CN111606468A - Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method - Google Patents
Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method Download PDFInfo
- Publication number
- CN111606468A CN111606468A CN202010393318.6A CN202010393318A CN111606468A CN 111606468 A CN111606468 A CN 111606468A CN 202010393318 A CN202010393318 A CN 202010393318A CN 111606468 A CN111606468 A CN 111606468A
- Authority
- CN
- China
- Prior art keywords
- water
- module
- ultraviolet
- oxidant
- virus
- 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
- 241000700605 Viruses Species 0.000 title claims abstract description 56
- 238000000034 method Methods 0.000 title claims abstract description 23
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 124
- 239000007800 oxidant agent Substances 0.000 claims abstract description 81
- 230000001590 oxidative effect Effects 0.000 claims abstract description 74
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 claims abstract description 66
- OSVXSBDYLRYLIG-UHFFFAOYSA-N dioxidochlorine(.) Chemical compound O=Cl=O OSVXSBDYLRYLIG-UHFFFAOYSA-N 0.000 claims abstract description 61
- 230000003647 oxidation Effects 0.000 claims abstract description 50
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 50
- 239000004155 Chlorine dioxide Substances 0.000 claims abstract description 29
- 235000019398 chlorine dioxide Nutrition 0.000 claims abstract description 29
- 241000196324 Embryophyta Species 0.000 claims abstract description 28
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 27
- 239000012528 membrane Substances 0.000 claims abstract description 26
- 230000009471 action Effects 0.000 claims abstract description 11
- 230000002265 prevention Effects 0.000 claims abstract description 11
- 238000000746 purification Methods 0.000 claims abstract description 10
- 238000010521 absorption reaction Methods 0.000 claims abstract description 7
- 238000001179 sorption measurement Methods 0.000 claims abstract description 5
- 238000006243 chemical reaction Methods 0.000 claims description 43
- 239000007788 liquid Substances 0.000 claims description 19
- 239000000523 sample Substances 0.000 claims description 14
- 238000003860 storage Methods 0.000 claims description 14
- 238000005273 aeration Methods 0.000 claims description 13
- 230000000694 effects Effects 0.000 claims description 11
- 239000003344 environmental pollutant Substances 0.000 claims description 10
- 231100000719 pollutant Toxicity 0.000 claims description 10
- 238000004140 cleaning Methods 0.000 claims description 8
- 238000009826 distribution Methods 0.000 claims description 7
- 239000007789 gas Substances 0.000 claims description 7
- 230000002147 killing effect Effects 0.000 claims description 7
- 239000000126 substance Substances 0.000 claims description 7
- 239000011159 matrix material Substances 0.000 claims description 6
- 239000010802 sludge Substances 0.000 claims description 6
- 238000004659 sterilization and disinfection Methods 0.000 claims description 5
- 230000005540 biological transmission Effects 0.000 claims description 4
- 244000205574 Acorus calamus Species 0.000 claims description 3
- 240000008436 Ipomoea aquatica Species 0.000 claims description 3
- 235000019004 Ipomoea aquatica Nutrition 0.000 claims description 3
- 235000017879 Nasturtium officinale Nutrition 0.000 claims description 3
- 240000001398 Typha domingensis Species 0.000 claims description 3
- 238000001471 micro-filtration Methods 0.000 claims description 3
- 230000000813 microbial effect Effects 0.000 claims description 3
- 230000005855 radiation Effects 0.000 claims description 3
- 239000012209 synthetic fiber Substances 0.000 claims description 3
- 229920002994 synthetic fiber Polymers 0.000 claims description 3
- 230000009466 transformation Effects 0.000 claims description 3
- 235000011996 Calamus deerratus Nutrition 0.000 claims description 2
- 244000211187 Lepidium sativum Species 0.000 claims description 2
- 241000219991 Lythraceae Species 0.000 claims description 2
- 241000383620 Allium mongolicum Species 0.000 claims 1
- 230000008901 benefit Effects 0.000 abstract description 4
- 238000001914 filtration Methods 0.000 abstract description 4
- 244000005700 microbiome Species 0.000 abstract description 4
- 238000000354 decomposition reaction Methods 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 3
- 208000028659 discharge Diseases 0.000 description 31
- 230000008569 process Effects 0.000 description 8
- 239000010865 sewage Substances 0.000 description 6
- 239000002352 surface water Substances 0.000 description 6
- 230000008878 coupling Effects 0.000 description 5
- 238000010168 coupling process Methods 0.000 description 5
- 238000005859 coupling reaction Methods 0.000 description 5
- 238000010586 diagram Methods 0.000 description 5
- 244000052616 bacterial pathogen Species 0.000 description 4
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 3
- QBWCMBCROVPCKQ-UHFFFAOYSA-N chlorous acid Chemical compound OCl=O QBWCMBCROVPCKQ-UHFFFAOYSA-N 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000005728 strengthening Methods 0.000 description 3
- 239000000758 substrate Substances 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- 238000005660 chlorination reaction Methods 0.000 description 2
- 238000004332 deodorization Methods 0.000 description 2
- TUJKJAMUKRIRHC-UHFFFAOYSA-N hydroxyl Chemical compound [OH] TUJKJAMUKRIRHC-UHFFFAOYSA-N 0.000 description 2
- 230000001965 increasing effect Effects 0.000 description 2
- 125000004430 oxygen atom Chemical group O* 0.000 description 2
- 238000006303 photolysis reaction Methods 0.000 description 2
- 230000015843 photosynthesis, light reaction Effects 0.000 description 2
- 230000005180 public health Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 230000000630 rising effect Effects 0.000 description 2
- 235000006480 Acorus calamus Nutrition 0.000 description 1
- 244000257727 Allium fistulosum Species 0.000 description 1
- 235000008553 Allium fistulosum Nutrition 0.000 description 1
- 241001678559 COVID-19 virus Species 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 241000195493 Cryptophyta Species 0.000 description 1
- 240000005407 Nasturtium officinale Species 0.000 description 1
- 206010036790 Productive cough Diseases 0.000 description 1
- 244000143231 Scirpus validus Species 0.000 description 1
- 235000008573 Scirpus validus Nutrition 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 235000004224 Typha angustifolia Nutrition 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 239000000443 aerosol Substances 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 230000001174 ascending effect Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000007795 chemical reaction product Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 230000002349 favourable effect Effects 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 238000007667 floating Methods 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- QWPPOHNGKGFGJK-UHFFFAOYSA-N hypochlorous acid Chemical compound ClO QWPPOHNGKGFGJK-UHFFFAOYSA-N 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 208000015181 infectious disease Diseases 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 238000011081 inoculation Methods 0.000 description 1
- 230000009545 invasion Effects 0.000 description 1
- 239000012982 microporous membrane Substances 0.000 description 1
- 238000006053 organic reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000036961 partial effect Effects 0.000 description 1
- 230000001699 photocatalysis Effects 0.000 description 1
- 238000007146 photocatalysis Methods 0.000 description 1
- 238000005086 pumping Methods 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 230000002829 reductive effect Effects 0.000 description 1
- 230000035945 sensitivity Effects 0.000 description 1
- 210000003802 sputum Anatomy 0.000 description 1
- 208000024794 sputum Diseases 0.000 description 1
- 150000003568 thioethers Chemical class 0.000 description 1
- 239000010455 vermiculite Substances 0.000 description 1
- 229910052902 vermiculite Inorganic materials 0.000 description 1
- 235000019354 vermiculite Nutrition 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
- C02F1/766—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens by means of halogens other than chlorine or of halogenated compounds containing halogen other than chlorine
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F2003/001—Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
- C02F2003/003—Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms using activated carbon or the like
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/009—Apparatus with independent power supply, e.g. solar cells, windpower or fuel cells
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/23—O3
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/04—Disinfection
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/26—Reducing the size of particles, liquid droplets or bubbles, e.g. by crushing, grinding, spraying, creation of microbubbles or nanobubbles
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Physical Water Treatments (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
The invention discloses a multistage processing system for preventing and controlling river discharge port viruses and an operation method, and is characterized in that the multistage processing system consists of an oxidant supply module, an ultraviolet oxidation combined module and a biological ecological processing module, wherein the oxidant supply module is arranged near a river discharge port and used for supplying green oxidants such as hydrogen peroxide, chlorine dioxide solution, ozone and the like to the ultraviolet oxidation combined module; the ultraviolet oxidation combination module can efficiently inactivate viruses in the discharged water through the combined action of ultraviolet and various oxidants and has the functions of water quality purification and odor removal; the biological ecological treatment module realizes the advanced treatment of the outlet water through the decomposition and assimilation of microorganisms, the interception and filtration of a filter membrane and the adsorption and absorption of a plant root system. Compared with the prior art, the invention has the advantages of good environmental, ecological, social and economic benefits and the like, and realizes the aims of virus prevention and control, water quality purification and odor removal of outlet water.
Description
Technical Field
The invention relates to the technical field of municipal sewage treatment, in particular to a multistage treatment system for preventing and controlling river course discharge port viruses and an operation method.
Background
The discharge port is used as an important component of a town drainage system, plays a role in discharging rainwater to surface water or entering the surface water after being treated by a sewage treatment plant and the like, is an important part worth paying attention to the upgrading and efficiency increasing action of the drainage system, and related researches show that the outlet of a river channel is an important carrier library of microorganisms and has various human viruses and pathogenic bacteria.
The 2019-nCoV virus may have potential transmission and exposure paths from the toilet to the drain network, to the discharge, and finally into the surface water. If the wastewater carrying a large amount of viruses or pathogenic bacteria flows into surface water through the discharge port, the viruses are easily diffused to a water source and enter a drinking water treatment and supply system, and the public health and the human health are harmed. In addition, due to the fact that the discharge port falls off due to fall or has rapid outflow, splashed water easily forms aerosol, the infection risk of surrounding residents or passing pedestrians is increased, and even a super-propagation event is caused.
The main routes for live viruses to reach the discharge include: the domestic sewage generated by virus infectors enters a combined drainage pipe network, and the viruses reach a discharge port and are discharged into surface water in rainy days; the split-flow rainwater pipeline with the rain and sewage mixed connection also has the problems; third, the surface runoff entraps the surface viruses to enter a shunt rainwater pipe network; sputum, droplets, touch articles and the like generated by virus infected persons outdoors enter a rainwater port through rainwater washing, and then enter a drainage system; the deposits in the drainage pipeline provide favorable environment for virus propagation and propagation, and the deposits carrying viruses are discharged through a discharge port when released into the river in rainy days. The virus has a plurality of ways to enter a drainage pipe network, and the sources of the virus are extremely dispersed, so that the invasion and inoculation of the virus are not easy to be stopped from the sources of a drainage system. But the wastewater in the drainage network will eventually be discharged from the discharge port, compared to the terminal discharge port of the drainage system, which is more feasible for virus killing.
At present, the method for killing germs in the field of water treatment mainly comprises the following steps: ultraviolet irradiation, ozone oxidation, strong oxidant oxidation, chlorination and disinfection, etc. Considering the environmental ecological sensitivity of the discharge port and the surface water body, a treatment process combining the environment-friendly oxidants such as ozone, hydrogen peroxide, chlorine dioxide and the like without secondary pollution and ultraviolet irradiation is adopted. Relevant researches show that the combination of multiple oxidants and ultraviolet can improve the virus killing and pollutant removing efficiency in water and achieve the treatment effect which is not achieved by a single oxidant or a single ultraviolet irradiation. For example: the reaction of pure ozone with organic substances is selective and does not completely decompose the organic substances into CO2And H2O; if the ozone and ultraviolet technologies are combined, the oxidation rate and efficiency can be effectively improved.
The action principle of the ozone and ultraviolet combined water purification and deodorization is shown in the following reaction formulas (1) to (3): wherein O is3Ozone, UV ultraviolet radiation, hv photolysis, O (C), (B), (C), (1D) Represents an excited oxygen atom,. OH represents a hydroxyl radical, H2O2Hydrogen peroxide is shown.
O3+ UV (or h v, lambda < 310nm) → O2+O(1D) (1)
O(1D)+H2O→·OH+·OH→H2O2(in water) (2)
O(1D)+H2O →. OH +. OH (moist air) (3)
Wherein, O3Ozone, UV ultraviolet radiation, hv photolysis, O (C), (B), (C), (1D) Represents an excited oxygen atom,. OH represents a hydroxyl radical, H2O2Hydrogen peroxide is shown.
And the coupling strengthening effect can also be generated by combining ozone and hydrogen peroxide, and the reaction principle is shown in the following reaction formula (4):
2O3+H2O2→·OH+·OH+3O2(4)
the reaction principle of the chlorine dioxide and hydrogen peroxide can generate hypochlorous acid with strong oxidizing property, and is shown in the following reaction formula (5):
2ClO2+H2O2→2HClO2+O2(5)
the combination of hydrogen peroxide and ultraviolet also has a coupling strengthening effect, and the reaction principle is shown in the following reaction formula (6):
H2O2+ UV (or h v, lambda ≈ 200 ~ 280nm) →. OH +. OH (6)
Also, for example, chlorine dioxide solution is used in combination with UV (R represents an organic reactant, R represents*Representing an organic reaction product), the principle of action of which is shown in the following reaction formulae (7) to (8):
R+ClO2→R*+ClO2 -(7)
ClO2 -+hν(λ<300nm)→2O(1D)+Cl-(8)
therefore, if a plurality of oxidants and ultraviolet combined technology are adopted at the discharge port to remove the virus and the pollutant in the sewage, a satisfactory treatment effect can be achieved. Scholars in the related art also propose: the application of biological treatment process cannot be ignored in the field of virus prevention and control in water treatment. For example, the MBR process has obviously better virus removal rate than chlorination. In fact, the decomposition and assimilation of microorganisms, the interception and filtration of filter membranes, and the adsorption and absorption of substrates and plant roots can all effectively remove viruses in water.
In conclusion, the municipal sewage treatment mainly adopts a biomembrane process, a microporous membrane process and an ecological floating bed process, and the wastewater polluted by viruses or pathogenic bacteria is disinfected and killed by adopting ultraviolet irradiation, ozone oxidation, strong oxidant oxidation, chlorine addition and the like.
Disclosure of Invention
The invention aims to provide a multistage treatment system and an operation method for preventing and controlling river channel discharge viruses aiming at the defects of the prior art, which adopt a multistage treatment technology combining ultraviolet and oxidation with a biomembrane, and realize virus blocking, sludge removal, water quality purification and odor treatment of discharge outlet water through the combined action of oxidant oxidation, ultraviolet irradiation, photocatalysis, biomembrane, aquatic plant, microfiltration membrane and the like, thereby not only effectively realizing the virus prevention and control of discharge outlet water, but also effectively degrading various refractory organic matters in the water, oxidizing reductive odor substances such as ammonia nitrogen, sulfide and the like, and the aquatic plant can absorb various pollutants in water while beautifying the landscape.
In order to realize the purpose of the invention, the technical scheme of the invention is as follows: a multi-stage treatment system for preventing and controlling the virus at the discharge opening of a river channel is characterized by consisting of an oxidant supply module, an ultraviolet oxidation combination module and a biological ecological treatment module. Further, the oxidizer supply module includes: the device comprises an oxidant supply cabin, a liquid oxidant discharge pump, a gaseous oxidant discharge pump, a microporous aeration disc, a multifunctional probe and an electric controller; the oxidant supply cabin consists of a hydrogen peroxide storage cabin, a chlorine dioxide solution storage cabin and an ozone generator; the liquid oxidant discharge pump is connected with the hydrogen peroxide storage cabin and the chlorine dioxide solution storage cabin, and the hydrogen peroxide and the chlorine dioxide solution are conveyed to the ultraviolet oxidation combination module through the liquid oxidant conveying pipe; the gaseous oxidant discharge pump is connected with the aeration disc through a gas transmission pipe; the ultraviolet oxidation combination module consists of a linkage impeller and an ultraviolet lamp which are arranged in the reaction chamber; the top of the reaction chamber is an open horn-shaped water collecting port, a plurality of linked impellers are arranged in the reaction chamber, a barrel with a plurality of water outlet holes is arranged at the lower part of the reaction chamber, and a microporous aeration disc, a multifunctional probe and a plurality of ultraviolet lamps are arranged in the reaction chamber; the biological ecological treatment module consists of a submersible pump, an upflow water distributor and a microporous filter membrane which are arranged in the barrel body; the top of the barrel body is in an open horn shape, a millipore filter membrane and aquatic plants are arranged in the barrel body, an upflow water distributor connected with a submersible pump is arranged in the middle of the barrel body, a plurality of suspended biological balls are arranged above the upflow water distributor, and a guide cylinder is arranged at the bottom of the barrel body and connected with a water outlet hole at the lower part of the reaction chamber; the electric controller is electrically connected with the liquid oxidant discharge pump, the gaseous oxidant discharge pump, the multifunctional probe and the linkage impeller, and the ozone output of the ozone generator and the air output of the gaseous oxidant discharge pump are adjusted according to the ultraviolet irradiation intensity and the water quality condition monitored by the multifunctional probe.
The river discharge outlet water is sequentially subjected to multi-stage treatment by the oxidant supply module, the ultraviolet oxidation combination module and the biological ecological treatment module and then is discharged to a river; the oxidant supply module is arranged near the discharge port of the river channel and used for supplying a plurality of oxidants to the ultraviolet oxidation combined module; the ultraviolet oxidation combination module can efficiently inactivate viruses in the discharged water through the combined action of ultraviolet and various oxidants and has the functions of water quality purification and odor removal; biological ecological treatment module centers on ultraviolet oxidation allies oneself with module setting, and it realizes the advanced treatment of escape effluent through decomposition and assimilation of microorganism, interception and the filtering action of filter membrane, the absorption and the absorption of matrix and plant roots.
Furthermore, the biological ecological treatment modules are a plurality of and are arranged around the ultraviolet oxidation combination module.
Furthermore, the aquatic plants are arranged above the microporous filter membrane through the planting pad, and the microporous filter membrane is horizontally arranged in a bell mouth at the top of the barrel body through a fixing ring and is used for intercepting and filtering viruses and insoluble particulate matters in ascending water flow; the planting pad is fixedly arranged on the fixing ring and used for planting aquatic plants; the plant planting mat comprises a frame net, a substrate and a flow groove; the frame net is positioned above the filter membrane fixing ring and used for filling the matrix; the substrate is made of ceramsite, zeolite, vermiculite, biochar, palm fiber or felt; the flow grooves are groove-shaped, the number of the flow grooves is 3-30, the flow grooves are uniformly distributed on the upper surface of the matrix and are used for guiding the water body treated by the suspended biological balls and the microporous filter membrane into river water.
Furthermore, the suspended biological balls are arranged between the upflow water distributor and the microporous filter membrane.
Furthermore, a cleaning door for removing sludge is arranged at the bottom of the reaction chamber.
Further, the ultraviolet lamp is fixedly arranged in the reaction chamber by a lamp holder, the ultraviolet wavelength of the ultraviolet lamp is 185-254 nm, and the irradiation intensity is 10-50 mJ/cm2(ii) a The lamp holder is made of SS316L or anticorrosive alloy; the shape of the water outlet hole is circular, rectangular or rhombicArea of 10-1000 cm2。
Furthermore, the multi-stage treatment system for preventing and controlling the virus at the discharge outlet of the river channel can realize the virus prevention and control of the discharged water, the water purification and the removal of the stink by using physical, chemical, biological and ecological methods, and the specific operation comprises the following steps:
a, step a: arranging an oxidant supply module, an ultraviolet oxidation combination module and a biological ecological treatment module at a river discharge port and a water area nearby the river discharge port, and realizing the power supply of the system;
b, step (b): when the electric controller of the oxidant supply module detects that the linkage impeller of the ultraviolet oxidation combined module rotates, the liquid oxidant discharge pump starts to add hydrogen peroxide and chlorine dioxide solution to the upper part of the water collecting port of the ultraviolet oxidation combined module through the liquid oxidant conveying pipe, and meanwhile, the gaseous oxidant discharge pump supplies ozone micro bubbles to the reaction chamber of the ultraviolet oxidation combined module through the gaseous oxidant conveying pipe and the microporous aeration disc;
c, step (c): the discharged water is buffered and energy-dissipated by a linkage impeller (21) of the ultraviolet oxidation combination module (2), and after being stirred and mixed, the virus disinfection and killing and pollutant removal of the discharged water (5) are realized through the combined action of ultraviolet, hydrogen peroxide, chlorine dioxide and ozone in a reaction chamber;
d, step: the water discharged from the discharge port treated by the ultraviolet oxidation coupling module enters the barrel body of the biological ecological treatment module from a water outlet hole at the lower part of the reaction chamber through a guide cylinder, sequentially flows through the suspended biological balls, the microporous filter membrane, the plant planting pad and the aquatic plant under the lifting and water distribution effects of the submersible pump and the upflow water distributor, and deeply removes viruses and pollutants in water through the comprehensive effects of microbial transformation, filter membrane interception, matrix adsorption and plant absorption.
Further, the pumping flow rates of the hydrogen peroxide solution and the chlorine dioxide solution from the liquid oxidant discharge pump are both 10-100L/m3And the fullness degree of the hydrogen peroxide storage cabin and the chlorine dioxide solution storage cabin is more than or equal to 20 percent; the purity of the hydrogen peroxide is 20-80%, and the concentration of the chlorine dioxide solution is 50-500 mg/L; the gaseous oxidant discharge pumpThe pressure of the gas is 1.5-10 atm, and the ozone concentration is 1-10 mg/L.
Further, the flow rate of the submersible pump is 5-50 m3The delivery lift is 1-5 m; the suspended biological ball is made of PE, PP or synthetic fiber, and the density rho of the suspended biological ball is 1g/cm2(ii) a The aquatic plant species comprise cattail, calamus, allium fistulosum, loosestrife, water spinach or cress, and the planting density is 10-30 plants/m2。
Further, the water quality of the water body monitored by the multifunctional probe comprises: dissolved oxygen, redox sites, pH, turbidity, temperature, total organic carbon, ammonia nitrogen and reducing sulfides.
Furthermore, the number of the linkage impellers is 1-10, and hubs of the linkage impellers are connected with a rotating shaft of the generator and used for converting partial kinetic energy of rotation of the impellers into electric energy so as to assist the power supply of the system.
Further, the bottom of the reaction chamber is provided with a cleaning and drawing door for removing sludge, the cleaning and drawing door is closed at ordinary times and is opened periodically to clean and draw impurities such as sludge, the cleaning and drawing door is rectangular in shape and 20-2000 cm in area2The frequency of opening the cleaning is 1-5 times/month.
Compared with the prior art, the invention has the following advantages:
1) high applicability
Through reasonable collocation and layout of the oxidant supply module, the ultraviolet oxidation combination module and the biological ecological treatment module in the receiving water body, the requirements of omnibearing, deep and high-efficiency virus prevention and control and water environment improvement of different types of river channel discharge openings can be met.
2) Fast and efficient
The multi-stage treatment system formed by the modules has a more rapid and efficient treatment effect than a single process, and the removal rate of viruses and pollutants is guaranteed in an all-round, multi-level and deep manner in the treatment process of the river discharge outlet water in the multi-stage treatment modules.
3) Multiple functions
The method has the functions of quickly killing the virus at the discharge port of the river channel, deeply removing ammonia nitrogen and refractory organic matters, improving the hydraulic circulation condition of the river channel, strengthening the self-cleaning capacity of the water body, inhibiting the growth of algae, improving the aesthetic value of landscape and the like.
4) Flexible operation
All modules of the system can run jointly to achieve the effect of multi-stage treatment of the water discharged from the discharge port of the river channel; other modules can be independently operated when a certain module is stopped to be maintained so as to ensure the effects of disinfection, water purification and deodorization of outlet water under special conditions.
5) High comprehensive profit
The method can effectively block the virus transmission way at the tail end of the urban drainage system, ensure and maintain public health and ecological system safety, improve water environment quality, and improve the human water affinity degree, thereby generating good environmental, ecological, social and economic benefits.
Drawings
FIG. 1 is a schematic diagram of a multi-stage processing system according to the present invention;
FIG. 2 is a schematic diagram of an oxidant supply module;
FIG. 3 is a schematic structural diagram of a UV oxidation coupling module;
FIG. 4 is a schematic structural diagram of a biological ecological treatment module;
FIG. 5 is a schematic diagram of a multi-stage processing system according to the present invention;
fig. 6 is a top plan view of fig. 5.
Detailed Description
Referring to the attached figure 1, the invention is composed of an oxidant supply module 1, an ultraviolet oxidation combination module 2 and a biological ecological treatment module 3, wherein the oxidant supply module 1 comprises: the system comprises an oxidant supply cabin 11, a liquid oxidant discharge pump 12, a gaseous oxidant discharge pump 14, a microporous aeration disc 16, a multifunctional probe 17 and an electric controller 18; the microporous aeration disc 16 and the multifunctional probe 17 are arranged in a reaction chamber 23 of the ultraviolet oxidation combined module 2; the electric controller 18 is electrically connected with the liquid oxidant discharge pump 12, the gaseous oxidant discharge pump 14, the multifunctional probe 17 and the linkage impeller 21, and the ozone output of the ozone generator 113 and the air output of the gaseous oxidant discharge pump 14 are adjusted according to the ultraviolet irradiation intensity and the water quality condition monitored by the multifunctional probe 17.
Referring to fig. 2, the oxidant supply compartment 11 is composed of a hydrogen peroxide storage compartment 111, a chlorine dioxide solution storage compartment 112 and an ozone generator 113; the liquid oxidant discharge pump 12 is connected with a hydrogen peroxide storage cabin 111 and a chlorine dioxide solution storage cabin 112, and hydrogen peroxide and the chlorine dioxide solution are conveyed to the ultraviolet oxidation combination module 2 through a liquid oxidant conveying pipe 13; the gaseous oxidant discharge pump 14 is connected with the aeration disc 16 through a gas pipe.
Referring to fig. 3, the ultraviolet oxidation module 2 is composed of a linkage impeller 21 and an ultraviolet lamp 24 which are arranged in a reaction chamber 23; the top of the reaction chamber 23 is provided with an open horn-shaped water collecting port 22, a plurality of linked impellers 21 are arranged in the reaction chamber, the lower part of the reaction chamber is provided with a barrel with a plurality of water outlet holes 25, and a microporous aeration disc 16, a multifunctional probe 17 and a plurality of ultraviolet lamps 24 are arranged in the reaction chamber; the bottom of the reaction chamber 23 is provided with a cleaning door 27 for removing sludge.
Referring to fig. 4, the bio-ecological treatment module 3 is composed of a submersible pump 33, an upflow water distributor 34 and a microporous filter membrane 36 which are arranged in a barrel 32; the top of the barrel body 32 is in an open horn shape, a millipore filter 36 and aquatic plants 39 are arranged in the barrel body, an upflow water distributor 34 connected with a submersible pump 33 is arranged in the middle of the barrel body 32, a plurality of suspended biological balls 35 are arranged above the upflow water distributor, and a guide cylinder 31 arranged at the bottom of the barrel body 32 is connected with a water outlet 25 at the lower part of the reaction chamber 23; the aquatic plants 39 are arranged above the microporous filter membrane 36 through a planting pad 38, and the microporous filter membrane 36 is horizontally arranged in a bell mouth at the top of the barrel body 32 through a fixing ring 37; the planting mat 38 is fixedly arranged on the fixing ring 37; the suspended biological balls 35 are arranged between the upflow water distributor 34 and the microporous filter membrane 36.
The upflow water distributor 34 is horizontally arranged in the barrel body 32, and the edge of the upflow water distributor is clamped with a rotary groove of a wheel disc arranged on the inner wall of the barrel body 32; the rising water distributor 34 is provided with water receiving holes and water distributing holes, the water receiving holes are single, the openings of the water receiving holes are downward and are arranged in the center of the rising water distributor 34 for collecting the water flow lifted by the lifting pump; the number of the water distribution holes is 5-50, the openings of the water distribution holes are upward and uniformly distributed in the upflow water distributor 34, and the water distribution holes are used for uniformly distributing water flow guided by the water receiving holes upward; the motor is linked with the upflow water distributor and drives the upflow water distributor to rotate, and the rotation rate of the upflow water distributor is 0.2-10 r/min; the upflow water distributor is provided with a water tank for communicating the water receiving hole and the water distribution hole.
The operation of the present invention will be further described in detail with reference to the following specific examples.
Example 1
Referring to the attached drawings 5-6, the invention realizes the virus prevention and control of the outlet water of the discharge port, the water quality purification and the odor removal by using physical, chemical, biological and ecological methods, and the specific operation comprises the following steps:
a, step a: arranging an oxidant supply module 1, an ultraviolet oxidation combined module 2 and a biological ecological treatment module 3 at a river discharge port 4 of a revetment 7 and a water area nearby the river discharge port, and realizing the power supply of the system, wherein the biological ecological treatment modules 3 are three modules which are arranged around the ultraviolet oxidation combined module 2 and are fixedly arranged on a river bottom 9 together with the ultraviolet oxidation combined module 2; the oxidant supply module 1 is arranged near the river discharge port 4 and used for supplying green oxidants such as hydrogen peroxide, chlorine dioxide solution and ozone to the ultraviolet oxidation combined module 2. The effluent 5 from the discharge outlet and the hydrogen peroxide and chlorine dioxide solution output by the oxidant supply module 1 flow into the water collecting port 22 of the ultraviolet oxidation combined module 2, and the flow rates of the hydrogen peroxide and the chlorine dioxide solution of the oxidant supply module 1 are both 10-100L/m3And the fullness degree of more than or equal to 20 percent is ensured; the purity of the hydrogen peroxide is 20-80%, and the concentration of the chlorine dioxide solution is 50-500 mg/L; the pressure of the gas pumped out by the gaseous oxidant discharge pump 14 is 1.5-10 atm, and the ozone concentration is 1-10 mg/L.
b, step (b): when the electric controller 18 of the oxidant supply module 1 detects that the linkage impeller 21 of the ultraviolet oxidation combined module 2 rotates, the liquid oxidant discharge pump 12 starts to add hydrogen peroxide and chlorine dioxide solution to the upper part of the water collecting port 22 of the ultraviolet oxidation combined module 2 through the liquid oxidant conveying pipe 13, and meanwhile, the gaseous oxidant discharge pump 14 supplies ozone microbubbles to the reaction chamber 23 of the ultraviolet oxidation combined module 2 through the gaseous oxidant conveying pipe 15 and the microporous aeration disc 16; the ultraviolet lamp 24 is fixed in the reaction chamber 23 by a lamp holder and has an ultraviolet wavelength185-254 nm, and the irradiation intensity is 10-50 mJ/cm2。
c, step (c): the water 5 discharged from the discharge port is buffered and energy-dissipated by the linked impeller 21 at the water collecting port 2, is stirred and mixed with hydrogen peroxide and chlorine dioxide solution and then enters the reaction chamber 23, and virus disinfection and killing and pollutant removal of the water 5 discharged from the discharge port are realized through the combined action of ultraviolet, hydrogen peroxide, chlorine dioxide and ozone.
d, step: the water 5 discharged from the discharge port treated by the ultraviolet oxidation coupling module 2 flows from a water outlet 25 at the lower part of the reaction chamber 23, the water flow 8 enters a barrel body 32 of the biological ecological treatment module 3 through a guide cylinder 31, and sequentially flows through a suspended biological ball 35, a microporous filter membrane 36, a plant planting pad 38 and an aquatic plant 39 under the lifting and water distribution effects of a submersible pump 33 and an upflow water distributor 34, so that viruses and pollutants in water are deeply removed through the comprehensive actions of microbial transformation, filter membrane interception, matrix adsorption and plant absorption; the flow rate of the submersible pump 33 is 5-50 m3The delivery lift is 1-5 m; the suspended biological ball 35 is made of PE, PP or synthetic fiber, and the density rho of the suspended biological ball is 1g/cm2(ii) a The aquatic plant 39 is selected from Typha angustifolia, Acorus calamus, Scirpus tabernaemontani, Lythra serpentinatum, water spinach or water cress, and has a planting density of 10-30 plants/m2。
And the outlet water 5 is discharged to the water surface of the river after being sequentially subjected to multistage treatment by the oxidant supply module 1, the ultraviolet oxidation combination module 2 and the biological ecological treatment module 3. The invention fully utilizes the water area space of the receiving water body, comprehensively utilizes physical, chemical, biological and ecological methods through the exquisite design and the multi-stage collocation of each functional module, and realizes the aims of virus prevention and control, water quality purification and odor removal of the outlet water of the discharge port. The above embodiments are only for further illustration of the present invention and are not intended to limit the present invention, and all equivalent implementations of the present invention should be included in the scope of the claims of the present invention.
Claims (9)
1. A multi-stage processing system for river course row mouth virus prevention and control, characterized in that this multi-stage processing system comprises oxidant supply module (1), ultraviolet oxidation allies oneself with module (2) and biological ecological treatment module (3), oxidant supply module (1) includes: an oxidant supply cabin (11), a liquid oxidant discharge pump (12), a gaseous oxidant discharge pump (14), a microporous aeration disc (16), a multifunctional probe (17) and an electric controller (18); the oxidant supply cabin (11) consists of a hydrogen peroxide storage cabin (111), a chlorine dioxide solution storage cabin (112) and an ozone generator (113); the liquid oxidant discharge pump (12) is connected with the hydrogen peroxide storage cabin (111) and the chlorine dioxide solution storage cabin (112), and the hydrogen peroxide and the chlorine dioxide solution are conveyed to the ultraviolet oxidation combination module (2) through the liquid oxidant conveying pipe (13); the gaseous oxidant discharge pump (14) is connected with the aeration disc (16) through a gas transmission pipe; the ultraviolet oxidation combined module (2) consists of a linkage impeller (21) and an ultraviolet lamp (24) which are arranged in a reaction chamber (23); the top of the reaction chamber (23) is provided with an open horn-shaped water collecting opening (22) in which a plurality of linked impellers (21) are arranged, the lower part of the reaction chamber is provided with a barrel provided with a plurality of water outlet holes (25), and a microporous aeration disc (16), a multifunctional probe (17) and a plurality of ultraviolet lamps (24) are arranged in the reaction chamber; the biological ecological treatment module (3) consists of a submersible pump (33), an upflow water distributor (34) and a microporous filter membrane (36) which are arranged in a barrel body (32); the top of the barrel body (32) is in an open horn shape, a microporous filter membrane (36) and aquatic plants (39) are arranged in the barrel body, an upflow water distributor (34) connected with a submersible pump (33) is arranged in the middle of the barrel body (32), a plurality of suspended biological balls (35) are arranged above the upflow water distributor, and a guide cylinder (31) is arranged at the bottom of the barrel body (32) and connected with a water outlet (25) at the lower part of the reaction chamber (23); the electric controller (18) is electrically connected with the liquid oxidant discharge pump (12), the gaseous oxidant discharge pump (14), the multifunctional probe (17) and the linkage impeller (21), and the ozone yield of the ozone generator (113) and the gas discharge amount of the gaseous oxidant discharge pump (14) are adjusted according to the ultraviolet radiation intensity and the water quality condition monitored by the multifunctional probe (17).
2. The multistage treatment system for preventing and controlling the virus at the drainage port of the river channel according to claim 1, wherein the number of the biological ecological treatment modules (3) is several, and the biological ecological treatment modules are arranged around the ultraviolet oxidation combined module (2).
3. The multi-stage treatment system for prevention and control of viruses at the discharge opening of a river channel according to claim 1, wherein the aquatic plants (39) are arranged above the microfiltration membrane (36) by a planting pad (38), and the microfiltration membrane (36) is horizontally arranged in a bell mouth at the top of the barrel body (32) by a fixing ring (37); the planting mat (38) is fixedly arranged on the fixing ring (37).
4. The multistage treatment system for preventing and controlling the virus at the drainage port of the river channel according to claim 1, wherein the suspended biological balls (35) are arranged between the upflow water distributor (34) and the microporous filter membrane (36).
5. The multistage treatment system for virus prevention and control of river discharge according to claim 1, wherein the bottom of the reaction chamber (23) is provided with a cleaning door (27) for removing sludge.
6. The multistage treatment system for preventing and controlling the virus at the drain outlet of the river channel according to claim 1, wherein the ultraviolet lamp (24) is fixedly arranged in the reaction chamber (23) by a lamp holder, the ultraviolet wavelength is 185-254 nm, and the irradiation intensity is 10-50 mJ/cm2。
7. The operation method of the multistage treatment system for preventing and controlling the virus at the drainage port of the river channel of claim 1 is characterized in that the multistage treatment system realizes the virus prevention and control of the drainage outlet water and the purification of water quality and the removal of foul smell by using physical, chemical, biological and ecological methods, and the specific operation comprises the following steps:
a, step a: arranging an oxidant supply module (1), an ultraviolet oxidation combined module (2) and a biological ecological treatment module (3) at a river discharge port (4) and a water area nearby the river discharge port, and realizing the power supply of the system;
b, step (b): when an electric controller (18) of an oxidant supply module (1) detects that a linkage impeller (21) of an ultraviolet oxidation combination module (2) rotates, a liquid oxidant discharge pump (12) starts to add hydrogen peroxide and chlorine dioxide solution above a water collecting port (22) of the ultraviolet oxidation combination module (2) through a liquid oxidant conveying pipe (13), and meanwhile, a gaseous oxidant discharge pump (14) supplies ozone microbubbles to a reaction chamber (23) of the ultraviolet oxidation combination module (2) through a gaseous oxidant conveying pipe (15) and a microporous aeration disc (16);
c, step (c): the discharged water (5) is buffered and energy-dissipated by a linkage impeller (21) of the ultraviolet oxidation combination module (2), and after being stirred and mixed, the virus disinfection and killing and pollutant removal of the discharged water (5) are realized through the combined action of ultraviolet, hydrogen peroxide, chlorine dioxide and ozone in a reaction chamber (23);
d, step: the water (5) discharged from the discharge port treated by the ultraviolet oxidation combination module (2) enters a barrel body (32) of the biological ecological treatment module (3) from a water outlet hole (25) at the lower part of the reaction chamber (23) through a guide cylinder (31), sequentially flows through suspended biological balls (35), a microporous filter membrane (36), a plant planting pad (38) and aquatic plants (39) under the lifting and water distribution effects of a submersible pump (33) and an upflow water distributor (34), and viruses and pollutants in water are deeply removed through the comprehensive actions of microbial transformation, filter membrane interception, matrix adsorption and plant absorption.
8. The treatment method of the multilevel processing system for preventing and controlling the river course discharge port virus according to claim 7, wherein the flow rates of the hydrogen peroxide solution and the chlorine dioxide solution of the oxidant supply module (1) are both 10-100L/m3And the fullness degree of more than or equal to 20 percent is ensured; the purity of the hydrogen peroxide is 20-80%, and the concentration of the chlorine dioxide solution is 50-500 mg/L; the pressure of the gas pumped out by the gaseous oxidant discharge pump (14) is 1.5-10 atm, and the ozone concentration is 1-10 mg/L.
9. The treatment method of the multistage treatment system for preventing and controlling the virus at the drainage port of the river channel according to claim 7, wherein the flow rate of the submersible pump (33) is 5-50 m3/h,The lift is 1-5 m; the suspended biological ball (35) is made of PE, PP or synthetic fiber with densityρ=1g/cm2(ii) a The aquatic plant (39) comprises cattail, calamus, allium mongolicum regel, loosestrife, water spinach or cress, and the planting density is 10-30 plants/m2。
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010393318.6A CN111606468B (en) | 2020-05-11 | 2020-05-11 | Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202010393318.6A CN111606468B (en) | 2020-05-11 | 2020-05-11 | Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method |
Publications (2)
Publication Number | Publication Date |
---|---|
CN111606468A true CN111606468A (en) | 2020-09-01 |
CN111606468B CN111606468B (en) | 2021-01-01 |
Family
ID=72204472
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202010393318.6A Active CN111606468B (en) | 2020-05-11 | 2020-05-11 | Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN111606468B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN114177757A (en) * | 2021-12-10 | 2022-03-15 | 中冶华天工程技术有限公司 | Municipal discharge port aerosol germ killing and foul gas collecting and removing device and method |
CN115259277A (en) * | 2022-08-16 | 2022-11-01 | 同济大学 | Device for discharging oral viruses, malodors and new pollutants |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100597072B1 (en) * | 2006-04-13 | 2006-07-04 | 주식회사 건화엔지니어링 | Sterilizer system for sewage using minute bubble and ultraviolet rays |
EP2436651A1 (en) * | 2010-09-30 | 2012-04-04 | Krones AG | Method and production assembly for manufacturing sterile water |
CN106745486A (en) * | 2017-01-19 | 2017-05-31 | 中南民族大学 | Light-catalyzed reaction purifier |
CN107857406A (en) * | 2017-11-27 | 2018-03-30 | 哈尔滨工业大学水资源国家工程研究中心有限公司 | A kind of Integral water purifying device and its application method of the ultrafiltration of ultraviolet catalytic oxidization combination |
CN209260850U (en) * | 2018-11-09 | 2019-08-16 | 润生环境科技(广州)有限公司扬州分公司 | A kind of riverbank discharge outlet sewage disposal system |
CN110436705A (en) * | 2019-07-31 | 2019-11-12 | 安徽环境科技集团股份有限公司 | A kind of reduction dispersion sewage draining exit is polluted into river device |
CN210367306U (en) * | 2019-07-22 | 2020-04-21 | 青岛科尔特水处理设备有限公司 | Sterilization device for water treatment |
-
2020
- 2020-05-11 CN CN202010393318.6A patent/CN111606468B/en active Active
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100597072B1 (en) * | 2006-04-13 | 2006-07-04 | 주식회사 건화엔지니어링 | Sterilizer system for sewage using minute bubble and ultraviolet rays |
EP2436651A1 (en) * | 2010-09-30 | 2012-04-04 | Krones AG | Method and production assembly for manufacturing sterile water |
CN106745486A (en) * | 2017-01-19 | 2017-05-31 | 中南民族大学 | Light-catalyzed reaction purifier |
CN107857406A (en) * | 2017-11-27 | 2018-03-30 | 哈尔滨工业大学水资源国家工程研究中心有限公司 | A kind of Integral water purifying device and its application method of the ultrafiltration of ultraviolet catalytic oxidization combination |
CN209260850U (en) * | 2018-11-09 | 2019-08-16 | 润生环境科技(广州)有限公司扬州分公司 | A kind of riverbank discharge outlet sewage disposal system |
CN210367306U (en) * | 2019-07-22 | 2020-04-21 | 青岛科尔特水处理设备有限公司 | Sterilization device for water treatment |
CN110436705A (en) * | 2019-07-31 | 2019-11-12 | 安徽环境科技集团股份有限公司 | A kind of reduction dispersion sewage draining exit is polluted into river device |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN114177757A (en) * | 2021-12-10 | 2022-03-15 | 中冶华天工程技术有限公司 | Municipal discharge port aerosol germ killing and foul gas collecting and removing device and method |
CN114177757B (en) * | 2021-12-10 | 2023-11-17 | 中冶华天工程技术有限公司 | Municipal exhaust aerosol germ killing and malodorous gas collecting and removing device and method |
CN115259277A (en) * | 2022-08-16 | 2022-11-01 | 同济大学 | Device for discharging oral viruses, malodors and new pollutants |
CN115259277B (en) * | 2022-08-16 | 2023-05-30 | 同济大学 | Device for purifying sewage outlet virus, malodor and emerging pollutants |
Also Published As
Publication number | Publication date |
---|---|
CN111606468B (en) | 2021-01-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106554129A (en) | Integral synchronous nitration denitrification sewage-treatment plant | |
CN106430847B (en) | Intensive pig raising wastewater treatment equipment | |
CN106554131A (en) | Integrated preposition denitrification sewage-treatment plant | |
CN111533340B (en) | Closed treatment device for virus prevention and control and water purification and deodorization of pipe network discharge port | |
CN111606468B (en) | Multi-stage processing system for preventing and controlling river channel discharge port viruses and operation method | |
JP2007185615A (en) | Water supply system and pump | |
CN109809642B (en) | Working method of multistage aerobic treatment rural household sewage modification purifying tank | |
KR200449463Y1 (en) | Floating water purification device of advanced oxidation process using solar energy | |
CN205368041U (en) | Ultraviolet -ozone catalytic oxidation wastewater treatment device | |
CN111592174B (en) | Discharge port purification system and purification method | |
CN104276722B (en) | Tail water carries mark system | |
CN101985380B (en) | Micro-polluted water treatment device | |
CN205953659U (en) | Bury formula deodorization and purify towards lavatory sewage treatment groove | |
CN1300020C (en) | Domestic sewage deeply treating process | |
CN102126809A (en) | Ozone-biological activated carbon water purification method and device | |
CN203256097U (en) | Ozone micron bubble-high density biological membrane filter device | |
CN214612084U (en) | Ozone contact oxidation pond for treating industrial wastewater in chemical industry park | |
CN210393863U (en) | Aquaculture wastewater ozone treatment equipment | |
CN111533341B (en) | Closed treatment method for virus prevention and control and water purification and deodorization of pipe network discharge port | |
CN111533378B (en) | Combined purification method suitable for pathogen control of discharge port | |
CN205442974U (en) | Membrane bioreaction device | |
CN111606470B (en) | Discharge port disinfection device combining multi-element oxidant and ultraviolet | |
CN212440656U (en) | Industrial sewage and waste gas treatment equipment | |
CN203890189U (en) | Sewage recovery treatment device | |
CN207330485U (en) | A kind of UV photocatalysis and ozones reaction tank |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |