CN107619110A - Integral anaerobic and scarce aerobic conversion combination wastewater treatment equipment - Google Patents
Integral anaerobic and scarce aerobic conversion combination wastewater treatment equipment Download PDFInfo
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- CN107619110A CN107619110A CN201711074556.5A CN201711074556A CN107619110A CN 107619110 A CN107619110 A CN 107619110A CN 201711074556 A CN201711074556 A CN 201711074556A CN 107619110 A CN107619110 A CN 107619110A
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- aerobic
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Abstract
Wastewater treatment equipment, including pond body are combined in a kind of integral anaerobic and scarce aerobic conversion, are divided into anaerobic zone, aerobic zone and anoxic zone spaced apart from each other in pond body;Anaerobism water inlet pipe, aerobic water inlet pipe and anoxic water inlet pipe are respectively arranged with each area, anaerobism water intaking valve is provided with each water inlet pipe;Each area top is provided with filter layer, downflow weir is provided with above filter layer, drainpipe is provided with the outside of downflow weir, anaerobic zone drainpipe connects with anoxic water inlet pipe, it is connected between anaerobic zone downflow weir and aerobic zone and detests aerobic communicating pipe, anoxic zone drainpipe is connected with anaerobism water inlet pipe, and scarce aerobic communicating pipe is connected between anoxic zone downflow weir and aerobic zone.The device sets anaerobic zone, aerobic zone and anoxic zone in a pond body, combination and use in conjunction by each area, the combination of single anaerobism, aerobic and hypoxia response and a variety of reaction formations can be achieved, to adapt to the needs of different quality, stable effluent quality.
Description
Technical field
The present invention relates to a kind of device for being used to carry out waste water anaerobism or scarce Aerobic Process for Treatment, belong to wastewater processing technology neck
Domain.
Background technology
In the prior art, the processing to waste water typically uses anaerobism, anoxic and aerobic reaction.Anaerobism refers in a kind of non-
Oxidation state, anaerobic reaction are used to release phosphorus bacterium, can change the biodegradability of sewage.Anoxic is the state of oxidation of hypodactylia oxygen, is lacked
Oxygen is reacted for NO3-N and NO2-N denitrification denitrogenation.It is aerobic to refer to oxygen abundance, it is available for aerobic microbiological to utilize, it is aerobic
React and remove BOD with aerobic activated sludge for nitrifying.Generally use anaerobism, anoxic and aerobic association response, it is useless to reach purification
The purpose of water.
Following various combinations can be carried out to the anaerobism, anoxic and aerobic reaction of sewage:
1. traditional anaerobism, anoxic and aerobic process (A2/O techniques), carried out with anaerobism, anoxic and aerobic order.
It is less in content of organics during A2/O PROCESS FOR TREATMENT waste water, it is necessary to containing more organic matter to ensure carbon source in water
In the case of, the technique can make denitrification denitrogenation undesirable, and the nitrate nitrogen that returned sludge brings anaerobic zone into makes polyP bacteria release phosphorus not
Fully, the polyP bacteria then influenceed in aerobic zone inhales phosphorus, causes effluent quality unstable, is extremely difficult to good simultaneous denitrification and removes
Phosphorus effect.
2. anaerobism and aerobic combined process (A/O techniques), major function is biological phosphate-eliminating.Anaerobic stages, polyP bacteria release
Phosphorus;Aerobic stage, phosphorus is absorbed, when discharging excess sludge, phosphorus is together excluded.
3. anoxic and aerobic combined process, major function is biological denitrificaion.Anoxic phases, nitrate, nitrite, nitric acid
Nitrogen and cultured water are converted into nitrogen.If ammonia nitrogen in sewage is very high, then by the sewage backflow of aerobic stage to anoxic pond.
In existing sewage disposal device, exist single anaerobic reactor, aerobic reactor, anaerobism with it is aerobic compound anti-
Answer device and scarce aerobic reactor.And anaerobism, anoxic and aerobic process (A2/O techniques) then use the structures of reaction tank more, take up an area
Area is big, and treatment effeciency is low.
But the equipment currently without multiple combinations processing can be carried out to waste water, allow it according to required technique
Any combination of Anaerobic Treatment, anoxic treatment and Aerobic Process for Treatment is realized, to improve treatment effeciency and effect.
The content of the invention
Present invention deficiency existing for existing wastewater processing technology, there is provided the achievable a variety of processing mode combinations of one kind,
The integral anaerobic and lack aerobic conversion combination wastewater treatment equipment that treatment effeciency is high, effluent quality is good.
The integral anaerobic of the present invention and scarce aerobic conversion combination wastewater treatment equipment, using following technical proposals:
The device, including pond body, it is divided into anaerobic zone, aerobic zone and anoxic zone spaced apart from each other in pond body;Aerobic zone is with lacking
Water valve was provided between oxygen area, be respectively arranged with anaerobic zone, aerobic zone and anoxic zone anaerobism water inlet pipe, aerobic water inlet pipe and
Anoxic water inlet pipe, anaerobism water intaking valve is provided with each water inlet pipe;The top of anaerobic zone is provided with gas-solid-liquid Disengagement zone, gas-solid-liquid
Anaerobism filter layer is provided with above Disengagement zone, is provided with anaerobism downflow weir above anaerobism filter layer, anaerobism downflow weir it is outer
Side is provided with anaerobism drainpipe, is provided with anaerobism drainpipe and detests anoxic reversal valve, detest anoxic reversal valve and anoxic water inlet pipe it
Between be connected with and detest anoxic communicating pipe, be connected between anaerobism downflow weir and aerobic zone and detest aerobic communicating pipe, detested on aerobic communicating pipe
It is provided with and detests aerobic communicating valve;The top of aerobic zone is provided with aerobic filter layer, and aerobic overflow is provided with above aerobic filter layer
Weir is flowed, aerobic drainpipe is provided with the outside of aerobic downflow weir, draining valve is provided with aerobic drainpipe, is provided with aerobic zone
Aerator;Anoxic air inlet pipe is provided with anoxic zone, the top of anoxic zone is provided with anoxic filter layer, anoxic filter layer top
Anoxic downflow weir is provided with, anoxic drainpipe is provided with the outside of anoxic downflow weir, scarce anaerobism is provided with anoxic drainpipe and is changed
To valve, lack and scarce anaerobism communicating pipe is connected between anaerobism reversal valve and anaerobism water inlet pipe, connect between anoxic downflow weir and aerobic zone
Scarce aerobic communicating pipe is connected to, lacks and is provided with scarce aerobic communicating valve on aerobic communicating pipe.
The bottom of the anaerobism water inlet pipe, aerobic water inlet pipe and anoxic water inlet pipe is respectively provided with water-locator.
The bottom of the anaerobic zone, aerobic zone and anoxic zone is provided with blow-off pipe, and blowoff valve is connected with blow-off pipe.
Flow valve is connected with the anoxic air inlet pipe, to control aeration quantity, anoxic zone is in anaerobic condition.
During above-mentioned wastewater treatment equipment operation, individually it can be reacted accordingly in anaerobic zone, aerobic zone and anoxic zone,
But carry out anaerobism and aerobic, anoxic with it is aerobic, aerobic with anoxic, anaerobism, anoxic and aerobic and anoxic, anaerobism with it is aerobic etc.
The combination of diversified forms, to adapt to the needs of different quality.
Strong adaptability of the present invention, anaerobic zone, aerobic zone and anoxic zone are set in a pond body, by the combination in each area and
Use in conjunction, single anaerobism, aerobic and hypoxia response, and the group of two kinds of reaction formations or three kinds of reaction formations can be achieved
Close, to adapt to the needs of different quality, improve treatment effeciency, effluent quality is greatly improved and stably.
Brief description of the drawings
Fig. 1 is integral anaerobic of the present invention and the structural representation for lacking aerobic conversion combination wastewater treatment equipment.
In figure:1st, pond body, 2, anaerobism blow-off pipe, 3, first partition, 4, aerobic blow-off pipe, 5, cross water valve, 6, second partition,
7th, anoxic blow-off pipe, 8, anoxic air inlet pipe, 9, flow valve, 10, lack aerobic communicating pipe, 11, anoxic zone, 12, anoxic water inlet pipe,
13rd, aerobic filter layer, 14, anoxic filter layer, 15, anoxic drainpipe, 16, lack anaerobism reversal valve, 17, lack anaerobism communicating pipe, 18,
Anoxic water intaking valve, 19, blast pipe, 20, aerobic water inlet pipe, 21, aerobic water intaking valve, 22, aeration tube, 23, anaerobism water intaking valve, 24,
Water inlet manifold, 25, anaerobism water inlet pipe, 26, biogas pipe, 27, anaerobism downflow weir, 28, anaerobism drainpipe, 29, anaerobism filter layer,
30th, gas-solid-liquid Disengagement zone, 31, aerobic downflow weir, 32, detest aerobic communicating pipe, 33, agitator, 34, aerobic drainpipe, 35, lack
Oxygen communicating valve, 36, detest aerobic communicating valve, 37, anaerobic zone, 38, aerobic zone, 39, anoxic downflow weir, 40, detest anoxic reversal valve,
41st, anaerobism communicating pipe is lacked.
Embodiment
As shown in figure 1, the integral anaerobic of the present invention and scarce aerobic conversion combination wastewater treatment equipment, including pond body 1.Pond
Divided in body 1 by vertical first partition 3 and second partition 6 for anaerobic zone 37 arranged side by side, aerobic zone 38 and anoxic zone 11.It is aerobic
The bottom of second partition 6 between area 38 and anoxic zone 11 was provided with water valve 5.In anaerobic zone 37, aerobic zone 38 and anoxic zone 11
Anaerobism water inlet pipe 23, aerobic water inlet pipe 20 and anoxic water inlet pipe 12 are respectively arranged with, anaerobism water inlet pipe 25 passes through anaerobism water intaking valve
23 are connected with water inlet manifold 24, and aerobic water inlet pipe 20 is connected by aerobic water intaking valve 21 with water inlet manifold 24, anoxic water inlet pipe 12
It is connected by anoxic water intaking valve 18 with water inlet manifold 24.Can be in anaerobism water inlet pipe 23, aerobic water inlet pipe 20 and anoxic water inlet pipe 12
Bottom set water-locator.
The bottom of anaerobic zone 37 is provided with anaerobism blow-off pipe 2, and blowoff valve is connected with anaerobism blow-off pipe 2.Anaerobic zone 37
Top is provided with gas-solid-liquid Disengagement zone 30, and the top of gas-solid-liquid Disengagement zone 30 is provided with anaerobism filter layer 29, anaerobism filter layer 29
Top be provided with anaerobism downflow weir 27, the outside of anaerobism downflow weir 27 is provided with anaerobism drainpipe 28.On anaerobism drainpipe 28
It is provided with and detests anoxic reversal valve 40, detests to be connected between anoxic reversal valve 40 and anoxic water inlet pipe 12 and detest anoxic communicating pipe 41.Detest
It is connected between oxygen downflow weir 27 and aerobic zone 38 and detests aerobic communicating pipe 32, is detested to be provided with aerobic communicating pipe 32 and detest aerobic connection
Valve 36.Agitator 33 is additionally provided with anaerobic zone 37 and stretches into the biogas pipe 26 of gas-solid-liquid Disengagement zone 30.Waste water is by always intaking
Pipe 24 (opening anaerobism water intaking valve 25) enters anaerobic zone 37, or (is changed and commutated by lacking anaerobism communicating pipe 17 by anoxic zone 11
Valve 16) enter anaerobic zone 37.After waste water enters anaerobic zone 37, anaerobic reaction is carried out by the stirring of agitator 33, then by gas
Solid-liquid displacement zone 30 carries out gas-solid-liquid separation, and caused biogas is discharged by biogas pipe 26, and sludge is trapped, and the water body after purification leads to
Cross after anaerobism filter layer 29 filters and enter anaerobism downflow weir 27, water in anaerobism downflow weir 27 or directly pass through anaerobism drainpipe
28 discharges (detesting anoxic reversal valve 40 to connect with anaerobism drainpipe 28), or enter aerobic zone 38 by detesting aerobic communicating pipe 32
(opening detests aerobic communicating valve 36), then carry out aerobic reaction processing.Structure in anaerobic zone 37 can also take other form.
The bottom of aerobic zone 38 is provided with aerobic blow-off pipe 4, and blowoff valve is connected with aerobic blow-off pipe 4.Aerobic zone 38
Top is provided with aerobic filter layer 13, and the top of aerobic filter layer 13 is provided with aerobic downflow weir 31, aerobic downflow weir 31 it is outer
Side is provided with aerobic drainpipe 34, and draining valve is provided with aerobic drainpipe 34.It is additionally provided with aerobic zone 38 and stretches into its bottom
Aeration tube 22, the bottom of aeration tube 22 set aeration head.Compressed air is passed through into aerobic zone 38 by aeration tube 22, exposed
Gas.Waste water enters aerobic zone 38 by water inlet manifold 24 (opening aerobic water intaking valve 21), or is entered by detesting aerobic communicating pipe 32
Oxygen area 38 (opening detests aerobic communicating valve 36), or lack and enter (the scarce aerobic communicating valve of opening of aerobic zone 38 aerobic communicating pipe 10
35).Water body after purification enters aerobic downflow weir 31 after being filtered by aerobic filter layer 13, the water in aerobic downflow weir 31 passes through
Aerobic drainpipe 34 is discharged and (opens the draining valve on aerobic drainpipe 34), is utilized.Structure in aerobic zone 38 can also adopt
Use other forms.
The bottom of anoxic zone 11 is provided with anoxic blow-off pipe 7, and blowoff valve is connected with anoxic blow-off pipe 7.Anoxic zone 11
Bottom is provided with anoxic air inlet pipe 8, and flow valve 9 is connected with anoxic air inlet pipe 8, to control aeration quantity, is in anoxic zone 11
Anaerobic condition.The top of anoxic zone 11 is provided with anoxic filter layer 14, and the top of anoxic filter layer 14 is provided with anoxic downflow weir 39,
The outside of anoxic downflow weir 39 is provided with anoxic drainpipe 15, and scarce anaerobism reversal valve 16 is provided with anoxic drainpipe 15, lacks and detests
Scarce anaerobism communicating pipe 17 is connected between oxygen reversal valve 16 and anaerobism water inlet pipe 23.Connect between anoxic downflow weir 39 and aerobic zone 38
Scarce aerobic communicating pipe 10 is connected to, lacks and is provided with scarce aerobic communicating valve 35 on aerobic communicating pipe 10.The row of being additionally provided with anoxic zone 11
Tracheae 19, caused waste gas are discharged by blast pipe 19.Waste water enters anoxic zone by water inlet manifold 24 (opening anoxic water intaking valve 18)
11, either enter anoxic zone 11 by water valve 5 by aerobic zone 38 or enter anoxic through detesting anoxic communicating pipe 41 by anaerobic zone 37
Area 11.Waste water enters anoxic zone 11 and carries out hypoxia response, and the water body after purification enters anoxic after being filtered by anoxic filter layer 14
Downflow weir 39, water in anoxic downflow weir 39 or directly discharged by anoxic drainpipe 15 (are opened on anoxic drainpipe 15
Draining valve), or enter aerobic zone 38 (open and lack aerobic communicating valve 35) aerobic communicating pipe 10 by lacking, then carry out aerobic reaction
Processing, or anaerobism reversal valve 16 is lacked by lacking anaerobism communicating pipe 17 into anaerobic zone 37 by changing.Structure in anoxic zone 11
Also can take other form.
Above-mentioned wastewater treatment equipment can carry out the conversion combination of following diversified forms, to adapt to the needs of different quality.
1. independent anaerobic reaction device
Anaerobism water intaking valve 23 is opened, detests anoxic reversal valve 40 and be converted to communicating with anaerobism drainpipe 28, and closes other valves
Door, waste water only enter anaerobic zone 37, are reacted in anaerobic zone 37, and be expelled directly out.
2. independent aerobic reaction device
The draining valve on aerobic water intaking valve 21 and aerobic drainpipe 34 is opened, and closes other valves, waste water only enters
Oxygen area 38, react, and be expelled directly out in aerobic zone 38.
3. independent hypoxia response device
Anoxic water intaking valve 18 is opened, scarce anaerobism reversal valve 16 is converted to be communicated with anoxic drainpipe 15, closes other valves,
Waste water only enters anoxic zone 11, is reacted in anoxic zone 11, and be expelled directly out.
4. anaerobism and aerobic reaction device
Open anaerobism water intaking valve 25, detest draining valve on aerobic communicating valve 36 and aerobic drainpipe 34, and close other valves
Door.Waste water enters after anaerobic zone 37 is reacted and enters aerobic zone 38 by detesting aerobic communicating pipe 32 again, and is expelled directly out by aerobic zone 38.
5. anoxic and aerobic reaction device
Draining valve on unlatching anoxic water intaking valve 18, scarce aerobic communicating valve 35 and aerobic drainpipe 34, and close other valves
Door.Waste water enters after anoxic zone 11 is reacted and enters aerobic zone 38 by lacking aerobic communicating pipe 10 again, and is expelled directly out by aerobic zone 38.
6. aerobic and hypoxia response device
Open aerobic water intaking valve 21 and cross water valve 5, scarce anaerobism reversal valve 16 is converted to be communicated with anoxic drainpipe 15, and is closed
Close other valves.Waste water enters after aerobic zone 38 is reacted and enters anoxic zone 11 by water valve 5 again, and is directly arranged by anoxic zone 11
Go out.
7. anaerobism, anoxic and aerobic reaction device
Draining valve on unlatching anaerobism water intaking valve 23, scarce aerobic communicating valve 35 and aerobic drainpipe 34, detests anoxic reversal valve
40 are converted to and are communicated with detesting anoxic communicating pipe 41, and close other valves.Waste water enters anaerobic zone by anaerobism water inlet pipe 25 first
37, enter anoxic zone 11 anoxic communicating pipe 41 by detesting again after anaerobic reaction, entered aerobic communicating pipe 10 by lacking again after hypoxia response
Aerobic zone 38, and be expelled directly out by aerobic zone 38.
8. anoxic, anaerobism and aerobic reaction device
Open anoxic water intaking valve 18, detest draining valve on aerobic communicating valve 36 and aerobic drainpipe 34, lack anaerobism reversal valve
16 communicate with scarce anaerobism communicating pipe 17, and close other valves.Waste water enters anoxic zone 11, anoxic by anoxic water inlet pipe 12 first
Enter anaerobic zone 37 anaerobism communicating pipe 17 by lacking again after reaction, enter aerobic zone by detesting aerobic communicating pipe 32 again after anaerobic reaction
38, and be expelled directly out by aerobic zone 38.
The combination of other forms can also be carried out as needed.
Claims (4)
1. a kind of integral anaerobic and scarce aerobic conversion combination wastewater treatment equipment, including pond body, it is characterized in that:It is divided into pond body
Anaerobic zone, aerobic zone and anoxic zone spaced apart from each other;Water valve, anaerobic zone, aerobic zone were provided between aerobic zone and anoxic zone
With anaerobism water inlet pipe, aerobic water inlet pipe and anoxic water inlet pipe are respectively arranged with anoxic zone, be provided with anaerobism on each water inlet pipe
Water intaking valve;The top of anaerobic zone is provided with gas-solid-liquid Disengagement zone, and anaerobism filter layer, anaerobism are provided with above gas-solid-liquid Disengagement zone
Anaerobism downflow weir is provided with above filter layer, anaerobism drainpipe is provided with the outside of anaerobism downflow weir, is set on anaerobism drainpipe
Be equipped with and detest anoxic reversal valve, detest to be connected between anoxic reversal valve and anoxic water inlet pipe and detest anoxic communicating pipe, anaerobism downflow weir with
It is connected between aerobic zone and detests aerobic communicating pipe, is detested to be provided with aerobic communicating pipe and detest aerobic communicating valve;The top of aerobic zone is set
Aerobic filter layer is equipped with, aerobic downflow weir is provided with above aerobic filter layer, aerobic row is provided with the outside of aerobic downflow weir
Water pipe, draining valve is provided with aerobic drainpipe, aerator is provided with aerobic zone;Anoxic air inlet is provided with anoxic zone
Pipe, the top of anoxic zone are provided with anoxic filter layer, are provided with anoxic downflow weir above anoxic filter layer, anoxic downflow weir it is outer
Side is provided with anoxic drainpipe, and scarce anaerobism reversal valve is provided with anoxic drainpipe, lack anaerobism reversal valve and anaerobism water inlet pipe it
Between be connected with scarce anaerobism communicating pipe, scarce aerobic communicating pipe is connected between anoxic downflow weir and aerobic zone, lack aerobic communicating pipe on
It is provided with scarce aerobic communicating valve.
2. integral anaerobic according to claim 1 and scarce aerobic conversion combination wastewater treatment equipment, it is characterized in that:It is described
The bottom of anaerobism water inlet pipe, aerobic water inlet pipe and anoxic water inlet pipe is respectively provided with water-locator.
3. integral anaerobic according to claim 1 and scarce aerobic conversion combination wastewater treatment equipment, it is characterized in that:It is described
The bottom of anaerobic zone, aerobic zone and anoxic zone is provided with blow-off pipe, and blowoff valve is connected with blow-off pipe.
4. integral anaerobic according to claim 1 and scarce aerobic conversion combination wastewater treatment equipment, it is characterized in that:It is described
Flow valve is connected with anoxic air inlet pipe.
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CN201711074556.5A CN107619110A (en) | 2017-11-03 | 2017-11-03 | Integral anaerobic and scarce aerobic conversion combination wastewater treatment equipment |
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004024965A (en) * | 2002-06-24 | 2004-01-29 | Kubota Corp | Scum discharging method in bioreactor and apparatus therefor |
CN205676215U (en) * | 2016-06-23 | 2016-11-09 | 山东省环境保护科学研究设计院 | A kind of eddy flow composite waste handles oxygen reactor well |
CN205803249U (en) * | 2016-06-23 | 2016-12-14 | 北京朗新明环保科技有限公司 | A kind of anaerobic/anoxic/aerobic MBR sewage-treatment plant |
CN207468287U (en) * | 2017-11-03 | 2018-06-08 | 山东省环境规划研究院 | Integral anaerobic and scarce aerobic transformation combination wastewater treatment equipment |
-
2017
- 2017-11-03 CN CN201711074556.5A patent/CN107619110A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2004024965A (en) * | 2002-06-24 | 2004-01-29 | Kubota Corp | Scum discharging method in bioreactor and apparatus therefor |
CN205676215U (en) * | 2016-06-23 | 2016-11-09 | 山东省环境保护科学研究设计院 | A kind of eddy flow composite waste handles oxygen reactor well |
CN205803249U (en) * | 2016-06-23 | 2016-12-14 | 北京朗新明环保科技有限公司 | A kind of anaerobic/anoxic/aerobic MBR sewage-treatment plant |
CN207468287U (en) * | 2017-11-03 | 2018-06-08 | 山东省环境规划研究院 | Integral anaerobic and scarce aerobic transformation combination wastewater treatment equipment |
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