CN106010565A - Organochlorine pesticide contaminated soil remediation agent - Google Patents
Organochlorine pesticide contaminated soil remediation agent Download PDFInfo
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- CN106010565A CN106010565A CN201610442960.2A CN201610442960A CN106010565A CN 106010565 A CN106010565 A CN 106010565A CN 201610442960 A CN201610442960 A CN 201610442960A CN 106010565 A CN106010565 A CN 106010565A
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- mycopowder
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- mucormycosis
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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
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
-
- C—CHEMISTRY; METALLURGY
- 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
- C09K2101/00—Agricultural use
Abstract
The invention belongs to the technical field of soil remediation and particularly relates to an organochlorine pesticide contaminated soil remediation agent. The organochlorine pesticide contaminated soil remediation agent is prepared from chitosan, bentonite, green algae, citric acid, shell powder, needle mushroom fungus chaff, corn cobs, rice bran, tea seed shells, walnut shells, areca catechu wood bits, palm wood bits, a composite enzyme preparation and a compound microbial agent. According to the soil remediation agent, under the condition that no other chemical solvent is introduced, the mild enzymes and the microbial agent are adopted to treating soil, no secondary pollution is caused, and action conditions are mild.
Description
Technical field
The invention belongs to technical field of soil remediation, be specifically related to a kind of organochlorine pesticide pollution soil-repairing agent.
Background technology
Organochlorine class is polluted, and mainly organic chlorine agriculture chemicals pollutes, and organic chlorine agriculture chemicals pollutes the environment being well recognized as
Priority pollutants, is also typical persistent pollutant, has and is difficult to degradability, half volatile, biology
Accumulation and high toxicity, existed for a long time in nature, and be enriched with by food chain, the degraded of a-HCH and Y-HCH
Half-life is 26 years and 42 years respectively.Gamma Hexaochlorocyclohexane and clofenotane are as main insecticide, in 20th century of China
The 60-70 age was once widely used, and western developed country 20 century 70 just has begun to disable organochlorine pesticide,
China also prohibits its production and use in nineteen eighty-three, but owing to usage amount is big, degraded is slowly in the environment,
Holdup time is long so that organochlorine pesticide remains the class organic pollution that recall rate in environment is the highest.
Organochlorine pesticide can be sunk by industrial wastewater and the discharge of sanitary sewage, agricultural runoff, the dry and wet of air
The various approach such as fall, soil erosion enter water body, but are because it and have the characteristic of hydrophobic parent's granule, the most very
Easily adsorbed by the suspended particulate matter in water body such as mineral, bioclast and colloid etc., and finally with emphatically
The physics chemical action such as power sedimentation enter in deposit, are enriched with in water-bed deposit.
Organochlorine pesticide enters environment mainly three kinds of approach: one is that pesticide directly sprays in soil, is used for preventing
Control subterranean pest-insect, go to cut weeds;Two is all kinds of pesticide prevented and treated disease pest and weed and be sprayed on crop, Qi Zhongzhi
I haven't seen you for ages has the pesticide of 56% to fall in the middle of soil;Three is that part pesticide fills the air when spraying and dusting use pesticide
In air, and along with air-flow and wind migrate, spreading to each corner of environment, once someone calculated, and 60
The clofenotane that the North Sea, age Europe settles every year from air is up to 3,000,000 tons more than.The longest for the half-life
Clofenotane, its distribution has almost spread over each corner in the world, in the age that organochlorine uses in a large number, some
Famous river, in the river of Mississippi, the Rhine, Danube etc., clofenotane the most once detected.
Restorative procedure to organochlorine class contaminated soil at present, mainly has following several:
Peripheral doses method, chemical repair method, plant absorption method, plant-microorganism associating system is to organic
The conversion of chloro pesticide, specific as follows:
Peripheral doses method: air injection is mainly used in repairing by nonaqueous phase liquid in situ, and particularly volatility has
The saturated soil of machine thing pollution and subsoil water.The sealed underground water system that biological restoration in the past utilizes often is made
Become oxygen not enough, and bio-inert well provides substantial amounts of oxygen, thus promote biodegradation efficiency.
Chemical repair method
Roy et al. extracts biosurfactant from peel, applies it to the cleaning of Gamma Hexaochlorocyclohexane in soil,
It is the 20 of clear water respectively that biosurfactant solution with 0.5% and 1% removes the efficiency of the Gamma Hexaochlorocyclohexane in soil
Again with 100 times.
Organochlorine pesticide in soil is mainly absorbed by plant absorption method by root system of plant, but plant roots
Being that the intensity absorbing organochlorine pesticide is not built, it is repaired by organochlorine pesticide contaminated soil, mainly depends on
The complexation produced organochlorine pesticide by root exudates and enzyme and degraded etc. act on organochlorine pesticide of degrading.Plant
Thing root system can secrete the nutrient substance such as sugar, alcohol, protein in soil, for microbe survival;Root system of plant is also
The chemical substances such as organic acid can be secreted, thus it is possible to vary the decomposition of the pH-value etc. of soil, beneficially organochlorine pesticide.
Research shows, has flourishing root system, the plant of root hair can promote that rhizosphere microorganism flora is to herbicide, parasite killing
The organic absorption such as agent and degraded.
The plant-microorganism associating system conversion to organochlorine pesticide, the mineralization of plant strengthening rhizosphere and bacterium
Root and had certain relation by raw bacterium, mycorhiza has micro-life as the coalition of fungus Yu plant to the impact of soil
Thing and the double grading of plant, the ad hoc structure of mycorrhizal plants makes the absorption area of root system increase, can reduce plant
And the fluid resistance between soil, promotes that root system is to moisture and the absorption of nutrient and utilization.Secretions from plant roots
Can also stimulate the transformation of antibacterial, form organic carbon at rhizospheric environment, the death of root cells simultaneously also can increase
Soil organic matter, the increase of these organic carbons can stop organochlorine pesticide to shift to subsoil water, it is possible to increases micro-life
The thing mineralization to organochlorine pesticide.There are some researches show, microorganism to the mineralization of atrazine also with soil
Organic carbon constituents is directly related.Additionally, plant is owing to having complicated root system, its huge root surface area
Also in place of being the boarding of microorganism, thus the growth for soil microorganism provides more existence place and environment,
The aerobic transformation enabling rhizospheric environment is normally carried out.
Although above-mentioned phytoremediation technology has many good qualities, but still there is a lot of incomplete place, actual
Having certain limitation in application, as in repair process, the condition such as soil, weather is had necessarily by some plant
Requirement, be easily subject to the restriction of self and extraneous factor.
Above-mentioned to the restorative procedure by organochlorine class contaminated soil, or can not eliminate in soil the most thoroughly
Organochlorine pollutant, or bring new pollutant, or it uses the restriction receiving environmental condition, exists each
Kind of defect, accordingly, it would be desirable to for above-mentioned present situation, grope a kind of remove organochlorine pesticide effective and warmer
Sum do not produce new contaminated soil renovation agent.
Summary of the invention
In order to solve above-mentioned technical problem, the invention provides one and control by organochlorine pesticide contaminated soil
Manage the effective and gentle renovation agent the most not bringing new pollution of action condition, this soil-repairing agent combine plant,
Enzyme and microorganism act on jointly by the soil of organochlorine pesticide, make the organochlorine pesticide in soil or absorption or quilt
Chelate or be degraded, reaching to administer the purpose of organochlorine pesticide pollution soil.
The present invention is to be realized by following technical scheme:
The soil-repairing agent of organochlorine pesticide pollution, including the component of following portions by weight:
Compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalatic enzyme alive 18.3 × 105U/g;Nitro is also
The enzyme of protoenzyme alive 8.9 × 105U/g;
Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 1-4:2-6:1-5;
Complex micro organism fungicide 0.005-0.048;
The active component of above-mentioned complex micro organism fungicide by alternate mucormycosis mycopowder, bacillus megaterium mycopowder,
Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder institute group
Become;
Above-mentioned alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, hay spore
Bacillus mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: (1-4): (1-5): (2-5):
(1-6): (1-5): (2-5);
The living bacteria count of alternate mucormycosis mycopowder is 2 × 108-9×109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 4 × 109-9×1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 5 × 108-9×109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 2.5 × 109-9×1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 3.5 × 109-9×1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 5.5 × 108-9×109cfu/g。
Preferably, the weight ratio of above-mentioned each mycopowder is:
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis
Mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
Compound enzymic preparation is 0.008 part;
Complex micro organism fungicide 0.036 part.
It is furthermore preferred that the soil-repairing agent of the present invention includes the component of following portions by weight:
Compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalase 18.3 × 105U/g;Nitroreductase 8.9
×105U/g;Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 2:4:3;
Complex micro organism fungicide 0.036;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 2 × 108-9×109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 4 × 109-9×1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 5 × 108-9×109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 2.5 × 109-9×1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 3.5 × 109-9×1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 5.5 × 108-9×109cfu/g。
Preferably, soil-repairing agent includes the component of following portions by weight:
Compound enzymic preparation is made up of aldehyde dehydrogenase, catalase, nitroreductase, polyphenol oxidase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalatic enzyme alive 18.3 × 105U/g;Nitro is also
The enzyme of protoenzyme alive 8.9 × 105U/g, the enzyme work of polyphenol oxidase are 11.3 × 105U/g;
Aldehyde dehydrogenase, catalase, nitroreductase, the ratio of weight and number of polyphenol oxidase are 2:5:2:
3;
Complex micro organism fungicide 0.036 part;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized.
It is furthermore preferred that the soil-repairing agent of organochlorine pesticide pollution, including the component of following portions by weight:
Mix with pedotheque, keep 48 hours;
Mycopowder of the present invention, enzyme are derived from commercially available;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized;
Add complex micro organism fungicide 0.036 part, mix homogeneously;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g。
The beneficial effects of the present invention is, use the soil-repairing agent of the present invention, do not introducing other chemistry
Under conditions of solvent, use gentle enzyme and microorganism fungus kind that soil is processed, do not bring new pollution into,
Action condition is gentle, and strain effectively degrades organochlorine pesticide.
Detailed description of the invention
Below in conjunction with specific embodiment, the present invention is further described, in order to those skilled in the art
Know more about the present invention, but and be not so limited the present invention.
Embodiment 1
Take by organochlorine pesticide contaminated soil sample, then join soil-repairing agent 50 by every 1000 grams of pedotheques
Gram ratio fetch earth soil repair agent;
In pedotheque, add following raw material: chitosan, bentonite, chlorella, citric acid, conch meal,
Flammulina velutiper (Fr.) Sing mushroom bran, corn cob, Testa oryzae, tea seed episperm, walnut shell, betelnut tree wood flour, palm wood flour;
The parts by weight of each raw material are as follows:
Mix with pedotheque, keep 48 hours;
Mycopowder of the present invention, enzyme are derived from commercially available;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized;
Add complex micro organism fungicide 0.036 part, mix homogeneously;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Above living bacteria count is approximate number, as follows;
Being eventually adding compound enzymic preparation 0.008 part, mix homogeneously, compound enzymic preparation is by aldehyde dehydrogenase, peroxidating
Hydrogen enzyme, nitroreductase, polyphenol oxidase are formed, and the enzyme of aldehyde dehydrogenase is lived and is about 5.4 × 105U/g;Cross
The enzyme of hydrogen oxide enzyme is lived and is about 18.3 × 105U/g;The enzyme of nitroreductase is lived and is about 8.9 × 105U/g, many
The enzyme of phenol oxidase is lived and is about 11.3 × 105U/g;Aldehyde dehydrogenase, catalase, nitroreductase, polyphenol
Oxidasic ratio of weight and number is 2:4:3:2;
This compound enzymic preparation first stirs in the water of 45 DEG C, is then sprayed in pedotheque, and will
Pedotheque stirs;
Above " part " is parts by weight, and following example are same, if no special instructions.
Inventor has been again following contrast experiment about the application, specific as follows:
Comparative example 1
With not being both of embodiment 1, in comparative example 1 and be provided without compound enzymic preparation, remaining is identical;
Comparative example 2
With not being both of embodiment 1, in comparative example 1 and be provided without complex micro organism fungicide, remaining complete phase
With;
Comparative example 3
With not being both of embodiment 1, complex micro organism fungicide is different, the concrete complex micro organism fungicide used
As follows:
Bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reduction
Bacterium mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:4:3:3:4;
Comparative example 4
With not being both of embodiment 1, it is compound that compound enzymic preparation is aldehyde dehydrogenase, catalase is formed
Enzyme, the enzyme work of aldehyde dehydrogenase is 5.4 × 105U/g;The work of catalase enzyme is 18.3 × 105U/g;Aldehyde takes off
Hydrogen enzyme, catalatic ratio of weight and number are 3:2.
Comparative example 5
As different from Example 1, it is provided without complex micro organism fungicide and compound enzymic preparation, remaining complete phase
With.When processing soil, and after pedotheque mixing, keep 48 hours.
Pedotheque and renovation agent being placed in the container of a cuboid, pedotheque is laid about with renovation agent
20-25 centimetre is thick, pedotheque and soil-repairing agent is fully mixed by above-mentioned and protected by the above-mentioned time
After holding, then trickle in a reservoir, keep pedotheque and renovation agent to moisten;Drip washing in every 10 days is once;Water
Solution is drained by outlet with filter screen below container.When 1 month, 2 months time, 3 months time respectively
Survey the content of Organochlorine Pesticides In Soil.Use the content of organochlorine pesticide in Soil by Gas Chromatography sample,
The computing formula of organochlorine pesticide degradation rate:
Y=(M-W)/M × 100%
In formula, Y is organochlorine pesticide degradation rate, %;W is residue organochlorine pesticide quality, g in pedotheque;
M is original organochlorine pesticide quality, g in pedotheque.
Each comparative example is also adopted by above-mentioned processing mode, and result is as follows:
Organochlorine pesticide degradation rate in the pedotheque of table 1 embodiment 1 and comparative example 1-5
Embodiment 2
Identical with the pedotheque in embodiment 1, use the method identical with embodiment 1 to remove soil
Organochlorine pesticide in sample, is a difference in that the parts by weight etc. of soil-repairing agent are had any different;
Compound enzymic preparation is made up of aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalase 18.3 × 105U/g;Nitroreductase 8.9
×105U/g, the enzyme work of polyphenol oxidase are 11.3 × 105U/g;
Aldehyde dehydrogenase, catalase, nitroreductase, the enzyme work of polyphenol oxidase are 2 for ratio of weight and number:
4:3:1;
Complex micro organism fungicide 0.005;
The active component of above-mentioned complex micro organism fungicide by alternate mucormycosis mycopowder, bacillus megaterium mycopowder,
Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder institute group
Become;
Above-mentioned alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, hay spore
Bacillus mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 1:1:2:1:1:2;
Above-mentioned alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, hay spore
In bacillus mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized.
Embodiment 3
Identical with the pedotheque in embodiment 1, use the method identical with embodiment 1 to remove soil
Organochlorine pesticide in sample, is a difference in that the parts by weight etc. of soil-repairing agent are had any different;
Compound enzymic preparation is aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105The work of U/g, catalase enzyme is 18.3 × 105U/g, nitro are also
The work of protoenzyme enzyme is 8.9 × 105U/g;The ratio of weight and number of aldehyde dehydrogenase, catalase and nitroreductase is
1:2:1;
Complex micro organism fungicide 0.048;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 4:5:5:6:5:5;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized;
Embodiment 4
Identical with the pedotheque in embodiment 1, use the method identical with embodiment 1 to remove soil
Organochlorine pesticide in sample, is a difference in that the parts by weight etc. of soil-repairing agent are had any different;
Soil-repairing agent includes the component of following portions by weight:
Compound enzymic preparation is made up of aldehyde dehydrogenase, catalase, nitroreductase, polyphenol oxidase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalatic enzyme alive 18.3 × 105U/g;Nitro is also
The enzyme of protoenzyme alive 8.9 × 105U/g, the enzyme work of polyphenol oxidase are 11.3 × 105U/g;
Aldehyde dehydrogenase, catalase, nitroreductase, the ratio of weight and number of polyphenol oxidase are 2:5:2:
3;
Complex micro organism fungicide 0.036 part;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized.
Embodiment 5
Identical with the pedotheque in embodiment 1, use the method identical with embodiment 1 to remove soil
Organochlorine pesticide in sample, is a difference in that the parts by weight etc. of soil-repairing agent are had any different;
Compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalase 18.3 × 105U/g;Nitroreductase 8.9
×105U/g;Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 2:4:3;
The active component of complex micro organism fungicide is by alternate mucormycosis mycopowder, bacillus megaterium mycopowder, bending vacation
Zymomonas mobilis mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder are formed;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis bacterium
Powder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 5 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 4 × 1010cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 6 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 6 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 7 × 109cfu/g。
After embodiment 2-5 all uses method same as in Example 1 to process, record organochlorine in pedotheque
The degradation rate result of pesticide is as follows:
1 month | 2 months | 3 months | |
Embodiment 2 | 27% | 64% | 81% |
Embodiment 3 | 27% | 67% | 83% |
Embodiment 4 | 31% | 62% | 88% |
Embodiment 5 | 26% | 65% | 83% |
Claims (7)
1. the soil-repairing agent of organochlorine pesticide pollution, including the component of following portions by weight:
Chitosan 1-3
Bentonite 80-200
Chlorella 10-25 citric acid 0.5-2
Conch meal 2-9 Flammulina velutiper (Fr.) Sing mushroom bran 5-15
Corn cob 40-80
Testa oryzae 10-20
Tea seed episperm 5-15 walnut shell 5-20
Betelnut tree wood flour 20-80 palm wood flour 25-60
Compound enzymic preparation 0.001-0.02;
Described compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of described aldehyde dehydrogenase alive 5.4 × 105U/g;Catalatic enzyme alive 18.3 × 105U/g ;The enzyme of nitroreductase alive 8.9 × 105U/g;Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 1-4:2-6:1-5;
Complex micro organism fungicide 0.005-0.048;
The active component of described complex micro organism fungicide is made up of alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder;
Described alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: (1-4): (1-5): (2-5): (1-6): (1-5): (2-5);
The living bacteria count of described alternate mucormycosis mycopowder is 2 × 108-9×109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 4 × 109-9×1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 5 × 108-9×109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 2.5 × 109-9×1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 3.5 × 109-9×1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 5.5 × 108-9×109cfu/g。
2. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that the weight ratio of each mycopowder is:
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4.
3. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that described compound enzymic preparation is 0.008 part.
4. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that described complex micro organism fungicide 0.036 part.
5. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that include the component of following portions by weight:
Chitosan 2
Bentonite 160
Chlorella 20 citric acid 1.5
Conch meal 6
Flammulina velutiper (Fr.) Sing mushroom bran 10
Corn cob 60
Testa oryzae 15
Tea seed episperm 10
Walnut shell 15
Betelnut tree wood flour 60
Palm wood flour 45
Compound enzymic preparation 0.008
Complex micro organism fungicide 0.036;
Described compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of described aldehyde dehydrogenase alive 5.4 × 105U/g;Catalase 18.3 × 105U/g ;Nitroreductase 8.9 × 105U/g;Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 2:4:3;
The active component of described complex micro organism fungicide is made up of alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder;
Described alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 2 × 108-9×109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 4 × 109-9×1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 5 × 108-9×109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 2.5 × 109-9×1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 3.5 × 109-9×1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 5.5 × 108-9×109cfu/g。
6. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that include the component of following portions by weight:
Soil-repairing agent includes the component of following portions by weight:
Chitosan 2.5
Bentonite 160
Chlorella 18
Citric acid 1.5
Conch meal 7
Flammulina velutiper (Fr.) Sing mushroom bran 12
Corn cob 60
Testa oryzae 16
Tea seed episperm 12
Walnut shell 18
Betelnut tree wood flour 60
Palm wood flour 50
Compound enzymic preparation 0.012;
Compound enzymic preparation is made up of aldehyde dehydrogenase, catalase, nitroreductase, polyphenol oxidase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalatic enzyme alive 18.3 × 105U/g ;The enzyme of nitroreductase alive 8.9 × 105U/g, the enzyme work of polyphenol oxidase are 11.3 × 105U/g;Aldehyde dehydrogenase, catalase, nitroreductase, the ratio of weight and number of polyphenol oxidase are 2:5:2:3;
Complex micro organism fungicide 0.036 part;
The active component of complex micro organism fungicide is made up of alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is about 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is about 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is about 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized.
7. the soil-repairing agent of organochlorine pesticide pollution as claimed in claim 1, it is characterised in that include the component of following portions by weight:
Chitosan 2
Bentonite 160
Chlorella 20
Citric acid 1.5
Conch meal 6
Flammulina velutiper (Fr.) Sing mushroom bran 10
Corn cob 60
Testa oryzae 15
Tea seed episperm 10
Walnut shell 15
Betelnut tree wood flour 60
Palm wood flour 45;
Chlorella is to shine the algae powder after dry doubling is pulverized, and its water content is 3%;
Corn cob is to shine the particulate matter after dry doubling is pulverized, and its water content is 4%;
Walnut shell is also for shining the powder after dry doubling is pulverized, and its water content is 3%;
Betelnut tree wood flour, palm wood flour be dry be 4% to moisture after and the bits shape thing pulverized;
Add complex micro organism fungicide 0.036 part, mix homogeneously;
The active component of complex micro organism fungicide is made up of alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, Ku Shi bar mycopowder;
Alternate mucormycosis mycopowder, bacillus megaterium mycopowder, Pseudomonas geniculate mycopowder, bacillus subtilis mycopowder, sulfate reducting bacteria mycopowder, the weight ratio of Ku Shi bar mycopowder be: 3:3:4:3:3:4;
The living bacteria count of alternate mucormycosis mycopowder is 8 × 109cfu/g;
The living bacteria count of bacillus megaterium mycopowder is 6 × 1011cfu/g;
The living bacteria count of Pseudomonas geniculate mycopowder is 7 × 109cfu/g;
The living bacteria count of bacillus subtilis mycopowder is 5 × 1010cfu/g;
The living bacteria count of sulfate reducting bacteria mycopowder is 5 × 1011cfu/g;
The living bacteria count of Ku Shi bar mycopowder is 6 × 109cfu/g;
Compound enzymic preparation 0.008;
Compound enzymic preparation includes aldehyde dehydrogenase, catalase, nitroreductase;
The enzyme of aldehyde dehydrogenase alive 5.4 × 105U/g;Catalase 18.3 × 105U/g ;Nitroreductase 8.9 × 105U/g;Aldehyde dehydrogenase, catalase, the ratio of weight and number of nitroreductase are 2:4:3.
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Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106583443A (en) * | 2016-12-28 | 2017-04-26 | 青岛理工大学 | Method capable of synchronously treating biogas residues and pesticide polluted soil |
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CN109821892A (en) * | 2019-03-25 | 2019-05-31 | 中国环境科学研究院 | In-situ immobilization organic polluted soil biomaterial, preparation method and application |
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CN117244935A (en) * | 2023-11-20 | 2023-12-19 | 秦皇岛金袋科技有限公司 | Method for degrading residual pesticide in soil |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104232095A (en) * | 2014-08-25 | 2014-12-24 | 青岛瀚普生物科技有限公司 | Biological type nematode-preventing soil conditioner and preparation method thereof |
CN104694428A (en) * | 2015-02-12 | 2015-06-10 | 何颖霞 | Microbial preparation for removing nitrotoluene in soil |
CN105237249A (en) * | 2015-11-24 | 2016-01-13 | 济南昊泽环保科技有限公司 | Compound fertilizer for promoting increasing of production and income of maize |
CN105347884A (en) * | 2015-11-20 | 2016-02-24 | 河北慈心环保科技有限公司 | Biological organic repairing agent for soil pollution and application and preparation method thereof |
CN105524889A (en) * | 2016-02-03 | 2016-04-27 | 常州市鼎日环保科技有限公司 | Preparation method of enzyme preparation for polycyclic aromatic hydrocarbon contaminated soil remediation |
-
2016
- 2016-06-17 CN CN201610442960.2A patent/CN106010565A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104232095A (en) * | 2014-08-25 | 2014-12-24 | 青岛瀚普生物科技有限公司 | Biological type nematode-preventing soil conditioner and preparation method thereof |
CN104694428A (en) * | 2015-02-12 | 2015-06-10 | 何颖霞 | Microbial preparation for removing nitrotoluene in soil |
CN105347884A (en) * | 2015-11-20 | 2016-02-24 | 河北慈心环保科技有限公司 | Biological organic repairing agent for soil pollution and application and preparation method thereof |
CN105237249A (en) * | 2015-11-24 | 2016-01-13 | 济南昊泽环保科技有限公司 | Compound fertilizer for promoting increasing of production and income of maize |
CN105524889A (en) * | 2016-02-03 | 2016-04-27 | 常州市鼎日环保科技有限公司 | Preparation method of enzyme preparation for polycyclic aromatic hydrocarbon contaminated soil remediation |
Non-Patent Citations (2)
Title |
---|
张甲耀: "《环境微生物学》", 31 December 2008, 武汉大学出版社 * |
王友保: "《土壤污染与生态修复实验指导》", 30 June 2015, 安徽师范大学出版社 * |
Cited By (9)
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CN106583443A (en) * | 2016-12-28 | 2017-04-26 | 青岛理工大学 | Method capable of synchronously treating biogas residues and pesticide polluted soil |
CN108410773A (en) * | 2018-04-12 | 2018-08-17 | 孙雪华 | A kind of composite bacteria agent and its application in repairing organochlorine pesticide pollution water body |
CN108795443A (en) * | 2018-08-23 | 2018-11-13 | 广州市环境保护工程设计院有限公司 | A kind of microbe soil restoration agent and preparation method thereof |
CN109821892A (en) * | 2019-03-25 | 2019-05-31 | 中国环境科学研究院 | In-situ immobilization organic polluted soil biomaterial, preparation method and application |
CN110218652A (en) * | 2019-05-27 | 2019-09-10 | 昆明理工大学 | A method of promoting micro algae growth and oil and fat accumulation in BG-11 culture medium |
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