CN110092475A - A kind of iron-carbon micro-electrolysis coupling submerged plant module and its application - Google Patents
A kind of iron-carbon micro-electrolysis coupling submerged plant module and its application Download PDFInfo
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- C02F1/00—Treatment of water, waste water, or sewage
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- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
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- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
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- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/322—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae use of algae
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Abstract
The present invention discloses a kind of iron-carbon micro-electrolysis coupling submerged plant module and its application.The module includes submerged plant system and aerating system, the submerged plant system includes field planting basket and submerged plant, submerged plant is fixed in the field planting basket, submerged plant root is wrapped up and fixed by iron carbon filler, and the submerged plant is fixed in the field planting basket by haydite;The aerating system is underwater aeration or surface aeration.The iron-carbon micro-electrolysis couples submerged plant module application in black smelly/eutrophication water is repaired, can be achieved 2 darknesses it is smelly/eutrophication water coloration, smelly threshold value be substantially reduced, the ordorless smell of 10d, water transparency obviously rise, and COD removal rate is up to 70% or more, ammonia nitrogen removal frank is up to 95% or more, denitrification percent is up to 60% or more, and for dephosphorizing rate up to 95% or more, dissolved oxygen reaches 2.5~5.5mg/L, transparency can reach 35~70cm, and microorganisms in water type increases.
Description
Technical field
The invention belongs to black smelly/eutrophication waters to repair field, in particular to a kind of iron-carbon micro-electrolysis couples heavy water and plants
Object module and its application.
Background technique
Due to the quick extensive style development of industrial or agricultural and the lag of sewage collecting handling rate, at present many rivers in China
Stream, lake water quality deteriorate seriously, and a large amount of pollutants enter river, and the pollutants such as COD, nitrogen, phosphorus are exceeded in water body, river water
Body pollution is serious, and water body occurs seasonal or black throughout the year smelly." black smelly " in river not only makes one to feel mood to people's stimulus to the sense organ
It is unhappy, moreover, gas that black and odorous water distributes (vulcanization oxygen, ammonia etc.) can directly be detrimental to health , ?smelly water body in anoxic
State influences fish and other aquatiles, normal growth and development in water body, it is a large amount of to will lead to aquatile when serious
Death, river aquatic ecosystem destroy completely, seriously threaten drinking for river and lake itself ecosystem health and nearby residents
Water security also greatly hinders the sustainable development of littoral industrial or agricultural.Therefore, black smelly, the improvement city water ring of urban river is eliminated
Border quality is very urgent, and research and development are cheap convenient, and safe and efficient quick recovery technique is extremely urgent.
Water body under the comprehensive function of the factors such as physics, chemistry and biology, makes pollutant after being included in certain pollutant
Concentration and quantity reduce, and so that contaminated water body is restored to the state before pollution, restore its normal ecological functions, this phenomenon
It is called " self-purification of water ".So however, after a large amount of polluter is discharged into water body, water body self-purification ability is far smaller than the amount of being discharged into
Afterwards, water body just generates black smelly.It has been that the larger molecular organics such as nitrogenous, carbon are degraded to by feeding microorganism first after water body is contaminated
Small organic molecule is finally changed into water and CO2.With further degradation, the dissolved oxygen in water body is further disappeared, and works as water
After body tends to anaerobic environment, anaerobe mass propagation.In an anaerobic environment, organic matter is decomposed and is generated greatly by anaerobe
Amount contains odour, such as CH4、H2S、NH3Etc. other gases for having peculiar smell, these gases enter atmosphere after escaping the water surface, send out water body
It is smelly.In addition, CH4、H2S etc. can carry slightly solubility particulate matter during escaping the water surface and enter water body, so that water body be made to black.Detest
Oxygen environment will cause the heavy metals such as Fe, Mn in water body and be reduced, and FeS, MnS etc. are formed in conjunction with S, make water body blackening.At present
The smelly mechanism of blackening is still not clear, but generally believes that black and odorous water has high organic pollution load, nitrogen, phosphorus, Fe, S, Mn and low DO,
More than low transparency several features.
The current research to black and odorous water processing technique both at home and abroad mainly has physics (cutting dirt, water is changed in dredging), chemistry (to throw
Add flocculant, add heavy metal fixative, strong oxidizer), biological (microorganism enhanced technology, biological oxidation of sediment technology, plant
Recovery technique).Although single physics, chemistry, biological method can administer black and odorous water to a certain extent, there is such as
Regulation effect is undesirable, cost is excessively high, generates the disadvantages of secondary pollution, regulation effect are difficult to ensure chronicity or deficiency.It compares
Under, in recent years, bio-ecological process improvement is realized according to the transfer of imitative biological theory, conversion and degradation water pollutant to certainly
The reinforcing and recovery of right boundary water body self-purification ability are the stable and long-acting important means for improving quality of water environment, just because of due to
Bio-ecological process has high treating effect, and operating cost is cheap, project cost is lower, can improve phase with greening environment and landscape
In conjunction with the advantages that, be most promising malodorous black water Treatment process.Structure while repairing black smelly/eutrophication water
The aquatic ecosystem with complete nutrition level structure is built, the self-purification capacity and life of black smelly/eutrophication water are fundamentally restored
State function, but still remain following problems: first is that bio-ecological process needs are carried out in the case where water body environment gradually improves,
For example nutrient concentration, water transparency, pH value, the dissolved oxygen of water body severely exceed, and can seriously affect bio-ecological process pair
The repairing effect of black smelly/eutrophication water;Second is that being easy by seasonal effect, plant growth is slow under low temperature, biodegrade effect
Rate is very low,;Third is that most of Polluted Urban surface water C/N are lower, and have the COD for being difficult to be degraded by microorganisms, influence
Microbial denitrogenation effect.
Summary of the invention
In order to overcome the disadvantages mentioned above and insufficient, the existing black smelly/eutrophied water treatment technology of solution of the prior art
Present in regulation effect is undesirable, cost is excessively high, generates the problems such as secondary pollution, regulation effect are difficult to ensure chronicity, is same
When overcome bio-ecological process that need to improve habitat, restrict technological deficiency by season and using carbon source, primary and foremost purpose of the invention exists
In providing a kind of iron-carbon micro-electrolysis coupling submerged plant module.
Another object of the present invention is to provide the applications of above-mentioned iron-carbon micro-electrolysis coupling submerged plant module.
A kind of iron-carbon micro-electrolysis coupling submerged plant module, including submerged plant system and aerating system, the heavy water are planted
Object system includes field planting basket and submerged plant, submerged plant is fixed in the field planting basket, submerged plant root is by iron carbon filler
It wraps up and fixes, surrounding is surrounded by haydite after fixing, and the submerged plant is fixed in the field planting basket by haydite;The aeration
System is underwater aeration or surface aeration.
Preferably, the mass ratio of the iron carbon filler and haydite is 1:3~1:20.
Preferably, the partial size of the iron carbon filler is 2~6mm.
Preferably, the iron carbon filler is the iron carbon filler acted in neutral conditions.
Preferably, the iron carbon filler is that can also be iron filings hybrid with active carbon for sintered type.
Preferably, the haydite is spherical shape, and partial size is 2~5mm, porosity of=40%.
Preferably, the aerating system is intermittent aeration, 2~8h/ days, is generally aerated in preceding 2d.
Preferably, the field planting basket is prepared using plastic material.
Preferably, the field planting basket is hollow out, but can ensure that the haydite and iron carbon filler will not leak out.
Preferably, 1~7 plant of submerged plant is fixed in the field planting basket.
Preferably, the submerged plant is one or two kinds of in eel grass, water caltrop, waterweed, hornwort, watermifoil and black algae
More than.
Preferably, the submerged plant root is wrapped up and is fixed by iron carbon filler specifically: uses geotextiles or kitchen floor drain
Bag is fixed.
Application of the iron-carbon micro-electrolysis coupling submerged plant module in black smelly/eutrophication water is repaired.
Preferably, application of the iron-carbon micro-electrolysis coupling submerged plant module in black smelly/eutrophication water is repaired
In, the injected volume of field planting basket is 10~60/square metre.
Iron-carbon micro-electrolysis of the present invention coupling submerged plant module in practical applications, according to the depth degree of water body,
It can be made into iron-carbon micro-electrolysis coupling submerged plant mattress, including mattress device and iron-carbon micro-electrolysis couple submerged plant module, institute
Stating mattress device includes supporting plate, floating ball and fixed frame, is arranged fluted on the supporting plate, and the field planting basket is fixed in groove.
The mechanism of action of black smelly/eutrophication water is quickly repaired using iron-carbon micro-electrolysis coupling submerged plant are as follows: haydite
There is suction-operated to organic matter, nitrogen, the phosphorus in black smelly/eutrophication water, attachment point can be provided for microorganism, promotes microorganism
Growth and metabolism;The more flourishing root system of plant of submerged plant can absorb nutritive salt, heavy metal or organic pollutant and is enriched in
Aerobic and oxygen, anaerobic zone are formed in submerged plant root zone in plant, auxiliary aeration is to improve Dissolved Oxygen in Water and oxidation also
Former current potential, rhizosphere enriched microorganism realize synchronous nitration denitrification denitrogenation and promote absorption of the plant to nitrogen phosphorus;Ferro element is micro-
The important component of bioelectronics transfer chain can intervene microbiological materials and energy metabolism, biochemical reaction can be improved
Speed, the activity of enhancing biological metabolism reaction, improves the NH of water body4+- N and NO3-- N removal efficiency;The original electricity of iron and carbon composition
Larger molecular organics in water body, can be decomposed into small organic molecule by pond reaction, bio-toxicity be reduced, conducive to the drop of microorganism
Solution;The Fe that iron-carbon micro-electrolysis anode generates2+H is generated with cathode surface2Also microbial metabolism and nitrification and anti-nitre can be effectively facilitated
Change effect, is conducive to denitrification denitrogenation;The Fe discharged in anode oxidation process2+And the Fe that oxidation generates3+With overlying water PO4 3-Instead
Stable FePO should be generated4Dephosphorization is precipitated, and part COD is removed by adsorption coprecipitation;Physical absorption, light electrolysis effect,
FePO4Precipitating, indigenous microorganism metabolism, plant absorption synergistic effect make so as to quickly and effectively improve water ecological setting
Black smelly/eutrophication water returns the ecological balance, promotes to restore water body self-purification ability and ecological functions.
Compared with prior art, the present invention has the following advantages and beneficial effects:
Black smelly/eutrophication water the coloration of 2d can be achieved in the present invention, smelly threshold value is substantially reduced, the ordorless smell of 10d, water body
Transparency obviously rises, and COD removal rate is up to 70% or more, and ammonia nitrogen removal frank is up to 95% or more, and denitrification percent is up to 60% or more, dephosphorization
For rate up to 95% or more, dissolved oxygen reaches 2.5-5.5mg/L, and transparency can reach 35-70cm, and microorganisms in water type increases, and
Occur zooplankter (such as water scabies class), aquatic ecosystem restores, do not have within six months after water remediation it is black it is smelly repeatedly, effect and not by
Season influences with using carbon source deficiency.
Detailed description of the invention
Fig. 1 is that a kind of iron-carbon micro-electrolysis of the present invention couples submerged plant module diagram.
Fig. 2 is that iron-carbon micro-electrolysis of the present invention couples submerged plant module assembled into the schematic diagram of mattress.
Specific embodiment
Below with reference to embodiment, the present invention is described in further detail, embodiments of the present invention are not limited thereto.
Black and odorous water described in embodiment is taken from Guangzhou Huangpu District four and gushes, and the iron carbon filler is the production of commercially available iron carbon
Product, the haydite are commercially available light-weight building haydite.
Embodiment 1
A kind of iron-carbon micro-electrolysis couples submerged plant module, has 6 plants of eel grass in field planting basket, eel grass root is filled out by 10g iron carbon
Material package, is fixed with ground for kitchen use leak-off pocket, is fixed in field planting basket after fixed with 50g haydite, and test 1d uses intermittent aerating
4h, 2h/ times.
Take 10L black and odorous water in simulation reaction device, reaction unit is that (staving diameter is for the plastic barrel of a cylindrical body
30cm is highly 30cm), takes 6 above-mentioned iron-carbon micro-electrolysis coupling submerged plant modules to be put into reaction unit, at this point, fixed
It plants basket and submerged plant is flooded by black and odorous water completely.
The initial water quality index parameter of black and odorous water is as shown in table 1.The smelly water body chroma of 2 darknesses, smelly threshold value are substantially reduced,
Ordorless smell, water transparency obviously rise after 10d, and COD removal rate is up to 76%, and up to 98%, denitrification percent reaches ammonia nitrogen removal frank
62%, for dephosphorizing rate up to 97%, dissolved oxygen 4.6mg/L, transparency reaches 30cm, microorganisms in water type, and aquatic ecosystem restores,
Device do not have after running six months it is black it is smelly and occur planktonic organism in water body repeatedly, effect and not by season with using carbon source
Deficiency influences.
The initial water quality index parameter of 1 black and odorous water of table
Embodiment 2
A kind of iron-carbon micro-electrolysis couples submerged plant module, has 5 plants of eel grass in field planting basket, eel grass root is by 5g iron carbon filler
Package, with white such as kitchen use leak-off pocket is fixed, and is fixed in field planting basket after fixed with 60g haydite, test 1d is using interval
Be aerated 6h, 3h/ times.
Take 10L black and odorous water in simulation reaction device, reaction unit is that (staving diameter is for the plastic barrel of a cylindrical body
30cm is highly 30cm), takes 6 above-mentioned iron-carbon micro-electrolysis coupling submerged plant modules to be put into reaction unit, at this point, fixed
It plants basket and submerged plant is flooded by black and odorous water completely.
The initial water quality index parameter of black and odorous water are as follows: COD 105.62mg/L, ammonia nitrogen 36.65mg/L, TP are
2.80mg/L, DO 0.35mg/L.Black smelly raw water lighter after processing 2 days, the ordorless smell of 7d, COD is after 21d
21.40mg/L, ammonia nitrogen 0.46mg/L, TP 0.02mg/L, DO 4.1mg/L, transparency reach 30cm, microorganisms in water kind
Class increases, and aquatic ecosystem restores, device do not have after running six months it is black it is smelly and occur planktonic organism in water body repeatedly, effect
And it is not influenced by season with using carbon source deficiency.
Embodiment 3
A kind of iron-carbon micro-electrolysis couples submerged plant module, has 4 plants of eel grass in field planting basket, eel grass root is filled out by 10g iron carbon
Material package, is fixed with ground for kitchen use leak-off pocket, is fixed in field planting basket after fixed with 80g haydite, and test 1d uses intermittent aerating
8h, 4h/ times.
Take 10L black and odorous water in simulation reaction device, reaction unit is that (staving diameter is for the plastic barrel of a cylindrical body
30cm is highly 30cm), takes 6 above-mentioned iron-carbon micro-electrolysis coupling submerged plant modules to be put into reaction unit, at this point, fixed
It plants basket and submerged plant is flooded by black and odorous water completely.
The initial water quality index parameter of black and odorous water are as follows: COD 65.5mg/L, ammonia nitrogen 23.25mg/L, TP are
2.54mg/L, DO 0.13mg/L.Black smelly raw water lighter after processing 2 days, COD is 14.41mg/L after 21d, and ammonia nitrogen is
0.25mg/L, TP 0.08mg/L, DO 4.5mg/L, transparency reach 30cm, and microorganisms in water type increases, Aquatic Ecosystem 2
System restores, device do not have after running six months it is black it is smelly and occur planktonic organism in water body repeatedly, effect and not by season with can benefit
It is influenced with carbon source deficiency.
In practical applications, according to the depth degree of water body, iron-carbon micro-electrolysis of the present invention couples submerged plant module
It can be assembled into mattress, including mattress device and iron-carbon micro-electrolysis couple submerged plant module, the mattress device includes supporting plate, floats
Ball and fixed frame, are arranged on the supporting plate fluted, and the field planting basket is fixed in groove;The submerged plant is immersed under water
30~40cm.
Fig. 1 is that a kind of iron-carbon micro-electrolysis of the present invention couples submerged plant module diagram.
Fig. 2 is that iron-carbon micro-electrolysis of the present invention couples submerged plant module assembled into the schematic diagram of mattress.
The above embodiment is a preferred embodiment of the present invention, but embodiments of the present invention are not by above-described embodiment
Limitation, other any changes, modifications, substitutions, combinations, simplifications made without departing from the spirit and principles of the present invention,
It should be equivalent substitute mode, be included within the scope of the present invention.
Claims (10)
1. a kind of iron-carbon micro-electrolysis couples submerged plant module, which is characterized in that including submerged plant system and aerating system, institute
Stating submerged plant system includes field planting basket and submerged plant, and submerged plant, submerged plant root quilt are fixed in the field planting basket
Iron carbon filler is wrapped up and is fixed, and surrounding is surrounded by haydite after fixing, and the submerged plant is fixed in the field planting basket by haydite;
The aerating system is underwater aeration or surface aeration.
2. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 1, which is characterized in that the iron carbon filler
Mass ratio with haydite is 1:3~1:20.
3. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 2, which is characterized in that the iron carbon filler
Partial size be 2~6mm;The haydite is spherical shape, and partial size is 2~5mm, porosity of=40%.
4. any one a kind of iron-carbon micro-electrolysis coupling submerged plant module according to claim 1~3, which is characterized in that institute
Stating iron carbon filler is the iron carbon filler acted in neutral conditions.
5. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 4, which is characterized in that the aerating system
For intermittent aeration, aeration time is 2~8h/ days.
6. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 5, which is characterized in that the field planting basket is adopted
It is prepared with plastic material.
7. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 6, which is characterized in that the field planting basket is
Hollow out;1~7 plant of submerged plant is fixed in the field planting basket.
8. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 1, which is characterized in that the submerged plant
It is one or more kinds of in eel grass, water caltrop, waterweed, hornwort, watermifoil and black algae.
9. a kind of iron-carbon micro-electrolysis couples submerged plant module according to claim 1, which is characterized in that the submerged plant
It is wrapped up and is fixed by iron carbon filler in root specifically: with geotextiles or kitchen leak-off pocket is fixed.
10. any one of the claim 1~9 iron-carbon micro-electrolysis coupling submerged plant module is repaired in black smelly/eutrophication water
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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CN110776104A (en) * | 2019-10-22 | 2020-02-11 | 中国水产科学研究院珠江水产研究所 | Ecological clean system to water alkylphenol eutrophication |
CN112266140A (en) * | 2020-11-24 | 2021-01-26 | 河南永泽环境科技有限公司 | Constructed wetland biomembrane coupling iron-carbon micro-electrolysis filler |
CN112537886A (en) * | 2020-12-17 | 2021-03-23 | 灵珑生态科技(江苏)有限公司 | A ecological heavy bed of automatic rising for submerged plant field planting |
CN115259291A (en) * | 2022-08-05 | 2022-11-01 | 辽宁省生态环境保护科技中心 | Method for in-situ remediation of black and odorous water body based on iron-carbon internal electrolysis-submerged plant-microorganism ternary coupling system |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107473389A (en) * | 2017-09-01 | 2017-12-15 | 北京科技大学 | Couple microorganism and light electrolysis combination floating bed device and the method for handling sanitary sewage |
CN108218114A (en) * | 2017-12-29 | 2018-06-29 | 广州市环境保护工程设计院有限公司 | A kind of Inner electrolysis couples ecological floating island system |
-
2019
- 2019-04-03 CN CN201910264485.8A patent/CN110092475A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107473389A (en) * | 2017-09-01 | 2017-12-15 | 北京科技大学 | Couple microorganism and light electrolysis combination floating bed device and the method for handling sanitary sewage |
CN108218114A (en) * | 2017-12-29 | 2018-06-29 | 广州市环境保护工程设计院有限公司 | A kind of Inner electrolysis couples ecological floating island system |
Non-Patent Citations (1)
Title |
---|
曾郴林 等: "《微电解法处理难降解有机废水的理论与实例分析》", 30 June 2017, 中国环境出版社 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110776104A (en) * | 2019-10-22 | 2020-02-11 | 中国水产科学研究院珠江水产研究所 | Ecological clean system to water alkylphenol eutrophication |
CN112266140A (en) * | 2020-11-24 | 2021-01-26 | 河南永泽环境科技有限公司 | Constructed wetland biomembrane coupling iron-carbon micro-electrolysis filler |
CN112537886A (en) * | 2020-12-17 | 2021-03-23 | 灵珑生态科技(江苏)有限公司 | A ecological heavy bed of automatic rising for submerged plant field planting |
CN115259291A (en) * | 2022-08-05 | 2022-11-01 | 辽宁省生态环境保护科技中心 | Method for in-situ remediation of black and odorous water body based on iron-carbon internal electrolysis-submerged plant-microorganism ternary coupling system |
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