CN108101311A - A kind of energy-saving sewage disposal system - Google Patents

A kind of energy-saving sewage disposal system Download PDF

Info

Publication number
CN108101311A
CN108101311A CN201711480836.6A CN201711480836A CN108101311A CN 108101311 A CN108101311 A CN 108101311A CN 201711480836 A CN201711480836 A CN 201711480836A CN 108101311 A CN108101311 A CN 108101311A
Authority
CN
China
Prior art keywords
level
anaerobic pond
aerobic tank
sewage disposal
pond
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201711480836.6A
Other languages
Chinese (zh)
Inventor
王振
陈玮
李桂芬
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tianjin Deqing Science And Technology Co Ltd
Original Assignee
Tianjin Deqing Science And Technology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tianjin Deqing Science And Technology Co Ltd filed Critical Tianjin Deqing Science And Technology Co Ltd
Priority to CN201711480836.6A priority Critical patent/CN108101311A/en
Publication of CN108101311A publication Critical patent/CN108101311A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5281Installations for water purification using chemical agents
    • 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
    • C02F2001/007Processes including a sedimentation step
    • 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
    • C02F2003/001Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
    • 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
    • C02F2003/001Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms
    • C02F2003/003Biological treatment of water, waste water, or sewage using granular carriers or supports for the microorganisms using activated carbon or the like
    • 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
    • C02F3/02Aerobic processes
    • 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
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/104Granular carriers
    • 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
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/105Characterized by the chemical composition
    • C02F3/106Carbonaceous materials
    • 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
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/105Characterized by the chemical composition
    • C02F3/107Inorganic materials, e.g. sand, silicates
    • 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
    • C02F3/02Aerobic processes
    • C02F3/10Packings; Fillings; Grids
    • C02F3/105Characterized by the chemical composition
    • C02F3/108Immobilising gels, polymers or the like
    • 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
    • C02F3/28Anaerobic digestion processes
    • 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
    • C02F3/28Anaerobic digestion processes
    • C02F3/286Anaerobic digestion processes including two or more steps
    • 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

Abstract

The present invention provides a kind of energy-saving sewage disposal systems, including collecting pit, sedimentation basin, flocculation basin, regulating reservoir, aerobic tank, anaerobic pond and aeration tank, wherein described sedimentation basin is divided into first stage precipitation tank, second-level settling pond, three-level sedimentation basin and level Four sedimentation basin, the flocculation basin includes level-one flocculation basin and two level flocculation basin, the anaerobic pond includes common anaerobic pond and ecological anaerobic pond, common anaerobic pond connection adjacent with ecological anaerobic pond, the aerobic tank includes common aerobic tank and ecological aerobic tank, common aerobic tank connection adjacent with ecological aerobic tank.The principles such as processing system provided by the invention make use of current to be freely oriented to, solid free sedimentation in addition to having added agitating device, air blower, avoid the use of mechanical equipment, greatly reduce the energy consumption in sewage disposal process as far as possible.

Description

A kind of energy-saving sewage disposal system
Technical field
The invention belongs to technical field of sewage, in particular to a kind of energy-saving sewage disposal system.
Background technology
With the getting worse of water scarcity situation, the Green GDP construction and cycling that especially country advocates energetically Economic proposition so that enterprise becomes particularly to pay attention to water-saving and emission-reducing with utilization of wastewater resource.In addition, the environmental protection with people The reinforcement of consciousness, the harm of waste water are gradually recognized by people, so as to receive the especially concern of people to the processing of waste water.Cause This, how economy, the raising enterprise water resources comprehensive utilization rate of high efficient and reliable be even up to " zero-emission " standard, be enterprise meet The important process of country, local government or even people's environmental requirement.
Mechanization degree is very high in existing sewage disposal technology, although, on wastewater treatment efficiency very significantly Due to the mechanization of high level, while other environmental problems or energy consumption problem are brought again, undoubtedly by an environment energy Source problem has attracted another environmental energy problem, so how more energy saving handle sewage will be more environmentally-friendlyly Those skilled in the art urgently make great efforts to need the realistic problem solved.
The content of the invention
It is a primary object of the present invention to provide a kind of energy-saving sewage disposal system, it is intended to right on the premise of low energy consumption Sewage is effectively handled.
In order to realize above-mentioned purpose, the present invention provides a kind of energy-saving sewage disposal system, including collecting pit, precipitation Pond, flocculation basin, regulating reservoir, aerobic tank, anaerobic pond and aeration tank,
The sedimentation basin is divided into first stage precipitation tank, second-level settling pond, three-level sedimentation basin and level Four sedimentation basin, and four described heavy Primary strainer, secondary filter, three-level strainer and level Four strainer are transversely provided in the pond of shallow lake respectively, is sunk to different degrees of sewage Shallow lake is handled, and sediment is stopped by strainer, and the position of water inlet pipe is higher than the height of strainer on each sedimentation basin Degree;
The flocculation basin includes level-one flocculation basin and two level flocculation basin, two flocculation basins be upper end opening it is big, under The small taper of end opening, and the flocculation basin upper end is equipped with flocculant feed inlet, and longitudinal agitating device is equipped in the flocculation basin;
The anaerobic pond includes common anaerobic pond and ecological anaerobic pond, common anaerobic pond company adjacent with ecological anaerobic pond It connects, and bottom is equipped with the activated sludge for being mixed with anaerobe carrier granular in the ecological anaerobic pond, sewage is successively by general Logical anaerobic pond and ecological anaerobic pond carry out Anaerobic Treatment;
The aerobic tank includes common aerobic tank and ecological aerobic tank, common aerobic tank company adjacent with ecological aerobic tank It connects, and bottom is equipped with aerobic microbiological carrier granular in the ecological aerobic tank, sewage passes through common aerobic tank and ecology successively Aerobic tank carries out Aerobic Process for Treatment.
Further, the sewage disposal system passes sequentially through connecting pipe connection collecting pit from front to back, level-one is sunk Shallow lake pond, level-one flocculation basin, second-level settling pond, two level flocculation basin, three-level sedimentation basin, regulating reservoir, common anaerobic pond, ecological anaerobism Pond, common aerobic tank, ecological aerobic tank, level Four sedimentation basin, aeration tank, detection cell and cistern, wherein collecting pit pass through multiple Inlet channel connects effluent outfall, and the connecting pipe is zigzag pipeline or straight pipeline, and the zigzag pipeline turns Angle is round and smooth design, and the cistern had not only connected collecting pit but also connected water equipment.
Further, the detection cell is equipped with long-distance intelligent detecting system.
Further, the long-distance intelligent detecting system includes detection module, analog-to-digital conversion module, communication module and remote Journey terminal module;
Wherein, the detection module includes detector, and the detector can detect water quality situation, soda acid degree and dissolved oxygen Situation;
The analog-to-digital conversion module is electrically connected with detection module, and the signal that detection module is gathered is converted into digital letter Number;
The communication module is electrically connected with analog-to-digital conversion module, and communication module receives the number that analog-to-digital conversion module is sent Signal;
Remote terminal module with communication module wireless connection, is handled digital signal data again.
Further, the aperture of filter screen of the primary strainer, secondary filter, three-level strainer and level Four strainer controls respectively In 3-4cm, 1-2cm, 0.5-1cm and 0.2-0.5cm.
Further, the level-one flocculation basin and the two level flocculation basin are poly- using inorganic polymer flocculant It closes one or two kinds of in aluminium chloride, polyaluminium sulfate, poly-ferric chloride or bodied ferric sulfate.
Further, the anaerobe carrier granular and aerobic microbiological carrier granular are zeolite, activated carbon, glass One kind in glass, plastics or synthetic resin.
Further, the anaerobe in the anaerobe carrier granular is nitrobacteria, described aerobic micro- Aerobic microbiological in bio-carrier particle is denitrifying bacteria.
Further, the collecting pit, sedimentation basin, flocculation basin, regulating reservoir, aerobic tank, anaerobic pond and the pond of aeration tank Bottom is equipped with mud discharging mouth.
Further, controllable valve is equipped on the connecting pipe, it is convenient to each ring in sewage disposal system Section maintenance and periodic maintenance.
It applies the technical scheme of the present invention, the originals such as entire processing system make use of current to be freely oriented to, solid free sedimentation Reason, in addition to having added agitating device (in level-one flocculation basin and two level flocculation basin), air blower (in aeration tank), avoids as far as possible The use of mechanical equipment, greatly reduces the energy consumption in sewage disposal process.In addition, it has been equipped with two simultaneously in present treatment system A anaerobic pond and two aerobic tanks, improve the height for the treatment of process, and further improve the effect of sewage disposal.
Description of the drawings
The accompanying drawings which form a part of this application are used for providing a further understanding of the present invention, and of the invention shows Meaning property embodiment and its explanation do not constitute improper limitations of the present invention for explaining the present invention.In the accompanying drawings:
Fig. 1 diagrammatically illustrates the flow chart of the energy-saving sewage disposal system of the present invention;
Wherein, above-mentioned attached drawing is marked including the following drawings:
1 is collecting pit, and 2 be first stage precipitation tank, and 3 be level-one flocculation basin, and 4 be second-level settling pond, and 5 be two level flocculation basin, and 6 are Three-level sedimentation basin, 7 be regulating reservoir, and 8 be common anaerobic pond, and 9 be ecological anaerobic pond, and 10 be common aerobic tank, and 11 is aerobic for ecology Pond, 12 be level Four sedimentation basin, and 13 be aeration tank, and 14 be detection cell, and 15 be cistern, and 16 be connecting pipe, 17 primary strainers, 18 Secondary filter, 19 three-level strainers, 20 level Four strainers, 21 mud discharging mouths.
Specific embodiment
It should be noted that in the case where there is no conflict, the feature in embodiment and embodiment in the application can phase Mutually combination.The present invention will be described in detail below with reference to the accompanying drawings and in conjunction with the embodiments.
It is noted that described further below be all exemplary, it is intended to provide further instruction to the application.It is unless another It indicates, all technical and scientific terms used herein has usual with the application person of an ordinary skill in the technical field The identical meanings of understanding.
It should be noted that term used herein above is merely to describe specific embodiment, and be not intended to restricted root According to the illustrative embodiments of the application.As used herein, unless the context clearly indicates otherwise, otherwise singulative It is also intended to include plural form, additionally, it should be understood that, when in the present specification using term "comprising" and/or " bag Include " when, indicate existing characteristics, step, operation, device, component and/or combination thereof.
It should be noted that term " first " in the description and claims of this application and above-mentioned attached drawing, " Two " etc. be the object for distinguishing similar, without being used to describe specific order or precedence.It should be appreciated that it so uses Data can exchange in the appropriate case, so that presently filed embodiment described herein for example can be with except herein Order beyond those of diagram or description is implemented.
In addition, belong to " comprising " and " having " and their any deformation, it is intended that cover it is non-exclusive include, example Such as, process, method, system, product or the equipment for containing series of steps or unit are not necessarily limited to those clearly listed Step or unit, but may include not list clearly or for intrinsic other of these processes, method, product or equipment Step or unit.
For ease of description, spatially relative term can be used herein, as " ... on ", " ... top ", " ... upper surface ", " above " etc., for describing such as a device shown in the figure or feature and other devices or spy The spatial relation of sign.It should be appreciated that spatially relative term is intended to comprising the orientation except device described in figure Outside different azimuth in use or operation.
For example, if the device in attached drawing is squeezed, it is described as " in the top of other devices or construction " or " at other On device or construction " device after will be positioned as " below other devices or construction " or " in other devices or construction Under ".Thus, exemplary term " in ... top " can include " in ... top " and " in ... lower section " two kinds of orientation. The device 90 degree of other different position rotatings or can also be described in other orientation, and to space used herein above is opposite Make respective explanations.
It is shown in Figure 1, the present invention provides a kind of energy-saving sewage disposal system, including collecting pit 1, sedimentation basin, wadding Solidifying pond, regulating reservoir 7, aerobic tank, anaerobic pond and aeration tank 13.
Wherein, the sedimentation basin is divided into first stage precipitation tank 2, second-level settling pond 4, three-level sedimentation basin 6 and level Four sedimentation basin 12, Primary strainer 17, secondary filter 18, three-level strainer 19 and level Four strainer 20 are transversely provided in four sedimentation basins respectively, to not Sewage with degree carries out precipitation process, and sediment is stopped by strainer, and the water inlet on each sedimentation basin The position of pipe is higher than the height of strainer.
Wherein, the flocculation basin includes level-one flocculation basin 3 and two level flocculation basin 5, and two flocculation basins are that upper end is opened The taper that mouth is big, lower ending opening is small, and the flocculation basin upper end is equipped with flocculant feed inlet, and longitudinal stirs is equipped in the flocculation basin Mix device.The sedimentation of flocculate is convenient in the design of pyramidal structure, and as far as possible the flocculate after sedimentation is avoided to be subject to agitating device Influence.
Wherein, the anaerobic pond includes common anaerobic pond 8 and ecological anaerobic pond 9, the common anaerobic pond 8 and ecological anaerobism 9 adjacent connection of pond, and bottom is equipped with the activated sludge for being mixed with anaerobe carrier granular, sewage in the ecological anaerobic pond 9 Successively Anaerobic Treatment is carried out by common anaerobic pond 8 and ecological anaerobic pond 9.
Wherein, the aerobic tank includes common aerobic tank 10 and ecological aerobic tank 11, the common aerobic tank 10 and ecology 11 adjacent connection of aerobic tank, and bottom is equipped with aerobic microbiological carrier granular in the ecological aerobic tank 11, sewage passes through successively Common aerobic tank 10 and ecological aerobic tank 11 carry out Aerobic Process for Treatment.Dissolved oxygen in the common aerobic tank 10 is controlled in 4mg/L Or so, the dissolved oxygen in the ecology aerobic tank 11 is preferably controlled in more than 6mg/L.
Specifically, in implementation process, the sewage disposal system passes sequentially through the connection of connecting pipe 16 and receives from front to back Collect pond 1, first stage precipitation tank 2, level-one flocculation basin 3, second-level settling pond 4, two level flocculation basin 5, three-level sedimentation basin 6, regulating reservoir 7, general Logical anaerobic pond 8, ecological anaerobic pond 9, common aerobic tank 10, ecological aerobic tank 11, level Four sedimentation basin 12, aeration tank 13, detection cell 14 and cistern 15.
Wherein, collecting pit 1 connects effluent outfall by multiple inlet channels, and sewage is tentatively collected.The company 16 are threaded a pipe as zigzag pipeline or straight pipeline, the high one end connection water outlet of Z-type pipeline, low one end connection water inlet end, It can ensure the proper flow of current;Straight pipeline connects the upper end of two neighboring processing pond, also needs ensureing current just Permanent current moves.In addition, the zigzag pipeline turning is round and smooth design, pipeline right angle causes blockages after avoiding long-time service, Facilitate cleaning and maintenance of the later stage to connecting pipe 16 simultaneously.
The cistern 15 had not only connected collecting pit 1 but also had connected water equipment.If the testing result of detection cell 14 shows water Matter is unqualified, can start the connecting pipe 16 between cistern 15 and collecting pit 1, its progress is made further to handle again, Until water quality is qualified.If after the results show water quality qualification of detection cell 14, illustrating that treated, sewage can be recycled, The effect of recycling can be realized by the connecting pipe 16 between startup and water equipment.
Specifically, being additionally provided with long-distance intelligent detecting system in the detection cell 14, long-distance intelligent detecting system can be at any time The water quality situation after detection process is detected, processing promptly and accurately can be made to different situations.
Further specifically, the long-distance intelligent detecting system includes detection module, analog-to-digital conversion module, communication module With remote terminal module:
The detection module includes detector, and the detector can detect water quality situation, soda acid degree and dissolved oxygen situation; In implementation process, the requirement situation of water can be either recycled with specific reference to the situation of treated sewage, detector is carried out Selection is prepared, and be emphasized that the project of detection is not limited to water quality, soda acid degree and dissolved oxygen situation, other Detection range belongs to the customary means displacement of technological means in the present invention, all belongs to the scope of protection of the present invention;
The analog-to-digital conversion module is electrically connected with detection module, and the signal that detection module is gathered is converted into digital letter Number;
The communication module is electrically connected with analog-to-digital conversion module, and communication module receives the number that analog-to-digital conversion module is sent Signal;
Remote terminal module with communication module wireless connection, is handled digital signal data again, specifically, described remote Journey terminal module includes display device and storage device, and display device can show the data of detection at any time, and storage device can be with Real-time data are preserved, convenient for the comparison in later stage or the utilization of scientific research.
It remarks additionally for long-distance intelligent detecting system, the module in system is normal in the prior art The module used, that is, the prior art is belonged to, those skilled in the art can be according to the situation of actual motion or cost feelings Condition etc. makes choice application in the prior art, and is not limited to some specific model, but belongs to the guarantor of the present invention Within the scope of shield.
Further, the aperture of filter screen of the primary strainer 17, secondary filter 18, three-level strainer 19 and level Four strainer 20 It is controlled respectively in 3-4cm, 1-2cm, 0.5-1cm and 0.2-0.5cm, solid-liquid is carried out to different degrees of sewage respectively and is located respectively Reason.In specific implementation process, the small size precipitation less than aperture can be gathered in the lower end of strainer, and the current of water outlet will not be right It has an impact, and also would not enter next processing pond with current;And for the precipitation positioned at strainer upper end of large volume, The current of control will not naturally also have an impact it.It certainly, can only be periodically in sedimentation basin pond for the solid precipitation of large volume Mouth is purged it, and cannot be discharged from the mud discharging mouth 21 of lower end;Or it needs to precipitate the solid of large volume and carry out Reprocessing, makes it be deposited to the lower end of strainer, is finally discharged from the mud discharging mouth 21 of lower end.
Further, the level-one flocculation basin 3 and the two level flocculation basin 5 are using inorganic polymer flocculant It is one or two kinds of in aluminium polychloride, polyaluminium sulfate, poly-ferric chloride or bodied ferric sulfate.Inorganic polymer flocculates Agent is more preferable than other inorganic flocculating agent effects, and reason is that it can provide substantial amounts of complex ion, and being capable of strong adsorption colloid Particle, by absorption, crane span structure, crosslinked action, so that coacervation of colloid.Physicochemical change also occurs simultaneously, it is micro- to neutralize colloid Grain and the charge on suspended matter surface, reduce δ current potentials, colloidal particles are made to become attracting from original repelling each other, it is steady to destroy micelle It is qualitative, colloidal particles is made mutually to collide, so as to form cotton-shaped coagulating sedimentation, the surface area of precipitation is up to 200-1000m2/ g, pole Has adsorption capacity.
Further, the anaerobe carrier granular and aerobic microbiological carrier granular are zeolite, activated carbon, glass One kind in glass, plastics or synthetic resin.
Further, the anaerobe in the anaerobe carrier granular is nitrobacteria, described aerobic micro- Aerobic microbiological in bio-carrier particle is denitrifying bacteria.
Further, the collecting pit 1, sedimentation basin, flocculation basin, regulating reservoir 7, aerobic tank, anaerobic pond and aeration tank 13 Bottom of pond end be equipped with mud discharging mouth 21.
Further, controllable valve (being not drawn into figure) is equipped on the connecting pipe 16, it is convenient to sewage disposal Links maintenance and periodic maintenance in system.
The foregoing is only a preferred embodiment of the present invention, is not intended to limit the invention, for the skill of this field For art personnel, the invention may be variously modified and varied.Within the spirit and principles of the invention, that is made any repaiies Change, equivalent substitution, improvement etc., should all be included in the protection scope of the present invention.

Claims (10)

1. a kind of energy-saving sewage disposal system, including collecting pit, sedimentation basin, flocculation basin, regulating reservoir, aerobic tank, anaerobic pond and Aeration tank, it is characterised in that:
The sedimentation basin is divided into first stage precipitation tank, second-level settling pond, three-level sedimentation basin and level Four sedimentation basin, four sedimentation basins Primary strainer, secondary filter, three-level strainer and level Four strainer are inside transversely provided with respectively, and place of settling is carried out to different degrees of sewage Reason, and sediment is stopped by strainer, and the position of water inlet pipe is higher than the height of strainer on each sedimentation basin;
The flocculation basin includes level-one flocculation basin and two level flocculation basin, and two flocculation basins are that upper end opening is big, lower end is opened The small taper of mouth, and the flocculation basin upper end is equipped with flocculant feed inlet, and longitudinal agitating device is equipped in the flocculation basin;
The anaerobic pond includes common anaerobic pond and ecological anaerobic pond, the common anaerobic pond and the adjacent connection of ecology anaerobic pond, And bottom is equipped with the activated sludge for being mixed with anaerobe carrier granular in the ecological anaerobic pond, sewage is successively by commonly detesting Oxygen pond and ecological anaerobic pond carry out Anaerobic Treatment;
The aerobic tank includes common aerobic tank and ecological aerobic tank, the common aerobic tank and the adjacent connection of ecology aerobic tank, And bottom is equipped with aerobic microbiological carrier granular in the ecological aerobic tank, sewage is aerobic by common aerobic tank and ecology successively Pond carries out Aerobic Process for Treatment.
2. a kind of energy-saving sewage disposal system as described in claim 1, it is characterised in that:The sewage disposal system is in the past Connecting pipe connection collecting pit, first stage precipitation tank, level-one flocculation basin, second-level settling pond, two level flocculation basin, three are passed sequentially through after Grade sedimentation basin, regulating reservoir, common anaerobic pond, ecological anaerobic pond, common aerobic tank, ecological aerobic tank, level Four sedimentation basin, aeration Pond, detection cell and cistern, wherein collecting pit connect effluent outfall by multiple inlet channels, and the connecting pipe is Z-shaped Shape pipeline or straight pipeline, and the zigzag pipeline turning is round and smooth design, the cistern had not only connected collecting pit but also had connected Water equipment.
3. a kind of energy-saving sewage disposal system as claimed in claim 2, it is characterised in that:The detection cell is equipped with long-range intelligence It can detecting system.
4. a kind of energy-saving sewage disposal system as claimed in claim 3, it is characterised in that:The long-distance intelligent detecting system Including detection module, analog-to-digital conversion module, communication module and remote terminal module;
Wherein, the detection module includes detector, and the detector can detect water quality situation, soda acid degree and dissolved oxygen shape Condition;
The analog-to-digital conversion module is electrically connected with detection module, and the signal that detection module is gathered is converted into digital signal;
The communication module is electrically connected with analog-to-digital conversion module, and communication module receives the number letter that analog-to-digital conversion module is sent Number;
Remote terminal module with communication module wireless connection, is handled digital signal data again.
5. a kind of energy-saving sewage disposal system as claimed in claim 2, it is characterised in that:The primary strainer, two level filter The aperture of filter screen of net, three-level strainer and level Four strainer is controlled respectively in 3-4cm, 1-2cm, 0.5-1cm and 0.2-0.5cm.
6. a kind of energy-saving sewage disposal system as claimed in claim 2, it is characterised in that:The level-one flocculation basin and described Two level flocculation basin is aluminium polychloride, polyaluminium sulfate, poly-ferric chloride or polymerised sulphur using inorganic polymer flocculant It is one or two kinds of in sour iron.
7. a kind of energy-saving sewage disposal system as claimed in claim 2, it is characterised in that:The anaerobe carrier Grain and aerobic microbiological carrier granular are one kind in zeolite, activated carbon, glass, plastics or synthetic resin.
8. a kind of energy-saving sewage disposal system as claimed in claim 2, it is characterised in that:The anaerobe carrier For anaerobe in grain for nitrobacteria, the aerobic microbiological in the aerobic microbiological carrier granular is denitrifying bacteria.
9. a kind of energy-saving sewage disposal system as described in claim 1-8 any bars, it is characterised in that:The collecting pit, Sedimentation basin, flocculation basin, regulating reservoir, aerobic tank, anaerobic pond and the bottom of pond of aeration tank end are equipped with mud discharging mouth.
10. a kind of energy-saving sewage disposal system as described in claim 2-8 any bars, it is characterised in that:The connecting pipe On be equipped with controllable valve, convenient links maintenance and periodic maintenance in sewage disposal system.
CN201711480836.6A 2017-12-29 2017-12-29 A kind of energy-saving sewage disposal system Pending CN108101311A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711480836.6A CN108101311A (en) 2017-12-29 2017-12-29 A kind of energy-saving sewage disposal system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711480836.6A CN108101311A (en) 2017-12-29 2017-12-29 A kind of energy-saving sewage disposal system

Publications (1)

Publication Number Publication Date
CN108101311A true CN108101311A (en) 2018-06-01

Family

ID=62215005

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711480836.6A Pending CN108101311A (en) 2017-12-29 2017-12-29 A kind of energy-saving sewage disposal system

Country Status (1)

Country Link
CN (1) CN108101311A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109292977A (en) * 2018-11-12 2019-02-01 中信环境技术(天津)有限公司 A kind of internet remotely controls biological film sewage treatment system

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003106351A1 (en) * 2002-06-18 2003-12-24 Sasol Technology (Pty) Ltd Method of purifying fischer-tropsch derived water
CN202643512U (en) * 2012-07-20 2013-01-02 浙江泰来环保科技有限公司 Micro-sludge domestic sewage treatment system
CN203007063U (en) * 2012-12-05 2013-06-19 西南科技大学 Comprehensive wastewater treatment device of inorganic laboratory
CN103466906A (en) * 2013-10-11 2013-12-25 大唐国际化工技术研究院有限公司 Coom pressurized gasification wastewater treatment system and treatment method, and application thereof
CN104944677A (en) * 2015-05-08 2015-09-30 广西风向标环保科技有限公司 Sewage treatment system
CN105399285A (en) * 2015-12-22 2016-03-16 杭州易宇环保科技有限公司 Sewage treatment method for sludge reduction

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003106351A1 (en) * 2002-06-18 2003-12-24 Sasol Technology (Pty) Ltd Method of purifying fischer-tropsch derived water
CN202643512U (en) * 2012-07-20 2013-01-02 浙江泰来环保科技有限公司 Micro-sludge domestic sewage treatment system
CN203007063U (en) * 2012-12-05 2013-06-19 西南科技大学 Comprehensive wastewater treatment device of inorganic laboratory
CN103466906A (en) * 2013-10-11 2013-12-25 大唐国际化工技术研究院有限公司 Coom pressurized gasification wastewater treatment system and treatment method, and application thereof
CN104944677A (en) * 2015-05-08 2015-09-30 广西风向标环保科技有限公司 Sewage treatment system
CN105399285A (en) * 2015-12-22 2016-03-16 杭州易宇环保科技有限公司 Sewage treatment method for sludge reduction

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109292977A (en) * 2018-11-12 2019-02-01 中信环境技术(天津)有限公司 A kind of internet remotely controls biological film sewage treatment system

Similar Documents

Publication Publication Date Title
CN104355478B (en) A kind of dyeing and printing sewage processes system
CN109694130B (en) Device for realizing sludge suspension and avoiding sludge loss and use method thereof
CN102657960A (en) Precipitation reaction and solid-liquid separation integral device
CN106045148A (en) Novel intelligent electric flocculation treatment apparatus of power plant coal-containing wastewater
CN206152483U (en) Sewage sedimentation tank
CN216946616U (en) Magnetic coagulation-flocculation reaction device and high-turbidity wastewater ultrafiltration treatment system
CN110697990A (en) Method for purifying sewage and reducing suspended matters in water body
CN208120937U (en) A kind of papermaking wastewater treatment system
CN108101311A (en) A kind of energy-saving sewage disposal system
CN211056859U (en) Construction wastewater treatment system
CN111153558A (en) Garbage transfer station leachate treatment device and treatment method thereof
CN204752409U (en) Nonmetal ore deposit beneficiation wastewater water purifier
CN106167333A (en) Refuse transfer station leachate collection and processing method
CN108996839A (en) A kind of refuse transfer station waste water treatment process and equipment
CN102951780A (en) Device for classification and collection of granular sludge of anaerobic ammonia oxidation
CN205917126U (en) Landfill leachate collects and processing system
CN211999336U (en) Leachate treatment device for garbage transfer station
CN105481171B (en) Unit equipment associated with a kind of more family sanitary sewage hydrolytic tanks and more processing units
CN210367319U (en) Black and odorous water body treatment system
CN213895520U (en) Municipal sewage cuts dirty regulation and holds and purifies integrated processing system
CN204737849U (en) Novel cities and towns sewage treatment device
CN209522624U (en) ECSF type integration electric flocculation high suspended matter wastewater treatment equipment
CN209721697U (en) A kind of device realized sludge suspension and avoid sludge loss
CN209010326U (en) A kind of integrated sewage treating apparatus of optimization
CN202063770U (en) Novel biofilm reactor

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20180601

RJ01 Rejection of invention patent application after publication