CN101591068B - Method for treating polluted river - Google Patents
Method for treating polluted river Download PDFInfo
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- CN101591068B CN101591068B CN2009100396563A CN200910039656A CN101591068B CN 101591068 B CN101591068 B CN 101591068B CN 2009100396563 A CN2009100396563 A CN 2009100396563A CN 200910039656 A CN200910039656 A CN 200910039656A CN 101591068 B CN101591068 B CN 101591068B
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- river
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- composite fungus
- polluted river
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention provides a method for treating a polluted river, which comprises the following steps: (1) detecting the pollution indexes of the river; (2) regulating the types and quantities of microbial agents; (3) putting a resulting composite microbial agent in a water body in an amount of 50 to 100 ppm; (4) allowing the composite microbial agent to transfer, covert and degrade pollutants in the water in the river; (5) detecting the pollution indexes of the river; and (51) repeating the steps from (2) to (5) till the river meets requirements. The microbial agents comprise photosynthetic bacteria, bacillus subtilis, nitrobacteria, lactic acid bacteria and yeasts. The method for treating the polluted river of the invention reduces and inorganizes pollutants in water in the river to treat the river and has the advantages of simple operation and low cost.
Description
Technical field
The present invention relates to the Ecological Disposal technical field, be specifically related to a kind of treatment process of polluted river.
Background technology
The contaminated appearance features in river---black smelly, mainly be that a large number of nutrients enrichment in water body of extraneous input causes, a large amount of pollutant sediments forms mud; Pollutent in the water body has consumed the dissolved oxygen of water body; The biological beginning of a large amount of aerobic water bodys is dead, and the anaerobion population is then very active, causes producing foul smell and many ferrous metal sulfide such as hydrogen sulfide; Make that original ecosystem is destroyed in the river course; And run down, final river loses self-purification capacity, progressively becomes black smelly.The influence factor of black smelly river improvement is numerous, and difficulty of governance is big, has become a great problem of puzzlement urban ecological environment.
Main at present employing cuts means integrated uses such as a dirt, desilting, pure oxygen aeration, artificial swamp, river water cleaning.Wherein:
1, cut dirt and be used for controlling the external source pollution, this generally adopts;
2, desilting is used for controlling sediment pollution, but cost is high, form secondary pollution;
3, pure oxygen aeration is mainly used in reduction sulfide, cuts down COD (COD), can appropriateness improve water quality, but cost is high, consume mass energy;
4, the artificial swamp floor space is big, cost is high;
5, river water cleaning is river to be dammed get into purifying treatment factory, enters the river course again after reducing its contamination index, and the very big input of needs comprises the many energy that consume in a large amount of found the factory land used and the treating processes like this.
Therefore, the treatment process that needs a kind of polluted river of invention is to address the above problem.
Summary of the invention
The treatment process that the purpose of this invention is to provide a kind of polluted river reduces and inorganicization the river water pollutent, reaches the effect that the river is handled, and has advantage simple to operate, with low cost.
For realizing above-mentioned purpose, adopt following technical scheme:
A kind of treatment process of polluted river comprises the steps:
(1) contamination index in detection river,
(2) allotment microbial inoculum kind and quantity,
(3) composite fungus agent that obtains is rendered in the water body by 50～100ppm,
(4) pollutent in composite fungus agent transfer, conversion and the degraded river,
(5) contamination index in detection river;
(51) repeating step (2)～(5) meet the requirements up to the river;
Described microbial inoculum comprises photosynthetic bacterium, subtilis, nitrobacteria, milk-acid bacteria and yeast.
As the preferred implementation of the treatment process of polluted river of the present invention, the treatment process of described polluted river comprises the steps: that also (6) throw in hydrocoles and/or plantation plant to the river.
As the preferred implementation of the treatment process of polluted river of the present invention, the parts by weight of described composite fungus agent are: photosynthetic bacterium 10～40, subtilis 10～40, nitrobacteria 10～30, milk-acid bacteria 5～15, yeast 5～15.
As the best preferred implementation of the treatment process of polluted river of the present invention, the parts by weight of described composite fungus agent are: photosynthetic bacterium 30, subtilis 30, nitrobacteria 20, milk-acid bacteria 10, yeast 10.
As the preferred implementation of the treatment process of polluted river of the present invention, described composite fungus agent also comprises aspergillus tubigensis.
More preferably embodiment as the treatment process of polluted river of the present invention comprises aspergillus tubigensis 1～10 weight part in the described composite fungus agent,
Photosynthetic bacterium in the described composite fungus agent belongs to the autotrophy mikrobe; It is an energy to accept light and heat; With organism or obnoxious flavour is matrix; Several physiological active substances such as nitrogenous compound such as synthesizing amino acid, nucleic acid and carbohydrate, these metabolites, the matrix that becomes other microbial reproduction that has.
Subtilis in the described composite fungus agent is a gram-positive microorganism, and 0.6～0.9 * 1.0～1.5 microns of gemma are oval to column, are positioned at thalline central authorities or inclined to one side slightly, and gemma forms the back thalline and do not expand.The bacterium colony surface irregularity is opaque, dirty white or little yellow, and when growing in the liquid medium within, the normal wrinkle mould that forms.Aerophil.Available protein, multiple sugar and starch decompose tryptophane and form indoles.The subtilyne that produces in the subtilis thalli growth process, polymyxin, nystatin, linear gramicidins isoreactivity material, these active substances have the obvious suppression effect to the conditioned pathogen of pathogenic bacterium or autogenous infection; Subtilis consumes the free oxygen in the environment rapidly, promotes the anerobes growth, and produces organic acid such as lactic acid, reduces environment pH value, suppresses other pathogenic bacterium indirectly and grows.
Nitrobacteria in the described composite fungus agent is a kind of aerobic bacteria, can in the water of aerobic or in the layer of sand, grow, and in nitrogen cycle purification of water quality process, play the part of very important role.They comprise a kind of bacillus, coccus or the spirobacteria of form inequality type.Belong to a type of property bacterium on one's own account, comprise two kinds of complete different metabolic crowds: nitrous acid Pseudomonas and nitric acid Pseudomonas.Nitrite bacteria (claiming ammonia oxidation bacteria again) becomes nitrous acid with ammonia oxidation.Nitrate bacteria (claiming nitrobacteria again) is oxidized to nitric acid with nitrous acid.These two types of bacterium can obtain the growth energy needed respectively from above oxidising process, and ammonia in the soil or ammonium salt must just can change nitrate salt under the acting in conjunction of above two bacterioids.Nitrobacteria has vital role in the nature Nitrogen Cycling.
The carbohydrate that milk-acid bacteria in the described composite fungus agent obtains with photosynthetic bacterium, yeast is a matrix, produces lactic acid.Because milk-acid bacteria has very strong sterilizing power, particularly suppress the harmful microbe breeding, and organic rapid corrupt the decomposition; Milk-acid bacteria can make the difficult organism that decomposes such as xylogen, Mierocrystalline cellulose decompose.
Yeast in the described composite fungus agent can both be grown in the environment of aerobic and anaerobic, and promptly yeast is a facultative anaerobe, and under the anoxybiotic situation, yeast becomes alcohol and carbonic acid gas to sugar decomposition.Under the situation of aerobic, it becomes carbonic acid gas and water to sugar decomposition, and when aerobic existed, the yeast growth was very fast.
Can also comprise aspergillus tubigensis in the described composite fungus agent; This flora can coexist with other mikrobe; Generation to promoting other effective microbe propagation matrix plays an important role, and has the effect of decomposing repugnant substance, and ability will at the corruption thing and bacillus eats, carbonization.
The treatment process of polluted river of the present invention is stressed the synergy of flora, and its process is: 1. shift, conversion and degradation of contaminant; 2. the pollutent in the water reduces, and it is clear that water just becomes, for the existence of other biological creates conditions; 3. combine to throw in hydrocoles, plantation plant etc., recover species diversity; 4. strengthen the self-purification capacity and the material cycle of water body; Finally realizing increasing water quality, index and water body become clearly, change target alive.
The treatment process of a kind of polluted river of the present invention reduces and inorganicization the river water pollutent, reaches the effect that the river is handled, and has advantage simple to operate, with low cost.
Description of drawings
Each item of the treatment process embodiment 1 of Fig. 1 polluted river of the present invention is administered the index comparison diagram.
Embodiment
For making the present invention be more prone to understand,, further set forth the present invention below in conjunction with specific embodiment.Should be understood that these embodiment only to be used to the present invention is described and be not used in the restriction scope of the present invention.
The microbial inoculum that the present invention uses is all available from beneficial source of students biotechnology company and normal peaceful thing Science and Technology Ltd..
COD among the present invention (COD), total nitrogen (TN) and total phosphorus content (TP) are several main detection indexs; The mensuration of ammonia nitrogen adopts the method for GB7479-87; The mensuration of total nitrogen adopts the method for GB11894-89, and the mensuration of total phosphorus adopts the method for GN11893-89.
Embodiment 1: drain canal in the Xiqing District of Tianjin and administer
In drain around the canal industrial enterprise and discharge about 6000 tons of industrial sewages and 9000 tons of sewages every day, and the pollution level of industrial sewage is very high.Adopt the treatment process of polluted river of the present invention to administer, concrete grammar is following:
(1) contamination index in detection river,
(2) allotment microbial inoculum kind and quantity,
(3) composite fungus agent that obtains is rendered in the water body by 50～100ppm,
(4) pollutent in composite fungus agent transfer, conversion and the degraded river,
(5) contamination index in detection river;
(51) repeating step (2)～(5) meet the requirements up to the river;
The weight part proportioning of described composite fungus agent is: photosynthetic bacterium 10～40, subtilis 10～40, nitrobacteria 10～30, milk-acid bacteria 5～15, yeast 5～15.
In the process of practice, the contriver finds that the weight part proportioning of described composite fungus agent is: photosynthetic bacterium, subtilis, nitrobacteria, milk-acid bacteria, saccharomycetic ratio are: 30: 30: 20: 10: 10 o'clock, and the best results of processing.
In composite fungus agent, can also add aspergillus tubigensis 1～10 weight part.Aspergillus tubigensis can coexist with other mikrobe, the generation that promotes other effective microbe propagation matrix is played an important role, and have the effect of decomposing repugnant substance, and ability will at the corruption thing and bacillus eats, carbonization.
In the later stage of administering, can also throw in hydrocoles and plantation plant.The hydrocoles of throwing in comprises: bivalves can be filtered algae and the organic debris that food suspends, and improves the transparency of lake water; The spiral shell sessile algae of ingesting, the short agglutinating matter of secretion simultaneously makes lake water become clear; Put silver carp, flathead in a suitable place to breed and directly remove algae.The plant of plantation can be lotus, duckweed etc.
Can see that from Fig. 1 processing has obtained significant effect, the principal pollutant index has all descended more than 90%.
Need to prove that in addition the water in river is mobile, water ecological setting changes very frequent, and very big to the impact of biotic population in the water body, its catchment area is very big, so pollution of area source is very big, also receives the influence of point-source pollution more easily.And the lake is for the river, and the water surface is big, storage capacity is big, water body environment is stable, it is very little to flow, and its catchment area is also less, so the pollution of area source in lake and point-source pollution are less relatively, water body environment is comparatively stable, also is easier to improvement.Therefore, the river is different with the improvement in lake.
Should be noted that at last; Above embodiment is only in order to technical scheme of the present invention to be described but not to the restriction of protection domain of the present invention; Although the present invention has been done detailed description with reference to preferred embodiment; Those of ordinary skill in the art should be appreciated that and can make amendment or be equal to replacement technical scheme of the present invention, and do not break away from the essence and the scope of technical scheme of the present invention.
Claims (5)
1. the treatment process of a polluted river comprises the steps:
(1) contamination index in detection river,
(2) allotment microbial inoculum kind and quantity,
(3) composite fungus agent that obtains is rendered in the water body by 50～100ppm,
(4) pollutent in composite fungus agent transfer, conversion and the degraded river,
(5) contamination index in detection river;
(51) repeating step (2)～(5) meet the requirements up to the river;
Described microbial inoculum comprises photosynthetic bacterium, subtilis, nitrobacteria, milk-acid bacteria and yeast;
The parts by weight of described composite fungus agent are:
Photosynthetic bacterium 10～40,
Subtilis 10～40,
Nitrobacteria 10～30,
Milk-acid bacteria 5～15,
Yeast 5～15.
2. the treatment process of polluted river according to claim 1 is characterized in that, the treatment process of described polluted river also comprises the steps:
(6) throw in hydrocoles and/or plantation plant to the river.
3. the treatment process of polluted river according to claim 1 is characterized in that, the parts by weight of described composite fungus agent are:
Photosynthetic bacterium 30,
Subtilis 30,
Nitrobacteria 20,
Milk-acid bacteria 10,
Yeast 10.
4. the treatment process of polluted river according to claim 1 is characterized in that, described composite fungus agent also comprises aspergillus tubigensis.
5. the treatment process of polluted river according to claim 4 is characterized in that, comprises aspergillus tubigensis 1～10 weight part in the described composite fungus agent.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
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| CN2009100396563A CN101591068B (en) | 2009-05-21 | 2009-05-21 | Method for treating polluted river |
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| CN2009100396563A CN101591068B (en) | 2009-05-21 | 2009-05-21 | Method for treating polluted river |
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| CN101591068A CN101591068A (en) | 2009-12-02 |
| CN101591068B true CN101591068B (en) | 2012-03-14 |
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Families Citing this family (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101979343B (en) * | 2010-10-08 | 2012-11-14 | 天津市市政工程设计研究院 | Process for treating landscape water eutrophication |
| CN102050523B (en) * | 2010-12-29 | 2012-07-04 | 赵亚勋 | Method for treatment and in-situ ecological restoration of black and stink riverway by using microorganism |
| CN102211822A (en) * | 2011-04-15 | 2011-10-12 | 武汉百安生物科技有限责任公司 | Method for comprehensively controlling black and odorous watercourse rivers and microbial inoculum drop irrigation device |
| CN103641229B (en) * | 2013-11-14 | 2015-06-03 | 钟国防 | Method for regulating and controlling of water quality of Litopenaeus Vannamei culture pond |
| CN104745487A (en) * | 2015-03-25 | 2015-07-01 | 广东海纳川药业股份有限公司 | Complex microbial inoculant for water quality purification and application thereof |
| CN105110485A (en) * | 2015-08-31 | 2015-12-02 | 东莞理工学院 | Composite biological filter tank with hyperbolic structure |
| CN105132342B (en) * | 2015-10-16 | 2018-06-22 | 杭州标航生物科技有限公司 | A kind of sanitary sewage disposal GS microbial inoculums and its application |
| CN106001103A (en) * | 2016-06-29 | 2016-10-12 | 惠州市东江园林工程有限公司 | Ecological restoration method for soil in chemical industrial area |
| CN106186343B (en) * | 2016-08-26 | 2017-10-03 | 广州市天瑞环保科技有限公司 | A kind of comprehensive processing method to urban river |
| CN106946363A (en) * | 2017-04-28 | 2017-07-14 | 董金伟 | A kind of method at purifying contaminated water source |
| CN108163981A (en) * | 2017-12-29 | 2018-06-15 | 广州普邦园林股份有限公司 | Method for restoring polluted lake landscape water body |
| CN109650553A (en) * | 2018-12-20 | 2019-04-19 | 周刚 | It is harnessed a river the method and its application of pollution using facultative heterotrophic microorganism |
| CN111040970A (en) * | 2019-12-27 | 2020-04-21 | 河北九华勘查测绘有限责任公司 | Compound microbial agent, preparation method thereof and application thereof in black and odorous water body remediation |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000232876A (en) * | 1998-12-15 | 2000-08-29 | Yoshimichi Monma | Raw material containing complex effective microorganism |
| CN1348987A (en) * | 2001-12-02 | 2002-05-15 | 重庆和润实业(集团)有限公司 | Prepn of microbial colony sludge for efficient treatment of sewage |
| CN101417840A (en) * | 2008-11-07 | 2009-04-29 | 黎赓桓 | A kind of black-odor river pollution treatment method |
-
2009
- 2009-05-21 CN CN2009100396563A patent/CN101591068B/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000232876A (en) * | 1998-12-15 | 2000-08-29 | Yoshimichi Monma | Raw material containing complex effective microorganism |
| CN1348987A (en) * | 2001-12-02 | 2002-05-15 | 重庆和润实业(集团)有限公司 | Prepn of microbial colony sludge for efficient treatment of sewage |
| CN101417840A (en) * | 2008-11-07 | 2009-04-29 | 黎赓桓 | A kind of black-odor river pollution treatment method |
Non-Patent Citations (1)
| Title |
|---|
| 周树礼.以光合细菌为主的生物修复受损生态系统研究.《中国优秀硕士学位论文全文数据库工程科技Ｉ辑》.2007,(第2期), * |
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