CN107879575A - A kind of pollutants in sediments locking means - Google Patents

A kind of pollutants in sediments locking means Download PDF

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Publication number
CN107879575A
CN107879575A CN201711331149.8A CN201711331149A CN107879575A CN 107879575 A CN107879575 A CN 107879575A CN 201711331149 A CN201711331149 A CN 201711331149A CN 107879575 A CN107879575 A CN 107879575A
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China
Prior art keywords
agent
conduit
bed mud
locking means
river
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Inventor
饶耀明
傅涛
古卫民
张紫薇
陈韶聪
季春明
何木帝
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Zhuhai Qingchuan Environmental Protection Technology Co Ltd
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Zhuhai Qingchuan Environmental Protection Technology Co Ltd
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Priority to CN201711331149.8A priority Critical patent/CN107879575A/en
Publication of CN107879575A publication Critical patent/CN107879575A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/101Sulfur compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/22O2
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/06Nutrients for stimulating the growth of microorganisms

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Molecular Biology (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a kind of pollutants in sediments locking means, specific locking means step is as follows:Step 1:The selection of material:By science and technology in the isolated beneficial bacterium renovation agent of nature;Artificial or mechanical method mixes composition oxygenation agent and bio-stimulant according to a certain percentage;The conduit of certain length;Step 2 is performed again.The dispensing that the present invention passes through beneficial bacterium renovation agent; can be according to beneficial bacterium renovation agent during breeding; pass through the microcirculation in small biological cycle and organism; consume in bed mud needed for raised growth by groups of contaminants into C, H, O, N, P and S system; the pollutants such as COD, ammonia nitrogen, sulfide in elimination bed mud; it is purified bed mud; not only implement convenient; save substantial amounts of human and material resources and financial resources; and protective effect has been reached to the ecosystem, improve the stability and security of the ecosystem.

Description

A kind of pollutants in sediments locking means
Technical field
The present invention relates to Dealing with Water-Area Pollution technical field, more particularly to a kind of pollutants in sediments locking means.
Background technology
Inland river water source seriously pollutes in most cities, and river nigrescence is smelly, and river surface drift has by being turned on the mud scum of river bed Thing, such has had a strong impact on the normal life of the river course nearby residents, and the masses have strong complaints, and are monitored through environmental monitoring station, water Matter is bad V classes, and aquatic animal, plantses are substantially without depositing, it has also become a great problem of urban ecological environment.Especially for water Pollutant in the bed mud of bottom depths, in existing technical field, it is substantially to take and exhausts water, then mud is carried out clear Reason, the time so spent, manpower and financial resources are huge, are not easy to implement.Therefore, a kind of pollutants in sediments locking means are invented Solve the above problems necessary.
The content of the invention
It is an object of the invention to provide a kind of pollutants in sediments locking means, to solve what is proposed in above-mentioned background technology Problem.
To achieve the above object, the present invention provides following technical scheme:A kind of pollutants in sediments locking means, specific locking Method and step is as follows:
Step 1:The selection of material:By science and technology in the isolated beneficial bacterium renovation agent of nature;Artificial or machine The method of tool mixes composition oxygenation agent and bio-stimulant according to a certain percentage;The conduit of certain length;Step 2 is performed again;
Step 2:Oxygenation agent is launched:After step 1 execution, a certain amount of oxygenation agent, Huo Zhetong are put into river Cross conduit and oxygenation agent is inputted into bed mud;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, put into river a certain amount of micro- Biological growth promoter, or bio-stimulant is inputted into bed mud by conduit;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, being put into river a certain amount of has Beneficial bacteria renovation agent is launched, or inputs the dispensing of beneficial bacterium renovation agent into bed mud by conduit;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Preferably, beneficial bacterium renovation agent is by the beneficial of aspergillus albicans, Eurotium, red bulk bacteria and yellow mould in step 1 Fungi flora and bacillus subtilis, actinomyces, the bacteria flora except thiobacillus denitrificans and nitrification bacteria mix;Oxygenation Agent is by BYM ferment fertilizers, azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and increasing Effect agent mixes according to a certain percentage;Bio-stimulant is made up of protease;Pipe inner wall is totally smooth.
Preferably, every square metre of bed mud oxygenation agent injected volume is 500g-900g in step 2.
Preferably, some time is arranged to 2h-5h in step 3, and every square metre of bottom mud microbe growth-promoting agent injected volume is 400g-800g。
Preferably, some time is arranged to 2h-5h in step 4, and every square metre of bed mud beneficial bacterium renovation agent injected volume is 300g-700g。
Preferably, Step 2: it is 0cm, 5cm and 10cm that conduit, which stretches into bed mud depth, in step 3 and step 4.
The technique effect and advantage of the present invention:
1st, by by aspergillus albicans, Eurotium, red bulk bacteria and the beneficial fungi flora of yellow mould and bacillus subtilis, The dispensing for the beneficial bacterium renovation agent that actinomyces, the bacteria flora except thiobacillus denitrificans and nitrification bacteria mix, Ke Yigen According to beneficial bacterium renovation agent during breeding, due to possessed small volume, specific surface area is big, absorbs more, conversion block, growth Prosperous, breeding is fast, strong adaptability, the characteristics of easily variation, by the microcirculation in small biological cycle and organism, consumes big in bed mud Needed for amount growth by groups of contaminants into C, H, O, N, P and S system, eliminate COD in bed mud, ammonia nitrogen, the pollution such as sulfide Thing, it is purified bed mud;
2nd, by the dispensing of oxygenation agent, increase the content of dissolved oxygen in bed mud, promote the growth of beneficial bacterium renovation agent and metabolism, Reach fast decoupled organic matter, beneficial bacterium renovation agent is played maximum effect;
3rd, the dispensing of bio-stimulant is passed through, it would be beneficial to various nutrition are provided required for the growth of bacterium renovation agent with efficiently carrying Body combines, and allows beneficial bacterium renovation agent quickly to absorb in sediment pollution substance environment, so as to improve the degraded energy to pollutant The impact resistance of power and system;
4th, by way of probioticses are launched and pollutant is purified, not only implement convenient, save a large amount of Human and material resources and financial resources, and protective effect has been reached to the ecosystem, has improved the stability and safety of the ecosystem Property.
Brief description of the drawings
Fig. 1 is the step schematic diagram of the present invention.
Embodiment
Below in conjunction with the accompanying drawing in the embodiment of the present invention, the technical scheme in the embodiment of the present invention is carried out clear, complete Site preparation describes, it is clear that described embodiment is only part of the embodiment of the present invention, rather than whole embodiments.It is based on Embodiment in the present invention, those of ordinary skill in the art are obtained every other under the premise of creative work is not made Embodiment, belong to the scope of protection of the invention.
Embodiment 1:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, 500g oxygenation is put into the river of every square metre of bed mud Agent;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, into the river of every square metre of bed mud Put into 700g bio-stimulants;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, into the river of every square metre of bed mud 300g beneficial bacteriums renovation agent is put into launch;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 2:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, 500g oxygenation is put into the river of every square metre of bed mud Agent;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, into the river of every square metre of bed mud Put into 700g bio-stimulants;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, into the river of every square metre of bed mud 500g beneficial bacteriums renovation agent is put into launch;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 3:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, 500g oxygenation is put into the river of every square metre of bed mud Agent;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, into the river of every square metre of bed mud Put into 700g bio-stimulants;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, into the river of every square metre of bed mud 700g beneficial bacteriums renovation agent is put into launch;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 4:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud surface, 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 700g microorganism growth-promotings are then put into the river of every square metre of bed mud by conduit Agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 300g beneficial bacterium reparations are then put into the river of every square metre of bed mud by conduit Agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 5:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud surface, 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 700g microorganism growth-promotings are then put into the river of every square metre of bed mud by conduit Agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 500g beneficial bacterium reparations are then put into the river of every square metre of bed mud by conduit Agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 6:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud surface, 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 700g microorganism growth-promotings are then put into the river of every square metre of bed mud by conduit Agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud surface, and 700g beneficial bacterium reparations are then put into the river of every square metre of bed mud by conduit Agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 7:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 5cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 300g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 8:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 5cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 500g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 9:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 5cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 5cm and gone out, and 700g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 10:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 10cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 300g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 11:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 10cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 500g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
Embodiment 12:A kind of pollutants in sediments locking means, specific locking means step are as follows:
Step 1:The selection of material:By science and technology nature it is isolated by aspergillus albicans, Eurotium, it is red dissipate It is capsule bacterium and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, thin except thiobacillus denitrificans and nitrification bacteria Bacterium flora mixes beneficial bacteria renovation agent;Artificial or mechanical method be mixed to get according to a certain percentage by BYM ferment fertilizers, Azophoska, DFM additives, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist mix according to a certain percentage Close into oxygenation agent and bio-stimulant is formed by protease;The clean smooth conduit of the inwall of certain length;Step is performed again Two;
Step 2:Oxygenation agent is launched:After step 1 execution, conduit is stretched into river bottom, i.e. conduit bottom is placed In bed mud bottom, 10cm goes out, and 500g oxygenation agents are then put into the river of every square metre of bed mud by conduit;Step is performed again Three;
Step 3:Bio-stimulant is launched:After step 2 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 700g microorganisms are then put into the river of every square metre of bed mud by conduit Growth-promoting agent;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, conduit is stretched into river bottom, i.e., Conduit bottom is positioned over bed mud bottom 10cm and gone out, and 700g beneficial bacteriums are then put into the river of every square metre of bed mud by conduit Renovation agent;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then to inspection Result is surveyed to make comments.
It is can be seen that by embodiment 1-12 when conduit stretches into bed mud bottom 5cm, then by conduit to every square metre When the river input 500g oxygenation agents of bed mud, 700g microorganisms launch agent and 500g beneficial bacterium renovation agents, pollutants in sediments is controlled It is best to manage effect.
Finally it should be noted that:The preferred embodiments of the present invention are the foregoing is only, are not intended to limit the invention, Although the present invention is described in detail with reference to the foregoing embodiments, for those skilled in the art, it still may be used To be modified to the technical scheme described in foregoing embodiments, or equivalent substitution is carried out to which part technical characteristic, Within the spirit and principles of the invention, any modification, equivalent substitution and improvements made etc., it should be included in the present invention's Within protection domain.

Claims (6)

1. a kind of pollutants in sediments locking means, it is characterised in that specific locking means step is as follows:
Step 1:The selection of material:By science and technology in the isolated beneficial bacterium renovation agent of nature;It is artificial or mechanical Method mixes composition oxygenation agent and bio-stimulant according to a certain percentage;The conduit of certain length;Step 2 is performed again;
Step 2:Oxygenation agent is launched:After step 1 execution, a certain amount of oxygenation agent is put into river, or by leading Pipe inputs oxygenation agent into bed mud;Step 3 is performed again;
Step 3:Bio-stimulant is launched:After step 2 performs some time, a certain amount of microorganism is put into river Growth-promoting agent, or bio-stimulant is inputted into bed mud by conduit;Step 4 is performed again;
Step 4:Beneficial bacterium renovation agent is launched:After step 3 performs some time, a certain amount of beneficial bacterium is put into river Renovation agent is launched, or inputs the dispensing of beneficial bacterium renovation agent into bed mud by conduit;Step 5 is performed again;
Step 5:Pollutant monitoring:After step 4 performs one day, choose bed mud and carry out pollutant monitoring, then detection is tied Fruit is made comments.
A kind of 2. pollutants in sediments locking means according to claim 1, it is characterised in that:Beneficial bacterium reparation in step 1 Agent is by aspergillus albicans, Eurotium, red bulk bacteria and the beneficial fungi flora of yellow mould and bacillus subtilis, actinomyces, removed The bacteria flora of thiobacillus denitrificans and nitrification bacteria mixes;Oxygenation agent is added by BYM ferment fertilizers, azophoska, DFM Agent, trace element, SODIUM PERCARBONATE, sustained release cosolvent, stabilizer and synergist is added to mix according to a certain percentage;Microorganism promotees Raw agent is made up of protease;Pipe inner wall is totally smooth.
A kind of 3. pollutants in sediments locking means according to claim 1, it is characterised in that:Every square metre of bottom in step 2 Mud oxygenation agent injected volume is 500g.
A kind of 4. pollutants in sediments locking means according to claim 1, it is characterised in that:Every square metre of bottom in step 3 Mud bio-stimulant injected volume is 700g.
A kind of 5. pollutants in sediments locking means according to claim 1, it is characterised in that:Every square metre of bottom in step 4 Mud beneficial bacterium renovation agent injected volume is 300g-700g.
A kind of 6. pollutants in sediments locking means according to claim 1, it is characterised in that:Step 2: step 3 and step It is 0cm, 5cm and 10cm that conduit, which stretches into bed mud depth, in rapid four.
CN201711331149.8A 2017-12-13 2017-12-13 A kind of pollutants in sediments locking means Pending CN107879575A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112321103A (en) * 2020-11-03 2021-02-05 中电建生态环境集团有限公司 Bottom mud pollutant locking method
CN115259587A (en) * 2022-06-20 2022-11-01 生态环境部南京环境科学研究所 In-situ remediation method for organic pollution of black and odorous bottom mud

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101607762B (en) * 2009-07-09 2011-06-15 东莞圣源环保科技有限公司 Ecological restoring method of river water body
CN103011541A (en) * 2012-12-19 2013-04-03 天津生态城环保有限公司 Bacteria-fungi combined processing method for bottom sediment contaminated by organochlorine pesticides
CN104445847A (en) * 2014-11-28 2015-03-25 浙江绿凯环保科技股份有限公司 Bottom sediment repairing agent and bottom sediment locking method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101607762B (en) * 2009-07-09 2011-06-15 东莞圣源环保科技有限公司 Ecological restoring method of river water body
CN103011541A (en) * 2012-12-19 2013-04-03 天津生态城环保有限公司 Bacteria-fungi combined processing method for bottom sediment contaminated by organochlorine pesticides
CN104445847A (en) * 2014-11-28 2015-03-25 浙江绿凯环保科技股份有限公司 Bottom sediment repairing agent and bottom sediment locking method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112321103A (en) * 2020-11-03 2021-02-05 中电建生态环境集团有限公司 Bottom mud pollutant locking method
CN115259587A (en) * 2022-06-20 2022-11-01 生态环境部南京环境科学研究所 In-situ remediation method for organic pollution of black and odorous bottom mud

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