CN1432537A - Active sludge processing system - Google Patents
Active sludge processing system Download PDFInfo
- Publication number
- CN1432537A CN1432537A CN02102034A CN02102034A CN1432537A CN 1432537 A CN1432537 A CN 1432537A CN 02102034 A CN02102034 A CN 02102034A CN 02102034 A CN02102034 A CN 02102034A CN 1432537 A CN1432537 A CN 1432537A
- Authority
- CN
- China
- Prior art keywords
- water
- sludge
- tank
- gas
- biological sludge
- 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.)
- Granted
Links
Images
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
The present invention relates to a power saving active sludge treating system only utilizing natural energy, in which a rotary structure for pressurizing biological sludge pressurizes and mixes the water with suspended matter containing biological sludge from the water treating tank as treating target and the gas supplies by other apparatus, the storing tank then separates excessive gas and returns the pressurized and processed water containing dissolved gas and dispersed gas into treating tank water, the pressurized water is opened into normal pressure at some specific location so as to spray the fine bubbles into the water treating tank, and one mechanical structure with water flow attracting function and water flow pushing function makes the sewage, biological sludge and fine bubbles fill the water treating tank for mixing, and contacting effectively.
Description
Technical field
The present invention relates to the active sludge processing system of the sewage of a kind of processing plant waste water and water drain etc.
Background technology
When purifying the sewage of plant effluent or water drain etc. with activated sludge process, what use is, be suspended in with making the biological sludge former state that constitutes by microorganism handle in the tank or it swum on attached to appropriate carriers after, pass through diffuser aeration air (oxygen) from gas blower or compressor, while also mixing the whole method that sewage is disposed of sewage of supplying with the spirrillum stirrer.
But, the problem below in existing active sludge processing system, existing.
From gas blower or compressor by diffuser aeration air, when mixing integral body, the machine that many, each consumption count the electric power more than the 10KW to be set usually by it.So not only from saving energy, be that the position of earth environmental protection is unfavorable, and because the electric lighting bill is heavy also is disadvantageous economically.
To the air fed maximum purpose of active sludge treatment groove is to make microbial survival and make its propagation for it being supplied with oxygen, but because the bubble that produces from diffuser is big, on its major part is directly floating, oxygen dissolved efficiency extreme difference.Its reason is, owing to be the system by aeration stirring system integral body when microorganism is supplied with oxygen, causes the result of deterioration of efficiency on the contrary.
When carrying out sewage disposal, be 2000PPM, therefore,, need the greatest area that is provided with in order to handle high-concentration sewage or big concentration sewage owing to its upper limit of sludge concentration is the highest in that the active sludge that is made of microorganism is suspended.In order to address this problem, use the parts of microorganic adhesion on plastic carrier will for example be swum in groove, with spiral helicine stirrer stirring it and make its blended method.
But, under these circumstances,, need many stirrers in order positively to stir, therefore, not only consume a lot of electric power, and, spend unnecessary expense owing to the shearing force of spiral is damaged expensive carrier.
That is, there is the shortcoming that needs greatest design area and waste electric power etc. in present active sludge processing system, overcomes the method for this shortcoming, is that institute is extensively anticipatory in industrial community and the commune.
Technical scheme
The inventor, in order to solve problem as described above, carried out diligent research, it found that thereby following technical scheme finished the present invention, this technical scheme is for by having the revolution structure portion that do not destroy the function that biological sludge just can pressurize from handling tank and attract and the object water of the seston that contains biological sludge etc. of pressurizeing, with its with mix by other the gas pressurization of unit feeding, then they are imported storage tanks, only separate superfluous ground gas supplied selectively, then, to contain the gas of dissolved state again and be turned back to this processing tank by this object water of the gas of dispersed state imperceptibly while keeping pressurized state, in the position of regulation it being opened is normal pressure, when making fine bubble be ejected into the inside of handling tank, make process object sewage on one side by having the physical structure portion that attracts the current function and release any setting of current function, biological sludge and fine bubble spread all over each corner of handling tank integral body, make them mix contact on one side efficiently, improve biological decomposition speed thus, thereby can carry out the processing that high density flows into dirty load water, under the situation of not using aerating apparatus, purify the sewage of plant effluent etc. simultaneously with few energy expenditure.
The description of the drawings
Fig. 1 is the general structural map of an example that expression is used in the embodiment of whipping appts of the present invention.
Fig. 2 is to use in the vertical view of the stator supporting plate of the driving part of whipping appts shown in Figure 1.
Embodiment
Below the present invention is described in detail.
The method according to this invention as the revolution structure, is provided with volume type pump, attracts treating water thus, from being located at air compressor the drainage piping in addition with pressure 3~6kg/cm
2Be pressed into air, simultaneously, send into this pressurized water from this pump to the pressurization tank of subsequent processing with the pressure of same degree.At this, with the air separation of supplying with superfluously, then, to wastewater treatment bottom of gullet pipe arrangement, pressure regulator valve is set at its front end from this pressurization tank by gas-liquid separation device with float-actuated valve etc.In this pipe arrangement, keeping the air of the treating water that contains under the situation of pressurized state as object, biological sludge, dissolved state and dispersive bubble imperceptibly.When making their runnings, setting pressure according to pressure regulator valve, the pressurized water that contains air opens in the wastewater treatment tank, because handling in the tank is normal pressure, according to Henry's law, oversaturated air becomes the micro bubble of diameter 3~30 μ m, is distributed to handle in the tank, is supplied in microorganism efficiently.Pump and air compressor as displacement type can use original piston-type pump or compressor respectively, still, consider preferably to use vane pump from function and energy-conservation aspect.
In the past in the aeration type active sludge processing system that is carried out and since the size of bubble be diameter 1~5mm or more than, the utilization ratio extreme difference of oxygen, in existing method, the relative oxygen of supplying with, the ratio of the oxygen that is utilized has only 8% degree.The ratio that contains aerial oxygen is 25%, has therefore only utilized for microorganism to be blown into 2% of air.Promptly in existing method, be blown into the air that makes microorganism activeization needed 50 times from gas blower or compressor, the efficient extreme difference.In contrast, in the method for the invention, can think that what supply to the oxygen of handling tank almost 100% is used in microorganism.If use system of the present invention, as long as supply with the oxygen of actual aequum.Therefore,, can reduce the air capacity that is pressed into, expenditure on power can be reduced to 1/8~1/10,, then can carry out the higher control of precision if often monitor with DO instrument (oxygen densitometer) owing to comparing with existing method by implementing method of the present invention.
As vane pump, be the such structure of waterwheel that has wall in the outside, have the wall in the outside and the blade of waterwheel and contact such airtight space.The wall in the outside is not circular, has height, uses rubber usually as the material of blade, and is flexible along its wall in order to make it, the spring that adds between axle and blade.Blade pass is crossed the centrifugal force that utilizes it to turn round with spring and rotor and produce, and is rotated closely contiguously with wall, obtains big outlet pressure.
But, when original employed vane pump is used in method of the present invention, microorganism in the treating water and other inclusion are wrapped on the spring, thereby the bounce of spring is weakened, produce the gap thus between blade and wall and can not obtain high discharge pressure, it is unsuitable therefore it being used in method of the present invention.As the vane pump that is used in the method for the present invention, preferably have and on the plug that is fixed in the rotating shaft, cover blade hood-likely, slide by this blade of the centrifugal force that is accompanied by rotation and connect airtight the vane pump of the structure on wall.When the material of blade is rubber, owing to a little less than its rigidity, have because inclusion makes the danger of this deformable blade.For fear of this problem of generation, preferably use the blade of the such synthetic resins of bronze carbon (Block ロ Application ズ カ-ボ Application) (BC, the bronze that hardness is high) or PVC.In addition, the material of wall is preferably used the metallicity material higher than the material hardness of blade.The dynamic efficiency of such vane pump can obtain the high value more than 0.98.
When replacing vane pump to use vortex pump, because its dynamic efficiency normally about 0.50~0.60 is considered undesirable from the aspect of saving.In addition, though the such reciprocating pump of piston pump can obtain and the same high dynamic efficiency of vane pump, generally it is relatively more expensive, less economical.Therefore, as the pump that is used in method of the present invention, preferably use above-mentioned such vane pump of constructing.
The method according to this invention owing to only be used for supplying with to biological sludge the purpose of oxygen as previously mentioned towards the aeration of treatment trough, is not enough to stirring system integral body.Therefore, outside this, stirrer must be set.Below whipping appts that the present invention is used be elaborated.
The structure that is used in the whipping appts of the inventive method is a suspension solid of revolution and have and make this solid of revolution shake the whipping appts of the function that rotatablely moves between the diaxon that be arranged in parallel, have orthogonal tabular or the orthogonal discoid solid of revolution that is called the three-dimensional shape of water droplet (オ ロ イ De) body, along with shaking of this solid of revolution rotatablely moves, move the vertical or horizontal position in generation cycle, rotatablely moving of uniqueness by its solid of revolution attracts its water layer on every side, produces the Yang Liliu that pushes its water layer on every side open simultaneously.Illustrate in greater detail and be, be the mode of the 8 word shapes described with the rectilinear orbit of the supporting-point of two forked bars connecting the bearing and turning body between bolster along producing the current of the main force with the direction of bolster approximate vertical.By utilizing such Yang Liliu (current band), can utilize the high effect of the dispersion current that produce periodically ground to carry out moving of water layer towards wide scope direction, therefore can carry out general stirring to the whole inside of treatment trough efficiently.
Employed whipping appts of the present invention, owing to mainly make vertical tabular or discoid solid of revolution swing movement, with compare by the condition of stirring that bubble carried out that diffuser is blown into from gas blower or compressor, only consume its 1/5~1/10 or energy still less.This solid of revolution is because produce the vortex sheet that the wing manufactures, and diminishes with the impedance of ambient water, therefore reduces power consumption significantly.Owing to make the rotator swing movement, and can not damage microbe carrier.As employed solid of revolution among the present invention, in addition also can use the spy to open the solid of revolution of flat 11-276874 number such water droplet shape of putting down in writing or other any solid of revolution.
Below present invention will be described in detail with reference to the accompanying the rotating part of employed whipping appts and the structure of driving part.
Fig. 1 is the summary pie graph of the embodiment of expression whipping appts used in the present invention.This whipping appts has solid of revolution 10 and drives the driving part 20 of this solid of revolution 10.But effect of the present invention is not limited to represented solid of revolution of this example and driving method thereof.
Gou Zao solid of revolution 10 is orthogonal flat solid of revolution like this, as the center axis body 11 is shaken with the central part of length direction on one side by driving part 20 and makes axis body 11 rotations on one side around the axle center.As shown in Figure 1, driving part 20 has a pair of supporting plate 21 and 22 that separates proper spacing and be provided with in parallel to each other, separates equidistantly the stator supporting plate 23 of configuration in parallel to each other between two supporting plates 21 and 22.Each supporting plate 21 interconnects its relative each corner part mutually with 22 by coupling shaft 24, and in addition, each corner part of stator supporting plate 23 is bearing in respectively on the central part of each coupling shaft 24.
The shape of orthogonal discoid solid of revolution is to have outstanding shape on the wing 12, and A Luoyide alloy shape for example is recorded in that the spy opens in flat 11-276874 number.
Fig. 2 is to use the vertical view of the stator supporting plate in the driving part of whipping appts shown in Figure 1.Forming a pair of communicating pores 23a on the stator supporting plate 23.In the outer circumference portion of each communicating pores 23a, be respectively equipped with step 23b, the stator 25 that constitutes motor is installed respectively on each step 23b.Equally spaced be provided with 12 outstanding stator core 25a of inside side at each stator 25 upper edge circumferentially spaced, on each stator core 25a, twining coil 25b respectively.
Central part at each stator 25 is disposing rotor 26 respectively.Each rotor 26 has the rotating shaft 26a with the configuration of stator 25 concentric shape ground, the end of each rotating shaft 26a is rotatably mounted by being located at bearing 27 on supporting plate 21 and 22 respectively, at the axial central part of the rotating shaft 26a of each rotor 26 to be respectively equipped with the round plate 26b of the external diameter bigger than the external diameter of rotating shaft 26a with rotating shaft 26a concentric.Outer peripheral edges portion at each round plate 26b is respectively equipped with high magnetic flux density magnet 26c along its full week.
Respectively the torque that each motor had that constitutes by each stator 25 and each rotor 26 be installed in each rotor 26 respectively on high magnetic flux density magnet 26c magnetic density and be directly proportional by the magneticstrength that width (length of radial direction) and the thickness of each high magnetic flux density magnet 26c determines, be flowing in the stator core 25a that is wrapped in each stator 25 respectively on coil 25b in the repulsion that is directly proportional of the magnitude of current become torque.Therefore, increase, and the density of each the coil 25b that is located on the stator 25 is increased, can increase the repulsion of each rotor 26, the torque that improves each rotor 26 for each stator 25 by the width dimensions that makes the high magnetic flux density magnet 26c that is installed on each rotor 26.
The end of rotating shaft 26a in each rotor 26 is outstanding from side's supporting plate 21 respectively, with each rotating shaft 26a universal coupling 28 is installed rotatably integratedly respectively on the end of the rotating shaft 26a that gives prominence to from supporting plate 21.
And, the joint portion of a pair of bar 15a of portion that on each universal coupling 28, is connecting each transom 15 of above-mentioned stirring body 10 respectively, thus, the axis body 11 of stirring body 10 can shake and is installed in rotatably on the driving part 20 with the tilt states of 45 degree of relative each rotating shaft 26a.
Each transom 15 respectively shakes the orthogonal mode of central shaft 15b with it and is installed on the universal coupling 28 under the state that phase shifting 90 is separately spent.
On each rotor 26 and the end end opposition side that universal coupling 28 is installed, electromagnetic type starting engine 29 is installed respectively.Each starting engine 29 has solenoid coil 29a respectively, at the front end of the plunger 29b of each solenoid coil 29a columned rotatable parts 29c is installed, and these rotatable parts 29c combines with rotating shaft 26a and makes the scope internal rotation of rotating shaft 26a at 45~90 degree.
Be provided with compression spring 29f between rotatable parts 29c and supporting plate 22, when making plunger 29b when sliding near the direction of supporting plate 22 to solenoid coil 29a energising, rotatable parts 29c revolts the elastic force of compression spring 29f and combines with rotating shaft 26a.Then, by rotatable parts 29c is rotated to prescribed direction, rotating shaft 26a rotates 45~90 degree along prescribed direction under such state.In contrast, when stopping solenoid coil 29a switched on, rotatable parts 29c removes and the combining of rotating shaft 26a under the elastic force effect of compression spring 29f and slide to solenoid coil 29a side.
Each stator 25 is when each the rotating shaft 26a rotation starting that makes driving part 20 respectively, and to solenoid coil 29a energising, the rotatable parts 29c that is located at the leading section of plunger 29b combines with each rotating shaft 26a respectively, makes each rotating shaft 26a rotate the degree of 45~90 degree respectively.Thus, each rotating shaft 26a obtains the moment of starting of 100kgfm degree respectively, and beginning is rotation sleekly.In addition, when each rotating shaft 26a began to rotate, thereafter, rotating shaft 26a was rotated by the torque of 1/3~1/5 degree of the torque in when starting.
Under the situation when being located at starting when initial start, after stopping of each rotating shaft 26a on each rotor 26 respectively etc. by generations such as fault rotation, need big torque, but at that time, switch on by the solenoid coil 29a short period of time to each stator 25, moment makes the plunger 29b action of each solenoid coil 29a respectively, and each rotating shaft 26a is rotated by high torque (HT).
In common electric motor, when starting, make rotor rotation and obtain high torque (HT) by geared motor, still, to consume many electric power in this case.In contrast, have the starting engine of solenoid coil 29a, can make solenoid coil 29a rotation, can reduce power consumption significantly by use.
In such structure whipping appts, in driving part 20, constitute each rotor 26 rotation in the opposite direction respectively of motor.Like this, side's rotor 26 is with the speed rotation higher than the benchmark speed of rotation of regulation, and during this period, the opposing party's rotor 26 is with the speed rotation lower than its benchmark speed of rotation.For example, each rotor 26 every pi/2 that rotated, the high speed rotating of each rotor 26 and low speed rotation are switched.
Each rotor 26 is by alternately carrying out high speed rotating and low speed rotation repeatedly, changes in 90 degree scopes while turn over 90 vergence directions of spending (pi/2), its axis body 11 around its axle center by the universal axis body 11 that connects the rotator 10 that nodal axisn 28 connects respectively of the rotating shaft 26a of each rotor 26.Therefore, when side's agitating wing 12 shakes downwards from the top, on one side around axis body 11, turn over pi/2, during this period, when the opposing party's agitating wing 12 shakes upward from the below, around axis body 11, turn over pi/2 week on one side.And solid of revolution 10 is by in turn carrying out such action repeatedly, and the wing 12 of each rotator is rotated off and on.
Like this, when being shaken, the flat wing 12 is rotated off and on, for example in the space that produces as fluidic water by each wing 12 extrusion, in turn flow into water, but the water of this inflow forms little eddy current group, and little eddy current group replaces continually, and the friction resistance that the frictional belt of the water of inflow and the water of halted state goes out reduces significantly.Therefore, even the rotary area that is considered to be wrapped in easily the end of a thread on the wing 12 of each rotator etc. and the wing 12 is near also being difficult to be inhaled into, even also can not damage them near microorganism carrier.Its result has reduced the power consumption of the wing 12 rotations that are used to make each solid of revolution.
In addition, while it rotated off and on and when extruding water, form the band of main current by the water that is forced out when the above-mentioned wing 12 that makes each rotator like that shakes.The band of these current becomes the little high velocity flow of runout angle (basin width) Tile Width little, flow velocity in its axle center relatively.Its result, the main current band that the wing 12 by each rotator can be produced is delivered to a distant place respectively.
Take advantage of from the micro bubble of pressurization tank ejection and to produce horizontal mobilely to processing tank integral body, spread in non-vertical ground come-up on such generation current on one side, do not have lavishly and supply with oxygen to the purpose microorganism, the oxygen that supplies in the treating water almost is consumed at this, and its result can assert that oxygen dissolved efficiency and oxygen move efficient and uprises.
Relative therewith, in the agitating wing of spiral etc., be large volume more, the runout angle in the relative axle center of formed main current band (basin width) is big more, and, rotation more at high speed, the current that produced by self sucking action around blade are remarkable more.Its result applies big resistance to the agitating wing of spiral etc., and its result needs big consumption electric power.
While keep pressurized state will contain the gas of dissolved state and imperceptibly this object water of the gas of dispersed state turn back to this processing tank once more, when making micro bubble be ejected into the inside of handling tank when this position in regulation is released to normal pressure, according to certain condition, adhered to sometimes micro bubble biological sludge come-up screw clamp top and become isolating state.For fear of producing this situation, also can and with consuming the few oar formula agitation mixer of electric power, mix upper layer selectively, peel off the bubble that adheres to and biological sludge disperseed, keep biological treatment effect.
Then, when such sewage of purified industrial waste water and water drain water, the carrier that has adhered to biological sludge is swum, and this carrier has big gap, better is that proportion is 0.90~0.98, preferably 0.95~0.98, specific surface 100m
2/ m
3Above plastic ball type carrier.When biological sludge attached on this time, the proportion of proportion and treating water is almost equal, floats in the treating water.In addition, when being sphere, can move towards all directions along with stirring the flowing of water that produces.In addition, because it rotates with going round and round, contacting of biological sludge and sewage composition is extremely good.In addition, under the state that biological sludge is swum, when making system of the present invention running, the top of biological sludge come-up screw clamp and isolating state occurs accidentally sometimes.But, when also usefulness has been adhered to the plastic carrier of biological sludge, can prevent this phenomenon.Since make carrier surface attachment the biological sludge of high density, not only go for the processing of the dirty compound sewage of high density, but also can reduce the area of treatment trough.
In addition, be used to make the motor of the machine driving of carrying out system of the present invention to use by the machine that the DC power supply directly drives by selection.And these motors preferably use the motor with high magnetic flux density magnet, and this high magnetic flux density magnet has the above magneticflux-density of 0.5 tesla.Such motor can obtain high torque with low current low voltage, promptly few electric energy.
According to method of the present invention,, can easily utilize from the electric energy of the natural energy of solar electrical energy generation and wind-power electricity generation etc., the energy transformation that promptly reclaims from natural phenomenon because the power consumption of vane pump and whipping appts is few.Because solar power generation can not generate electricity at night, therefore and when being stored in remaining electric power in the store battery, can holding concurrently round the clock and turn round capablely with wind-power electricity generation.
When consumption electric power in entire system ground is big, in order to utilize these natural energies, need jumbo power generation assembly, unfavorable economically, jeopardize practicality.Therefore, owing in the construction of jumbo natural energy power generation assembly, need great energy, can not say the energy balance of integral body useful.Therefore in order to realize utilizing the system of natural energy, must reduce energy charge as best one can.From this viewpoint, by method of the present invention, realized all utilizing for the first time the Waste Water Treatment of natural energy.Method of the present invention, even utilization also is ideal by the electric power of the burning acquisition of the fossil oil of oil or Sweet natural gas etc. from energy-conservation position, but by utilizing natural energy just to find out the social effect of the present invention that conservation of natural environment is such.
In addition, method of the present invention owing to adopt the method that makes microorganic adhesion carry out wastewater treatment on plastic carrier, therefore, can be handled the high high-concentration waste water of pollution load with the processing tank of low capacity, can reduce the area that is provided with of entire system.When considering above-mentioned pollution-free energy, can wait to the sightseeing ground of intermountain portion treatment system of the present invention is set without barrier.
As mentioned above, method of the present invention helps the minimization of energy-conservation, pollution-free energy and plant facilities, adopts its economy of method of the present invention and social effect very big.
Below, specifically describe method of the present invention by embodiment, but method of the present invention is not limited to this.
[embodiment]
Putting into BOD concentration in the waste water treatment tank of width 6m, depth 30m, degree of depth 4.5m is 600mg/m
3Waste water 760m
3, to wherein supplying with diameter 25mm, specific surface 285m
2/ m
3The ball type carrier 10m of polypropylene system
3, made microorganic adhesion on this carrier through one month.Then, use vane pump that the wall by the blade of PVC system and Hasiteluoyi system constitutes with mean flow rate 41m
3Attract this waste water, from being located at elsewhere same vane pump with 3.1kg/cm
2Pressure in the discharge pipe arrangement of this vane pump, be pressed into air, simultaneously through the pressurization tank with this pressurized water from portion foremost that this pressurization tank is provided in the pipe arrangement on this wastewater treatment groove bottom by pressure regulator valve with 3.0kg/cm
2Pressure when being put into this pressure water in the waste water treatment tank, produce the micro bubble of diameter 8 μ m.In addition, with making major diameter is that the orthogonal discoid solid of revolution of 500mm shakes on the bottom surface that the whipping appts that rotatablely moves is arranged on this waste water treatment tank, when its speed with 60rpm is rotated, this fine bubble spreads all over the processing tank and moves all sidedly, in such Waste Water Treatment, with above waste water with 25m
3The flow of/hr supplies to when handling in this waste water treatment tank, and the BOD for the treatment of water becomes 20mg/m
3, reduced rate is 96.5%.
These handle needed electric energy is that pressurized water is supplied with the total 4.18kw with vane pump 2.93kw, compressed air-feed vane pump 0.75kw, whipping appts 0.50kw.Use the solar generator of output rating 10kw and the aerogenerator of output rating 15kw as the electric power supply source, after the electric power with surplus temporarily is stored in the store battery of market sale, can be from this store battery to each machine supply capability.
[comparative example]
In order to compare, with the same processing water yield during with the waste water shown in the existing aeration type Wastewater Treated by Activated Sludge Process embodiment that does not use microbe carrier, in order to obtain processing with water quality, the waste water treatment tank that needs width 6m depth 50m degree of depth 4m, power needs 2 on the compressor of 15kw, has amounted to 30kw.
The effect of invention
According to the present invention, in the method with the sewage of activated sludge purification industrial wastewater etc., pass through tool There is the revolution structure section that does not destroy the function that biological sludge just can pressurize to attract also from processing tank Pressurization contains the object water of the floating material of biological sludge etc., with itself and the gas of unit feeding by other Pressurization mixes, and then they is imported accumulator tank, only separates selectively the gas of supplying with superfluously, Then, while keep pressurized state and will contain the gas of dissolved state and be dispersed imperceptibly This object water of the gas of state turns back to this processing tank, and is in the position of regulation that it is open for normal Press, when making fine bubble be ejected into the inside of processing tank, by having the current of attraction function Make processing object sewage, biological sludge on one side with the mechanical realization section of any setting of releasing the current function And fine bubble spreads all over each corner of processing tank integral body, makes efficiently their mixing on one side Contact improves biological decomposition speed thus, flows into locating of dirty load water thereby can carry out high concentration Reason simultaneously purifies plant chimney stalk etc. with few energy consumption in the situation of not using aerator Sewage.
Claims (6)
1. active sludge processing system, it is characterized in that, in method with the sewage of activated sludge purification trade effluent etc., by having the revolution structure portion that do not destroy the function that biological sludge just can pressurize from handling tank and attract and pressurization containing the object water of the seston of biological sludge etc., with its with mix by other the gas pressurization of unit feeding, then they are imported storage tanks, only separate superfluous ground gas supplied selectively, then, to contain the gas of dissolved state and be turned back to this processing tank again by this object water of the gas of dispersed state imperceptibly while keeping pressurized state, in the position of regulation it being opened is normal pressure, when making fine bubble be ejected into the inside of handling tank, make process object sewage on one side by having the physical structure portion that attracts the current function and release any setting of current function, biological sludge and fine bubble spread all over each corner of handling tank integral body, make them mix contact on one side efficiently, improve biological decomposition speed thus, thereby can carry out the processing that high density flows into dirty load water, under the situation of not using aerating apparatus, purify the sewage of plant effluent etc. simultaneously with few energy expenditure.
2. active sludge processing system as claimed in claim 1, it is characterized in that, even the structure of the turning valve of revolution structure has volume type pump function, that power consumption is few of not destroying biological sludge and can keep pressurized state continuously under the situation that foreign matter exists.
3. active sludge processing system as claimed in claim 1, it is characterized in that, have function that attracts current and the physical structure thing that extrudes the function of these current and be solid of revolution is suspended in two between centers that be arranged in parallel and have and make this rotator shake the whipping appts of the function of return motion.
4. active sludge processing system as claimed in claim 1, it is characterized in that, the gas that will contain dissolved state turns back to this processing tank with this object water that is separated into the gas of fine state once more while keeping pressurized state, in that its position in regulation is released to normal pressure fine bubble is ejected into when handling tank inside, become isolating state for fear of the top of the biological sludge come-up screw clamp that has adhered to micro bubble, the few oar formula agitation mixer of electrification consumption simultaneously, mix upper layer selectively, peel off the bubble that adheres to, make the biological sludge redispersion, keep biological treatment effect.
5. active sludge processing system as claimed in claim 1, it is characterized in that, in waste water treatment tank, plastics system carrier with big gap is swum, the biological sludge that makes high density is preventing that attached on this carrier micro bubble from adhering to the isolating processing of carrying out high density load sewage simultaneously of come-up of the biological sludge that is brought.
6. active sludge processing system as claimed in claim 1, it is characterized in that, the CD-ROM drive motor that will be used to drive all machines is chosen as the machine that directly drives with the DC power supply, uses as its whole driving power that have will be from the energy transformation of the natural phenomenon recovery power supply as the function of electric energy.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB021020345A CN100453477C (en) | 2002-01-17 | 2002-01-17 | Active sludge processing system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB021020345A CN100453477C (en) | 2002-01-17 | 2002-01-17 | Active sludge processing system |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1432537A true CN1432537A (en) | 2003-07-30 |
CN100453477C CN100453477C (en) | 2009-01-21 |
Family
ID=27627445
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB021020345A Expired - Fee Related CN100453477C (en) | 2002-01-17 | 2002-01-17 | Active sludge processing system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN100453477C (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106458650A (en) * | 2014-08-01 | 2017-02-22 | 住友电气工业株式会社 | Water treatment system |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3434064A1 (en) * | 1984-09-17 | 1986-03-27 | Oloid Ag, Basel | DEVICE FOR DRIVING A BODY WHICH DOES A STILLING AND ROTATING MOTION |
CN1049409C (en) * | 1994-08-04 | 2000-02-16 | 卢喜林 | Synchronous intensified jet method of biological dephenolized mud mixed nutrient sewage |
JPH11276874A (en) * | 1997-12-26 | 1999-10-12 | Stm Engineering Kk | Agitating apparatus and agitation using the same |
CN1081612C (en) * | 1998-11-19 | 2002-03-27 | 昆明金京田科贸有限责任公司 | Technology and apparatus for treatment of sewage by double baffle type biological process |
-
2002
- 2002-01-17 CN CNB021020345A patent/CN100453477C/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106458650A (en) * | 2014-08-01 | 2017-02-22 | 住友电气工业株式会社 | Water treatment system |
Also Published As
Publication number | Publication date |
---|---|
CN100453477C (en) | 2009-01-21 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN1875193A (en) | Fluid circulation system | |
CN108358364B (en) | A water purifies agitating unit for river course is administered | |
WO2007023864A1 (en) | Bubble generator | |
CN108046415B (en) | Biological rotating disc | |
WO2016174656A1 (en) | Water-driven device, system and method for aerating or mixing a body of water | |
JP4335888B2 (en) | Liquid purification treatment equipment | |
CN111302508A (en) | Efficient rotary-circulation oxygen-increasing and air-distributing device | |
CN100453477C (en) | Active sludge processing system | |
CN219469819U (en) | Biochemical reaction tank | |
CN1291925C (en) | Horizontal integrated three phase inner circulation fluidized reactor and its biological reaction process | |
CN217323476U (en) | Electric flocculation and magnetic separation combined device for treating micro-plastics in sewage | |
CN203807239U (en) | Biological rotating disc wastewater treatment device | |
CN102701456A (en) | Micro-nano active oxygen treatment method of sewage | |
CN202499750U (en) | Solar blowing aeration system | |
CN202785912U (en) | Water- driven compound biological sewage treatment device | |
CN112744933B (en) | Water body ecological restoration device | |
CN212894091U (en) | Hydraulic mixing device and sewage treatment equipment | |
CN101412569B (en) | Aeration water-drawing technology | |
JP2006281183A (en) | Water treatment apparatus using biological membrane | |
CN1915861A (en) | Axial flow type self oxygenated aerator for activated sludge | |
CN1331773C (en) | Membrane rector with rotary brush | |
CN108101138B (en) | Air flotation head for dissolved air in cavitation | |
CN2641035Y (en) | Air supply low pressure jet aerator | |
JP2003181486A (en) | System for treating activated sludge | |
CN110182950A (en) | Horizontal integrated oxidation ditch tank |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C17 | Cessation of patent right | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20090121 Termination date: 20100219 |