CN105084555A - Water body pollution treatment method taking microbiological method as main body - Google Patents
Water body pollution treatment method taking microbiological method as main body Download PDFInfo
- Publication number
- CN105084555A CN105084555A CN201510494437.XA CN201510494437A CN105084555A CN 105084555 A CN105084555 A CN 105084555A CN 201510494437 A CN201510494437 A CN 201510494437A CN 105084555 A CN105084555 A CN 105084555A
- Authority
- CN
- China
- Prior art keywords
- water
- sewage
- main body
- microorganism
- treatment
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims abstract description 57
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 50
- 238000013048 microbiological method Methods 0.000 title abstract 4
- 238000000746 purification Methods 0.000 claims abstract description 7
- 244000005700 microbiome Species 0.000 claims description 36
- 239000010865 sewage Substances 0.000 claims description 22
- 239000003795 chemical substances by application Substances 0.000 claims description 21
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 18
- 239000001301 oxygen Substances 0.000 claims description 18
- 229910052760 oxygen Inorganic materials 0.000 claims description 18
- 238000005273 aeration Methods 0.000 claims description 17
- 238000007711 solidification Methods 0.000 claims description 17
- 230000008023 solidification Effects 0.000 claims description 17
- 238000003911 water pollution Methods 0.000 claims description 13
- 238000003860 storage Methods 0.000 claims description 10
- 230000000813 microbial effect Effects 0.000 claims description 9
- 238000002203 pretreatment Methods 0.000 claims description 8
- 238000007670 refining Methods 0.000 claims description 8
- 230000010354 integration Effects 0.000 claims description 7
- 239000010801 sewage sludge Substances 0.000 claims description 6
- 238000005728 strengthening Methods 0.000 claims description 6
- 241000251468 Actinopterygii Species 0.000 claims description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 4
- 230000002906 microbiologic effect Effects 0.000 claims description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 3
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims description 3
- 239000011575 calcium Substances 0.000 claims description 3
- 229910052791 calcium Inorganic materials 0.000 claims description 3
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 3
- 239000011777 magnesium Substances 0.000 claims description 3
- 229910052749 magnesium Inorganic materials 0.000 claims description 3
- 239000011707 mineral Substances 0.000 claims description 3
- 238000005507 spraying Methods 0.000 claims description 3
- 238000007599 discharging Methods 0.000 claims description 2
- 229910052742 iron Inorganic materials 0.000 claims description 2
- 239000007921 spray Substances 0.000 claims description 2
- 239000000126 substance Substances 0.000 abstract description 7
- 241000195493 Cryptophyta Species 0.000 abstract description 5
- 238000012851 eutrophication Methods 0.000 abstract description 5
- 238000005516 engineering process Methods 0.000 abstract description 3
- 238000012423 maintenance Methods 0.000 abstract description 3
- 238000000354 decomposition reaction Methods 0.000 abstract description 2
- 238000009434 installation Methods 0.000 abstract description 2
- 230000002787 reinforcement Effects 0.000 abstract 2
- 238000004332 deodorization Methods 0.000 abstract 1
- 238000005265 energy consumption Methods 0.000 abstract 1
- 238000004519 manufacturing process Methods 0.000 abstract 1
- 238000005067 remediation Methods 0.000 abstract 1
- 239000010802 sludge Substances 0.000 abstract 1
- 230000000694 effects Effects 0.000 description 8
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 239000007789 gas Substances 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 3
- 238000010276 construction Methods 0.000 description 3
- 238000011065 in-situ storage Methods 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 239000003643 water by type Substances 0.000 description 3
- 239000000463 material Substances 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 230000001360 synchronised effect Effects 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 208000034189 Sclerosis Diseases 0.000 description 1
- 230000000274 adsorptive effect Effects 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 230000001877 deodorizing effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 238000004146 energy storage Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 230000000050 nutritive effect Effects 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 208000024891 symptom Diseases 0.000 description 1
Classifications
-
- 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
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention relates to a water body pollution treatment method taking a microbiological method as a main body. The method adopts a combined treatment technology comprising a pretreatment reinforcement part, a main body treatment part and an auxiliary treatment part and is suitable for pollution abatement of water bodies such as watercourses, lakes and reservoirs which are more severe in eutrophication. The pretreatment reinforcement part is used for removing a large number of algae and substances difficult to degrade and arranged when a large number of the algae or black and odorous phenomena exist in the water bodies; the main body treatment part adopts the microbiological method, and therefore water body bioremediation and biological decomposition of bottom mud can be achieved; the auxiliary treatment part aims at achieving ecological remediation of the water bodies. The water body pollution treatment method taking the microbiological method as the main body has the advantages that water purification, sludge removal and deodorization can be synchronously achieved, the treatment efficiency is high, the energy consumption is low, the production cost is low, and installation and maintenance are easy.
Description
Technical field
The invention belongs to water pollution Treatment process field, be specifically related to a kind of water pollution administering method based on microbial method.
Background technology
In recent years, along with the sustainable growth of China's economy and the quickening day by day of urbanization process, city size is expanded rapidly, urban population sharply expands; Meanwhile, the source of pollution in a large number containing nitrogen, phosphoric nutritive substance also enter in the water bodys such as river course, lake, reservoir continuously, and the Nutrient loads amount of water body is constantly increased, and water quality condition worse and worse.
At present, the eutrophication of water body has become the comparatively outstanding environmental problem of one, China.
(1) also there is eutrophication, as Huangpu River Basin, Guangzhou Section of Pearl River etc. in part section in some rivers.
(2) many large-size lake, as Chaohu, Taihu Lake, Poyang Lake, Dian Chi etc., have all been in eutrophy or heavy eutrophic state.
(3) some reservoirs also receive pollution in various degree and have had influence on the drinking water safety of resident.
Due to water body once enter the eutrophy stage will lose its due function, affect economic construction and social development, water pollution administer become create civilized communities, one of faced problem in the urgent need to address of building a harmonious society.
Traditional water pollution administering method spatially position division can be divided into dystopy facture, in situ treatment, bypass treatment.The treatment effect of dystopy facture depends on Technology and the operation conditions of the sewage work built in strange land completely, and construction investment costly.In situ treatment comprises Physical, chemical method, aeration, throwing bacterium method, biomembrance process, plant method, animal law etc., although do not need the pipe network system of separately building shunting, whole river directly processes in river course, lake.Bypass treatment comprises land treatment systems method, oxidation pond process, artificial-strengthening bio-reactor method etc., the typical method land treatment systems method in this method, and in general, there is floor space comparatively large, long-time running also exists the problem of filling soil property or clogged with material.
In Practical Project, adopt the more of in situ treatment, as the method such as Physical (desilting, water distribution, substrate sclerosis, open channel cover), chemical method (algae is killed in dispensing), aeration, throwing bacterium method, some engineering additionally uses combination process, these methods have effect that can be certain, but there is following problem:
A () destroys original ecosystem, as desilting method.
B () is costly, as substrate hardening process.
C () is cured the symptoms, not the disease, easily recur, there is secondary pollution, as chemical method.
D () combination process falls flat, as chemical method+throwing bacterium method+artificial floating island, Unit selection non-optimal, combining is not play the effect of mutually promoting, and what have also plays negative effect.
Summary of the invention
For above-mentioned problems of the prior art, the object of the present invention is to provide a kind of water pollution administering method based on microorganism avoiding occurring above-mentioned technological deficiency.
In order to realize foregoing invention object, the technical scheme of this practicality invention is as follows:
A water pollution administering method based on microbial method, is characterized in that, strengthens step, main body treatment step, ancillary process steps form, be specially by pre-treatment:
1) pre-treatment strengthening: by sewage-treating agent: clear water is 1:(2.5-4) proportional arrangement sewage disposal agent solution, adopt high pressure spraying hydraulic giant by sewage-treating agent spray solution in polluted water surface, the dosage of sewage disposal agent solution is by 50 ~ 100g/ ton water.
2) main body process: adopt the sewage sludge refining plant of integration to process the sewage after pre-treatment strengthening, the sewage sludge refining plant of described integration swims on the treatment sewage water surface, by discharging the microorganism of multiple types in sewage, realize the degraded to dirty water purification and mud.
The sewage sludge refining plant of described integration is floatation type structure, comprise box main body, one FRP buoyancy tank 1,2nd FRP buoyancy tank 7, solidification microorganism memotron oxygen supply blower fan 2, micropore aeration pipe oxygen supply blower fan 3, solar panels 4, switch box 5, solar storage battery 6, micropore aeration pipe 8 and solidification microorganism memotron 9; Wherein a FRP buoyancy tank 1 and the 2nd FRP buoyancy tank 7 are arranged on the both sides of box main body, solar panels 4 are arranged on the top of box main body, and be connected with solar storage battery 6, solar storage battery 6, solidification microorganism memotron oxygen supply blower fan 2, micropore aeration pipe oxygen supply blower fan 3 and switch box 5 are arranged on the top of box main body, and switch box 5 respectively with solidification microorganism memotron oxygen supply blower fan 2, micropore aeration pipe oxygen supply blower fan 3 and solar storage battery 6 are electrically connected; Micropore aeration pipe 8 and solidification microorganism memotron 9 are arranged on the bottom of box main body, place microorganism species in solidification microorganism memotron 9.
3) auxiliary treatment: after main body process, arranges waterplant and adds restoration of the ecosystem and the purification that fish realize water body in water body.
Further, by sewage-treating agent: clear water is the proportional arrangement sewage disposal agent solution of 1:3; The dosage of sewage disposal agent solution is by 80g/ ton water.
Further, described sewage-treating agent is preferably nanometer mineral matters sewage-treating agent, wherein contains calcium, the magnesium of 25% and the iron of 8% of 20% by percentage to the quality.
Further, described solidification microorganism memotron 9 is built with microorganism species, and polytype microorganism is discharged in water body continuously and goes, and produces and reaches 10
7the microorganism species of individual/cc, wherein anaerobion flora accounts for 25% of flora total amount, and aerobic microbiological flora accounts for 55% of flora total amount, and aerobic-anaerobic microbe flora accounts for 20% of flora total amount.
Advantageous Effects of the present invention is:
1) synchronous water purification and remove mud, deodorizing.While improvement sewage, mud can be removed, removes the stench in water body and algae.The lake, river of polluting, reservoir do not need desilting, and cleaning effect is firm for a long time.
2) processing efficiency is high.(1) BOD, COD, TSS (suspended solid) can be reduced fast, have very strong removal ability to nitrogen and phosphorus, within very short time, bad 5 class water can be transformed into more than 3 classes; (2) stink can be eliminated in 3-7 days; (3) dispose of sewage and the mud time short.The fastest monthly minimizing one meter.At 50000 square metres of waters surface, in three meters of dark mud situations, within every 10 days, can eat up mud 10 ~ 55%, the BOD that degrades every day can reach 20%.Within 3 months, can be disposed according to standard.
3) energy-saving effect is remarkable, and working cost is low.Power-equipment adopts solar powered, and set of system all devices power sum is less than 3kW, and thus working cost is low.
4) installation and maintenance are simple and convenient.Main body treating part integration apparatus is floatation type, comprises gas blower, kickboard, bacterial classification storatron, the parts such as pipeline, and parts are few, therefore installs and convenience easy to maintenance.
Accompanying drawing explanation
Fig. 1 is Pollution abatement technical process of the present invention composition structural representation;
Fig. 2 is Pollution abatement principle of work schematic diagram of the present invention;
Fig. 3 is integrated sewage water mud refining plant structural representation of the present invention;
In figure, 1-the one FRP buoyancy tank, 2-solidifies microorganism memotron oxygen supply blower fan, 3-micropore aeration pipe oxygen supply blower fan, 4-solar panels, 5-switch box, 6-solar storage battery, 7-the 2nd FRP buoyancy tank, and 8-micropore aeration pipe, 9-solidifies microorganism memotron.
Embodiment
Below in conjunction with drawings and the specific embodiments, the present invention will be further described.
As depicted in figs. 1 and 2, this water pollution administering method is made up of pre-treatment strengthening, main body process, auxiliary treatment three parts.Wherein pre-treatment reinforced portion is to remove a large amount of algae and hard-degraded substance; Main body treating part adopts microbial method, can realize the biological decomposition of bioremediation of waters and bed mud; Auxiliary treatment part is the restoration of the ecosystem in order to realize water body.The material that pretreatment stage adds is called sewage-treating agent, preferred nanometer mineral matters sewage-treating agent, and main component comprises the calcium constituent being about 20wt%, the magnesium elements of 25wt%, the ferro element of 8wt%, and other nearly two Ten microelements close and account for about 47%.Described sewage-treating agent has powerful oxidation capacity, adsorptive power.This product operation is simple and convenient, and can not produce secondary pollution, does not affect aquatic fish and plant.During use, diluted by water conditioner by 1:3 multiple clear water, adopt high pressure spraying hydraulic giant to be sprayed at polluted water surface, dosage presses 80g/ ton water, and concrete data can be done a lab scale and determine before construction.
As shown in Figure 3, integrated sewage water mud refining plant is adopted the treatment stage of main body, this device can discharge the high-effective microorganism of multiple types, part microorganism carries out active adsorption, conversion and degraded to the organism in water body and nitrogen, phosphoric, set up the flora ecosystem simultaneously, form aerobic water body, effectively can alleviate water pollution (eutrophication, black smelly) degree; Another part microorganism can the mud of successively exploded bottom, forms bed mud degraded layer, realize the synchronous improvement of sewage and mud.This device is portable, comprises box main body, FRP buoyancy tank the 1, a two FRP buoyancy tank 7, solidification microorganism memotron oxygen supply blower fan 2, micropore aeration pipe oxygen supply blower fan 3, solar panels 4, switch box 5, solar storage battery 6, micropore aeration pipe 8 and solidification microorganism memotron 9.The principle of work of this device is, solidification microorganism memotron is built with microorganism, polytype microorganism is discharged in water body continuously and goes, the microorganism species reaching 107/cc can be produced, comprise more than 10 and plant microbial organisms, flora is mainly divided into anaerobion (accounting for 25% of flora total amount), aerobic microbiological (accounting for 55% of flora total amount), aerobic-anaerobic microbe (accounting for 20% of flora total amount) three major types.It has very strong processing power to the BOD in sewage and biological organism especially, also has good Degradation to mud.Gas blower provides oxygen for aerobic microbiological, micro-gas aeration tube can provide oxygen dissolution efficiency, solar panels can be gas blower and provide electric energy, the unnecessary energy storage that solar panels absorb can be got up in night or overcast and rainy utilization by store battery, and the effect of buoyancy tank allows whole device be suspended on the water surface.Single covering device physical dimension is LxBxH=4x2x2m, and device total power is less than 3kW, and service area is about 3000m
2.For the waters that area is larger, for being reduced to the quantity of covering device, specialized designs can be carried out.
The auxiliary treatment stage adopts submerged plant and fish stocking, increases diversity of organism, forms self purification of water body system.Concrete kind, the quantity of submerged plant and fish, need according to project reality, and research selection is determined.
Sewage water treatment method of the present invention is applicable to the repairing and treating of the more serious river course of eutrophication, lake, reservoir.
The above embodiment only have expressed embodiments of the present invention, and it describes comparatively concrete and detailed, but therefore can not be interpreted as the restriction to the scope of the claims of the present invention.It should be pointed out that for the person of ordinary skill of the art, without departing from the inventive concept of the premise, can also make some distortion and improvement, these all belong to protection scope of the present invention.Therefore, the protection domain of patent of the present invention should be as the criterion with claims.
Claims (4)
1. the water pollution administering method based on microbial method, is characterized in that, strengthens step, main body treatment step, ancillary process steps form, be specially by pre-treatment:
1) pre-treatment strengthening: by sewage-treating agent: clear water is 1:(2.5-4) proportional arrangement sewage disposal agent solution, adopt high pressure spraying hydraulic giant by sewage-treating agent spray solution in polluted water surface, the dosage of sewage disposal agent solution is by 50 ~ 100g/ ton water.
2) main body process: adopt the sewage sludge refining plant of integration to process the sewage after pre-treatment strengthening, the sewage sludge refining plant of described integration swims on the treatment sewage water surface, by discharging the microorganism of multiple types in sewage, realize the degraded to dirty water purification and mud.
The sewage sludge refining plant of described integration is floatation type structure, comprise box main body, one FRP buoyancy tank (1), 2nd FRP buoyancy tank (7), solidification microorganism memotron oxygen supply blower fan (2), micropore aeration pipe oxygen supply blower fan (3), solar panels (4), switch box (5), solar storage battery (6), micropore aeration pipe (8) and solidification microorganism memotron (9), wherein a FRP buoyancy tank (1) and the 2nd FRP buoyancy tank (7) are arranged on the both sides of box main body, solar panels (4) are arranged on the top of box main body, and be connected with solar storage battery (6), solar storage battery (6), solidification microorganism memotron oxygen supply blower fan (2), micropore aeration pipe oxygen supply blower fan (3) and switch box (5) are arranged on the top of box main body, and switch box (5) respectively with solidification microorganism memotron oxygen supply blower fan (2), micropore aeration pipe oxygen supply blower fan (3) and solar storage battery (6) electrical connection, micropore aeration pipe (8) and solidification microorganism memotron (9) are arranged on the bottom of box main body, place microorganism species in solidification microorganism memotron (9).
3) auxiliary treatment: after main body process, arranges waterplant and adds restoration of the ecosystem and the purification that fish realize water body in water body.
2. a kind of water pollution administering method based on microbial method according to claim 1, is characterized in that, by sewage-treating agent: clear water is the proportional arrangement sewage disposal agent solution of 1:3; The dosage of sewage disposal agent solution is by 80g/ ton water.
3. a kind of water pollution administering method based on microbial method according to claim 1, it is characterized in that, described sewage-treating agent is preferably nanometer mineral matters sewage-treating agent, wherein contains calcium, the magnesium of 25% and the iron of 8% of 20% by percentage to the quality.
4. a kind of water pollution administering method based on microbial method according to claim 1, it is characterized in that, described solidification microorganism memotron (9) is built with microorganism species, and polytype microorganism is discharged in water body continuously and goes, and produces and reaches 10
7the microorganism species of individual/cc, wherein anaerobion flora accounts for 25% of flora total amount, and aerobic microbiological flora accounts for 55% of flora total amount, and aerobic-anaerobic microbe flora accounts for 20% of flora total amount.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510494437.XA CN105084555B (en) | 2015-08-12 | 2015-08-12 | Water body pollution treatment method taking microbiological method as main body |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510494437.XA CN105084555B (en) | 2015-08-12 | 2015-08-12 | Water body pollution treatment method taking microbiological method as main body |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105084555A true CN105084555A (en) | 2015-11-25 |
| CN105084555B CN105084555B (en) | 2017-04-26 |
Family
ID=54566006
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201510494437.XA Active CN105084555B (en) | 2015-08-12 | 2015-08-12 | Water body pollution treatment method taking microbiological method as main body |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105084555B (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106430623A (en) * | 2016-10-13 | 2017-02-22 | 宁波池泓环保设备工程有限公司 | River channel wastewater original-ecological treatment apparatus |
| CN108928925A (en) * | 2018-07-24 | 2018-12-04 | 烟台市帅恒机械科技有限公司 | A kind of method for cleaning treatment of sewage using the flotation gear for being applied to water pollution processing |
| CN108946959A (en) * | 2018-07-24 | 2018-12-07 | 烟台市帅恒机械科技有限公司 | A kind of flotation gear applied to water pollution processing |
| CN110272169A (en) * | 2019-07-24 | 2019-09-24 | 辽东学院 | A kind of microorganism water purification method |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101050043A (en) * | 2007-05-11 | 2007-10-10 | 胡法 | Ecological management method for water pollution |
| CN202038919U (en) * | 2011-05-17 | 2011-11-16 | 襄樊赛洁环保科技有限公司 | Riverway ecology construction and water restoration system |
-
2015
- 2015-08-12 CN CN201510494437.XA patent/CN105084555B/en active Active
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101050043A (en) * | 2007-05-11 | 2007-10-10 | 胡法 | Ecological management method for water pollution |
| CN202038919U (en) * | 2011-05-17 | 2011-11-16 | 襄樊赛洁环保科技有限公司 | Riverway ecology construction and water restoration system |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106430623A (en) * | 2016-10-13 | 2017-02-22 | 宁波池泓环保设备工程有限公司 | River channel wastewater original-ecological treatment apparatus |
| CN108928925A (en) * | 2018-07-24 | 2018-12-04 | 烟台市帅恒机械科技有限公司 | A kind of method for cleaning treatment of sewage using the flotation gear for being applied to water pollution processing |
| CN108946959A (en) * | 2018-07-24 | 2018-12-07 | 烟台市帅恒机械科技有限公司 | A kind of flotation gear applied to water pollution processing |
| CN110272169A (en) * | 2019-07-24 | 2019-09-24 | 辽东学院 | A kind of microorganism water purification method |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105084555B (en) | 2017-04-26 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102775025B (en) | Municipal life wastewater treatment system with high efficiency and low energy consumption | |
| CN2898003Y (en) | Landscape sewage ecological treating pool in residential estate | |
| CN102674549B (en) | Treatment method for applying urban reclaimed water to landscape water | |
| CN105084555B (en) | Water body pollution treatment method taking microbiological method as main body | |
| CN102276067A (en) | Solar-power-driven micro-power artificial wet land sewage treatment device | |
| CN109607975B (en) | Constructed wetland structure for repairing super-eutrophic water body and endogenous pollution | |
| CN106986501A (en) | A kind of method and device of electronic permeable reactive wall and artificial swamp coupling treatment of sewage water | |
| CN201762217U (en) | Constructed wetland sewage purification system | |
| CN207435274U (en) | A kind of Heihe road cleaning treatment system | |
| CN106517677B (en) | Quality of reclaimed water landscape water body keeps structure | |
| CN104478161A (en) | Integrated biochemical wetland purification sewage treatment system | |
| CN104671408A (en) | Scattered small integrated sewage processing device for rural areas | |
| CN101269874B (en) | Layered geology mineral filter chamber sewage treatment system | |
| CN103159317A (en) | Artificial-aeration-reinforced Land percolation water treatment device | |
| CN103241906B (en) | Sewage treatment method and device for reusing reclaimed water as landscape water | |
| CN202379857U (en) | Wetland ecological treatment device for municipal domestic sewage | |
| CN113480099B (en) | In-situ circulation treatment process for landscape lake water | |
| CN212559882U (en) | Water quality purifying device | |
| CN103601291A (en) | Method and denitrification infiltration system for treating sewage with low carbon-nitrogen ratio | |
| CN104058507B (en) | Reinforced composite artificial wetland sewage treatment system | |
| CN204162582U (en) | Townm refuse turnover station percolation liquid treating system | |
| CN2818472Y (en) | In situ composite reaction treater for domestic and fecal sewage | |
| CN210595665U (en) | Anoxic biofilter-aerobic artificial wetland sewage treatment system | |
| CN203976470U (en) | A kind of denitrification filtration system for the treatment of low carbon-nitrogen ratio sewage | |
| CN102515413B (en) | Sewage treatment system and treatment method of composite horizontal undercurrent constructed wetland |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CP03 | Change of name, title or address | ||
| CP03 | Change of name, title or address |
Address after: 100073 502, 5th floor, building 2, yard 9, Guang'an Road, Fengtai District, Beijing Patentee after: BEIJING YOUFU ENVIRONMENT TECHNOLOGY Co.,Ltd. Address before: Room 2-1035, lin831-nei, Changping Road, Anning North Road, Haidian District, Beijing 100085 Patentee before: BEIJING LICHEN ENVIRONMENT PROTECTION AND ENERGY SAVING TECHNOLOGY Co.,Ltd. Address after: No. 1561, floor 9, building 19, District 16, No. 188, South Fourth Ring West Road, Fengtai District, Beijing 100070 Patentee after: Beijing Youfu Technology Co.,Ltd. Address before: 100073 502, 5th floor, building 2, yard 9, Guang'an Road, Fengtai District, Beijing Patentee before: BEIJING YOUFU ENVIRONMENT TECHNOLOGY Co.,Ltd. |
|
| TR01 | Transfer of patent right | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20210825 Address after: 530218 room 1011, unit 1, building 6, Longyin Phoenix, No. 9, Changfu Road, Qingxiu District, Nanning City, Guangxi Zhuang Autonomous Region Patentee after: Guangxi Youfu Environmental Technology Co.,Ltd. Address before: No. 1561, floor 9, building 19, District 16, No. 188, South Fourth Ring West Road, Fengtai District, Beijing 100070 Patentee before: Beijing Youfu Technology Co.,Ltd. |
|
| CP01 | Change in the name or title of a patent holder | ||
| CP01 | Change in the name or title of a patent holder |
Address after: 530218 room 1011, unit 1, building 6, Longyin Phoenix, No. 9, Changfu Road, Qingxiu District, Nanning City, Guangxi Zhuang Autonomous Region Patentee after: Guangxi ziyulan Environmental Technology Co.,Ltd. Address before: 530218 room 1011, unit 1, building 6, Longyin Phoenix, No. 9, Changfu Road, Qingxiu District, Nanning City, Guangxi Zhuang Autonomous Region Patentee before: Guangxi Youfu Environmental Technology Co.,Ltd. |
|
| TR01 | Transfer of patent right | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20211026 Address after: 530218 No. 1101, unit 1, building 6, Longyin Phoenix, No. 9, Changfu Road, Qingxiu District, Nanning City, Guangxi Zhuang Autonomous Region Patentee after: Guangxi mubi planning and Design Co.,Ltd. Address before: 530218 room 1011, unit 1, building 6, Longyin Phoenix, No. 9, Changfu Road, Qingxiu District, Nanning City, Guangxi Zhuang Autonomous Region Patentee before: Guangxi ziyulan Environmental Technology Co.,Ltd. |