CN105585230A - Sewage treatment device - Google Patents

Sewage treatment device Download PDF

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Publication number
CN105585230A
CN105585230A CN201610144285.5A CN201610144285A CN105585230A CN 105585230 A CN105585230 A CN 105585230A CN 201610144285 A CN201610144285 A CN 201610144285A CN 105585230 A CN105585230 A CN 105585230A
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China
Prior art keywords
waterpower
sewage
overflow water
treatment plant
biofilm reactor
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CN201610144285.5A
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Chinese (zh)
Inventor
陈建和
陈慧颖
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Yixing Lyuya Environment Engineering Co Ltd
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Yixing Lyuya Environment Engineering Co Ltd
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Priority to CN201610144285.5A priority Critical patent/CN105585230A/en
Publication of CN105585230A publication Critical patent/CN105585230A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/302Nitrification and denitrification treatment

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  • 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)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention discloses a sewage treatment device. The device comprises a first water power distributor, a second water power distributor, a third water power distributor, a fourth water power distributor, a fifth water power distributor, an A-level biofilm reactor, a B-level biofilm reactor, a first overflowing water collection tank, a second overflowing water collection tank, a third overflowing water collection tank, a fourth overflowing water collection tank and a fifth overflowing water collection tank, and the first water power distributor, the A-level biofilm reactor, the first overflowing water collection tank, the second water power distributor, the B-level biofilm reactor, the second overflowing water collection tank, the third water power distributor, a clean-water and sewage separator, the third overflowing water collection tank, the fourth water power distributor, a sterilization and disinfection tank, the fourth overflowing water collection tank, the fifth water power distributor, an electrolytic phosphate removing reactor and the fifth overflowing water collection tank are sequentially connected. The sewage treatment device is low in investment, novel in phosphate removing process, low in operating cost, good in treatment effect and free of secondary pollution.

Description

A kind of sewage-treatment plant
Technical field
The present invention relates to technical field of sewage, relate in particular to a kind of sewage-treatment plant.
Background technology
Along with the reinforcement of domestic and international Urbanization Construction dynamics, the dilatation speed in cities and towns is more and more faster, and day increasinglyThe fast generation of urbanization population, along with the raising of people's living standard, in the sanitary sewage discharging notBut contain a certain amount of organic matter and ammonia nitrogen, and contain the pollutant such as germ, phosphorus, if do not dealt carefully with,To have a strong impact on surrounding environment. Therefore, present cities and towns and rural environmental pollution are very outstanding and severe.Although domestic Some Cities And Towns and rural area village village is supporting Sewage Treatment Facilities, invests high, power consumptionGreatly, without dephosphorization process, treatment effect-as, operational administrative is loaded down with trivial details. Therefore we have invented a kind of equipmentReduced investment, dephosphorization process is new, operating cost is low, treatment effect is good, the small towns of non-secondary pollution life dirtyWater treatment plant's (station) technique and complexes thereof.
Current conventional domestic sewage processing method mainly contains:
1. biological contact oxidation process technique
Its advantage has:
(1) biological concentration is high, and the ability of anti-shock loading is stronger;
(2) mass transfer condition is good, and coefficient of oxygen utilization is high, and power consumption is few;
(3) sludge creation amount is less, and does not have the problem of sludge bulking;
(4) do not need sludge reflux, operating cost is low;
(5) specific area of filler is large, and floor space is less.
Its shortcoming is:
(1) on filler, biomembrane actual quantity becomes with BOD loading. BOD loading is high, biomembrane numberAmount is many; Vice versa;
(2) biofilm biomass increases with load, loads too high, and biomembrane is blocked up, fills out at someIn material, be easy to stop up;
(3) because filler setting makes the structure of oxidation pond comparatively complicated, the installation and maintenance of aerator is notAs activated sludge process is come conveniently;
(4) filler is selected improperly, can have a strong impact on the normal use of contact oxidation method technique.
2.SBR method technique
Its advantage has:
(1) desirable plug-flow process increases biochemical reaction motive force, and efficiency improves, anaerobism, good in pondOxygen is in alternating state, good purification;
(2) operational effect is stable, and sewage precipitates under desirable inactive state, needs short, efficiency of timeHeight, effluent quality is good;
(3) anti impulsion load, has the processing water of delay in pond, sewage is had to dilution, cushioning effect, hasThe impact of the effect opposing water yield and organic dirt;
(4) the each operation in technical process can be adjusted according to water quality, the water yield, flexible operation;
(5) treatment facility is few, simple structure, convenient operation and maintenance management;
(6) in reaction tank, there is DO, BOD5 concentration gradient, effectively control activated sludge bulking;
(7) SBR method system itself is also suitable for combined type building method, is beneficial to the enlarging of waste water treatment plantAnd transformation;
(8) denitrogenation dephosphorizing, suitably Controlling operation method, realizes aerobic, anoxic, anaerobic state alternately,There is good Nitrogen/Phosphorus Removal;
(9) technological process is simple, cost is low. Main equipment only has a batch-type batch reactor, without twoHeavy pond, sludge reflux system, regulating reservoir, preliminary sedimentation tank also can omit, characteristics of compact layout, small accommodation area.
Its shortcoming is:
(1) automation control requires high;
(2) when water discharge time short (when intermittent drainage), and draining, require not stir precipitating sludge layer, because ofAnd need special drainage equipment (straining hydrophone), and very high to straining the requirement of hydrophone;
(3) equipment for after-treatment requires large: as very large in sterilizing equipment decontaminating apparatus, contact chamber volume is also very large, pumping equipmentAs also very large in drainage pipeline;
(4) owing to not establishing preliminary sedimentation tank, easily produce scum silica frost, scum problem is not yet properly settled.
3.A/O biological treatment
Its advantage has:
(1) flow process is simple, does not need additional carbon and rear aeration tank, taking raw sewage as carbon source, builds and fortuneRow expense is lower;
(2) denitrification is front, nitrated rear, establishes interior circulation, using the organic substrates in raw sewage as carbonSource, effective, anti-nitration reaction is abundant;
(3) aeration tank, rear, makes denitrification residue be able to further removal, has improved processing water water quality;
(4) A section stirs, and only rises and makes sludge suspension, and avoid the increase of DO. The leading portion of O section adopts strongAeration, back segment reduces tolerance, the DO content of interior circulation fluid is reduced, to ensure the anaerobic condition of A section.
Its shortcoming is:
(1) owing to there is no independently sludge reflux system, thereby can not turn out the dirt with unique functionMud, the degradation rate of hard-degraded substance is lower;
(2), if will improve nitric efficiency, must strengthen nitrate recirculation ratio, thereby strengthen operating cost. From outside,Interior circulation fluid, from aeration tank, contains certain DO, makes A section be difficult to the anaerobic condition that keeps desirable,Affect denitrification effect, denitrification percent is difficult to reach 90%;
(3) influence factor hydraulic detention time (nitrated > 6h, denitrification < 2h), recycle ratio MLSS(> 3000mg/L), sludge age (> 30d), N/MLSS rate of load condensate (< 0.03), water inlet total nitrogenConcentration (< 30mg/L).
Summary of the invention
The technical problem to be solved in the present invention is, provides a kind of suitable cities and towns, village, village sanitary sewage to useAnd have that cost of investment is low, technological process is simple, capacity of resisting impact load is strong, Nitrogen/Phosphorus Removal is excellent,Floor space is little, effluent quality good, operation energy consumption is low, automaticity is high, management easy to operate, without twoThe sewage-treatment plant of inferior pollution.
The technical solution adopted for the present invention to solve the technical problems is:
The invention provides a kind of sewage-treatment plant, comprise waterpower distributor, biofilm reactor, overflowAdfluxion tank, the separator of removing contamination, sterilizing pond and electrolysis dephosphorizing reactor;
Described waterpower distributor comprises that a waterpower distributor, No. two waterpower distributors, No. three waterpower distributeDevice, No. four waterpower distributors and No. five waterpower distributors;
Described biofilm reactor comprises A level biofilm reactor and B level biofilm reactor;
Described overflow water leg comprises that an overflow water leg, No. two overflow water legs, No. three overflows catchmentGroove, No. four overflow water legs and No. five overflow water legs;
A described waterpower distributor, described A level biofilm reactor, a described overflow water leg,Described No. two waterpower distributors, described B level biofilm reactor, described No. two overflow water legs, described inNo. three waterpower distributors, described in remove contamination separator, described No. three overflow water legs, described No. four waterpower divideCloth device, described sterilizing pond, described No. four overflow water legs, described No. five waterpower distribute, described electricitySolution dephosphorizing reactor, described No. five overflow water legs connect successively.
Improve as the one to technical scheme of the present invention, also comprise grid, elevator pump and collecting-tank,Described grid is communicated with described collecting-tank.
Improve as one to technical scheme of the present invention, also comprise water inlet, described water inlet withThe water inlet end of a described waterpower distributor connects.
Improve as one to technical scheme of the present invention, also comprise outlet pipe, described outlet pipe withThe water side of described No. six overflow water legs connects.
Improve as one to technical scheme of the present invention, also comprise stripper plant, described in remove contamination pointPrecipitating sludge in device is back to described A level biofilm reactor through described stripper plant.
Improve as one to technical scheme of the present invention, also comprise preliminary sedimentation tank, described preliminary sedimentation tank withThe described honeycomb inclined-tube filler of removing contamination and all installing respectively in separator, its inclined tube filler angle 45~65 itBetween.
Improve as the one to technical scheme of the present invention, in described biofilm reactor, oxygenation adoptsCorundum ball-type micro-pore aeration.
Improve as the one to technical scheme of the present invention, described overflow water leg is zigzag, instituteStating sewage distributor is stainless steel porous type. Each stage reactor all configures zigzag rectangle overflow water leg,Sewage from flowing to pipeline through the water outlet of porous sewage distributor, has water distribution even through overflow water leg, canFurther reduce organic matter of sewage pollutant, for subsequent treatment eases off the pressure.
Improve as the one to technical scheme of the present invention, what described electrolysis dephosphorizing reactor adopted isThe titanium alloy bar of plating particulate metal material makes positive electrode and metallic titanium plate is made negative electrode, carries out cell reaction generationFerrous phosphate and the dephosphorization of ferric phosphate precipitation. Electrolysis dephosphorization process adopts titanium anode and titanium net cathode electrode pair,Mainly lose electron production ferrous ion by anode, and then react generation precipitation with the phosphate radical in solution,Phosphate radical is removed; Electrolysis nitrogen process adopts titanium net anode and titanium cathode electrode pair, is produced by anodeChlorine enter and produce reaction after solution and generate effective chlorine residue, and with water in ammonia nitrogen produce oxidation reaction, ammoniaNitrogen is oxidized to nitrogen and is removed.
Improve as the one to technical scheme of the present invention, also comprise grille well.
Therefore, sewage-treatment plant provided by the invention, have microorganism nitrated, denitrification function andThe advantage of electrolytic oxidation, absorption, in removing organic matter, killing germ, denitrogenation effectively,Dephosphorization and removal sewage comprise that heavy metal ion is at interior venomous injurant; And low equipment investment, removePhosphorus technique is new, operating cost is low, treatment effect is good, non-secondary pollution.
Brief description of the drawings
Below in conjunction with drawings and Examples, the invention will be further described, in accompanying drawing:
Fig. 1 is the overall structure schematic diagram of sewage-treatment plant of the present invention;
Fig. 2 is the structural representation of the waterpower distributor of sewage-treatment plant of the present invention;
Fig. 3 is the structural representation of the electrolysis dephosphorizing reactor of sewage-treatment plant of the present invention;
Now by as follows the label declaration in accompanying drawing: 30 is peasant household, 40 is grille well, and 50 is collecting-tank,60 is blower fan, and 70 is farmland, and 1 is grid, and 2 is elevator pump, and 3 is water inlet, and 4 is that a waterpower is dividedCloth device, 5 is an overflow water leg, and 6 is A level biofilm reactor, and 7 is No. two waterpower distributors,8 is B and biofilm reactor, and 9 is No. two overflow water legs, and 10 is No. three waterpower distributors, and 11 areThe separator of removing contamination, 12 is No. three overflow water legs, and 13 is No. four waterpower distributors, and 14 is sterilizing pond,15 is No. four overflow water legs, and 16 is No. five waterpower distributors, and 17 is electrolysis dephosphorizing reactor, and 18 areNo. five overflow water legs, 19 is outlet pipe, and 20 is air-lift device, and 41 is distributor porous plate, and 51 arePlating ruthenium titanium web plate, 52 is titanium plate, 53 is porous plate.
Detailed description of the invention
In order to make object of the present invention, technical scheme and advantage clearer, below in conjunction with accompanying drawing andEmbodiment, is further elaborated to the present invention. Should be appreciated that concrete enforcement described hereinExample only, in order to explain the present invention, is not intended to limit the present invention.
In preferred embodiment of the present invention, Fig. 1 is the overall structure schematic diagram of sewage-treatment plant of the present invention,As shown in Figure 1, the sewage-treatment plant of the specific embodiment of the invention, comprises waterpower distributor, biomembraneReactor, overflow water leg, the separator 11 of removing contamination, sterilizing pond 14 and electrolysis dephosphorizing reactor 17;
Waterpower distributor comprises waterpower distributor 4, No. two waterpower distributors 7, No. three waterpower distributors10, No. four waterpower distributors 13 and No. five waterpower distributors 16;
Biofilm reactor comprises A level biofilm reactor 6 and B level biofilm reactor 8;
Overflow water leg comprises overflow water leg 5, No. two overflow water legs 9, No. three overflow water legs12, No. four overflow water legs 15 and No. five overflow water legs 18;
Waterpower distributor 4, A level biofilm reactor 6, overflow water leg 5, No. two waterpowerDistributor 7, B level biofilm reactor 8, No. two overflow water legs 9, No. three waterpower distributors 10, clearPollution discharge separator 11, No. three overflow water legs 12, No. four waterpower distributors 13, sterilizing pond 14, fourNumber overflow water leg 15, No. five waterpower distribute 16, electrolysis dephosphorizing reactor 17, No. five overflow water legs18 connect successively.
Sewage-treatment plant of the present invention also comprises grid 1, elevator pump 2 grille wells 40 and collecting-tank 50,Grid 1 is communicated with collecting-tank 50, and collecting-tank is used for collecting sewage, the balanced water yield, water quality; Also comprise intoThe mouth of a river 3 and outlet pipe 19, water inlet 3 is connected with the water inlet end of a waterpower distributor 4, outlet pipe 19Be connected with the water side of No. six overflow water legs 15, also comprise stripper plant 20, remove contamination in separator 11Precipitating sludge be back to A level biofilm reactor 6 through stripper plant 20.
Particularly, the water after grid 1 is removed contamination, from flowing to collecting-tank, is promoted to water inlet 3 by elevator pump 2Be connected with a waterpower distributor 4, carry out equal water distribution through a waterpower distributor 4, No. one waterpower distributesThe moisture of device 4 is distributed in A level biofilm reactor 6, and the water outlet of A level biofilm reactor 6 enters No. one5, numbers overflow water legs 5 of overflow water leg are connected with No. two waterpower distributors 7, No. two waterpower distributors7 sewage is distributed in B level biofilm reactor 8, and B level biofilm reactor 8 is from flowing to overflow collection No. three9, No. three overflow water legs 9 of tank are connected with No. three waterpower distributors 10, No. three waterpower distributors 10Water outlet is to the separator 11 of removing contamination, and the water outlet of the separator 11 of removing contamination is from flowing to overflow water leg 12, four No. fourNumber overflow water leg 12 is connected with No. four waterpower distributors 13, and the sewage of No. four waterpower distributors 13 distributesIn sterilizing pond 14, the sewage self-flowing in sterilizing pond 14 enters No. five overflow water legs 15, No. fiveOverflow water leg 15 is connected with No. five waterpower distributors 16, and the sewage of No. five waterpower distributors 16 evenly dividesBe distributed in electrolysis dephosphorizing reactor 17, sewage is through anode and cathode electrolysis dephosphorization, and the water outlet of anode and cathode electrolysis dephosphorization extremely18, No. six overflow water legs 18 of No. six overflow water legs are connected with outlet pipe 19, outside outlet pipe 19 connectsComb qualified discharge. The precipitating sludge of removing contamination in separator 11 in addition, is back to A through stripper plant 20Level biofilm reactor 6, together flows into B level biological processor 8 after mixing with water inlet, carries out subsequent treatment,Residue dirt drains into farmland 70 outward and makees fertilizer.
In the specific embodiment of the invention, the material of the shell of a whole set of sewage-treatment plant (body) can root JuActual requirement is selected the material such as fiberglass, carbon steel or stainless steel.
The present invention also comprises blower fan 60, and what select here is swinging blower fan. For biofilm reactor providesOxygen carries out aeration biochemical, reaches qualified discharge.
Fig. 2 is the structural representation of the waterpower distributor of sewage-treatment plant of the present invention, waterpower distributor bagDraw together distributor porous plate 41, the waterpower distributor in figure is served respectively A level biofilm reactor 6, BLevel biofilm reactor 8, the separator 11 of removing contamination, sterilizing pond 14 and electrolysis dephosphorizing reactor 17Water distribution work, its effect is under the prerequisite of water distribution uniformity, the turbulent flow of pre-bilge water resisting.
Fig. 3 is the structural representation of the electrolysis dephosphorizing reactor of sewage-treatment plant of the present invention, electrolysis dephosphorizationReactor comprises spaced plating ruthenium titanium web plate 51 and titanium plate 52, titanium web plate 51 and titanium plateBetween 52, be also provided with porous plate 53, the sewage after sterilizing catchments and goes out with waterpower distributor through overflowThe mouth of a river flow to electrolysis dephosphorizing reactor certainly, in the ferrous ion producing by anode and iron ion and sewagePhosphate reaction, generates ferrous phosphate and ferric phosphate precipitation: part iron ion within the scope of different pH values withThe hydroxy compounds of the OH-reaction generation iron in solution and ferrous hydroxide (FeOH2), iron hydroxide(FeOH3) precipitation; The micro-bubble that the hydrogen (H2) that negative electrode produces simultaneously forms, has promoted phosphoric acidThe flocculation rate of radical ion (PO43-), has increased the flocculating effect of phosphate anion (PO43-), fromAnd made a concentrated effort to finish the absorption of ferrous hydroxide (FeOH2), iron hydroxide (FeOH3), precipitate phosphoric acid rootIon (PO43-), when ferrous hydroxide, ferric hydroxide precipitate, a large amount of phosphate radicals is being adsorbed on surfaceIon (PO43-) precipitation task, has realized omnidistance sewage denitrification and dephosphorization, has removed organic matter without interpolation timesWhat medicament and the object of qualified discharge.
Sewage-treatment plant of the present invention is first at A level biofilm reactor 6 and B level biofilm reactorIn 8 operation, utilize facultative microbe and aerobic microbiological to carry out organic metabolism, through the separator of removing contaminationPhegma in 11 be back to A level biofilm reactor 6 by air-lift device 20 and B level biomembrane anti-Answer in device 8, form nitrification and denitrification reaction. Now aerobic-anaerobic microbe transforms the organic nitrogen in sewageResolve into NH3-N, utilize organic carbon source to make electron donor simultaneously, NO2, NO3-N are changed into N3,And utilize part organic carbon and NH3-N to synthesize new cellular material. At B level biofilm reactor,Under the oxygenic aeration effect of micro-hole aerator, organic matter obtains further oxidation Decomposition, simultaneously in carbonizationEffect under, carry out nitration reaction, under the interaction of aerobic-anaerobic microbe and aerobic microbiological, finally disappearExcept polluted by nitrogen, reduce phosphorus content.
Sewage-treatment plant of the present invention is first at A level biofilm reactor 6 and B level biofilm reactorIn the operation of 8 denitrogenation dephosphorizing, the basicity of an output will be produced. Therefore, a whole set of sewage disposal process withoutAdd alkali, regulate pH value.
The technique of sewage-treatment plant of the present invention is applicable to other sewage and industrial wastewater organic matter and de-In the operation of nitrogen dephosphorization.
Sewage-treatment plant performance requirement of the present invention is as follows:
(1) influent quality requirement
The requirement of table 2-1 influent quality
Water quality parameter CODcr BOD5 SS TP NH3-N TN Vegetable and animals oils pH
Value (mg/L) ≤500 ≤250 ≤300 ≤8 ≤30 ≤40 ≤3 6-9
(2) effluent quality index
After processing, effluent quality reaches and is better than " urban wastewater treatment firm pollutant emission standard "(GB18918-2002) the one-level A standard in.
Table 2-2 effluent quality index
Water quality parameter CODcr BOD5 SS TP NH3-N TN Vegetable and animals oils Colibacillus of excrement number pH
Value (mg/L) ≤50 ≤10 ≤10 ≤0.1 ≤0.5 ≤2 ≤1 ≤1000MPN/L 6-9
Note: the outer numerical value of bracket is water temperature>control index 12 DEG C times, the outer numerical value of bracket is water temperature<12 DEG CTime control index.
(3) removal effect
Table 2-3 removal efficiency
Water quality parameter CODcr BOD5 SS TP NH3-N TN Vegetable and animals oils Colibacillus of excrement number pH
Clearance 90% 96% 97% 98% 98% 95% 67% - -
The advantage of sewage-treatment plant of the present invention has:
(1) apparatus structure compactness of the present invention, handling process is simple.
Device collection sand setting of the present invention, nitrated, denitrification, sludge reflux, sterilization, the separation of removing contamination,The operations such as electrolysis dephosphorization are in one, and integrated degree is high, and pipeline connects few, and novel, volume is little,Small accommodation area.
(2) building is few, capital cost is low.
Building floor space of the present invention is little, only needs a collecting-tank and Equipment Foundations, heavy without biochemistryThe capital construction facilities such as pond, shallow lake, intermediate pool.
(3) energy consumption is little, operating cost is low.
In course of reaction of the present invention, without heating, add soda acid, and need not add additional agent, so operationConvenient, simple to operate, wide accommodation, automaticity is high simultaneously, the sewage between each reative cellBe gravity flow operation, and sludge reflux is by stripping reflux, without elevator pump is installed, in whole invention, onlyProduce electric power at blast aerator and device for removing phosphorous by electrolysis. Therefore whole treatment system operating costLow compared with conventional treatment equipment, the cost of one ton of sanitary sewage of every processing is only 0.15~0.18 yuan.
(4) good, the non-secondary pollution for the treatment of effect
The present invention adopts AAOR bio membrane process maturation, reliable and stable, and operating maintenance is very convenient,Without carrying out a large amount of sludge refluxes. Cycle of operation flexibility and changeability, anti impulsion load performance is strong. Can realize sameTime nitrated/denitrification to remove CODcr and ammonia nitrogen etc. in sewage, and can realize excessive biological oxidation, processEfficiency is high, and effluent quality is good. Dephosphorization adopts efficient electrolysis dephosphorization, and clearance reaches more than 98%. ThisOutward, by precipitate and separate device surface loading, available depth, the design parameters such as slip bucket inclination angle rationally selectSelect, thereby improved the effect of Separation of Solid and Liquid.
Due to this process using AAOR biomembrance process, the buried design of equipment, upper table greening, simultaneously at exhaust outletOdor removal is set, therefore the peculiar smell of complete equipment is relatively less, basic free from extraneous odour produces. Sewage disposal systemIn system, noise source is mainly blower fan. For this reason, our elite slow-revving swinging blower fan, wind usedMachine noise is little, and in blower fan is imported and exported, muffler is set, and fills soft joint, base in the outlet of blower fanShock absorber is set, and through this series of control, noise can reach the standard in two class areas.
Qing wu separator sludge reflux is further biochemical to one-level biofilm reactor, thereby reduces sludge quantity.In sludge digestion device, remain a small amount of mud and regularly process, general annual 1~2 time. Therefore, the present inventionIn running, can not produce the secondary pollution of foul smell, noise and mud.
(5) reduced investment, instant effect
Equipment of the present invention is the integral life sewage set treatment device of buried glass fibre reinforced plastic structure, fortuneTo the on-the-spot inlet tube and outlet tube of connecting, air inlet pipe and power supply, can normally move. The material that equipment adopts isMechanical winding glass reinforced plastic composite construction, the moulding of producing once, has four layers of protective materials. Have high strength,The functions such as antiseep, corrosion-resistant, anti-aging and ultraviolet radiation resisting, long service life, normal use canWith 50 years.
(6) easy to maintenance, manageability
The present invention adopts the PLC computer program control of remote automation, has the warning function of automation,Discovering device fault, processes accordingly and adjusts in time, manages without many people, reduces operationAdministrative staff, simple to operate, convenient management, improves the efficiency of management, effectively reduces maintenance cost.
(7) unique denitrogenation, dephosphorization apparatus
The present invention adopts efficient anodic-cathodic electrolysis principle, ferrous ion and iron ion wadding that anode is producedPhosphate reaction solidifying, that adsorb in sewage generates ferrous phosphate and ferric phosphate precipitation, realizes without adding medicineAgent completes efficient dephosphorization. As the nucleus equipment of electrolysis dephosphorization--positive plate and minus plate all adopt particulate metalThe Titanium alloy bar of material makes positive electrode and metallic titanium plate is made negative electrode, carries out cell reaction and generates phosphoric acid AsiaIron and the dephosphorization of ferric phosphate precipitation. Its denitrogenation, dephosphorization efficiency by using are high, and equipment is durable in use is difficult for passivation.
Should be understood that, for those of ordinary skills, can be changed according to the above descriptionEnter or convert, and all these improvement and conversion all should belong to the protection domain of claims of the present invention.

Claims (10)

1. a sewage-treatment plant, is characterized in that, comprises waterpower distributor, biofilm reactor, overflow water leg, the separator of removing contamination, sterilizing pond and electrolysis dephosphorizing reactor;
Described waterpower distributor comprises a waterpower distributor, No. two waterpower distributors, No. three waterpower distributors, No. four waterpower distributors and No. five waterpower distributors;
Described biofilm reactor comprises A level biofilm reactor and B level biofilm reactor;
Described overflow water leg comprises an overflow water leg, No. two overflow water legs, No. three overflow water legs, No. four overflow water legs and No. five overflow water legs;
A described waterpower distributor, described A level biofilm reactor, a described overflow water leg, described No. two waterpower distributors, described B level biofilm reactor, described No. two overflow water legs, described No. three waterpower distributors, the described separator of removing contamination, described No. three overflow water legs, described No. four waterpower distributors, described sterilizing pond, described No. four overflow water legs, described No. five waterpower distribute, described electrolysis dephosphorizing reactor, described No. five overflow water legs connect successively.
2. sewage-treatment plant according to claim 1, is characterized in that, also comprises grid, elevator pump and collecting-tank, and described grid is communicated with described collecting-tank.
3. sewage-treatment plant according to claim 1, is characterized in that, also comprises water inlet, and described water inlet is connected with the water inlet end of a described waterpower distributor.
4. sewage-treatment plant according to claim 1, is characterized in that, also comprises outlet pipe, and described outlet pipe is connected with the water side of described No. six overflow water legs.
5. sewage-treatment plant according to claim 1, is characterized in that, also comprises stripper plant, described in the precipitating sludge of removing contamination in separator be back to described A level biofilm reactor through described stripper plant.
6. sewage-treatment plant according to claim 1, is characterized in that, also comprises preliminary sedimentation tank, described preliminary sedimentation tank with described in the honeycomb inclined-tube filler of removing contamination and all installing respectively in separator, its inclined tube filler angle is between 45~65.
7. sewage-treatment plant according to claim 1, is characterized in that, in described biofilm reactor, oxygenation adopts corundum ball-type micro-pore aeration.
8. sewage-treatment plant according to claim 1, is characterized in that, described overflow water leg is zigzag, and described sewage distributor is stainless steel porous type.
9. sewage-treatment plant according to claim 1, it is characterized in that, the titanium alloy bar of what described electrolysis dephosphorizing reactor adopted is plating particulate metal material is made positive electrode with metallic titanium plate is made negative electrode, carries out that cell reaction generates ferrous phosphate and ferric phosphate precipitates dephosphorization.
10. sewage-treatment plant according to claim 1, is characterized in that, also comprises grille well.
CN201610144285.5A 2016-03-14 2016-03-14 Sewage treatment device Pending CN105585230A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107459175A (en) * 2017-09-21 2017-12-12 陕西泽远石油技术服务有限公司 Produced Water In Oil-gas Fields, Ngi reinjection technology technique up to standard and device

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20030013491A (en) * 2003-01-10 2003-02-14 신성메디아 주식회사 Sewage treatment system utilized bio-ball, bio-tank and lock-filter
CN200955034Y (en) * 2006-09-07 2007-10-03 曾郴林 Integrated hospital's sewage treatment apparatus
CN101362624A (en) * 2008-07-10 2009-02-11 昆明理工大学 Dispersive high-efficiency purification treatment equipment of sewage
CN201660524U (en) * 2009-12-09 2010-12-01 苏州市德健环保工程有限公司 Medium-size or small-size high-efficiency modularized terminal treatment device for domestic sewage treatment
CN202011777U (en) * 2010-11-30 2011-10-19 株洲南方宇航环保工业有限公司 Filler device for integrated sewage treatment equipment
CN204039217U (en) * 2014-07-29 2014-12-24 沭阳嘉净环保科技有限公司 Integral life sewage focuses on equipment
CN204298194U (en) * 2014-01-24 2015-04-29 重庆木兰环保工程有限公司 A kind of integrated sewage treating apparatus
CN204385028U (en) * 2014-12-23 2015-06-10 重庆澄露环境工程有限公司 A kind of waste disposal plant
CN104973727A (en) * 2015-05-07 2015-10-14 广西壮族自治区环境保护科学研究院 Integrated sewage treatment facilities
CN205710286U (en) * 2016-03-14 2016-11-23 宜兴市绿亚环境工程有限公司 A kind of sewage-treatment plant

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20030013491A (en) * 2003-01-10 2003-02-14 신성메디아 주식회사 Sewage treatment system utilized bio-ball, bio-tank and lock-filter
CN200955034Y (en) * 2006-09-07 2007-10-03 曾郴林 Integrated hospital's sewage treatment apparatus
CN101362624A (en) * 2008-07-10 2009-02-11 昆明理工大学 Dispersive high-efficiency purification treatment equipment of sewage
CN201660524U (en) * 2009-12-09 2010-12-01 苏州市德健环保工程有限公司 Medium-size or small-size high-efficiency modularized terminal treatment device for domestic sewage treatment
CN202011777U (en) * 2010-11-30 2011-10-19 株洲南方宇航环保工业有限公司 Filler device for integrated sewage treatment equipment
CN204298194U (en) * 2014-01-24 2015-04-29 重庆木兰环保工程有限公司 A kind of integrated sewage treating apparatus
CN204039217U (en) * 2014-07-29 2014-12-24 沭阳嘉净环保科技有限公司 Integral life sewage focuses on equipment
CN204385028U (en) * 2014-12-23 2015-06-10 重庆澄露环境工程有限公司 A kind of waste disposal plant
CN104973727A (en) * 2015-05-07 2015-10-14 广西壮族自治区环境保护科学研究院 Integrated sewage treatment facilities
CN205710286U (en) * 2016-03-14 2016-11-23 宜兴市绿亚环境工程有限公司 A kind of sewage-treatment plant

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
姜湘山,詹友良主编: "《污(废)水处理技术与工程实例》", 31 January 2012, 机械工业出版社 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107459175A (en) * 2017-09-21 2017-12-12 陕西泽远石油技术服务有限公司 Produced Water In Oil-gas Fields, Ngi reinjection technology technique up to standard and device

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