CN208265954U - SBBR Combined sewage processing equipment - Google Patents
SBBR Combined sewage processing equipment Download PDFInfo
- Publication number
- CN208265954U CN208265954U CN201820221140.5U CN201820221140U CN208265954U CN 208265954 U CN208265954 U CN 208265954U CN 201820221140 U CN201820221140 U CN 201820221140U CN 208265954 U CN208265954 U CN 208265954U
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- Prior art keywords
- sbbr
- aeration
- sewage
- aerator
- processing equipment
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Abstract
The utility model relates to SBBR Combined sewage processing equipments, the improvement including aerator and layout and electrochemical reactor;Aerator lines up V-type sequence and is known as V-type sequence device, and aerator includes impulse generator and air blower;Electrochemical reactor is by wastewater electrochemical treatment catalytic oxidation treatment;SBBR technique is increased into electrochemical catalytic oxidation process flow, it handles in sewage containing reluctant pollution factors such as phenols, aeration area is greatly strengthened by optimal aeration quantity and V-type aeration method, save aeration pool space, meet process sewage target Scheme from the basic SBBR that solves, not only there is good denitrogenation dephosphorizing efficiency to also add sewage treatment capacity, but also realize sewage treatment integration, occupied area is few, can save part capital expenditure and operational administrative is more convenient.
Description
Technical field
The utility model relates to the improvement of technical field of sewage and sewage treatment process, since phenol draws in the environment
The pollution risen is more serious, so the technique not only solves the contaminant problems such as phenol and also improves Nitrogen/Phosphorus Removal, more specifically
Ground, which is said, refers to SBBR Combined sewage processing equipment.
Background technique
It is existing due to SBBR Combined sewage processing equipment method, forefathers' research is less, and reliability data is less, and technique is also
It need to the summing up experience in a large amount of practices.
" zero-emission " may be implemented to solve the industrial wastewater that high concentration is difficult to degrade, sewage treatment one may be implemented
The problems such as change, occupied area is few, saves fund, convenient operation and management, proposes SBBR Combined sewage processing equipment.
Therefore, it is necessary to develop SBBR Combined sewage processing equipment.
Summary of the invention
The purpose of the utility model is to overcome the defects of the prior art, provide SBBR Combined sewage processing equipment, real
Now raising filling gas quality is accurate, and frequency converter turning operation facilitates high-efficient.
In order to solve the above technical problems, the utility model provide SBBR Combined sewage processing equipment, including aeration tank and
Electrochemical reactor, the aeration tank are V-type sequential aeration device, and the aerator includes impulse generator and air blast
Machine, the electrochemical reactor is by wastewater electrochemical treatment catalytic oxidation treatment.
Further scheme is that the aerator is aerated using pulsed, and shape is sector.
Further scheme is that resistance type air bearing dustproof cover is installed in the aperture of the aerator, prevents sludge from entering device.
Further scheme is that the air bearing dustproof cover is equipped with solarization air cap.
Further scheme is that the phenols electrolytics formula in the electrolytics reactor is R+MOx (OH) y → CO2+
Phenols harmful substance is converted to harmless substance by MOx+yH++e- or R+MOx+1 → MOx+RO.
Further scheme is that the sludge of the sludge-tank transports to soot by dewaterer dehydration and sludge are outer together.
Further scheme is that additive liquid chlorine, ozone, chlorine dioxide, ultraviolet light are added in the sterilization pool and carries out disinfection.
The beneficial effect of the utility model compared with prior art is: SBBR technique is increased electrochemical catalytic oxidation processing
Process is handled in sewage containing reluctant pollution factors such as phenols, is greatly enhanced by optimal aeration quantity and V-type aeration method
Aeration area saves aeration pool space, increases the contact area of sewage and activated sludge, solves SBBR compound work from basic
Skill handles sewage target Scheme, and the processing capacity of high pollution sewage is not only also added with good denitrogenation dephosphorizing efficiency, and
And sewage treatment integration is realized, occupied area is few, can save part capital expenditure and operational administrative is more convenient.It can satisfy
The requirement of Small Urban sewage treatment at this stage technically and economically, this method have important practical application value.
Detailed description of the invention
Fig. 1 is the V-type train pulse Aeration tank structure schematic diagram of the utility model specific embodiment;
Fig. 2 is the intermission aeration apparatus structure schematic diagram of the utility model specific embodiment;
Fig. 3 is the equipment and process structure schematic diagram of the utility model specific embodiment.
Appended drawing reference: 1, aeration tank;2, aerator;21, resistance type air bearing dustproof cover;22, solarization air cap;23, slot;
24, impulse generator;25, air blower.
Specific embodiment
The utility model is described in further detail with reference to the accompanying drawing.
As shown in Figure 1 to Figure 3, specific embodiment of the utility model, including aeration tank 1 and electrochemical reactor, aeration
Pond 1 is V-type sequential aeration device 2, and aerator 2 includes impulse generator 24 and air blower 25, and electrochemical reactor will be dirty
Aqueous electrochemical catalytic oxidation treatment;
The SBBR Combined sewage process flow is as follows:
A, it is fed sequentially into coarse rack and fine fack into sewage, removes big rubbish and residue;
B, conditioning tank is entered back into, controls the pH value and water of sewage, and retain 8 hours;
C, sewage is then passed through into primary sedimentation tank, sludge settling is removed;
D, sewage is sent into V-type sequential aeration pond 1 again with intake pump, adjusts aerator 2 as staggered form aeration, adjustment exposes
Tolerance optimum value is in 72~90L/h;
E, the sewage after aeration enters electrochemical reactor, is electrolysed by positive and negative anodes, is electrolysed to phenols harmful substance,
Resolve into innocuous substance;
F, the sewage after electrochemical reactor is electrolysed enters back into biomembrane processing pond, with blender, number hole aerator
Activated sewage processing is carried out with air pump;
G, biomembrane processing pond is equipped with sludge mouth and sludge-tank and is discharged sludge, water trap will treated sewage transport to disappearing
Malicious pond;
H, it is disinfected after discharge purified water;
I, sludge is transported to soot.
Further, the V-shaped sequence arrangement in 1 pool wall of aeration tank of aerator 2, air blower 25 is against in aeration tank 1
The V-shaped blowing of sewage, using impulse generator 24 pulsed be aerated, shape be sector, bottom be equipped with slot 23, face expose
Gas pond 1, such V-type intersect aeration, enhance aeration area, save 1 space of aeration tank.
Further, resistance type air bearing dustproof cover 21 is installed in the aperture of aerator 2, prevents sludge from entering device.
Further, air bearing dustproof cover is equipped with solarization air cap 22, blows out bubble and is aerated to sewage, and aeration raises gas purification effect
Fruit is good.
Further, phenols electrolytics formula is MOx+H2O=MOx (OH)+H++e-=MOx (OH)=MOx+1+H
++ e- is converted to harmless substance by phenols harmful substance.
Further, the sludge of sludge-tank transports to soot by dewaterer dehydration and sludge are outer together.
Further, additive liquid chlorine, ozone, chlorine dioxide, ultraviolet light are added in sterilization pool to carry out disinfection.
Coarse rack: sewage enters coarse rack, removes large-scale pollutant;
Fine fack: sewage enters fine fack, removes small-sized pollutant;
Conditioning tank: regulating water quality water, adjustment pH value, the residence time 8 hours;
Primary sedimentation tank: sewage layering removes sinker and floating material;
Aeration tank 1: aerator 2 uses pulsed aeration, is arranged in 1 pool wall of aeration tank by V-type sequence.It is acted on
It is to make activated sludge in aeration tank 1 sufficiently and waste water, has oxygenolysis to the organic pollutant in sewage.
Electrochemical reactor: the technique uses direct oxidation method, and principle is: being generated by metal oxide MOx (resistance)
The high oxide MOx+1 that the aoxidizes pollutant preferably and free radical MOx (OH) for preferably making pollutant oxidizing fire, makes pollutant
Noxious material is changed into innocuous substance, or the organic matter of biocompatible is converted into biocompatible substance (such as aromatic substance
Ring-opening oxidation is fatty acid), further to implement biological treatment.
Reaction equation is as follows:
MOx+H2O→MOx(·OH)+H++e-
Then existing oxygen reaction on the hydroxyl free radical and anode adsorbed, and the oxygen in hydroxyl free radical is made to be transferred to gold
Belong to oxide lattice, form high oxide MOx+1:
MOx(·OH)→MOx+1+H++e-
When organic matter is not present in solution, the active oxygen following steps of two states carry out oxygen evolution reaction:
MOx(·OH)→O2+MOx+H++e-
MOx+1→MOx+O2
When, there are when oxidable Organic Pollutants R, reaction is as follows in solution:
R+MOx(·OH)y→CO2+MOx+yH++e-
R+MOx+1→MOx+RO
RO is the pollutant after oxidation, nontoxic.The reactor is containing cyanide, is containing phenol, alcohol-containing, nitrogenous organic dyestuff
Wastewater treatment in, direct electrochemical oxidation has all played very effective effect;
Sequencing batch biofilm reactor (SBBR) process is as follows:
The reactor one complete period is total to about 8 hours.After starting SBBR, waste water is transported to reactor by intake pump
In, after water level reaches high water level electrode, self-con-tained unit stops water inlet;Blender starts to stir, and it is anti-to carry out 2 hours anaerobism
It answers;Subsequent air pump is started to work, and is carried out aeration by aeration tank 1 (containing activated sludge) and is kept aeration quantity in 72~90L/h, instead
Answer device denitrification effect best, TN removal rate reaches 73.4%.Flow is adjusted with spinner flowmeter, is aerated aerobic stage totally 5 hours,
It is precipitated 0.5 hour after aeration, starts to drain after precipitating, stop draining when water level reaches lowest water level electrode heel row water control hydrophone,
It finally leaves unused and allows within 0.5 hour activated sludge activity recovery.
SBBR technique is increased electrochemical catalytic oxidation process flow by the utility model, is handled in sewage and is difficult to containing phenols etc.
The pollution factor of processing reaches optimal aeration quantity by improving aerator composition and layout.V-type aeration method greatly enhances
Aeration area saves 1 space of aeration tank, meets process sewage target Scheme from the basic SBBR that solves, not only has good
Good denitrogenation dephosphorizing efficiency also adds sewage treatment capacity, and realizes sewage treatment integration, and occupied area is few, can save
Province part capital expenditure and operational administrative are more convenient.These features can meet Small Urban sewage treatment at this stage in skill
Art and requirement economically, this method have important practical application value.
The foregoing is merely this patent preferred embodiments, not limit this patent range, all using specification and attached
Equivalent structure or equivalent flow shift made by figure content is directly or indirectly used in other relevant technical fields, belongs to
The scope of this patent.
Claims (4)
1.SBBR Combined sewage processing equipment, it is characterised in that: including aeration tank and electrochemical reactor, the aeration tank is
V-type sequential aeration device, the aerator include impulse generator and air blower;The electrochemical reactor is electric by sewage
Chemical catalytic oxidation processing.
2. SBBR Combined sewage processing equipment as described in claim 1, it is characterised in that: the aerator uses pulse
Formula aeration, shape are sector.
3. SBBR Combined sewage processing equipment as claimed in claim 1 or 2, it is characterised in that: the hole of the aerator
Mouth installation resistance type air bearing dustproof cover, prevents sludge from entering device.
4. SBBR Combined sewage processing equipment as claimed in claim 3, it is characterised in that: the air bearing dustproof cover, which is equipped with, to expose
Stomata.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CN201820221140.5U CN208265954U (en) | 2018-02-08 | 2018-02-08 | SBBR Combined sewage processing equipment |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201820221140.5U CN208265954U (en) | 2018-02-08 | 2018-02-08 | SBBR Combined sewage processing equipment |
Publications (1)
Publication Number | Publication Date |
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CN208265954U true CN208265954U (en) | 2018-12-21 |
Family
ID=64675273
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CN201820221140.5U Expired - Fee Related CN208265954U (en) | 2018-02-08 | 2018-02-08 | SBBR Combined sewage processing equipment |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110127929A (en) * | 2018-02-08 | 2019-08-16 | 孙双霜 | SBBR Combined sewage processing equipment and technique |
-
2018
- 2018-02-08 CN CN201820221140.5U patent/CN208265954U/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110127929A (en) * | 2018-02-08 | 2019-08-16 | 孙双霜 | SBBR Combined sewage processing equipment and technique |
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GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20181221 Termination date: 20220208 |
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CF01 | Termination of patent right due to non-payment of annual fee |