CN104445813A - Preparation for removing heavy metal ion and industrial COD in sewage - Google Patents

Preparation for removing heavy metal ion and industrial COD in sewage Download PDF

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Publication number
CN104445813A
CN104445813A CN201410644913.7A CN201410644913A CN104445813A CN 104445813 A CN104445813 A CN 104445813A CN 201410644913 A CN201410644913 A CN 201410644913A CN 104445813 A CN104445813 A CN 104445813A
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China
Prior art keywords
heavy metal
sewage
preparation
pseudomonas aeruginosa
bacillus
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CN201410644913.7A
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Chinese (zh)
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CN104445813B (en
Inventor
张连瑞
王东阳
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Guangdong Ruijie Environmental Protection Engineering Co Ltd
Original Assignee
JUNAN POWER SUPPLY CO Ltd
State Grid Corp of China SGCC
Linyi Power Supply Co of State Grid Shandong Electric Power Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F2001/007Processes including a sedimentation step
    • 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
    • C02F2101/20Heavy metals or heavy metal 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
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • 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
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/348Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed

Abstract

The invention belongs to the field of sewage treatment, and discloses a preparation for removing a heavy metal ion and industrial COD in sewage. The preparation comprises a heavy metal complexing agent and a biological microbial inoculum, wherein the heavy metal complexing agent and the biological microbial inoculum are independently used. The preparation disclosed by the invention is low in cost, easily available and capable of effectively removing the heavy metal and the industrial COD.

Description

A kind of preparation removing heavy metal ions in sewage and industrial COD
Technical field
The invention belongs to sewage treatment area, relate to a kind of preparation removing heavy metal ions in sewage and industrial COD.
 
Background technology
Due to heavy metal ion not biodegradable, the bioconcentration in plating or battery sewage, as the key industry of heavy metal contamination, one of contaminated industry that the Yi Shi world today is the most serious, the governing problem of the heavy metal containing sewage produced has become the focus of field of Environment Protection concern.
The method of current process plating or battery sewage mainly contains Physical, chemical method, physico-chemical processes, biological process etc.Wherein Physical refers to and utilizes physical action to be separated the main pollution substance in suspended state in sewage, as the oil removing in sewage, evaporation concentration reuse water etc.But in the technique of disposing of sewage, physical method, just as the link of in other treatment processs, is seldom used alone.Chemical process mainly comprises chemical oxidization method, chemical reduction method, chemical precipitation method, hydroxide precipitation method, the chromic salt precipitator method, the ferrite precipitator method, chemical neutralization method etc.Physico-chemical process mainly comprises By Bubble-floating Method, ion exchange method, extraction process, active carbon adsorption, electrolytic process etc., and first three methods also exists that floor space is large, running expense is high, have secondary pollution problem.
 
Summary of the invention
In order to overcome the deficiencies in the prior art, the invention provides a kind of preparation removing heavy metal ions in sewage and industrial COD.Invention formulation comprises heavy metal complexing agent and bacteria agent, and use said preparation can greatly reduce the content of heavy metal and industrial COD, treatment process is simple, decreases floor space, reduces investment outlay.
The present invention adopts following technical scheme to realize:
Remove a preparation of heavy metal ions in sewage and industrial COD, said preparation comprises heavy metal complexing agent and bacteria agent, and described heavy metal complexing agent and bacteria agent separately use;
Described complexing agent is prepared as follows and forms: get sodium alginate, aluminum oxide, potassium humate, ferrous sulfate according to the mass ratio of 1:1:2:4, mix together;
Described bacteria agent is prepared as follows and forms:
Thiobacillus denitrificans, pseudomonas aeruginosa, bacillus cereus or bacillus megaterium being trained respectively concentration is 1 × 10 8the bacterium liquid of individual/ml, mixes according to the volume ratio of 1:2:2:1, then with sawdust according to the quality of 1:2 than mixing and stirring, finally carry out cryodrying, drying temperature is 20-30 DEG C, and after dry, water content is 20%; Obtain;
Preferably,
Described thiobacillus denitrificans is thiobacillus denitrificans (Thiobacillus denitrificans) ATCC 25259;
Described pseudomonas aeruginosa is pseudomonas aeruginosa (Pseudomonas aeruginosa) ATCC 15442;
Described bacillus cereus is bacillus cereus (Bacillus cereus) ATCC 10876;
Described bacillus megaterium is bacillus megaterium (Bacillus megatherium) CGMCC No:1487;
Utilize above-mentioned preparation to remove the technique of heavy metal ions in sewage and industrial COD, it comprises the steps:
1) removing impurity by means of precipitation: sewage passes through grid, remove bulk solid matters, then sewage is drained into settling tank, leave standstill 24-48 hour, wherein, the bottom filling of settling tank is the river sand of 100cm thickness, and the particle diameter of river sand is 1-2mm, to metal fragment and colloid floss etc., tentatively can adsorb and precipitate;
2) complexing: sewage is drained in complexing pond, according to 1kg complexing agent: the ratio of 1 ton of sewage adds complexing agent, subsequently with 200-300 turn/speed of min stirs 30-60min, then leaves standstill 6-8 hour; Wherein, complexing agent is prepared as follows and forms: get sodium alginate, aluminum oxide, potassium humate, ferrous sulfate according to the mass ratio of 1:2:3:3, mix together;
3) bio-oxidation: the sewage behind complexing pond is drained into bio-oxidation pond, first the pH of sewage is regulated to be 7-8, then add bacteria agent 10 grams by every cubic metre of liquid at every turn, add 1 every day, add two days later continuously, leave standstill five days again, liquid is filtered by plate filter, finally discharges; Wherein, bacteria agent is prepared as follows and forms:
Thiobacillus denitrificans, pseudomonas aeruginosa, bacillus cereus or bacillus megaterium being trained respectively concentration is 1 × 10 8the bacterium liquid of individual/ml, mixes according to the volume ratio of 1:2:2:2, then with sawdust according to the quality of 1:2 than mixing and stirring, finally carry out cryodrying, drying temperature is 20-30 DEG C, and after dry, water content is 20%; Obtain.
Bacterial classification of the present invention belongs to conventional bacterial strain, all can buy from commercial sources such as Chinese General Microbiological Culture preservation administrative center (CGMCC) or American Type Culture collection warehousings (ATCC) and obtain.The enlarged culturing of each bacterial classification of the present invention is the cellar culture mode of this area, is not innovative point of the present invention, does not describe in detail herein.
The beneficial effect that the present invention obtains mainly comprises:
Invention formulation comprises complexing agent and bacteria agent, with low cost, be easy to get, can removal heavy metal and industrial COD effectively, and easily prepares; Reasonable compatibility between each bacterial classification in bacteria agent of the present invention, symbiosis is coordinated, mutually not antagonism, can effectively reduce industrial COD; Complex compound of the present invention is composite by raw material, plays synergy, has broad spectrum, can effectively remove the heavy metals such as nickel, chromium, copper, zinc; Treatment process of the present invention is simple, decreases floor space, reduces investment outlay, and is easy to operational management.
 
Embodiment
By adopting the mode of specific embodiment, the present invention is further elaborated below, but it should not be construed the restriction to core initiative spirit of the present invention.
Embodiment 1
Remove a preparation of heavy metal ions in sewage and industrial COD, said preparation comprises heavy metal complexing agent and bacteria agent, and wherein, heavy metal complexing agent and bacteria agent separately use;
Complexing agent is prepared as follows and forms: get sodium alginate, aluminum oxide, potassium humate, ferrous sulfate according to the mass ratio of 1:2:3:3, mix together;
Bacteria agent is prepared as follows and forms:
Thiobacillus denitrificans, pseudomonas aeruginosa, bacillus cereus or bacillus megaterium being trained respectively concentration is 1 × 10 8the bacterium liquid of individual/ml, mixes according to the volume ratio of 1:2:2:2, then with sawdust according to the quality of 1:2 than mixing and stirring, finally carry out cryodrying, drying temperature is 20 DEG C, and after dry, water content is 20%; Obtain;
Described thiobacillus denitrificans is thiobacillus denitrificans (Thiobacillus denitrificans) ATCC 25259(such as reference APPLIED AND ENVIRONMENTAL MICROBIOLOGY, May 2007, p. 3265 – 3271);
Described pseudomonas aeruginosa ( pseudomonas aeruginosa) for pseudomonas aeruginosa ATCC 15442(is see document Adaptation of Pseudomonas aeruginosa ATCC 15442 to didecyldimethylammonium bromide induces changes in membrane fatty acid composition and in resistance of cells, Journal of Applied Microbiology, 2001);
Described bacillus cereus (Bacillus cereus) for ATCC 10876(such as new J. Chem., 2007, 31, 748-755);
Described bacillus megaterium is bacillus megaterium (Bacillus megatherium) CGMCC No:1487 (CN101074421A).
Embodiment 2
Utilize the preparation of embodiment 1 to remove the technique of heavy metal ions in sewage and industrial COD, it comprises the steps:
1) removing impurity by means of precipitation: sewage, by grid, is removed bulk solid matters, then sewage is drained into settling tank, leave standstill 24 hours, wherein, the bottom filling of settling tank is the river sand of 100cm thickness, the particle diameter of river sand is 1mm, to metal fragment and colloid floss etc., tentatively can adsorb and precipitate;
2) complexing: sewage is drained in complexing pond, according to 1kg complexing agent: the ratio of 1 ton of sewage adds complexing agent, stirs 30min subsequently with the speed of 200 turns/min, then leaves standstill 6 hours;
3) bio-oxidation: the sewage behind complexing pond is drained into bio-oxidation pond, first the pH of sewage is regulated to be 7, then add bacteria agent 10 grams by every cubic metre of liquid at every turn, add 1 every day, add two days later continuously, leave standstill five days again, liquid is filtered by plate filter, finally discharges.The every leading indicator of sewage before treatment is (mg/L): COD 1895, Ni 2+106, Cr 6+24, Cu 2+53, after process, every leading indicator is: COD 32, Ni 2+0.53, Cr 6+0.20, Cu 2+25.
Although above done detailed explanation with general explanation and embodiment to this case, on basis of the present invention, can make some modifications or improvements it, this will be apparent to those skilled in the art.Therefore, amendment done without departing from theon the basis of the spirit of the present invention or improvement, all belong to the scope of protection of present invention.

Claims (3)

1. remove a preparation of heavy metal ions in sewage and industrial COD, it is characterized in that, described preparation comprises heavy metal complexing agent and bacteria agent, and described heavy metal complexing agent and bacteria agent separately use;
Described heavy metal complexing agent is prepared as follows and forms: get sodium alginate, aluminum oxide, potassium humate, ferrous sulfate according to the mass ratio of 1:2:3:3, mix together;
Described bacteria agent is prepared as follows and forms:
Thiobacillus denitrificans, pseudomonas aeruginosa, bacillus cereus or bacillus megaterium being trained respectively concentration is 1 × 10 8the bacterium liquid of individual/ml, mixes according to the volume ratio of 1:2:2:2, then with sawdust according to the quality of 1:2 than mixing and stirring, finally carry out cryodrying, drying temperature is 20-30 DEG C, and after dry, water content is 20%; Obtain.
2. preparation according to claim 1, is characterized in that,
Described thiobacillus denitrificans is thiobacillus denitrificans (Thiobacillus denitrificans) ATCC 25259;
Described pseudomonas aeruginosa is pseudomonas aeruginosa (Pseudomonas aeruginosa) ATCC 15442;
Described bacillus cereus is bacillus cereus (Bacillus cereus) ATCC 10876;
Described bacillus megaterium is bacillus megaterium (Bacillus megatherium) CGMCC No:1487.
3. the technique utilizing the preparation described in claim 1 or 2 to remove heavy metal ions in sewage and industrial COD.
CN201410644913.7A 2014-11-14 2014-11-14 A kind of preparation removing heavy metal ions in sewage and industrial COD Active CN104445813B (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107099483A (en) * 2017-06-26 2017-08-29 金文忠 A kind of composite biological agent and its application in processing mercury-containing waste water
CN107540101A (en) * 2017-10-26 2018-01-05 广东睿洁环保工程有限公司 A kind of purifying agent for polluted water and its application
CN116477772A (en) * 2023-05-11 2023-07-25 盐城工学院 Method for removing chromium and desulfurizing bacillus cereus in water and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998013308A1 (en) * 1996-09-24 1998-04-02 Tecnologias Zero-Red, S.L. Process for the treatment and decontamination of acid waters which contain dissolved metals and their conversion into fertilizers (pidra process)
CN101054250A (en) * 2006-04-13 2007-10-17 广州吉源生物环保科技有限公司 Technique for treating garbage percolate by combinated physicochemistry and organism bacterium
WO2012112136A1 (en) * 2011-02-14 2012-08-23 Empire Technology Development Llc Organism metabolites for removal of pollutants from brine
CN102964014A (en) * 2012-11-15 2013-03-13 新疆德安环保科技有限公司 Treatment method of acid heavy metal wastewater

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1998013308A1 (en) * 1996-09-24 1998-04-02 Tecnologias Zero-Red, S.L. Process for the treatment and decontamination of acid waters which contain dissolved metals and their conversion into fertilizers (pidra process)
CN101054250A (en) * 2006-04-13 2007-10-17 广州吉源生物环保科技有限公司 Technique for treating garbage percolate by combinated physicochemistry and organism bacterium
WO2012112136A1 (en) * 2011-02-14 2012-08-23 Empire Technology Development Llc Organism metabolites for removal of pollutants from brine
CN102964014A (en) * 2012-11-15 2013-03-13 新疆德安环保科技有限公司 Treatment method of acid heavy metal wastewater

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107099483A (en) * 2017-06-26 2017-08-29 金文忠 A kind of composite biological agent and its application in processing mercury-containing waste water
CN107099483B (en) * 2017-06-26 2020-09-18 杭州富阳佳畅机械有限公司 Composite biological agent and application thereof in treatment of mercury-containing wastewater
CN107540101A (en) * 2017-10-26 2018-01-05 广东睿洁环保工程有限公司 A kind of purifying agent for polluted water and its application
CN116477772A (en) * 2023-05-11 2023-07-25 盐城工学院 Method for removing chromium and desulfurizing bacillus cereus in water and application thereof
CN116477772B (en) * 2023-05-11 2023-11-14 盐城工学院 Method for removing chromium and desulfurizing bacillus cereus in water and application thereof

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GR01 Patent grant
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Inventor after: Luo Fusheng

Inventor after: Pan Shengqiang

Inventor after: Peng Zhongxin

Inventor after: Hu Chaohan

Inventor before: Zhang Lianrui

Inventor before: Wang Dongyang

CB03 Change of inventor or designer information
TR01 Transfer of patent right

Effective date of registration: 20170511

Address after: Medina Road 516000 Guangdong city of Huizhou province. Huicheng District Sheng Ping Yuan tower B201

Patentee after: GUANGDONG RUIJIE ENVIRONMENTAL PROTECTION ENGINEERING CO., LTD.

Address before: 100761 West Chang'an Avenue, Beijing, No. 86, No.

Co-patentee before: Linyi Electric Power Company of Guo Wang Shandong Province Utilities Electric Co.

Patentee before: State Grid Corporation of China

Co-patentee before: Junan Power Supply Co.,Ltd.

TR01 Transfer of patent right