CN203625123U - Sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from two ends of device - Google Patents
Sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from two ends of device Download PDFInfo
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- CN203625123U CN203625123U CN201320394752.1U CN201320394752U CN203625123U CN 203625123 U CN203625123 U CN 203625123U CN 201320394752 U CN201320394752 U CN 201320394752U CN 203625123 U CN203625123 U CN 203625123U
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- inlet
- outlet
- water
- carbon
- reactor body
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 49
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 title claims abstract description 35
- 229910052799 carbon Inorganic materials 0.000 title claims abstract description 35
- 239000010865 sewage Substances 0.000 title abstract description 12
- 238000012545 processing Methods 0.000 title abstract description 8
- 238000007599 discharging Methods 0.000 title abstract 3
- 238000005273 aeration Methods 0.000 claims abstract description 11
- 239000000945 filler Substances 0.000 claims abstract description 7
- 238000012856 packing Methods 0.000 claims description 17
- 239000002699 waste material Substances 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 3
- 230000000813 microbial effect Effects 0.000 claims description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 18
- 238000000034 method Methods 0.000 abstract description 12
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 9
- 230000000694 effects Effects 0.000 abstract description 5
- 238000003756 stirring Methods 0.000 abstract description 5
- 238000004062 sedimentation Methods 0.000 abstract 2
- 238000001914 filtration Methods 0.000 abstract 1
- 238000006243 chemical reaction Methods 0.000 description 5
- 239000003245 coal Substances 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 238000007254 oxidation reaction Methods 0.000 description 4
- 238000011160 research Methods 0.000 description 4
- 239000010802 sludge Substances 0.000 description 3
- 206010002660 Anoxia Diseases 0.000 description 2
- 241000976983 Anoxia Species 0.000 description 2
- 206010021143 Hypoxia Diseases 0.000 description 2
- IPQVRLSXWJPESU-UHFFFAOYSA-N [N].ON=O Chemical compound [N].ON=O IPQVRLSXWJPESU-UHFFFAOYSA-N 0.000 description 2
- 230000007953 anoxia Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 238000012851 eutrophication Methods 0.000 description 2
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 description 2
- 230000002045 lasting effect Effects 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 1
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention discloses a sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from the two ends of the device. The sewage processing device comprises a reactor body, a water in-and-out system arranged on the reactor body, aeration devices, and a control system; the inner of the reactor body is divided into a plurality of cells through guide plates, the cells in the leftmost end and the rightmost end are sedimentation tanks provided with a filler filtering device, a stirring device is arranged under the sedimentation tanks, and the rest cells are aeration tanks; the bottom of each cell is provided with an aeration device, the water in-and-out system, the aeration devices, and the stirring device are all connected to the control system; and the first inlet/outlet and the second inlet/outlet of the water in-and-out system alternately complete the periodical water exchanging through introducing water into the device and discharging water out of the device. The sewage processing device has the advantages that: the device can be used to remove carbon and nitrogen from the sewage, which is generated during the process of denitrification of raw water carbon source; the water inlet end can store a large amount of organic matters which can be taken as the carbon source for the denitrification of nitric nitrogen which flows into the device in a reverse direction in the latter half period, thus the total nitrogen is removed, and the denitrogenation effect is maximally improved.
Description
Technical field
The utility model relate to one have storage the denitrifying two ends of carbon replace Inlet and outlet water waste disposal plant, belong to sewage treatment area.
Background technology
Nitrogen is a very important pollution factor that causes body eutrophication and environmental pollution.Denitrogenation is a link very important in sewage treatment process.Traditional biological denitrification process, is first under aerobic condition, and ammonia nitrogen is oxidized to nitrous acid nitrogen by Nitrosomas, and then nitrous acid nitrogen is further oxidized to nitrate nitrogen by Nitromonas.Under anoxia condition, nitrogen as nitrate or nitrite is reduced into gaseous nitrogen by denitrifying bacteria subsequently.
Biological denitrification needs organic carbon source as electron donor, and along with environmental pollution and eutrophication problem constantly increase the weight of, for the processing of some nitrogenous effluents, carbon source deficiency is the subject matter that affects denitrification effect.Carbon source used generally has three classes: additional carbon, raw waste water carbon source and internal carbon source.Because the organic loading of municipal effluent is generally not high, therefore utilize the general TN clearance of Prepositive denitrification technique of former water carbon source not high.If further improve nitric efficiency, need additional carbon to carry out denitrification.
Nearest research is found, in biological denitrificaion process, bioenergy is internal carbon source by most of solvability substrate conversion, be stored in cell with internal carbon source (being mainly PHB form), in the situation that anoxia condition there is no additional carbon, the polymkeric substance storing can be served as electron donor, and denitrification process is carried out smoothly, improves the denitrification effect of system.Therefore, the denitrifying research carried out of internal carbon source storing for matrix is valuable, and less for the denitrogenation research directly storing by carbon source in Sludge System in research both at home and abroad, and substantially without the application of Practical Project.
Summary of the invention
For the problem that affect denitrification effect in conventional treatment process because carbon source is not enough, the utility model proposes one and there are the denitrifying two ends of carbon of storage and replace Inlet and outlet water waste disposal plant.
Described in the utility model have storage the denitrifying two ends of carbon replace Inlet and outlet water waste disposal plant, it is characterized in that: comprise reactor body, be arranged on inlet and outlet system, aerating apparatus and Controlling System on reactor body, the inside of described reactor body is divided into some cells by flow deflector, wherein the cell of high order end and low order end is the settling tank with packing filter device, and whipping appts is set below settling tank, remaining cell is aeration tank; The bottom of each described cell is all furnished with aerating apparatus, described inlet and outlet system, described aerating apparatus and described whipping appts are all connected with described Controlling System, and the first inlet/outlet of described inlet and outlet system and the second inlet/outlet alternately complete into the periodicity of water and water outlet and exchange.
The first inlet/outlet of described inlet and outlet system, the second described inlet/outlet are separately positioned on high order end and the low order end of described reactor body.
Described flow deflector is evenly distributed from left to right along reactor body, and the aperture position of flow deflector described in adjacent two staggers.
In packing filter device in described settling tank, be provided with filler and with microbial film, and storage carbon source is housed in described packing filter device.
Biologic packing material in described filler filter tank is haydite or plastic hoop.
The lasting time in each cycle is adjusted according to processing water water quality.
Working process: first by active sludge injecting reactor main body, then open treatment unit, the intake-outlet of Controlling System control inlet and outlet system periodically exchanges, the front semi-period: left end the first inlet/outlet water inlet, right-hand member the second inlet/outlet water outlet, through the settling tank of high order end, in former water, large amount of organic is adsorbed and is stored in in biomembranous packing filter device, the whipping appts in aerating apparatus and left side starts, the settling tank in left side becomes reaction zone, sewage is the settling tank through stirring successively, aeration tank completes oxidation of coal and nitrated, standing settling tank bottom settlings, right-hand member settling tank completes denitrification and filters water outlet, the later half cycle: right-hand member the second inlet/outlet water inlet, left end the first inlet/outlet water outlet, through the settling tank of low order end, in former water, large amount of organic is adsorbed and is stored in in biomembranous packing filter device, the whipping appts on aerating apparatus and right side starts, right side settling tank becomes reaction zone, settling tank bottom through stirring, aeration tank complete oxidation of coal and nitrated, standing settling tank bottom is precipitated, the settling tank of left end completes denitrification and filters water outlet, thereby realizing inversed baffled process to sewage successively again.
The beneficial effects of the utility model are: realize former water carbon source for the processing of denitrifying sewage carbon and nitrogen removal, carrier biofilm in feed-water end packing filter device can store the nitric nitrogen that organism a large amount of in former water goes out as later half cycle reverse direction flow and complete denitrifying carbon source, realize the removal of total nitrogen, farthest improve denitrification effect, and in whole process without returned sluge.
Accompanying drawing explanation
Fig. 1 be structural representation of the present utility model (the front semi-period: left end the first inlet/outlet water inlet, right-hand member the second inlet/outlet water outlet, arrow represent effluent stream to; 5 represent bubble).
Fig. 2 is structural representation of the present utility model (the later half cycle: right-hand member the second inlet/outlet water inlet, left end the first inlet/outlet water outlet).
Embodiment
Further illustrate the utility model below in conjunction with accompanying drawing
With reference to accompanying drawing:
Described in the utility model have the storage denitrifying two ends of a carbon waste disposal plant of alternately intaking, comprise reactor body 1, be arranged on inlet and outlet system 2, aerating apparatus 3 and Controlling System on reactor body, the inside of described reactor body 1 is divided into some cells 11 by flow deflector 12, wherein the cell of high order end and low order end is the settling tank 111 with packing filter device 1111, and whipping appts 13 is set below settling tank 111, remaining cell is aeration tank 112; The bottom of each described cell is all furnished with aerating apparatus 3, described inlet and outlet system 2, described aerating apparatus 3 and described whipping appts 13 are all connected with described Controlling System, and the first inlet/outlet 21 of described inlet and outlet system and the second inlet/outlet 22 alternately complete into the periodicity of water and water outlet and exchange.
The first inlet/outlet 21 of described inlet and outlet system 2, the second described inlet/outlet 22 are separately positioned on high order end and the low order end of described reactor body 1.
Described flow deflector 12 is evenly distributed from left to right along reactor body 1, and the aperture position of flow deflector 12 described in adjacent two staggers.
In packing filter device 1111 in described settling tank 111, be provided with filler and with microbial film, and storage carbon source is housed in described packing filter device.
Biologic packing material in described filler filter tank 111 is haydite or plastic hoop.
The lasting time in each cycle is adjusted according to processing water water quality.
Working process: first by active sludge 4 injecting reactor main bodys 1, then open treatment unit, the intake-outlet of Controlling System control inlet and outlet system 2 periodically exchanges, the front semi-period: left end the first inlet/outlet 21 is intake, right-hand member the second inlet/outlet 22 water outlets, through the settling tank 111 of high order end, in former water, large amount of organic is adsorbed and is stored in in biomembranous packing filter device 1111, the whipping appts 13 in aerating apparatus 3 and left side starts, the settling tank 111 in left side becomes reaction zone, sewage is the settling tank 111 through stirring successively, aeration tank 112 completes oxidation of coal and nitrated, standing settling tank 111 bottom settlingss, right-hand member settling tank 111 completes denitrification and filters water outlet, the later half cycle: right-hand member the second inlet/outlet 22 is intake, left end the first inlet/outlet 21 water outlets, through the settling tank 111 of low order end, in former water, large amount of organic is adsorbed and is stored in in biomembranous packing filter device 1111, the whipping appts 13 on aerating apparatus 3 and right side starts, right side settling tank becomes reaction zone, sewage completes oxidation of coal through settling tank 111 bottoms, the aeration tank 112 stirred successively again and nitrated, standing settling tank 111 bottoms are precipitated, the settling tank 111 of left end completes denitrification and filter water outlet, thereby realize inversed baffled process.
Content described in this specification sheets embodiment is only enumerating of way of realization to utility model design; protection domain of the present utility model should not be regarded as only limiting to the specific form that embodiment states, protection domain of the present utility model also comprises that those skilled in the art conceive the equivalent technologies means that can expect according to the utility model.
Claims (5)
1. there are the storage denitrifying two ends of carbon and replace Inlet and outlet water waste disposal plant, it is characterized in that: comprise reactor body, be arranged on inlet and outlet system, aerating apparatus and Controlling System on reactor body, the inside of described reactor body is divided into some cells by flow deflector, wherein the cell of high order end and low order end is the settling tank with packing filter device, and whipping appts is set below settling tank, remaining cell is aeration tank; The bottom of each described cell is all furnished with aerating apparatus, described inlet and outlet system, described aerating apparatus and described whipping appts are all connected with described Controlling System, and the first inlet/outlet of described inlet and outlet system and the second inlet/outlet alternately complete into the periodicity of water and water outlet and exchange.
2. as claimed in claim 1 have the storage denitrifying two ends of carbon and replace Inlet and outlet water waste disposal plant, it is characterized in that: the first inlet/outlet of described inlet and outlet system, the second described inlet/outlet are separately positioned on high order end and the low order end of described reactor body.
3. as claimed in claim 2 have the storage denitrifying two ends of carbon and replace Inlet and outlet water waste disposal plant, it is characterized in that: described flow deflector is evenly distributed from left to right along reactor body, and the aperture position of flow deflector described in adjacent two staggers.
As claimed in claim 3 have storage the denitrifying two ends of carbon replace Inlet and outlet water waste disposal plant, it is characterized in that: in the packing filter device in described settling tank, be provided with filler and with microbial film, and storage carbon source is housed in described packing filter device.
As claimed in claim 4 have storage the denitrifying two ends of carbon replace Inlet and outlet water waste disposal plant, it is characterized in that: the biologic packing material in described filler filter tank is haydite or plastic hoop.
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CN201320394752.1U CN203625123U (en) | 2013-07-02 | 2013-07-02 | Sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from two ends of device |
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CN201320394752.1U CN203625123U (en) | 2013-07-02 | 2013-07-02 | Sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from two ends of device |
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CN201320394752.1U Expired - Fee Related CN203625123U (en) | 2013-07-02 | 2013-07-02 | Sewage processing device with carbon storage and denitrification functions and capable of alternately introducing water and discharging water from two ends of device |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107032483A (en) * | 2017-05-09 | 2017-08-11 | 中国联合工程公司 | Double inversed baffled formula continuous flow reactors of biofilter material and its processing waster water process |
CN116395838A (en) * | 2023-05-11 | 2023-07-07 | 苏州太湖中法环境技术有限公司 | Sewage treatment device based on PN/A coupling biochar SPD technology |
-
2013
- 2013-07-02 CN CN201320394752.1U patent/CN203625123U/en not_active Expired - Fee Related
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107032483A (en) * | 2017-05-09 | 2017-08-11 | 中国联合工程公司 | Double inversed baffled formula continuous flow reactors of biofilter material and its processing waster water process |
CN107032483B (en) * | 2017-05-09 | 2022-11-11 | 中国联合工程有限公司 | Double-biological-filter-material reverse baffling type continuous flow reactor and wastewater treatment process thereof |
CN116395838A (en) * | 2023-05-11 | 2023-07-07 | 苏州太湖中法环境技术有限公司 | Sewage treatment device based on PN/A coupling biochar SPD technology |
CN116395838B (en) * | 2023-05-11 | 2024-02-06 | 苏州太湖中法环境技术有限公司 | Sewage treatment device based on PN/A coupling biochar SPD technology |
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Granted publication date: 20140604 Termination date: 20180702 |
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