkaline by humic acid, calcium dihydrogen phosphate, calcium carbonate, polyaluminium sulfate as modifying agent C components The earth's surface, is then turned over, and is kept for 3-5 days;
(4) modifying agent component A is uniformly sprinkling upon the saline and alkaline the earth's surface processed by step (3), and is turned over, make mixing equal It is even, kept for 5-10 days.
6. heavy metal pollution saline and alkali land improvement method according to claim 5, it is characterised in that:Every gram of modifying agent A In component, bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, the viable bacteria of bacillusmusilaginosiengineering Number is respectively greater than 3.5x108、2.7x108、3.5x107、3.0x108And 2.0x108
7. heavy metal pollution saline and alkali land improvement method according to claim 5, it is characterised in that:The composite microbial bacteria The preparation method of agent is:By bacillus subtilis, bacillus licheniformis, bacillus laterosporus, Streptomyces jingyangensis, gel-shaped gemma Then be well mixed for nutrient solution and obtain final product by the bacterium powder of bacillus respectively through respective nutrient solution is made after activation and domestication culture.
8. heavy metal pollution saline and alkali land improvement method according to claim 5, it is characterised in that:In step (1), keeping During, 3-4 ventilation is stirred weekly.
9. heavy metal pollution saline and alkali land improvement method according to claim 5, it is characterised in that:Step (2) is to step (4) In, ploughed depth is respectively 18-25cm.
10. the heavy metal pollution alkaline land modifying agent based on spent bleaching clay as described in any one of Claims 1-4 claim Application in heavy metal pollution alkaline land improving.
CN201710205940.8A 2017-03-31 2017-03-31 Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay Pending CN106831266A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710205940.8A CN106831266A (en) 2017-03-31 2017-03-31 Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710205940.8A CN106831266A (en) 2017-03-31 2017-03-31 Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay

Publications (1)

Publication Number Publication Date
CN106831266A true CN106831266A (en) 2017-06-13

Family

ID=59142845

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710205940.8A Pending CN106831266A (en) 2017-03-31 2017-03-31 Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay

Country Status (1)

Country Link
CN (1) CN106831266A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107285913A (en) * 2017-08-07 2017-10-24 镇江万山红遍农业园 A kind of fertilizer for improving pear tree planting soil and preparation method thereof
CN109233861A (en) * 2018-11-05 2019-01-18 湖南泰谷生态工程有限公司 A kind of preparation method of macromolecular soil conditioner

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105103757A (en) * 2015-08-28 2015-12-02 贵州开磷集团股份有限公司 Method for improving saline and alkaline land by using ardealite, tetrametilenpentaurea and biological bacteria
CN105622297A (en) * 2016-03-21 2016-06-01 上海鲲鹏环保科技有限公司 Compound microbial fertilizer taking waste clay minerals as main raw material
CN106278705A (en) * 2016-07-27 2017-01-04 北京盖希尔科技股份有限公司 A kind of alkaline land improving fertilizer special for organic and its preparation method and application
CN106337030A (en) * 2016-08-24 2017-01-18 宁波枫叶杰科生物技术有限公司 Microbial product for treatment of heavy metal polluted saline-alkaline land and manufacture method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105103757A (en) * 2015-08-28 2015-12-02 贵州开磷集团股份有限公司 Method for improving saline and alkaline land by using ardealite, tetrametilenpentaurea and biological bacteria
CN105622297A (en) * 2016-03-21 2016-06-01 上海鲲鹏环保科技有限公司 Compound microbial fertilizer taking waste clay minerals as main raw material
CN106278705A (en) * 2016-07-27 2017-01-04 北京盖希尔科技股份有限公司 A kind of alkaline land improving fertilizer special for organic and its preparation method and application
CN106337030A (en) * 2016-08-24 2017-01-18 宁波枫叶杰科生物技术有限公司 Microbial product for treatment of heavy metal polluted saline-alkaline land and manufacture method thereof

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
何燧源等: "《环境化学》", 28 February 1995, 华东化工学院出版社 *
何连生等: "《重金属污染调查与治理技术》", 31 December 2013, 中国环境出版社 *
张乃明: "《环境土壤学》", 31 January 2013, 中国农业大学出版社 *
李永祺等: "《海洋恢复生态学》", 31 March 2016, 中国海洋大学出版社 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107285913A (en) * 2017-08-07 2017-10-24 镇江万山红遍农业园 A kind of fertilizer for improving pear tree planting soil and preparation method thereof
CN109233861A (en) * 2018-11-05 2019-01-18 湖南泰谷生态工程有限公司 A kind of preparation method of macromolecular soil conditioner

Similar Documents

Publication Publication Date Title
CN104056852B (en) The chemistry of compound heavy-metal contaminated soil and microbial association restorative procedure and application
CN104059671B (en) The secondary NO of facility 3-salty soils modifying agent, preparation method and modification method
CN106590671B (en) Soil conditioner and preparation method and application thereof
CN104788265A (en) Saline-alkali soil biological improved fertilizer based on high-sulfur gangue and preparation method thereof
CN104230601A (en) Soil remediation agent and preparation method thereof
CN106833671A (en) Alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay and phosphatization slag
CN106278705A (en) A kind of alkaline land improving fertilizer special for organic and its preparation method and application
CN107935767A (en) A kind of alkaline land improving fertilizer
CN106083481B (en) A kind of production technology improveing salt-soda soil bio-organic fertilizer
CN106905982A (en) Using the heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method of spent bleaching clay
CN106905052A (en) Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method comprising spent bleaching clay
CN106986703A (en) Multifunctional biological fertilizer and its application
CN106947716A (en) The agent of heavy metal pollution Saline-alkali Field Control and saline-alkali soil treatment method comprising spent bleaching clay
CN106977304A (en) A kind of biological organic fertilizer and its application based on spent bleaching clay
CN106701101A (en) Saline and alkaline land conditioner and saline and alkaline land conditioning method
CN106831266A (en) Heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay
CN107721602A (en) A kind of alkaline Sandy Soil improvement matrix and preparation method thereof
CN106977305A (en) Multifunctional biological fertilizer and its application based on spent bleaching clay
CN107089861A (en) Recycle biological organic fertilizer and its application of spent bleaching clay
CN106753417A (en) Alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay and desulfurated plaster
CN106753418A (en) Alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay
CN106833672A (en) Alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay and waste residue
CN106905983A (en) Using the heavy metal pollution alkaline land modifying agent and saline and alkali land improvement method of spent bleaching clay
Abdel-Rahman Effect of mineral potassium, compost and biofertilizers on soil physio-chemical properties and productivity of sesame grown on salt affected soils
CN106977303A (en) Biological organic fertilizer and its application based on spent bleaching clay

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right
TA01 Transfer of patent application right

Effective date of registration: 20200103

Address after: 730030 room 603, floor 6, unit 6, No. 567-6, duanjiatan Road, gongxingdun street, Chengguan District, Lanzhou City, Gansu Province

Applicant after: Gansu tiannongyihe Agriculture Co.,Ltd.

Address before: 201203 Shanghai city Pudong New Area Zhuqiao 12 No. 2 gold smell Road Building 2 storey 173 room

Applicant before: SHANGHAI LICHANG ENVIRONMENTAL ENGINEERING Co.,Ltd.

RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170613