CN107244785A - A kind of microkinetic septic tank - Google Patents

A kind of microkinetic septic tank Download PDF

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Publication number
CN107244785A
CN107244785A CN201710616985.4A CN201710616985A CN107244785A CN 107244785 A CN107244785 A CN 107244785A CN 201710616985 A CN201710616985 A CN 201710616985A CN 107244785 A CN107244785 A CN 107244785A
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Prior art keywords
lattice
septic tank
dividing plate
aerobic
filler
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CN201710616985.4A
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Chinese (zh)
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CN107244785B (en
Inventor
吴卫东
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Guangzhou Zhuo Guan Environmental Protection Technology Co Ltd
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Guangzhou Zhuo Guan Environmental Protection Technology Co Ltd
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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
    • C02F2001/007Processes including a sedimentation step
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/002Construction details of the apparatus
    • C02F2201/007Modular design
    • 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
    • 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
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used

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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)
  • Biological Treatment Of Waste Water (AREA)

Abstract

The present invention discloses a kind of septic tank for sanitary sewage disposal, and septic tank of the invention includes septic tank body, and the septic tank body is spaced one from into the first lattice, the second lattice and the 3rd lattice by the first dividing plate, second partition;The connector top rake for leading to the second lattice in the first lattice installs one piece of grid filter screen, the suspension of the overwhelming majority can be obstructed close to the connector of the one or two lattice, aeration type filter is there is also mounted on connector in addition, not only play filter suspended solids, the good environment depended on for existence is also provided to microorganism simultaneously, filler is full of aerobic microbiological and the suspension that is retained down during work, and suspension is just decomposed digestion as the nutrients of aerobic microbiological.Therefore, suspension did not resulted in the blocking of the mouth of a river and septic tank system.The septic tank of the present invention is obviously improved to the treatment effect of organic matter of sewage and improves treatment effeciency, significantly improves the phenomenons such as the slough that occurs current short circuit in pond, improves the dischargeable capacity in pond.

Description

A kind of microkinetic septic tank
Technical field
The present invention relates to a kind of processing pond for sewage disposal, especially a kind of septic tank for sewage disposal, category In sewage treatment facility technical field.
Background technology
Septic tank is as important component in living drainage system, and it is mainly removed using precipitation and anaerobic digestion Suspension in water etc., preliminary treatment is played a part of to sewage.So far the septic tank generally used, due to its internal structure not A series of reasons such as enough reasonable and used processing modes are single, cause its treatment effect and efficiency poor.Traditional septic tank Greatest problem present on internal structure is connected using pipeline or aperture between every lattice, and sewage fluidised form is to be in direct current flashing shape State, easily causes short stream and slough phenomenon, reduces the dischargeable capacity in pond, influence overall treatment effect.In addition, current Septic tank is single to use anaerobic ferment process, and is that can not meet having for directly discharge or follow-up Ecological Disposal only with anaerobic technique Machine thing and ammonia nitrogen index request.Rural area and discrete areas for not yet building sewage collecting pipe network, septic tank now is It is difficult to meet demand.
The content of the invention
There is provided it is an object of the invention to overcome in place of above-mentioned the deficiencies in the prior art one kind can effectively solve the problem that it is existing Septic tank treatment effect and treatment effeciency are low, easily block, there are problems that the microkinetic septic tank of short stream in pond.
To achieve the above object, the technical scheme taken of the present invention is:A kind of microkinetic septic tank, including septic tank sheet Body, the septic tank body is spaced one from into the first lattice, the second lattice and the 3rd lattice by the first dividing plate, second partition;Described first Dividing plate is located between first lattice and the second lattice, and the second partition is located between second lattice and the 3rd lattice;Described Connected, connected between second lattice and the 3rd lattice by bridge piece by connector between one lattice and second lattice Logical, the bridge piece is located at the bottom of the outs opens of second lattice vertically the second lattice;
Provided with water inlet, grid and aeration type filter in first lattice, the water inlet is located at first lattice Top;The grid is connected between the top and bottom of first lattice, and the aeration type filter is located at the connector Towards the side of the first lattice;
Anaerobism filler and regulating weir are provided with second lattice, the regulating weir is located at connector one towards the second lattice Side;
The 3rd lattice are separated into by anoxic zone, water by the 3rd dividing plate, the 4th dividing plate, the 5th dividing plate respectively in 3rd lattice Flow area, aerobic zone, settling zone;The bottom of the anoxic zone is connected with the current area, the top in the current area with it is described good Oxygen area is connected, and the bottom of the aerobic zone is connected with the settling zone;The anoxic zone includes anoxic filler and lacked located at described The anoxic aeration head of oxygen area bottom, is provided with the sky for current between the bottom of the anoxic filler and the bottom of the anoxic zone Between;The aerobic zone include aerobic filler and the aerobic aeration head located at the aerobic zone bottom, the aerobic filler with it is described The space for current is provided between the bottom of aerobic zone;The top of the settling zone is provided with delivery port.
As the preferred embodiment of microkinetic septic tank of the present invention, the grid in first lattice is described first Connection is tilted between at the top and bottom of lattice, and the angle between the grid and the first lattice bottom towards the second lattice direction is small In 90 °.
As the preferred embodiment of microkinetic septic tank of the present invention, the aeration type filter includes shell, filled out The filter packing and the aeration head located at the filler bottom filled in the shell, the shell is network structure.
As the preferred embodiment of microkinetic septic tank of the present invention, the aeration type filter is trapezium structure, And the bottom of the aeration type filter of the trapezium structure is connected with the connector.
As the preferred embodiment of microkinetic septic tank of the present invention, the anaerobism filler bottom in second lattice is consolidated The bottom of second lattice is scheduled on, the sky for current is provided between the periphery of the anaerobism filler and the side wall of second lattice Between.
As the preferred embodiment of microkinetic septic tank of the present invention, in the 3rd lattice, the anoxic in anoxic zone It is close to the second partition and the 3rd dividing plate in the periphery of filler;It is close to the described 4th in the periphery of aerobic filler in the aerobic zone Dividing plate and the 5th dividing plate.
It is used as the preferred embodiment of microkinetic septic tank of the present invention, bottom and the anoxic of the 3rd dividing plate The bottom of filler maintains an equal level, and the top of the 3rd dividing plate is higher than the height of the bridge piece.
As the preferred embodiment of microkinetic septic tank of the present invention, the bottom of the 4th dividing plate is fixed on described The bottom of 3rd lattice, the top of the 4th dividing plate maintains an equal level with the top of the aerobic filler.
As the preferred embodiment of microkinetic septic tank of the present invention, the bottom of the 5th dividing plate with it is described aerobic The bottom of filler maintains an equal level, and the top of the 5th dividing plate is higher than the height of the bridge piece.
As the preferred embodiment of microkinetic septic tank of the present invention, the bottom of the settling zone is oblique provided with water conservancy diversion Plate, the lower end of the flow guiding inclined plate is fixed on the bottom of the settling zone, and the upper end of the flow guiding inclined plate is fixed on the described 3rd On the side wall of lattice.
The microkinetic septic tank of the present invention has the advantages that:
1) water quality of water outlet is significantly improved.The present invention, which changes into the single anaerobic fermentation handling process of traditional septic tank, to be detested The group technology of oxygen-and oxygen-Aerobic Process for Treatment, the technique of these three different characteristics complements each other, hence it is evident that improve organic to sewage The treatment effect of thing and improve treatment effeciency.
2) incidence of septic tank blocking is significantly reduced.The present invention pacifies in the connector top rake that the first lattice lead to the second lattice One piece of grid filter screen is filled, the suspension of the overwhelming majority can be obstructed close to the connector of the one or two lattice, gone back in addition on connector It is mounted with to be aerated type filter, the filter is shaped as prismatoid, and shell is stamped to form by gross porosity grid, inside is full of filtering Filler, and filler bottom is provided with aeration head, make filter interior be in aerobic state.It is outstanding that filter packing not only plays filtering The effect of floating solid, while also provide the good environment depended on for existence to microorganism, during work filler full of aerobic microbiological and The suspension being retained down, suspension is just decomposed digestion as the nutrients of aerobic microbiological.Therefore, suspension will not Caused the blocking of the mouth of a river and septic tank system.
3) significantly improve and occur the phenomenons such as the short-circuit slough of current in pond, improve the dischargeable capacity in pond.One or two Aeration type filter housing on lattice connector is the trapezoidal solids that grid is stamped to form, and current can enter from multiple directions Inside filter, i.e. the current of the first lattice to the second lattice are the flowings of circulation flashing form, in the absence of short stream and slough.Two or three Flow-guiding channel is provided with inside lattice, current, which rely on drop potential energy, to be promoted and moved from entrance toward outlet, thus be also not present backflow, it is short-circuit With the phenomenon such as slough.
Brief description of the drawings
Fig. 1 is a kind of structural representation of embodiment of microkinetic septic tank of the present invention.
In figure, 1 it is the first lattice, 2 is the second lattice, 3 is the 3rd lattice, 10 is the first dividing plate, 20 is second partition, 30 is the 3rd Dividing plate, 40 be the 4th dividing plate, 50 be the 5th dividing plate, 11 be water inlet, 12 be aeration type filter, 13 be connector, 14 be lattice Grid, 21 be anaerobism filler, 22 be bridge piece, 23 be regulating weir, 31 be anoxic zone, 32 be current area, 33 be aerobic zone, 34 be Settling zone, 310 be anoxic filler, 311 be anoxic aeration head, 330 be aerobic filler, 331 be aerobic aeration head, 340 be water conservancy diversion Swash plate, 341 are delivery port.
Embodiment
To better illustrate the object, technical solutions and advantages of the present invention, below in conjunction with the drawings and specific embodiments pair The present invention is described further.
A kind of embodiment of microkinetic septic tank of the present invention, as shown in Figure 1, the microkinetic septic tank of the present embodiment include Septic tank body, the septic tank body is spaced one from into the first lattice 1, the second lattice 2 and by the first dividing plate 10, second partition 20 Three lattice 3;First dividing plate 10 is located between the lattice 2 of the first lattice 1 and second, and the second partition 20 is located at second lattice 2 and the 3rd between lattice 3;Connected between first lattice 1 and second lattice 2 by connector 13, second lattice 2 with it is described Connected between 3rd lattice 3 by bridge piece 22, the bridge piece 22 is located at the outs open of second lattice 2 vertically The bottom of second lattice 2;
Provided with water inlet 11, grid 14 and aeration type filter 12 in first lattice 1, the water inlet 11 is located at described The top of first lattice 1;The grid 14 is connected between the top and bottom of first lattice 1, the aeration type filter 12 Located at the connector 13 towards the side of the first lattice 1;
It is provided with anaerobism filler 21 and regulating weir 23 in second lattice 2, the regulating weir 23 is located at connector 13 towards the The side of two lattice 2;
The 3rd lattice 3 are separated into respectively by the 3rd dividing plate 30, the 4th dividing plate 40, the 5th dividing plate 50 in 3rd lattice 3 Anoxic zone 31, current area 32, aerobic zone 33, settling zone 34;The bottom of the anoxic zone 31 is connected with the current area 32, described The top in current area 32 is connected with the aerobic zone 33, and the bottom of the aerobic zone 33 is connected with the settling zone 34;It is described to lack Oxygen area 31 includes anoxic filler 310 and the anoxic aeration head 311 located at the bottom of anoxic zone 31, the anoxic filler 310 The space for current is provided between the bottom of bottom and the anoxic zone 31;The aerobic zone 33 includes the aerobic He of filler 330 Aerobic aeration first 331 located at the bottom of aerobic zone 33, is provided between the aerobic filler 330 and the bottom of the aerobic zone 33 Space for current;The top of the settling zone 34 is provided with delivery port 341.
It is preferred that as shown in Figure 1, the grid 14 in first lattice 1 inclines between the top and bottom of the first lattice 1 Tiltedly connection, and the angle in direction the second lattice 2 direction is less than 90 ° between the grid 14 and the bottom of the first lattice 1.
It is preferred that as shown in Figure 1, the aeration type filter 12 includes shell, the filtering being filled in the shell Filler and the aeration head located at the filler bottom, the shell are network structure.
It is preferred that as shown in Figure 1, the type filter 12 that is aerated is trapezium structure, and the aeration of the trapezium structure The bottom of type filter 12 is connected with the connector 13.
It is preferred that as shown in Figure 1, the bottom of anaerobism filler 21 in second lattice 2 is fixed on the bottom of second lattice 2 The space for current is provided between the side wall of portion, the periphery of the anaerobism filler 21 and second lattice 2.
It is preferred that as shown in Figure 1, in the 3rd lattice 3, institute is close on the periphery of the anoxic filler 310 in anoxic zone 31 State the dividing plate 30 of second partition 20 and the 3rd;It is close to the 4th dividing plate 40 in the periphery of aerobic filler 330 in the aerobic zone 33 With the 5th dividing plate 50.
It is preferred that as shown in Figure 1, the bottom of the 3rd dividing plate 30 maintains an equal level with the bottom of the anoxic filler 310, institute The top for stating the 3rd dividing plate 30 is higher than the height of the bridge piece 22.
It is preferred that as shown in Figure 1, the bottom of the 4th dividing plate 40 is fixed on the bottom of the 3rd lattice 3, described The top of four dividing plates 40 and the top of the aerobic filler 330 maintain an equal level.
It is preferred that as shown in Figure 1, the bottom of the 5th dividing plate 50 and the bottom of the aerobic filler 330 maintain an equal level, institute The top for stating the 5th dividing plate 50 is higher than the height of the bridge piece 22.
It is preferred that as shown in Figure 1, the bottom of the settling zone 34 is provided with flow guiding inclined plate 340, the flow guiding inclined plate 340 Lower end be fixed on the bottom of the settling zone 34, the upper end of the flow guiding inclined plate 340 is fixed on the side wall of the 3rd lattice 3 On.
In the present embodiment, the top rake of connector 13 for leading to the second lattice 2 in the first lattice 1 installs one piece of grid 14;First Lattice 1, which lead on the connector 13 of the second lattice 2, installs an aeration type filter 12, and being shaped as the aeration type filter 12 is trapezoidal Body, shell is stamped to form by grid, and inside is full of filter packing, and filler bottom is provided with aeration head;The court of connector 13 Regulating weir 23 is installed on to the direction of the second lattice 2;Second lattice 2 are built-in with anaerobism filler 21, anaerobism filler 21 and the dividing plate of both sides first 10 and second partition 20 keep suitable distance, as water stream channel;Second lattice 2 are connected with the 3rd lattice 3 by bridge piece 22, even Connect the bent tube section direction bottom of pond of the second lattice 2 of bend pipe 22;3rd lattice 3 are divided into four regions, and first area is anoxic from left to right Anoxic filler 310 and anoxic aeration head 311 are installed in area 31, anoxic zone 31, anoxic filler 310 and bottom of pond retain appropriately distance with As water stream channel, the right side of anoxic filler 310 is close to install under the 3rd dividing plate 30, the bottom of the 3rd dividing plate 30 and anoxic filler 310 Side maintains an equal level, and the top of the 3rd dividing plate 30 is more slightly higher than the tube top of bridge piece 22, and the 3rd dividing plate 30 makees fixed pivot by front and rear pool wall; It is the second area of the 3rd lattice 3, i.e. current area 32 between 3rd dividing plate 30 and the 4th dividing plate 40, current area 32 is logical as current Road;It is the 3rd region of the 3rd lattice 3, i.e. aerobic zone 33 between 4th dividing plate 40 and the 5th dividing plate 50, aerobic zone 33 installs aerobic It is close to bottom of pond, the top of the 4th dividing plate 40 and the aerobic top of filler 330 in filler 330 and aerobic aeration first 331, the bottom of the 4th dividing plate 40 Maintain an equal level, aerobic filler 330 is close to the 4th dividing plate 40 and installed, the bottom of aerobic filler 330 and bottom of pond retain suitable distance for use as Water stream channel;It is close to aerobic filler 330 and the 5th dividing plate 50 is installed, the bottom of the 5th dividing plate 50 is held with the aerobic lower sideline of filler 330 Flat, the top of the 5th dividing plate 50 is more slightly higher than the tube top of bridge piece 22, is the 4th region between the 5th dividing plate 50 and right pool wall, i.e., Settling zone 34, the precipitation that settling zone 34 is used as suspension is used;One piece is installed to the 3rd region aerobic zone 33 in the bottom of settling zone 34 Inclined deflector.
Microkinetic septic tank described in the present embodiment, in use, concrete processing procedure is as follows:
1st, sanitary sewage flows into the first lattice 1 by water inlet 11, and after precipitation and anaerobic fermentation, sewage is divided into three layers:Bottom Layer sludge settling thing, middle level mixed liquor, upper strata excrement skin suspension.Grid 14 prevents bulky grain suspension from being connected close to two lattice are led to Hole, thus the only middle level mixed liquor that can be flowed into after grid 14.These mixed liquors flow into aeration type filter 12, particle quilt again Filter packing is retained, and filter packing is full of aerobic microbiological, and these particle suspensions of the positive good utilisation of these aerobic microbiologicals are made It is able to decompose removing for the suspension of the nutrients of growth, thus retention.Mixed liquor is by being aerated type filter 12 and regulating weir Enter the second lattice 2 after 23.In addition, the connector 13 of the first lattice 1 and the second lattice 2 is adjusted for one towards installation on the direction of the second lattice 2 Weir 23, the second lattice 2 are quantitatively delivered to by the mixed liquor of the first lattice 1, and the flowed fluctuation of sanitary sewage is made buffering by the first lattice 1 and adjusted Section;
2nd, the mixed liquor into the second lattice 2 is from side infiltration anaerobism filler 21, and anaerobism filler 21 has been covered with the micro- life of anaerobism Thing, these anaerobes carry out anaerobic reaction to the organic matter inside sewage, and mixed liquor after Anaerobic Treatment is from anaerobism The opposite side outflow of filler 21, then enter the 3rd lattice 3 by bridge piece 22;
3rd, the mixed liquor into the 3rd lattice 3 first flows through anoxic filler 310, the abundant simultaneous oxygen of anoxic filler 310 from top to bottom Microorganism carries out anoxic degraded to the organic matter of sewage, after hypoxia response, promotion of the mixed liquor in the drop potential energy that always comes in and goes out Under, the water stream channel of bottom and side through anoxic filler 310 flow to the top of aerobic filler 330 from lower to upper.Mixed liquor is again Aerobic filler 330 is flowed through from top to bottom, and the abundant aerobic microbiological of aerobic filler 330 carries out aerobic drop to the organic matter of mixed liquor Solution.After the combination degradation technique of anaerobism-anoxic-aerobic, hence it is evident that improve the total removal rate and whole process of organic matter Reaction efficiency.
4th, the mixed liquor for flowing to the aerobic bottom of filler 330 enters settling zone 34 by the inlet port of settling zone 34, through precipitation Afterwards, supernatant is drained by delivery port 341, under guide functions of the sludge by flow guiding inclined plate 340, enters back into aerobic filler 330 Bottom, these sludge deliver to the inside of aerobic filler 330 again by the air-flow of aerobic aeration first 331, as strain and microorganism Nutrients.
Finally, it should be noted that the above embodiments are merely illustrative of the technical solutions of the present invention rather than the present invention is protected The limitation of scope is protected, although being explained in detail with reference to preferred embodiment to the present invention, one of ordinary skill in the art should Understand, technical scheme can be modified or equivalent substitution, without departing from the essence of technical solution of the present invention And scope.

Claims (10)

1. a kind of microkinetic septic tank, it is characterised in that including septic tank body, the septic tank body is by the first dividing plate, Two dividing plates are spaced one from into the first lattice, the second lattice and the 3rd lattice;First dividing plate is located between first lattice and the second lattice, The second partition is located between second lattice and the 3rd lattice;Connected between first lattice and second lattice by connector It is logical, connected between second lattice and the 3rd lattice by bridge piece, the bridge piece is located at the portion of second lattice Separate the bottom of mouth vertically the second lattice;
Provided with water inlet, grid and aeration type filter in first lattice, the water inlet is located at the top of first lattice; The grid is connected between the top and bottom of first lattice, and the aeration type filter is located at the connector towards the The side of one lattice;
Anaerobism filler and regulating weir are provided with second lattice, the regulating weir is located at the side of connector the second lattice of direction;
The 3rd lattice are separated into by anoxic zone, current by the 3rd dividing plate, the 4th dividing plate, the 5th dividing plate respectively in 3rd lattice Area, aerobic zone, settling zone;The bottom of the anoxic zone is connected with the current area, the top in the current area with it is described aerobic Area is connected, and the bottom of the aerobic zone is connected with the settling zone;The anoxic zone includes anoxic filler and located at the anoxic The anoxic aeration head of area bottom, is provided with the sky for current between the bottom of the anoxic filler and the bottom of the anoxic zone Between;The aerobic zone include aerobic filler and the aerobic aeration head located at the aerobic zone bottom, the aerobic filler with it is described The space for current is provided between the bottom of aerobic zone;The top of the settling zone is provided with delivery port.
2. microkinetic septic tank as claimed in claim 1, it is characterised in that the grid in first lattice is in first lattice Connection is tilted between top and bottom, and the angle in the second lattice direction of direction is less than between the grid and the first lattice bottom 90°。
3. microkinetic septic tank as claimed in claim 2, it is characterised in that the aeration type filter includes shell, filling Filter packing in the shell and the aeration head located at the filler bottom, the shell are network structure.
4. microkinetic septic tank as claimed in claim 3, it is characterised in that the aeration type filter is trapezium structure, and The bottom of the aeration type filter of the trapezium structure is connected with the connector.
5. microkinetic septic tank as claimed in claim 1, it is characterised in that the anaerobism filler bottom in second lattice is fixed The sky for current is provided with the bottom of second lattice, between the periphery of the anaerobism filler and the side wall of second lattice Between.
6. microkinetic septic tank as claimed in claim 1, it is characterised in that in the 3rd lattice, the anoxic in anoxic zone is filled out It is close to the second partition and the 3rd dividing plate in the periphery of material;The periphery of aerobic filler in the aerobic zone be close to the described 4th every Plate and the 5th dividing plate.
7. microkinetic septic tank as claimed in claim 1, it is characterised in that the bottom of the 3rd dividing plate is filled out with the anoxic The bottom of material maintains an equal level, and the top of the 3rd dividing plate is higher than the height of the bridge piece.
8. microkinetic septic tank as claimed in claim 1, it is characterised in that the bottom of the 4th dividing plate is fixed on described The bottom of three lattice, the top of the 4th dividing plate maintains an equal level with the top of the aerobic filler.
9. microkinetic septic tank as claimed in claim 1, it is characterised in that the bottom of the 5th dividing plate aerobic is filled out with described The bottom of material maintains an equal level, and the top of the 5th dividing plate is higher than the height of the bridge piece.
10. microkinetic septic tank as claimed in claim 1, it is characterised in that the bottom of the settling zone is provided with flow guiding inclined plate, The lower end of the flow guiding inclined plate is fixed on the bottom of the settling zone, and the upper end of the flow guiding inclined plate is fixed on the 3rd lattice On the wall of side.
CN201710616985.4A 2017-07-26 2017-07-26 Micro-power septic tank Active CN107244785B (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108046547A (en) * 2018-01-29 2018-05-18 武汉都市环保工程技术股份有限公司 Cultivate treatment for cow manure integrating device and system
CN109867403A (en) * 2017-12-01 2019-06-11 中国水利水电科学研究院 A kind of processing unit and sewage water treatment method of dispersing type sewage
CN110342748A (en) * 2019-07-24 2019-10-18 杭州李春环境科技有限公司 Toilet sewage purifier and method
CN117735721A (en) * 2024-02-20 2024-03-22 中国市政工程华北设计研究总院有限公司 Denitrification type low-carbon-emission five-grid septic tank and treatment process thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006314991A (en) * 2005-05-11 2006-11-24 Ji Sun Ryu Apparatus and method for treating high-concentration nitrogen-containing dirty waste water such as waste water from livestock farmer and excreta
CN201045215Y (en) * 2007-05-29 2008-04-09 武汉大学 Multifunctional three divisions septic tanks
JP2011000555A (en) * 2009-06-19 2011-01-06 Kubota Corp Wastewater treatment facility and method of rebuilding the same
US20110079554A1 (en) * 2008-04-08 2011-04-07 Nanjing University Method for treating mixed wastewater from pharmaceutical chemical industry park
WO2012010096A1 (en) * 2010-07-20 2012-01-26 华南理工大学 Device for synchronously removing nitrogen and phosphorus in mixed municipal sewage and fecal sewage by using a2/o-biomembrane and method thereof
US20140097136A1 (en) * 2011-07-05 2014-04-10 Daewoong Ecosystems And Solution Composite microorganism reactor, and apparatus and method for water treatment using the same
CN106554131A (en) * 2015-09-25 2017-04-05 上海凡清环境工程有限公司 Integrated preposition denitrification sewage-treatment plant
CN206289143U (en) * 2016-11-24 2017-06-30 保山益佰工贸有限责任公司 A kind of sewage treatment unit of dynamic glass-reinforced plastic material

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006314991A (en) * 2005-05-11 2006-11-24 Ji Sun Ryu Apparatus and method for treating high-concentration nitrogen-containing dirty waste water such as waste water from livestock farmer and excreta
CN201045215Y (en) * 2007-05-29 2008-04-09 武汉大学 Multifunctional three divisions septic tanks
US20110079554A1 (en) * 2008-04-08 2011-04-07 Nanjing University Method for treating mixed wastewater from pharmaceutical chemical industry park
JP2011000555A (en) * 2009-06-19 2011-01-06 Kubota Corp Wastewater treatment facility and method of rebuilding the same
WO2012010096A1 (en) * 2010-07-20 2012-01-26 华南理工大学 Device for synchronously removing nitrogen and phosphorus in mixed municipal sewage and fecal sewage by using a2/o-biomembrane and method thereof
US20140097136A1 (en) * 2011-07-05 2014-04-10 Daewoong Ecosystems And Solution Composite microorganism reactor, and apparatus and method for water treatment using the same
CN106554131A (en) * 2015-09-25 2017-04-05 上海凡清环境工程有限公司 Integrated preposition denitrification sewage-treatment plant
CN206289143U (en) * 2016-11-24 2017-06-30 保山益佰工贸有限责任公司 A kind of sewage treatment unit of dynamic glass-reinforced plastic material

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109867403A (en) * 2017-12-01 2019-06-11 中国水利水电科学研究院 A kind of processing unit and sewage water treatment method of dispersing type sewage
CN109867403B (en) * 2017-12-01 2023-09-22 中国水利水电科学研究院 Decentralized sewage treatment device and sewage treatment method
CN108046547A (en) * 2018-01-29 2018-05-18 武汉都市环保工程技术股份有限公司 Cultivate treatment for cow manure integrating device and system
CN110342748A (en) * 2019-07-24 2019-10-18 杭州李春环境科技有限公司 Toilet sewage purifier and method
CN117735721A (en) * 2024-02-20 2024-03-22 中国市政工程华北设计研究总院有限公司 Denitrification type low-carbon-emission five-grid septic tank and treatment process thereof

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