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CN205527993U - Good oxygen integrated reactor of anaerobism - Google Patents

Good oxygen integrated reactor of anaerobism Download PDF

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Publication number
CN205527993U
CN205527993U CN201520899377.5U CN201520899377U CN205527993U CN 205527993 U CN205527993 U CN 205527993U CN 201520899377 U CN201520899377 U CN 201520899377U CN 205527993 U CN205527993 U CN 205527993U
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Prior art keywords
anaerobic
aerobic
anaerobism
mud
phase separator
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张东胜
李娇妍
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Inner Mongolia Yili Industrial Group Co Ltd
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Inner Mongolia Yili Industrial Group Co Ltd
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Abstract

The utility model provides a good oxygen integrated reactor of anaerobism, it includes the casing, the casing lower part is anaerobism react unit, anaerobism react unit's inside sets up three -phase separator, and oxygen processing unit has been set up when gas in the three -phase separator separation anaerobism mud scum, liquid and mud above the settling area that forms. The utility model discloses a bodyization reactor area is little, the cost low, can effectively reduce anaerobism mud runs off, the anaerobic treatment unit can have been acceptted the oxygen unit to pack and go up the activated sludge that the nature drops, can regard as the replenishment of anaerobism mud, good oxygen processing unit excess sludge's reduction has alleviateed sewage treatment system's sludge treatment expense, good oxygen mud is in aging, and partial mud is generated marsh gas by anaerobic digestion, and the increase of marsh gas output is favorable to resources recovery and utilization, and anaerobic microorganisms's nutrition still can be regarded as to partial mud, is favorable to it to breed, has finally increased the microorganism total amount of system, has promoted the throughput of system.

Description

A kind of anaerobic aerobic integratedization reactor
Technical field
This utility model relates to apparatus for treating sewage, particularly relates to a kind of anaerobic aerobic integratedization reactor, belongs to environmental protection neck Territory.
Background technology
At present, the technique of Dairy Industry sewage disposal is usually anaerobic treatment+aerobic treatment process, and two process single Unit is independent processing system, and anaerobic effluent, after anaerobic treatment, is introduced aerobic unit and pollutes by treatment sewage Degrading again of material.Research shows to use at least existence in this technique following not enough:
(1) two overlaps single technique unit, and floor space is big, and cost is high;
(2) Dairy Industry sewage is higher containing lactoprotein and casein, easily occurs on anaerobic sludge in processing procedure The floating phenomenon separated, causes anaerobic sludge to run off serious, and anaerobic sludge to be anaerobic system degradation of contaminant mainly undertake Person, once sludge loss needs renewed vaccination to buy anaerobic sludge, period system recovery need 2~3 months, there is draining Problem the most up to standard, environmental risk is very big;Additionally, the minimizing of anaerobic sludge causes system fluctuation of service the most at last, Causing and increase aerobic unit load, sludge output is big, increases sewage disposal expense;
(3) easily occur system to become sour when anaerobism influent load raises, cause pH to reduce, microorganism deactivated, detest Oxygen unit mud runs off further, and final disposal ability reduces.
For solving the technical problem that anaerobic sludge runs off, it is anti-that CN203411391U discloses a kind of upflow anaerobic sludge Answering device, this reactor is to set a zeolite filler district between suspended sludge bed and three phase separator, and this zeolite filler district can Effectively stoping the loss of anaerobic sludge, microorganism simultaneously can grow on zeolite, the beneficially process of sewage.But this Class Sludge Bed packing area with run the time increase easily blockage phenomenon, make anaerobic system occur short flowing to and local Become sour.
CN100506721C discloses the device improving three phase separating efficiency of baffle type anaerobic biological reactor, this device The loss that anaerobic sludge causes is reduced due to waterpower and aerogenesis by arranging the baffle plate of multiple band corner.Yet with needs Arranging multiple corner units, the load of anaerobic pond can not be too high, and processed in units amount load height still exists sludge loss and asks Topic.
The technical scheme that anaerobic sludge runs off is solved although prior art provides, due to the defect being individually present, its Being not particularly suited for Dairy Industry sewage disposal, therefore, floor space is little, cost is low, can reduce anaerobism to find one The reactor of sludge loss is that this area is needed badly and solved the technical problem that.
Utility model content
One of the purpose of this utility model is to provide a kind of anaerobic aerobic integratedization reactor, described anaerobic aerobic integrated Change reactor and there is the advantage that floor space is little, cost is low and can reduce anaerobic sludge loss.
Another object of the present utility model is to provide a kind of sewage disposal system.
For achieving the above object, this utility model provides a kind of anaerobic aerobic integratedization reactor, including housing, wherein: Described lower housing portion is anaerobic reaction unit, and the inside of described anaerobic reaction unit arranges three phase separator, at three-phase separate The decanting zone formed during gas, liquid and mud in device separation anaerobism mud scum is provided above aerobic treatment unit; Preferably, described aerobic treatment unit is arranged on the surface of described decanting zone.
This utility model research finds that anaerobism mud scum is the major reason that anaerobic sludge runs off, and anaerobism mud scum is by anaerobism The induced gas that mud produces during being entrained in anaerobic treatment, when anaerobism mud scum is in agitation, and major part is detested Oxygen mud scum can settle and fall back in anaerobic treatment unit cells, and only small part density can flow out system with water less than the mud scum of water System, this utility model, by being placed in anaerobic treatment unit in aerobic treatment unit, has exposure in this aerobic treatment unit Device of air, when anaerobic sludge gas enclosure floats, can be agitated below the packing area in aerobic unit, make bubble divide From, mud falls after rise to anaerobic reaction district, effectively prevent the loss of mud.
Anaerobic aerobic integratedization reactor of the present utility model saves technique floor space, reduces construction costs, is solving Existing technique floor space is big, while cost height, solves the problem that anaerobic sludge loss is serious further.
Additionally, while solving anaerobic sludge loss, natural on anaerobic treatment unit also receivability aerobic unit filler The activated sludge come off, this activated sludge turns through transition (being converted into anaerobism mud by aerobic mud) during landing Become the mud of anaerobic system, can supplementing as anaerobic sludge;The minimizing of aerobic treatment unit excess sludge also alleviates The Treatment of Sludge expense of sewage disposal system;Aerobic sludge is in the maturing process being converted into anaerobic sludge, and part is dirty Mud is anaerobically digested and forms methane, and biogas output increases, and beneficially resource reclaim and utilization, partial sludge is alternatively arranged as The nutrition of anaerobe, is conducive to its breeding, ultimately increases the microorganism total amount of system, improve cell processing Ability.
According to detailed description of the invention of the present utility model, in described anaerobic aerobic integratedization reactor, wherein, institute State aerobic treatment unit and include aerobic filler assembly, and aeration head is towards described aerobic filler assembly the exposure that supplies to it Device of air.Preferably, described aeration head is positioned at the lower section of described aerobic filler assembly.
This utility model aerator in aerobic treatment unit is not construed as limiting, it is preferable that good in described anaerobism In oxygen integrated reactor, described aerator is that perforated pipe aeration apparatus, outstanding mixed aerator and/or micropore expose Device of air.
This utility model aerobic filler assembly in aerobic treatment unit is not construed as limiting, it is preferable that detest described In oxygen aerobic integratedization reactor, described aerobic filler assembly is fiber hair filler, elastic filler or floating stuffing.
According to detailed description of the invention of the present utility model, in described anaerobic aerobic integratedization reactor, this anaerobism is good Oxygen integrated reactor also includes being positioned at the anaerobism distribution channel above described housing and being connected with described anaerobism distribution channel The anaerobic water pipe that treatment sewage is caused anaerobic reaction unit.Prior art is typically to pass through treatment sewage Anaerobic treatment unit squeezed into by the configured water distributor in bottom of pump, and the easy fouling and clogging of this water intake mode was tieed up for the later stage It is the most unfavorable to repair, and water distribution manner of the present utility model can thoroughly solve pipeline blockage and the uneven problem of water distribution.
According to detailed description of the invention of the present utility model, in described anaerobic aerobic integratedization reactor, described shell Internal it is provided with two groups of described three phase separators the most independent, and often organizes described three phase separator separation anaerobism respectively The decanting zone formed during gas, liquid and mud in mud scum is provided above described aerobic treatment unit.
The form of described three phase separator is not construed as limiting by this utility model, can be the most current UASB reactor Conventional kind form, it is preferable that according to detailed description of the invention of the present utility model, described anaerobic aerobic integrated Changing in reactor, described three phase separator is immersion Air-chamber type three phase separator or liquid above formula Air-chamber type three phase separation Device.Wherein, the structure of described immersion Air-chamber type three phase separator as in Fig. 1 1.~3. shown in, described liquid The structure of above formula Air-chamber type three phase separator as in Fig. 1 4.~6. shown in;It is highly preferred that described three phase separator Result as in Fig. 1 2. or 3. shown in.
According to detailed description of the invention of the present utility model, in described anaerobic aerobic integratedization reactor, described aerobic Processing unit is provided above the integral system discharged by the sewage after described anaerobic aerobic integratedization reactor for treatment Receive tank.Optionally, described anaerobic aerobic integratedization reactor also set up discharge pipeline, manhole, thermometer and/ Or pH meter.
Another object of the present utility model is to provide a kind of sewage disposal system, and wherein, described sewerage includes this Anaerobic aerobic integratedization reactor described in utility model.
According to detailed description of the invention of the present utility model, in described sewage disposal system, described sewage disposal system Including for storing the intermediate pool for the treatment of sewage, anaerobic aerobic integratedization reactor and second pond, described intermediate pool with Between described anaerobic aerobic integratedization reactor, the pipeline that treatment sewage causes described anaerobic unit is set;Described detest Sewage after processing is set between oxygen aerobic integratedization reactor and described second pond and causes the pipeline of second pond.
In sum, the anaerobic aerobic integratedization reactor that this utility model provides has the advantages that
(1) this utility model integrated reactor floor space is little, cost is low;
(2) this utility model integrated reactor is effectively reduced anaerobic sludge loss;
(3) natural on the also receivability aerobic unit filler of the anaerobic treatment unit in this utility model integrated reactor The activated sludge come off, this activated sludge turns through transition (being converted into anaerobism mud by aerobic mud) during landing Become the mud of anaerobic system, can supplementing as anaerobic sludge;The minimizing of aerobic treatment unit excess sludge also mitigates The Treatment of Sludge expense of sewage disposal system;Aerobic sludge in the maturing process being converted into anaerobic sludge, partial sludge Being anaerobically digested and form methane, biogas output increases, and beneficially resource reclaim and utilization, partial sludge is alternatively arranged as detesting The nutrition of oxygen animalcule, is conducive to its breeding, ultimately increases the microorganism total amount of system, and the system that improves processes energy Power.
Accompanying drawing explanation
Fig. 1 is the type that can be used for three phase separator of the present utility model;1.~3. Fig. 1 is immersion Air-chamber type three Phase separator, 4.~is 6. liquid above formula Air-chamber type three phase separator;In Fig. 1,11 represent gas, after 12 represent separation Liquid;
Fig. 2 is the structural representation of the anaerobic aerobic integratedization reactor described in embodiment 1;Label in Fig. 2 has Represent following meaning:
21: housing;22: anaerobic reaction unit;221: three phase separator;2210: three phase separator separation anaerobism The decanting zone formed during gas, liquid and mud in mud scum;2211: lower baffle plate on the left of three phase separator;2212 Overhead gage on the left of three phase separator;2213: lower baffle plate on the right side of three phase separator;2214: upper gear on the right side of three phase separator Plate;2215: the special-shaped beam of three phase separator;23: aerobic treatment unit;231: aerobic filler assembly;232: expose Device of air;2321: aeration head;2322: gas enters pipe;24: anaerobism distribution channel;241: anaerobism distribution channel is dirty Water out;25: anaerobism sparge pipe;26: integral system receives tank;27:pH counts;28: discharge pipeline;29: Manhole;210: thermometer;211: collection chamber;2111: form the gas collection plate of collection chamber;212: water sampling pipe;
Fig. 3 is the Structure and Process schematic diagram of the sewage disposal system described in embodiment 2;Label in Fig. 3 has as follows Meaning:
31: intermediate pool;32: anaerobic aerobic integratedization reactor;33: second pond;312: connect intermediate pool and detest The pipeline of oxygen aerobic integratedization reactor;321: the mud used during anaerobic treatment;322: connect the pipe of collection chamber Road;323: connect the pipeline of anaerobic aerobic integratedization reactor and second pond;331: discharge pipe line.
Detailed description of the invention
In order to technical characteristic of the present utility model, purpose and beneficial effect are more clearly understood from, in conjunction with specifically The technical solution of the utility model is carried out described further below by embodiment and accompanying drawing, it should be understood that these embodiments are only used for This utility model is described rather than limits scope of the present utility model.The step mentioned the most in detail in each embodiment Carry out according to the routine operation of art.
Fig. 1 is the structural representation that can be used for three phase separator of the present utility model, is 1.~3. immersion gas in Fig. 1 Room type three phase separator, 4.~is 6. liquid above formula Air-chamber type three phase separator;In Fig. 1,11 represent gas, and 12 represent Liquid after separation;Wherein, 2. or 3. Fig. 1 it is the preferred three phase separator of this utility model.
Embodiment 1
The present embodiment provides a kind of anaerobic aerobic integratedization reactor, as in figure 2 it is shown, it includes housing 21, described Housing 21 bottom is anaerobic reaction unit 22, the inside of described anaerobic reaction unit 22 arrange two groups the most independent Three phase separator 221, and respectively often organize described three phase separator 221 separate the gas in anaerobism mud scum, liquid and The decanting zone 2210 formed during mud is provided above aerobic treatment unit 23, is preferably arranged above aerobic place at it Reason unit 23;
Described aerobic treatment unit 23 includes Aerobic Process for Treatment filler assembly 231, and aeration head 2321 is towards described aerobic Filler assembly 231 aerator 232 supplied to it;Described aeration head 2321 is positioned at described aerobic filler assembly The lower section of 231, preferably underface, described aerator 232 also includes that gas enters pipe 2322;Described aeration dress Put 232 for microporous aeration device, it is also possible to select mesopore aerator;Described aerobic filler assembly 231 is elastic Filler, can also select fiber hair filler or floating stuffing according to processing operating mode difference;
The most roughly the same with Fig. 1 of the three phase separator basic structure that the present embodiment is used, only special-shaped beam has necessarily Difference, described three phase separator 221 includes gas in anaerobism mud scum is caused the different of the three phase separator of collection chamber 211 Type beam 2215, collection chamber 211 is formed by the gas collection plate 2111 and housing 21 forming collection chamber;Three phase separator Special-shaped beam 2,215 two pieces of spaced baffle plates are each side set, the most spaced and mutual dislocation is parallel Baffle plate, respectively overhead gage 2212, three-phase separate on the left of lower baffle plate 2211, three phase separator on the left of three phase separator Overhead gage 2214 on the right side of lower baffle plate 2213, three phase separator, overhead gage 2212 on the left of three phase separator on the right side of device With overhead gage on the right side of three phase separator 2214 almost symmetry in vertical direction, lower baffle plate 2211 on the left of three phase separator With lower baffle plate on the right side of three phase separator 2213 at vertical direction almost symmetry;The special-shaped beam 2215 and two of three phase separator Gap is all had between side overhead gage and lower baffle plate.The vertical cross-section of this special-shaped beam is tetragon;
Described anaerobic aerobic integratedization reactor also include being positioned at the anaerobism distribution channel 24 above described housing 21 and with The anaerobic water pipe 25 that treatment sewage is caused anaerobic reaction unit 22 that described anaerobism distribution channel 24 connects;Should Being provided with pending anaerobism distribution channel outlet of sewer 241 below anaerobism distribution channel 24, it is by flexible pipe and anaerobism cloth Water pipe 25 is connected, and the upper end of anaerobic water pipe 25 is steel pipe, and lower end is flexible pipe;
Described aerobic treatment unit 23 is provided above arranging the sewage after described anaerobic aerobic integratedization reactor for treatment The integral system gone out receives tank 26, and arranges pH meter 27, discharge pipeline 28, manhole on described housing 21 29, thermometer 210 and water sampling pipe 212.
In specific implementation process, waste water causes anaerobic treatment unit by anaerobism distribution channel 24 through anaerobism sparge pipe 25 The bottom of 22, sewage upwards flow separately through the anaerobic mud bed district (not shown in figure 1) in anaerobic treatment unit 22, Three phase separator 221, through three phase separator separate, gas phase enter collection chamber 211, liquid-solid entrance three phase separation 221 Decanting zone 2210, in decanting zone 2210, partial sludge precipitates, through the special-shaped beam 2215 of three phase separator And the slit between lower baffle plate falls into anaerobic reaction district, through three phase separator the most unsegregated gas enclosure anaerobism mud scum aerobic Being agitated below district, force bubble separation, mud is between special-shaped beam 2215 and the lower baffle plate of three phase separator Anaerobic reaction district is fallen back in slit sedimentation.
Embodiment 2
The present embodiment provides a set of sewage disposal system, as it is shown on figure 3, described sewage disposal system includes for storing The intermediate pool 31 for the treatment of sewage, anaerobic aerobic integratedization reactor 32 and second pond 33, as can be seen from Figure 3 The anaerobic aerobic integratedization reactor 32 that the present embodiment uses is substantially the same manner as Example 1, is only some adnexa (examples Such as discharge pipeline, manhole) setting be slightly different, do not repeat at this, anaerobic aerobic integratedization reactor 32 The mud 321 used when bottom is equipped with anaerobic treatment;
Arrange between described intermediate pool 31 and described anaerobic aerobic integratedization reactor 32 and treatment sewage is caused anaerobism The pipeline 312 connecting intermediate pool and anaerobic aerobic integratedization reactor of unit;Described anaerobic aerobic integratedization reactor Sewage after processing is set between 32 and described second pond 32 and causes the connection anaerobic aerobic integratedization reaction of second pond Device and the pipeline 323 of second pond;Described anaerobic aerobic integratedization reactor 32 is additionally provided with the pipeline connecting collection chamber 322, to recycle produced biogas;
Described second pond 33 is provided with the discharge pipe line 331 discharged by the water after up to standard.
In the specific implementation, 312 the sewage in intermediate pool 31 is introduced anaerobic aerobic integratedization reactor 32 by the road, Through process as in Example 1,323 gravity by the road of the sewage after process flow into second pond 33 and do mud-water separation, After separation, water up to standard is discharged through discharge pipe line 331.
Finally illustrate: above example is merely to illustrate implementation process of the present utility model and feature, and unrestricted The technical solution of the utility model, although this utility model being described in detail with reference to above-described embodiment, this area Those of ordinary skill it is understood that still this utility model can be modified or equivalent, without deviating from Any modification or partial replacement of spirit and scope of the present utility model, all should contain at protection domain of the present utility model In the middle of.

Claims (7)

1. an anaerobic aerobic integratedization reactor, this anaerobic aerobic integratedization reactor includes a housing, and in described housing, bottom is anaerobic reaction unit, and the inside of described anaerobic reaction unit arranges three phase separator, it is characterised in that:
Described three phase separator is immersion Air-chamber type three phase separator or liquid above formula Air-chamber type three phase separator, directly arranges aerobic treatment unit above the decanting zone formed during gas, liquid and mud in three phase separator separation anaerobism mud scum;The integral system being provided above discharging the sewage after described anaerobic aerobic integratedization reactor for treatment in described aerobic treatment unit receives tank;
Further, this anaerobic aerobic integratedization reactor also includes the anaerobic water pipe that treatment sewage is directed directly to downwards anaerobic reaction unit from anaerobism distribution channel being positioned at the anaerobism distribution channel above described housing and being connected with described anaerobism distribution channel.
Anaerobic aerobic integratedization reactor the most according to claim 1, it is characterised in that: described aerobic treatment unit includes aerobic filler assembly, and aeration head is towards described aerobic filler assembly the aerator that supplies to it.
Anaerobic aerobic integratedization reactor the most according to claim 2, it is characterised in that: described aerobic filler assembly is fiber hair filler, elastic filler or floating stuffing.
Anaerobic aerobic integratedization reactor the most according to claim 2, it is characterised in that: described aerator is perforated pipe aeration apparatus, outstanding mixed aerator and/or microporous aeration device.
5. according to the anaerobic aerobic integratedization reactor according to any one of Claims 1 to 4, it is characterized in that: in described housing, be provided with two groups of described three phase separators the most independent, and respectively gas, liquid and the mud in often organizing described three phase separator separation anaerobism mud scum time the decanting zone that formed be provided above described aerobic treatment unit.
6. a sewage disposal system, it is characterised in that: described sewerage includes the anaerobic aerobic integratedization reactor according to any one of Claims 1 to 5.
Sewage disposal system the most according to claim 6, it is characterized in that: described sewage disposal system includes, for storing the intermediate pool for the treatment of sewage, anaerobic aerobic integratedization reactor and second pond, arranging, between described intermediate pool and described anaerobic aerobic integratedization reactor, the pipeline that treatment sewage causes described anaerobic unit;Sewage after processing is set between described anaerobic aerobic integratedization reactor and described second pond and causes the pipeline of second pond.
CN201520899377.5U 2015-11-10 2015-11-10 Good oxygen integrated reactor of anaerobism Active CN205527993U (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106430584A (en) * 2016-10-20 2017-02-22 王海燕 Baffled bioreactor
CN108191048A (en) * 2017-12-29 2018-06-22 湖南中集环境投资有限公司 A sludge internal circulation MBBR sewage treatment device and its application
CN112320950A (en) * 2020-11-09 2021-02-05 上海复森环境科技发展有限公司 A membrane anaerobic and MBBR membrane aerobic integrated sewage treatment device
CN115893736A (en) * 2022-11-25 2023-04-04 苏州仕净科技股份有限公司 Restaurant wastewater treatment process

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106430584A (en) * 2016-10-20 2017-02-22 王海燕 Baffled bioreactor
CN108191048A (en) * 2017-12-29 2018-06-22 湖南中集环境投资有限公司 A sludge internal circulation MBBR sewage treatment device and its application
CN112320950A (en) * 2020-11-09 2021-02-05 上海复森环境科技发展有限公司 A membrane anaerobic and MBBR membrane aerobic integrated sewage treatment device
CN115893736A (en) * 2022-11-25 2023-04-04 苏州仕净科技股份有限公司 Restaurant wastewater treatment process

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