WO1983002769A1 - Water treatment apparatus - Google Patents
Water treatment apparatus Download PDFInfo
- Publication number
- WO1983002769A1 WO1983002769A1 PCT/JP1983/000038 JP8300038W WO8302769A1 WO 1983002769 A1 WO1983002769 A1 WO 1983002769A1 JP 8300038 W JP8300038 W JP 8300038W WO 8302769 A1 WO8302769 A1 WO 8302769A1
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- WIPO (PCT)
- Prior art keywords
- sewage
- water
- cylinder
- outlet
- bubble
- 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.)
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Classifications
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
Definitions
- the present invention relates to an improvement in a water treatment apparatus for sewage containing filth, for example, oil, BOD, COD.SS, and a melt (salt, pigment, etc.).
- a water treatment apparatus for sewage containing filth for example, oil, BOD, COD.SS, and a melt (salt, pigment, etc.).
- the separation, separation, and the like are performed by utilizing the buoyancy and sedimentation power of the filth itself, such as adhesion, sedimentation, and floating. Therefore, the treatment capacity is very poor, and the sludge removal rate is at most about 90%, so it is difficult to reach.Therefore, even if it is clean water, it must be diluted with water and then discharged. did not become. Also, in the by that 15 devices in the activated sludge system and required a very wide land to the installation you]? (For example, if the treated water 2,000 tz, had been required of about 6 6 0 w 2 land The running cost was also very high. Before using this method, the processing time was about 24 hours, and the remaining
- An object of the present invention is to improve the above drawbacks and to provide a water treatment apparatus having a high water purification capacity, a compact structure, a small installation area, and a low cost of footprint. Target.
- a waste coagulation device in which an inorganic coagulant, an alkaline agent, and a polymer coagulant are sequentially injected to a downstream side, and an upward flow in which wastewater from the waste coagulation device is guided to a lower portion.
- a downward flow path following the flow path a fine bubble mixed water introduction pipe is connected to a lower part of the upward flow path, and a floating waste above the upward flow path described in ⁇ 0.
- a water treatment apparatus characterized by including a pressurized flotation / sedimentation tank having a reservoir section, and a bubble mixed water generator connected to the fine bubble mixing / water introduction pipe.
- the filth removal rate has been significantly improved, and the treated water has fallen below the water quality regulation value 3 ⁇ 4, so that it can be discharged without being rarely diluted.
- the area required for installation of the equipment was minimized, and the cost of Rankin 'was significantly reduced. Therefore, in the present invention, the wastewater is treated while being moved, so that the treatment time is remarkably reduced, and almost no sludge sludge remains in the apparatus.
- FIG. 1 is a system diagram showing one embodiment of the present invention
- FIG. 2 is a cutaway front view of a detached louver
- FIG. 3 is a side view thereof
- FIG. Fig. 5 is a vertical cross-sectional view of the bubble mixed fluid generator
- Fig. 6 is a Vi-M end view of Fig. 5,
- FIG. 7 is a cross-sectional view showing another embodiment of the separated fission body.
- the figure is a cutaway front view showing still another embodiment.
- the present invention provides a separation tower 1A, an oil aggregating apparatus 2A, a pressurized floating sedimentation tower 3A, and a bubble mixing apparatus for generating and feeding bubble mixed water to the pressurized floating settling tank.
- Liquid generator A Liquid generator A
- the separation vessel 1A is a container having a bottomed rectangular tube having a sewage inlet 11a and a purified water outlet 11b on the bottom wall 11.
- a support plate provided between the outlet 1 1b and the lower part of the main body 1 for dividing the lower part of the main body 1 into an inlet-side sewage rise area 1a and an outlet-side purified water descending area 1b (FIG. 2). It has a filth coarse-graining member 6 supported by the member 5 J9, a filth accumulation amount detection unit 7, a cleaning air pipe 8, and a drain pipe 9.
- the upper part of the main body 1] is the floating waste reservoir.
- the cover 2 is formed with two reduced diameter portions 2a and 2b that are stacked in a stepwise manner. That is, the first reduced diameter portion 2a is reduced in diameter so that the left and right side walls have an upward small diameter.
- OMPI The horizontal step part 2 1 that prevents Then, in the center of the upper wall, a second shrinkable portion 2b having a side wall having a right cylindrical shape and a horizontal step portion 22 similar to that described above is attached with a gun. Furthermore, a large part of the elbow 3 having a different diameter is connected to the center of the horizontal step part 22 of the second reduced diameter part 2b.
- a waste pipe provided with a solenoid valve which is intermittently opened and closed, not shown, is attached to the small diameter portion of the elpo.
- a support member 5 is provided horizontally below the upper end of the partition plate 4 and a plurality of golds H ′ are superimposed on the support member 5.
- the coarse-grained member 6 dirty water area 1 a The side is Sa and the water purification area 1b side is 6b).
- the dirt accumulation amount detector 7 is composed of the first oil amount detector 7 1 and the second oil amount detector 72 using the electrode 7 a], the rear wall of the first reduced diameter portion 2 a and the tower body. It is protruding from the upper rear wall of and 1.
- a pair of left and right cleaning air pipes 8 are provided at the bottom of the tower body 1 and closed at both ends to form a U-shaped pipe 81 with a large number of air ejection holes 81a and attached horizontally. Air is supplied via the connecting member 82. Drain extubation
- a pair of right and left 9 is provided on both bottom walls 11 sandwiching the partition plate 4.
- 10a is a leg provided at the position 2 'of the bottom wall 11 in the pair line
- 10b is a vibration damping member projecting from the separation tank
- 31 is an automatic exhaust valve. Mounting seat.
- a mixing device 2 10 in which a coagulant mixer 2 11, an aluminum coagulant mixer 2 12 and a polymer coagulant mixer 2 13 are provided side by side, and an inorganic coagulant pump 2 2 1, Alkali agent pump 2 2 2 and polymer flocculant pump 2 23, inorganic flocculant tank 2 3 1, Alkali agent tank 2 3 2 And a chemical tank 230 containing a polymer flocculant tank 2 33;
- Each of the mixers is sent from the separation filter, and flows from the upstream side to the downstream side according to the flow path of the liquid in which the oil remains, and the inorganic flocculant mixer 211 and the alkaline agent mixer 2 12 and the polymer flocculant mixer 2 13 are connected in series.
- the liquid proceeds in each of these mixers along the length direction.
- a number of baffles (not shown) are provided at right angles to the direction of travel of the liquid, and zigzag. A flow path is being formed.
- inorganic coagulation fed through pumps 22 1, 22 22 and 23 from the various tanks 23 1, 23 32 and 23 33 respectively
- the supply pipes 241, 242, and 243 of the agent, alloy agent, and high molecular coagulant are connected and opened.
- the 2 shown! ⁇
- the liquid supply line to the separation tower 1 A or al mixing device 2 1 0, 2 P 2 is Ru Ah in the feed tube to the next step.
- inorganic flocculant aluminum chloride is used as the inorganic flocculant
- caustic soda is used as the alkaline agent.
- Acryl Lock A — 1 0.1 (trade name) mainly composed of acrylic polymer Organic agents such as Gaku Co., Ltd. (Tokyo) and polyacrylamide are suitable.
- the pressurized floating sedimentation tank 3A is composed of a first cylinder 310, a second cylinder 320, a third cylinder 330, and a fourth cylinder whose outer shapes are vertical cylinders. 340, a bubble mixed water introduction pipe 350 connected to the first cylinder 310, and the second cylinder 3
- the first cylinder 310 has a cylindrical shape with a bottom, a sewage supply pipe serving as the water inlet 311 is connected to the bottom wall, and a bubble-mixed water introduction pipe opening upward on the lower side wall. 350 is penetrated.
- the top of the first cylinder 310 is an open wastewater outlet 312.2.
- the second cylinder 320 is concentrically arranged with respect to the first cylinder 310 via a gap piece 320a, and the upper and lower ends thereof are opened.
- the second cylinder 320 has a lower portion disposed concentrically with the first cylinder, and an upper portion has a step 32 above the first cylinder 310.
- a large-diameter portion 3 23 is formed through 3 a, and a waste discharge pipe 360 is connected to the upper end of the floating material outlet 3 21.
- the third cylinder 330 is sheathed concentrically with respect to the second cylinder with a space therebetween, and the fluid outlet 331, at the upper end thereof, is provided with the large-diameter portion.
- a flange 332 is provided outward from the upper end of the third cylinder. It is.
- the first cylinder 310 is passed through the center of the bottom wall 33 33 of the third cylinder 330.
- the lower part of the third cylinder 330 is a waste sedimentation chamber 330a, and a sediment discharge pipe 370 with an on-off valve with a waste outlet 333b opened in the bottom wall 333. Is connected.
- the fourth cylinder 340 is covered with the third cylinder 340 left concentrically with respect to the third cylinder 340.
- the side wall 341, top wall 342, and bottom wall 343 of the fourth cylinder 340 also serve as the outer side wall of the pressurized floating tower 3.
- an upper layer 340a of activated carbon or the like is provided on the receiving member 440 (below it, a large number of pores are provided on the lower surface below).
- the clean water outlet pipe 38 1 is connected via an annular water collecting pipe 38 0 having the following structure: 38 2 is a back washing water supply pipe connected to the other side of the water collecting pipe 38 0, 3 Reference numeral 83 denotes a backwash water discharge pipe provided on the top wall 34 of the fourth cylinder.
- the waste discharge pipe 360 is connected to the upper end of the second cylinder 320 and fixed to the top of the main body of the pressurized floating sedimentation tank. Then, in order from bottom to top, a right circular cylindrical part 361, which has the same diameter as the upper end of the second cylinder, a conical first constricted part 362, whose upper part has a reduced diameter, and a mysterious lipo-shaped part 2 Consists of a reduced diameter section 3 6 3.
- a solenoid valve (not shown), which is automatically opened and closed intermittently, is connected to the tip of the second shrinking part 363, and discharges the waste collected in the waste discharge pipe 360 intermittently. It is structured.
- the bubble-mixed liquid generator Ap is composed of gas bubbles (air nozzles 410, liquid (water) nozzles 420) having concentric gas (air nozzles 410).
- the gas nozzle 410 has a horizontal gas ejection direction, and a male screw 411a into which the liquid nozzle 420 is screwed on the outer periphery of the tip is located at the center.
- a base portion 411 formed with a stepped air chamber 4 1 1b having a tapered taper, and an intermediate hole 4 1 2a connected to the air chamber 4 1 1b, and an unopened space following it. It is the same as the tip part 4 12 provided with the taper outlet 4 12 b.
- the liquid nozzle 420 has a long cylindrical shape along the center line, and has a water inlet hole 420a at the base.
- a liquid chamber 4 2 1 which communicates with the hole 4 2 0 a, and a non-wide tapered hole 4 2 2 formed from the liquid chamber 4 2 1 and concentric with the center line of the jet port 4 12 b.
- the liquid is formed such that the liquid flows from around the ejection port 412b toward the position immediately before the ejection port 412b and joins on the center line of the ejection port.
- At the base of the fluid nozzle 420 is the gas nozzle g I.
- a female screw 42 0a to be screwed with the 10 male screw 4 11a is provided.
- the four workers are packing.
- the bubble generating section 4A has a taper angle of the ejection port 4 12b, and a ⁇ 0 angle of the Suehiro taper hole 4 22.
- the transition corner Q is a smooth bevel so that the fluid becomes laminar.
- the jet air flow from 410 is a suehiro te
- a flow of fluid is formed.
- the following condition of 0 also contributes to the formation of a laminar flow of the fluid, and the liquid fills the liquid chamber 4 21 to obtain an average water flow to the hole 4 22 from the peripheral force of the ejection port 4 12 b.
- the bubble stabilizing section 4B is a Suehiro tape of the bubble generating section 4A.
- An outer cylinder 430 communicating with the hole 4222, and a flow direction perpendicular to the inflow direction of the bubble-mixed water from the divergent taper hole 422 provided inside the outer cylinder.
- the first change portion 440, the second change portion 450, and the third change 3 ⁇ 4460 are composed of strong obstruction members.
- the outer cylinder 430 has a horizontal axis and has a side wall 431 along the fluid inflow direction, and an end provided on the fluid inflow side of the side wall 431. J from wall 4 3 2
- the end wall 432 is provided with a first inflow hole 432a for liquid at the center thereof.
- the first diverting portion 4440 is located on the inner upstream side of the outer cylinder 4330 and has a circular plate-like side (which is perpendicular to the fluid inflow direction) facing the liquid inlet hole 432a.
- a plate-like vertical member (fluid of fluid) that is in contact with a member 441 and a plurality of portions of the outer edge of the horizontal plate member 441 and is bonded to the horizontal member 441 3 ⁇ 4 the end wall 432.
- the gap between the vertical member 4 42 and the end wall 4 32 between the vertical member 4 42 and the end member 4 42 is the first liquid. It is a turning channel (Fig. 6).
- the second changing portion 450 is provided at a middle portion of the outer cylinder 43 0, along the outer cylinder side wall 43 1 -a cylindrical vertical member 45 1, and an upper portion of the vertical member 45 1
- the first horizontal member 452 connects the downstream end to the outer cylinder side wall, and the second horizontal member 453 closes the downstream end of the vertical member 451.
- the vertical member 45 1 is provided with a large number of horizontal holes 45 1 a, which are ⁇ 2 diverting flow paths, in the periphery thereof, and the first vertical member 45 2 has a vertical member in the center thereof.
- the second inflow hole 452a into which the is closely fitted is opened.
- the second diverting hole 4 51 a is the vertical member 4 5 1 on the same circumference are provided at equal intervals and at equal intervals in the vertical direction ⁇
- the third turning part 460 is a first horizontal member 461 2 that partitions the inside of the outer cylinder on the inner and downstream side of the outer cylinder 430, and a plurality of ridges connecting these two horizontal members.
- the vertical member 463 and a plate-shaped third horizontal member 464 supported in the middle of the vertical member 463, and the first stacking member 461 At the center thereof, a 5 m inlet hole 461 a is provided, and at the center of the second horizontal member 462, a liquid outlet hole 462 a is provided.
- a portion other than the vertical member 464 before and after the third horizontal member 464 is a third variable R3 flow passage.
- the bubble mixed water pressure adjustment tank 4C has a bubble mixed water outlet 4 at the lower part.
- a second pressure regulating device consisting of a cylindrical side wall 4 7 1 having a vertical axis with 70 a 3 ⁇ 4 and a top wall 4 7 2 having a valved air discharge hole 4 7 2 a and a bottom wall 4 7 3
- the tank body 470, an inlet pipe 480 for receiving the bubble mixed water sent from the bubble stabilizer 4B provided therein, and a downstream part of the inlet pipe 480 are a And a first pressure regulating chamber 490.
- the introduction pipe 480 is installed at the lower part of the main body 470, and is connected to a horizontal cylindrical section 481, which opens on the inner and downstream sides of the outer cylinder 431 of the bubble stabilizing section 4B.
- a vertical cylindrical portion 482 that opens downward into the first pressure regulating chamber 490]).
- ⁇ 482 is the part of the tank where the flow path is diverted.
- the lower end of the vertical cylindrical side wall 491 concentric with the vertical cylindrical portion 482 and having a larger diameter than the cylindrical portion 482 is formed in the tank main body 470.
- the bottom wall 473 is made watertight, and the top is covered with a top 492 having a large number of injection holes 492a.
- 4 7 4 is a pressure gauge mounting seat.
- the water mixed with filth is subjected to pump pressure, and the inlet 11a! ) It is sent to the entrance side sewage area 1a in the tower.
- large particles float through the wire mesh due to large buoyancy, and gather near the lower surface of the cover-2.
- fine filth with weak buoyancy is combined with other fine filth in the wire mesh 6a ⁇ and coarsened, and the buoyancy increases and the levitation rises.
- the filth collected near the lower surface of the cover-2 is opened by a solenoid valve (not shown) openly.
- the accumulated waste is separated because the elbow 3, especially the cover 2, has been reduced in diameter so that the lower part is largely opened and the upper part is reduced in diameter. Extruded over the entire area of the top. Also, in the case of a cover having such a shape, even when the separating fission is considerably troublesome, the water surface reaches the lower opening of the second reduced diameter portion 2b, and water is used instead of dirt. There is no fear of being pushed out. The water thus purified is discharged from the outlet lib through the water purification area 1b on the outlet side.
- the wire mesh 6b above the water purification area 1b serves as a waste filter so that coarse-grained waste is not discharged during this discharge.
- the first detector 71 is filled with dirt near the lower surface of the cover 2, the water surface is lowered by the dirt, and the interface between water and the dirt reaches the position of the oil amount detector 71. It senses that it has dropped and opens the solenoid valve on the waste pipe. Also, the second oil detector 72 helps to control the opening of the solenoid valve when the interface is lowered to the installation height of the device, and thus the interface is always in contact with the first oil detector. It is maintained at a height between and the installation positions of the second oil detectors 71 and 72.
- the cleaning air pipe 8 injects air at the time of cleaning the inside of the separation tank, and causes air bubbles to associate with the oil component adhering to the inside of the tank and the filth coarsening member 6 to form an oil mass and float. This is to make it happen.
- the mesh-like body layer in which the wire mesh, the synthetic resin mesh, the metal, and the synthetic resin woven body are laminated at random is used as the filth coarsening member 6, so that the conventional method is used.
- the sewage adhesion rate is lower and cleaning is easier.
- each chemical is added at the inlet. Then, each chemical flows down in a zigzag manner in each of the mixers, and is mixed well with the liquid in this downflow to block the fine oil.
- polychlorinated aluminum is added to the liquid in the inorganic coagulant mixer 211, the oil in the liquid is coagulated, and the next alloy is formed.
- the pH is adjusted to about 6.5 to 7.5, and in the final polymer coagulant mixer 2 13, the scattered fine particles are coagulated and strengthened in the block by a crosslinking action.
- the pressure floatation sedimentation separation fission an oil mass of an appropriate size that is easy to separate is formed.
- the water mixed with the flocculed filth is subjected to a pump pressure, and from the sewage inlet 311 to the first cylinder 3.
- the water mixed with the fine bubbles is sent into the first cylinder through the bubble mixed water generator Ap at the same time. Therefore, air bubbles adhere to the waste in the first cylinder, the buoyancy of the waste is increased, and the waste is accumulated in the waste guide pipe ⁇ 360 through the large diameter portion 323. Then, the remaining water from which the dirt has been removed] flows down the second cylinder 320 from the top to the bottom, and the remaining heavy dirt is discharged into the waste sedimentation pipe 330a. Is deposited.
- the water proceeds further and passes through the third cylinder 340 from bottom to top and enters the fourth cylinder 340.
- the water that has proceeded to the fourth cylinder 340 is purified through the furnace superstructure 340a, collected in the water collecting pipe 380 provided at the lower part, and the clean water outlet pipe 381] ) leak.
- the filth outlet pipe 360 is filled with filth, the water surface is reduced by the filth, and the interface between water and the filth is the oil amount detector 3a. It senses that it has fallen to the position of 90a and opens the solenoid valve of the waste discharge pipe 360. Also, the second oil detector 390b serves to control the opening of the solenoid valve when the interface drops to the installation height of the detector. In this way, the interface is always maintained at a height between the first and second oil changers 3900a and 39Ob.
- the sediment discharge pipe 370 collects in the waste sedimentation chamber 330a. Opened when discharging precipitated sediment.
- the upper end of the first cylinder 310 may be located in the lower cylindrical portion 361 of the waste guiding pipe 360, or the number of the waste discharging pipe 360 may be small. It is sufficient if at least a part has an upper narrowed diameter portion, and the second reduced diameter portion 363 does not have a taper and may be an elliptical diameter.
- the liquid inlet hole 420a is formed in the bubble generating section 4A.
- the water flowing into the liquid chamber 4 21 via the gas nozzle 4 is generated by the bubble expansion action in the divergent taper hole 4 22 by the jet air of the gas nozzle 4 10] 9.
- the mixture is converted into fine bubble mixed water and sent to the bubble stabilizing section 4B.
- the first bubble changing water pressure adjusting tank 4C passes through the first changing section 44, the second changing section 450, and the third changing section 460 according to the arrow F.
- the bubble-mixed water collides with each of the obstructing members and repeats the direction change, so that the mixed water is stirred and the bubble-bonding is prevented. It will be finely divided.
- the bubble-mixed water enters the inlet pipe 480 in the next pressure adjusting tank 4 C and is deflected, and pulsation is prevented in the first pressure adjusting chamber 490 to regulate the pressure. Since the air is gradually injected from the injection holes 492a, the bubbles are not coarsened.
- the pressure adjustment tank 4C helps prevent pulsation of bubbles and mixed water sent to the next process.
- OMFI Excess air accumulates in the upper part of the body 470], and the discharge hole 472a is discharged to the outside.
- mixed water having fine bubbles for example, 30 A
- the bubbles are maintained stably without disappearing for a long time, for example, about one hour.
- the bubble generating section 4A and the bubble stabilizing section 4B may have their axes oriented vertically.
- the upper side of the bubble stabilizing section 4B is connected to the center of the bottom wall 473 of the pressure adjusting tank 4C, and a baffle plate is provided above the vertical inlet pipe 480, and the inlet pipe 48 The fluid from 0 hits the baffle and is diverted horizontally and enters the first control room 490.
- FIG. 7 shows a cross section of another embodiment in which the inside of the vessel of the separation tank 1A is partitioned by a cylindrical partition plate 40 and divided into an inlet sewage zone 1 and an outlet purification zone 1b.
- a plurality of outlets 1 are inserted into a center of a sewage area 1a provided in the center of the casser body 1 and a plurality of outlets 1 in a water purification area 1b formed on the outer periphery of the partition plate 40.
- FIG. 8 is a partially cut-away side view of an embodiment of a separation tower having two main bodies 10 A and 10 B capable of treating a large amount of sewage. That is, the 1st minute 0A and the 2nd minute filament 10B are connected by the connecting pipe 10 bent in a Z shape, and the original port 10a is located downward at the center of the first separation ellipse 0A. ⁇ The opening 10b is opened in the upward direction of the center of the second separated fission 10B. The front end 10 b is covered with a cap-shaped wire mesh 62. According to the structure of this embodiment, when sewage is introduced from the inlet 11a provided in the lower corner, the sewage rises and becomes coarse when passing through the wire netting 61.
- the sewage is sent to the second separation tower 10B via the connecting pipe 10 and is again passed through the cap-shaped wire netting 62 so that the coarse-graining action is imparted thereto.
- Purified water is available at outlet 1 1.
- the filth coarsened by the golds 61 and 62 is given buoyancy and collected in reduced diameters ⁇ 20 and 20, and is pumped and discharged through elbow-shaped discharge pipes 30 and 30, respectively. It is done.
- the reduced diameter portions 2 and 20 may not be stepped as shown in FIG. Also, discharge pipe 3
- , 30 is a curved pipe that can prevent the upward flow of filth jets from blowing up in a straight line.
- the filth removal rate is about 9.9% or more (can produce fresh water from seawater), and the installation area is about 60%.
- Processing time is about 15 to 20 minutes] 3, and the running cost is about 1 / 3 ⁇ 4 of that of the conventional one.
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Abstract
Dispositif de traitement d'eau possédant un bassin de séparation (1A) possédant un orifice d'entrée et un orifice de sortie pour l'eau usée dans sa partie inférieure pour faire flotter et séparer les contaminants dans l'eau usée, un agglomérateur de contaminants (2A) servant à faire passer l'eau usée du bassin dans un agent d'agglomération inorganique, un agent alcalin et un agent d'agglomération macromoléculaire de manière séquentielle en partant du côté en amont vers le côté en aval d'un passage, un passage montant pour transporter l'eau usée de l'agglomérateur à la partie inférieure, et un passage descendant à la suite du passage montant, un tube (350) relié à la partie inférieure du passage montant et servant à guider une mousse fine mélangée à l'eau, un bassin de flottement et de sédimentation à pression (3A) possédant un réservoir de contaminants flottants au-dessus du passage montant, et un générateur de mousse mélangée avec de l'eau Ap relié au tube (350).Water treatment device having a separation tank (1A) having an inlet and an outlet for waste water in its lower part to float and separate the contaminants in the waste water, contaminants (2A) used to pass the used water from the basin through an inorganic agglomerating agent, an alkaline agent and a macromolecular agglomerating agent sequentially from the upstream side to the downstream side of a passage , an ascending passage for transporting the waste water from the agglomerator to the lower part, and a descending passage following the ascending passage, a tube (350) connected to the lower part of the ascending passage and serving to guide a fine foam mixed with water, a floating float and pressure sedimentation tank (3A) having a reservoir of floating contaminants above the rising passage, and a generator of foam mixed with water Ap re linked to the tube (350).
Description
明 細 Details
発明の名称 Title of invention
水処理装置 Water treatment equipment
技術分野 Technical field
5 本発明は、 汚物、 例えば油、 B 0 D、 C O D . S S や溶融物 ( 塩分 , 色素等 ) が含ま れた汚水の水処理装 置の改良に 関する。 5 The present invention relates to an improvement in a water treatment apparatus for sewage containing filth, for example, oil, BOD, COD.SS, and a melt (salt, pigment, etc.).
背景技術 Background art
従来の水処理装置では、 例えば 、 分離糟で汚物その 10 も のの浮力及び沈澱力を利用 して、 付着、 沈澱、 浮上 な どさせて分離 していた。 従って処理能力が非常に悪 く 、 汚泥除去率がせぃぜぃ 9 0 %程度に しカ 達 しなカ つだので、 清浄水と はいって も 水で う すめてか ら放流 しな ければな ら なかった。 ま た、 活性汚泥方式に よ る 15 装置ではその据付に非常に広い土地を要 してお ]? ( 例 えば、 処理水 2,000 tz の場合、 約 6 6 0 w2の土地を 要 していた ) ラ ン ニ ン グ コ ス ト も 非常に高かった。 ま えこの方式の場合、 処理時間は約 2 4 時間を要 し、 残In a conventional water treatment apparatus, for example, the separation, separation, and the like are performed by utilizing the buoyancy and sedimentation power of the filth itself, such as adhesion, sedimentation, and floating. Therefore, the treatment capacity is very poor, and the sludge removal rate is at most about 90%, so it is difficult to reach.Therefore, even if it is clean water, it must be diluted with water and then discharged. did not become. Also, in the by that 15 devices in the activated sludge system and required a very wide land to the installation you]? (For example, if the treated water 2,000 tz, had been required of about 6 6 0 w 2 land The running cost was also very high. Before using this method, the processing time was about 24 hours, and the remaining
■ . ■.
溜汚泥が蓄積するため、 1 年に 1 〜 2 回装置の稼動を 20 停めて掃除をする必要があった。 Due to the accumulation of accumulated sludge, it was necessary to stop the operation of the equipment once or twice a year for 20 cleaning.
¾ 発明の開示 の Disclosure of the invention
本発明は上記欠点を改良 し、 浄水能力が高 く 、 構造 が コ ン パ ク 卜 で狭い据付面積で足 p ラ ン ニ ン ク' コ ス ト の低い水処理装置を提供する こ と を 目 的 とする。 An object of the present invention is to improve the above drawbacks and to provide a water treatment apparatus having a high water purification capacity, a compact structure, a small installation area, and a low cost of footprint. Target.
OMPI - 本発明は下部に汚水の入口 お よ び出 口 を有 し汚水中 の汚物を浮上分離させる分離糟 と 、 該分離櫓か ら の汚 物を通過させる と 共にその流路の上流側か ら 下流側へ 順に無機凝集剤、 ア ル カ リ 剤及び高分子凝集剤が注入 さ れる よ う に した汚物凝集装置 と 、 該汚物凝集装置か らの汚水が下部に導人される 上向 き 流 と 、 これに続 く 下向 き 流路 と を有 し、 前記上向 き 流路の 下部に微細 気泡混合水導入管が接続さ れ、 かつ、 §0記上向流路の 上方 に浮上汚物の溜 ] 部を持つ加圧浮上沈截槽 と 、 前 記微細気泡混合'水導入管に接続された気泡混合水発生 機と を含む こ と を特徵 と する 水処理装置で る。 OMPI -The present invention provides a separation tank having a sewage inlet and an outlet at a lower portion to float and separate sewage in the sewage, and allows the sewage from the separation tower to pass therethrough and from the upstream side of the flow path. A waste coagulation device in which an inorganic coagulant, an alkaline agent, and a polymer coagulant are sequentially injected to a downstream side, and an upward flow in which wastewater from the waste coagulation device is guided to a lower portion. And a downward flow path following the flow path, a fine bubble mixed water introduction pipe is connected to a lower part of the upward flow path, and a floating waste above the upward flow path described in §0. A water treatment apparatus characterized by including a pressurized flotation / sedimentation tank having a reservoir section, and a bubble mixed water generator connected to the fine bubble mixing / water introduction pipe.
従って、 汚物除去率が格段に 向上 し、 従つて処理水 は水質規制値 ¾下に な るの で、 稀 しや く せずに放流で き る こ と と なつた。 ま た装置据付に要する 面積は最少 限と な 、 ラ ン ニ ン ク' コ ス ト も 大幅に低下 した。 その う え本発明 では汚水は潇動 しな が ら処 Sさ れる ので、 処理時間 も 格段に短縮され、 しか も 装置内 に沈癜汚泥 が殆ん ど残る こ と が な い。 Therefore, the filth removal rate has been significantly improved, and the treated water has fallen below the water quality regulation value ¾, so that it can be discharged without being rarely diluted. In addition, the area required for installation of the equipment was minimized, and the cost of Rankin 'was significantly reduced. Therefore, in the present invention, the wastewater is treated while being moved, so that the treatment time is remarkably reduced, and almost no sludge sludge remains in the apparatus.
図面の簡単な 説明 Brief description of the drawings
第 1 図は本発明の一実施例を示す系統図、 第 2 図は 分離稽の切欠正面図、 第 3 図はその側面図、 第 4.図は 加圧浮上沈澱不 1の縦断面図、 第 5 図は気泡混合流体発 生機の縦断面図、 第 6 図は第 5 図の Vi - M端面図、 第 FIG. 1 is a system diagram showing one embodiment of the present invention, FIG. 2 is a cutaway front view of a detached louver, FIG. 3 is a side view thereof, FIG. Fig. 5 is a vertical cross-sectional view of the bubble mixed fluid generator, Fig. 6 is a Vi-M end view of Fig. 5,
7 図は分離樗本体の他の実施例を示す横断面図、 第 8 図は更に他の実施例を示す切欠正面 図 で あ る。 FIG. 7 is a cross-sectional view showing another embodiment of the separated fission body. The figure is a cutaway front view showing still another embodiment.
発明を実 施する ための最良の形態 BEST MODE FOR CARRYING OUT THE INVENTION
以下本発明 を よ D 詳細に 説述する ため に添付図面 に 従って説明する。 Hereinafter, the present invention will be described in more detail with reference to the accompanying drawings.
本発明は第 1 図示の如 く 分離櫓 1 A と 、 油分凝集装 置 2 A と 、 加圧浮上沈澱櫓 3 A と 、 該加圧浮上沈澱糟 への気泡混合水を発生圧送す る気泡混合液体発生機 A As shown in FIG. 1, the present invention provides a separation tower 1A, an oil aggregating apparatus 2A, a pressurized floating sedimentation tower 3A, and a bubble mixing apparatus for generating and feeding bubble mixed water to the pressurized floating settling tank. Liquid generator A
P と を組合せて な る 。 Combine P and.
しか して 、 分離糟 1 Aは第 2 図 およ び第 3 図 に示す 如 く 、 底壁 1 1 に汚水入口 1 1 a , 浄水出口 1 1 b を 有する 有底角筒か ら な る容器状糟本体 1 と 、 前記樗本 体 1 の上側 を湲 ぅ カ バ — 2 と 、 該カ バ — 2 の上端に接 続さ れた汚物排出用の エ ル ボ 3 と 、 前記入口 1 1 a と 出 口 1 1 b と の 間に設け ら れ、 かつ、 本体 1 の 下部を 入口側汚水上昇域 1 a と 出 口側浄水下降域 1 b ( 第 2 図 ) と に仕切る 仕切板 と 、 支持部材 5 に よ J9 支持さ れる汚物粗粒化部材 6 と 、 汚物蓄積量.検知部 7 と 、 洗 滌用空気管 8 と 、 ド レ - ン 抜管 9 と 'を 有する。 そ し て 本体 1 の 上部 よ ] 上方 の部分が浮上汚物溜 ]? 部 S と な る。 However, as shown in FIGS. 2 and 3, the separation vessel 1A is a container having a bottomed rectangular tube having a sewage inlet 11a and a purified water outlet 11b on the bottom wall 11. The body 1 of the container, the cover 2 on the upper side of the body 1, the elbow 3 for discharging waste connected to the upper end of the cover 2, and the inlet 11a. And a support plate provided between the outlet 1 1b and the lower part of the main body 1 for dividing the lower part of the main body 1 into an inlet-side sewage rise area 1a and an outlet-side purified water descending area 1b (FIG. 2). It has a filth coarse-graining member 6 supported by the member 5 J9, a filth accumulation amount detection unit 7, a cleaning air pipe 8, and a drain pipe 9. The upper part of the main body 1] is the floating waste reservoir.
しか して、 前記 カ バ ー 2 は実施例に よ る と 、 段階的 に積重さ れた 2 つの縮径部 2 a , 2 b が形成さ れる。 即 ち、 第 1 縮径部 2 a は左右側壁が上 向小径 と な る よ ぅ 縮径さ れ、 上壁は液体の 上向流路に対 し、 その流動 However, according to the embodiment, the cover 2 is formed with two reduced diameter portions 2a and 2b that are stacked in a stepwise manner. That is, the first reduced diameter portion 2a is reduced in diameter so that the left and right side walls have an upward small diameter.
OMPI を阻止する 水平段部 2 1 と される。 そ して、 該上壁の 中央に、 側壁が直円筒をな し、 上壁が前記 と 同様の水 平段部 2 2 と された第 2 縮怪部 2 b が接銃'される。 更 に、 該第 2 縮径部 2 b の水平段部 2 2 の中央には径違 いエ ル ボ 3 の大怪部が連結される 。 該ェル ポ の小径部 には図示外の間欠開閉される電磁弁を備えた汚物排送 管が接銃されている。 前記仕切板 4 の上端部よ ]? 下方 位置には支持部材 5 が水平に設け られ、 該支持部材 5 に複数枚の金 H'を重ね合わせた污 ¾粗粒化部材 6 ( 汚 水域 1 a 側が S a , 浄水域 1 b 側が 6 b ) が載置固定 される。 OMPI The horizontal step part 2 1 that prevents Then, in the center of the upper wall, a second shrinkable portion 2b having a side wall having a right cylindrical shape and a horizontal step portion 22 similar to that described above is attached with a gun. Furthermore, a large part of the elbow 3 having a different diameter is connected to the center of the horizontal step part 22 of the second reduced diameter part 2b. A waste pipe provided with a solenoid valve which is intermittently opened and closed, not shown, is attached to the small diameter portion of the elpo. A support member 5 is provided horizontally below the upper end of the partition plate 4 and a plurality of golds H ′ are superimposed on the support member 5. The coarse-grained member 6 (dirty water area 1 a The side is Sa and the water purification area 1b side is 6b).
汚 蓄積量検知部 7 は電極 7 a を利用 した第 1 油量 検出.器 7 1 と第 2 油量検出器 7 2 とか ら な ]? 、 第 1 縮 径部 2 a の後壁と櫓本体 1 の上部後壁 と に突設されて いる。 洗滌用空気管 8 は櫓本体 1 の底部に左右一対設 け られ、 両端が閉止さ 、 上面に多数の空気噴出孔 8 1 a を有 して水平に と つけ られた U字状管 8 1 に接 続部材 8 2 を介 して空気が送入される。 ド レ ン抜管 The dirt accumulation amount detector 7 is composed of the first oil amount detector 7 1 and the second oil amount detector 72 using the electrode 7 a], the rear wall of the first reduced diameter portion 2 a and the tower body. It is protruding from the upper rear wall of and 1. A pair of left and right cleaning air pipes 8 are provided at the bottom of the tower body 1 and closed at both ends to form a U-shaped pipe 81 with a large number of air ejection holes 81a and attached horizontally. Air is supplied via the connecting member 82. Drain extubation
9 は前記仕切板 4 を挾む両側底壁 1 1 に左右一対設け られる。 A pair of right and left 9 is provided on both bottom walls 11 sandwiching the partition plate 4.
な お、 図中 1 0 a は底壁 1 1 の対^線位置 2 '個所に 設け られた脚、 1 0 b は分離槽か ら突設された動振止 部材、 3 1 は 自動排気弁取付座であ る。 In the figure, 10a is a leg provided at the position 2 'of the bottom wall 11 in the pair line, 10b is a vibration damping member projecting from the separation tank, and 31 is an automatic exhaust valve. Mounting seat.
次に、 第 1 図 において、 油分凝集装置 2 Aは、 無機 Next, in FIG. 1, the oil aggregating device 2 A
ΟΗΡΙ 凝集剤混合器 2 1 1 、 ア ル 力 リ 剤混合器 2 1 2 お よ び 高分子凝集剤混合器 2 1 3 が並設さ れた混合装置 2 1 0 と 、 無機凝集剤ポ ン プ 2 2 1 , ア ル カ リ 剤ポ ン プ 2 2 2 お よ び高分子凝集剤ポ ン プ 2 2 3 と 、 無機凝集剤 タ ン ク 2 3 1 , ア ル 力 リ 剤タ ン ク 2 3 2 お よ び高分子 凝集剤タ ン ク 2 3 3 が収容さ れた薬品糟 2 3 0 と ;^ ら な る 。 前記各混合器は分離樗か ら送 ら れ、 ま だ油分の 残留する液体の流路に従っ て上流側か ら 下流側へ無機 凝集剤混合器 2 1 1 , ア ル カ リ 剤混合 器 2 1 2 、 高分 子凝集剤混合器 2 1 3 の順に直列に接続さ れる。 液体 は これ ら各混合 器内 を長さ 方 向 に 沿っ て進むが、 各混 合器内 に は図示省略 したが多数の邪魔板が 前記液体の 進行方向 に直角 に設け られ、 ジ グザ グ流路を形成 して い る。 各混合器の流体入口 側に は夫 々 、 前記各種タ ン ク 2 3 1 , 2 3 2 , 2 3 3 よ ポ ン プ 2 2 1 , 2 2 2 2 2 3 を経て送給さ れる無機凝集 剤 , ア ル 力 リ 剤 , 高 分子凝集 剤の送給管 2 4 1 , 2 4 2 , 2 4 3 が接続開 口さ れてい る。 な お図示の 2 !^は分離櫓 1 Aか ら 混合 装置 2 1 0 への液体供給管、 2 P2は次工程への給送管で あ る。 ΟΗΡΙ A mixing device 2 10 in which a coagulant mixer 2 11, an aluminum coagulant mixer 2 12 and a polymer coagulant mixer 2 13 are provided side by side, and an inorganic coagulant pump 2 2 1, Alkali agent pump 2 2 2 and polymer flocculant pump 2 23, inorganic flocculant tank 2 3 1, Alkali agent tank 2 3 2 And a chemical tank 230 containing a polymer flocculant tank 2 33; Each of the mixers is sent from the separation filter, and flows from the upstream side to the downstream side according to the flow path of the liquid in which the oil remains, and the inorganic flocculant mixer 211 and the alkaline agent mixer 2 12 and the polymer flocculant mixer 2 13 are connected in series. The liquid proceeds in each of these mixers along the length direction. In each of the mixers, a number of baffles (not shown) are provided at right angles to the direction of travel of the liquid, and zigzag. A flow path is being formed. At the fluid inlet side of each mixer, inorganic coagulation fed through pumps 22 1, 22 22 and 23 from the various tanks 23 1, 23 32 and 23 33 respectively The supply pipes 241, 242, and 243 of the agent, alloy agent, and high molecular coagulant are connected and opened. The 2 shown! ^ The liquid supply line to the separation tower 1 A or al mixing device 2 1 0, 2 P 2 is Ru Ah in the feed tube to the next step.
こ こ で、 無機凝集剤 と し ては例えば、 ボ リ 塩化 ア ル ミ が用い られ、 ア ル カ リ 剤は苛性 ソ ー ダ な どが用い ら れる。 ま え高分子凝集剤 と してはア ク リ ル 系 ポ リ マ 主体の商品名 ァ ロ ン フ 'ロ ッ ク A — 1 0.1 ( 東亜合成化 学株式会社 ( 東京都 ) 製 ) , ポ リ ア ク リ ルア ミ ド 系の も の な どの有機剤が適当である。 Here, for example, aluminum chloride is used as the inorganic flocculant, and caustic soda is used as the alkaline agent. As a polymer flocculant, Acryl Lock A — 1 0.1 (trade name) mainly composed of acrylic polymer Organic agents such as Gaku Co., Ltd. (Tokyo) and polyacrylamide are suitable.
また、 加圧浮上沈澱糟 3 Aは、 第 4 図に示す如 く 外 形が鉛直円筒状を なす第 1 筒 3 1 0 、 第 2 筒 3 2 0 、 第 3 筒 3 3 0 、 第 4 筒 3 4 0 と 、 前記第 1 筒 3 1 0 へ 連結された気泡混合水導入管 3 5 0 と、 前記第 2 筒 3 As shown in Fig. 4, the pressurized floating sedimentation tank 3A is composed of a first cylinder 310, a second cylinder 320, a third cylinder 330, and a fourth cylinder whose outer shapes are vertical cylinders. 340, a bubble mixed water introduction pipe 350 connected to the first cylinder 310, and the second cylinder 3
2 0 の上部に接続された汚物導出管 3 6 0 、 下部に接 続された沈證输排出管 3 7 0 とを有 3 る o O There is a waste discharge pipe 360 connected to the upper part and a sediment discharge pipe 370 connected to the lower part.
第 1 筒 3 1 0 は有底の円筒状を な し、 底壁に污水入 口 3 1 1 と な る汚水供給管が接続され、 ま た下部側壁 には上向開口する気泡混合水導入管 3 5 0 が貫通され ている。 第 1 筒 3 1 0 の頂部は開放された汚水出口 3 1 2. と な る。 第 2 筒 3 2 0 は前記第 1 筒 3 1 0 に対 し て同心に、 隙間ピー ス 3 2 0 a を介 して外被され 上 下端が開放されて夫々 、 浮遊汚物出□ 3 2 1 , 流体出 口 3 2 2 と なってい る ま た、 第 2 筒 3 2 0 はその下 部が前記第 1 筒 と同心に配置され、 上部は前記第 1 筒 3 1 0 の上方において段 3 2 3 a を介 して大径部 3 2 3 と され、 前記浮遊物出口 3 2 1 の上端には汚物導出 管 3 6 0 が接続される。 The first cylinder 310 has a cylindrical shape with a bottom, a sewage supply pipe serving as the water inlet 311 is connected to the bottom wall, and a bubble-mixed water introduction pipe opening upward on the lower side wall. 350 is penetrated. The top of the first cylinder 310 is an open wastewater outlet 312.2. The second cylinder 320 is concentrically arranged with respect to the first cylinder 310 via a gap piece 320a, and the upper and lower ends thereof are opened. The second cylinder 320 has a lower portion disposed concentrically with the first cylinder, and an upper portion has a step 32 above the first cylinder 310. A large-diameter portion 3 23 is formed through 3 a, and a waste discharge pipe 360 is connected to the upper end of the floating material outlet 3 21.
第 3 筒 3 3 0 は前記第 2 筒に対 し同心に間隔を残 し て外被され、 その上端の流体出口 3 3 1 は前記大径部 The third cylinder 330 is sheathed concentrically with respect to the second cylinder with a space therebetween, and the fluid outlet 331, at the upper end thereof, is provided with the large-diameter portion.
3 2 3 の周壁下方に位置する。 該出口 3 3 1 の下部に は、 第 3 筒の上端か ら外方へ フ ラ ン ジ 3 3 2 が設け ら 一, O れる。 第 3 筒 3 3 0 の底壁 3 3 3 中央に 前記第 1 筒 3 1 0 が莨通 さ れる。 第 3 筒 3 3 0 の下部は汚物沈澱室 3 3 0 a と さ れ、 その底壁 3 3 3 に汚物出 口 3 3 3 b を開口 さ れた 開閉弁付の沈澱物排出管 3 7 0 が接続さ れる。 It is located below the peripheral wall of 3 2 3. At the lower part of the outlet 331, a flange 332 is provided outward from the upper end of the third cylinder. It is. The first cylinder 310 is passed through the center of the bottom wall 33 33 of the third cylinder 330. The lower part of the third cylinder 330 is a waste sedimentation chamber 330a, and a sediment discharge pipe 370 with an on-off valve with a waste outlet 333b opened in the bottom wall 333. Is connected.
更に、 第 3 筒 3 3 0 に対 し同心に間隔を残 して第 4 筒 3 4 0 が外被さ れる 。 第 4 筒 3 4 0 の側壁 3 4 1 , 頂壁 3 4 2 , 底壁 3 4 3 は、 加圧浮上污澱櫓体 3 丄の 外側壁を 兼ね る。 第 4 筒 3 4 0 内の 下半部に は、 受合 4 4 上 に活性炭等の ' 過層 3 4 0 a が設け られてい る( そ して、 その 下方 には下面 に多数の細孔を 有する 環状 の集水管 3 8 0 を 経て清浄水導出管 3 8 1 が接続さ れ る。 お、 3 8 2 は 前記集水管 3 8 0 の他方側に接続 された逆洗用水供給管、 3 8 3 は第 4 筒頂壁 3 4 2 に 設け られた逆洗用水排出管で あ る。 Further, the fourth cylinder 340 is covered with the third cylinder 340 left concentrically with respect to the third cylinder 340. The side wall 341, top wall 342, and bottom wall 343 of the fourth cylinder 340 also serve as the outer side wall of the pressurized floating tower 3. In the lower half of the fourth cylinder 340, an upper layer 340a of activated carbon or the like is provided on the receiving member 440 (below it, a large number of pores are provided on the lower surface below). The clean water outlet pipe 38 1 is connected via an annular water collecting pipe 38 0 having the following structure: 38 2 is a back washing water supply pipe connected to the other side of the water collecting pipe 38 0, 3 Reference numeral 83 denotes a backwash water discharge pipe provided on the top wall 34 of the fourth cylinder.
汚物導出管 3 6 0 は. §記第 2 筒 3 2 0 の 上端に接続 さ れて、 加圧浮上沈澱糟本体 3 工の頂部に固定さ れる。 そ して 下か ら上へ順に第 2 筒 上端 と 同 径の直円 筒部 3 6 1 , 上狭縮径さ れた円錐第 1 縮怪部 3 6 2 及び怪違 いヱル ポ状の第 2 縮径部 3 6 3 か ら な る 。 第 2 縮怪部 3 6 3 の先端には間欠 自 動開 閉さ れる 電磁弁 ( 図示省 略 ) が接続さ れ、 前記汚物導出管 3 6 0 内 に溜った汚 物を間欠的に排出する 禱造 と な ってい る。 The waste discharge pipe 360 is connected to the upper end of the second cylinder 320 and fixed to the top of the main body of the pressurized floating sedimentation tank. Then, in order from bottom to top, a right circular cylindrical part 361, which has the same diameter as the upper end of the second cylinder, a conical first constricted part 362, whose upper part has a reduced diameter, and a mysterious lipo-shaped part 2 Consists of a reduced diameter section 3 6 3. A solenoid valve (not shown), which is automatically opened and closed intermittently, is connected to the tip of the second shrinking part 363, and discharges the waste collected in the waste discharge pipe 360 intermittently. It is structured.
汚物導出 '管 3 6 0 の下部円 筒部 3 6 - 1 の側方 には上 o 下に第 1 第 2 油検出器 3 9 0 a , 3 9 0 b が設け られ てい る。 Discharge of waste '' The upper part beside the lower cylindrical part 36-1 of the pipe 360 The first and second oil detectors 390a and 390b are provided below.
- 更に、 第 5 図およ び第 6 図において、 気泡混合液体 発生機 Apは互いに同心の気体 ( 空気 ノ ズ ル 4 1 0 , 液体 ( 水 ) ノ ズ ル 4 2 0 を有する気泡発生部 4 A と 、 内部に気泡混合水の第 1 変向部 4 4 0 、 第 2 変向部 4 5 -0 , 第 3 変向部 4 6 0 が形成された気泡安定部 4 B と、 内部に変向導入管 4 8 0 、 第 1 圧力詢整室 4 9 0 を備えた気泡混合水圧力調整タ ン ク 4 C とか ら な る。 -Further, in Figs. 5 and 6, the bubble-mixed liquid generator Ap is composed of gas bubbles (air nozzles 410, liquid (water) nozzles 420) having concentric gas (air nozzles 410). A and a bubble stabilizing section 4B in which a first diverting section 44, a second diverting section 45-0, and a third diverting section 460 are formed inside the bubble-mixed water. It is composed of an air introduction pipe 480 and a bubble mixed water pressure adjusting tank 4C having a first pressure checking chamber 490.
気泡発生部 4 A において、 気体ノ ズ ル 4 1 0 は気体 噴出方向を水平と され、 先端外周に液体ノ ズ ル 4 2 0 が螺合される雄ね じ 4 1 1 a が、 中心部に先細テ -パ を有する段付空気室 4 1 1 b が形成された基部 4 1 1 と、 前記空気室 4 1 1 b に違結する中 間孔 4 1 2 a お よ びそれに続 く 未広テ ーパ噴出口 4 1 2 b が設け られ た先部 4 1 2 とカゝ らな .る。 液体ノ ズル 4 2 0 は中心線 に沿って長い円筒状をな し、 基部に水導入孔 4 2 0 a を備え、 前記気体ノ ズ ル先部 4 1 2 の外周に形成され It記水導入孔 4 2 0 a と違通する液体室 4 2 1 と、 該 液体室 4 2 1 か ら前記噴出口 4 1 2 b の中心線と 同心 に穿設された未広テ パ孔 4 2 2 と を有 し、 前記噴出 口 4 1 2 b の周囲か ら液体が噴出口 4 1 2 b の直前に 向って、 該噴出口の中心線上に合流する よ う 形成され ている。 流体ノ ズ ル 4 2 0 の基部には前記気体ノ ズル g I 。 1 0 の雄ね じ 4 1 1 a と 螺合す る 雌ね じ 4 2 0 a が 設け られる。 4 工はパ ッ キ ン で あ る 。 In the bubble generating section 4A, the gas nozzle 410 has a horizontal gas ejection direction, and a male screw 411a into which the liquid nozzle 420 is screwed on the outer periphery of the tip is located at the center. A base portion 411 formed with a stepped air chamber 4 1 1b having a tapered taper, and an intermediate hole 4 1 2a connected to the air chamber 4 1 1b, and an unopened space following it. It is the same as the tip part 4 12 provided with the taper outlet 4 12 b. The liquid nozzle 420 has a long cylindrical shape along the center line, and has a water inlet hole 420a at the base. A liquid chamber 4 2 1 which communicates with the hole 4 2 0 a, and a non-wide tapered hole 4 2 2 formed from the liquid chamber 4 2 1 and concentric with the center line of the jet port 4 12 b. The liquid is formed such that the liquid flows from around the ejection port 412b toward the position immediately before the ejection port 412b and joins on the center line of the ejection port. At the base of the fluid nozzle 420 is the gas nozzle g I. A female screw 42 0a to be screwed with the 10 male screw 4 11a is provided. The four workers are packing.
前記気泡発生部 4 A は噴出口 4 1 2 b の テ - パ角 度 を な 、 末広 テ ー パ 孔 4 2 2 の テ ー ノヽ0角 度^、前記噴出 口 The bubble generating section 4A has a taper angle of the ejection port 4 12b, and a ヽ0 angle of the Suehiro taper hole 4 22.
1 2 b の ^周延長面 と 末広テ — パ 孔 4 2 2 の!^周面 と の仮想交点を P と し、 ま た、 液体室 4 2 1 か ら末広 テ - パ孔 4 2 2 へ の移行角 部を Q と した場合に 、 該移 行角部 Q力 ら液体ノ ズ ル 4 2 0 の先端ま での長さ を L、 前記仮想交点 P ま での距離を ^ i、気体 ノ ズ ル 4 1 0 の 先端ま で の距離を と し、 更に 、 前記気体 ノ ズ ル 4 1 0 の先端か ら 水導入孔 4 2 0 a の 中 心線ま での距離を 1 2 b ^ perimeter extension surface and Suehiro Te-hole 4 2 2! ^ Let P be the virtual intersection with the peripheral surface and Q be the transition angle from the liquid chamber 42 1 to the Suehiro taper hole 42 2, Let L be the length up to the tip of the liquid nozzle 420, ^ i be the distance up to the virtual intersection P, and L be the distance up to the tip of the gas nozzle 410. The distance from the tip of the nozzle 410 to the center line of the water inlet hole 420a
3と する と 、 これ ら の 間に は次 の関係式が成立する よ う 形成さ れる。 If it is 3, the following relational expression is formed between them.
1°≤ α ≤ 3 0 ° 1 ° ≤ α ≤ 30 °
1°≤ ^ ≤ 3 0° 1 ° ≤ ^ ≤30 °
a > β a> β
0 < £λ< L 0 <£ λ <L
> o > o
£5> o £ 5 > o
な お、 前記移行角部 Qは流体が層流 と な る よ う に滑 ら かな 面取 ]? 部と さ れる。 The transition corner Q is a smooth bevel so that the fluid becomes laminar.
さ て こ こ で、 1°≤ α ≤ 30° と したため 、 空気 ノ ズ ル Here, since 1 ° ≤ α ≤ 30 °, the air nozzle
4 1 0 か ら の噴射空気流は液体ノ ズ ル 4 2 0 の末広 テ The jet air flow from 410 is a suehiro te
- パ孔 4 2 2 の 内壁面 に衝突 して旋回流 を起 こ し、 加 -Collision with the inner wall of the hole 4 2 2 generates a swirling flow,
O PI ' 圧下において水と の攪拌に よ ]9 空気は水中に加圧溶融 O PI ' Mixing with water under pressure] 9 Air melts in water under pressure
する。 し力 A して、 α の値カミ 1 ° よ も小さい場合、 空気 噴流は孔 4 2 2 の内壁に衝突せず該孔 4 2 2 を突き 抜 I do. When the force A is smaller than the value of α by 1 °, the air jet does not collide with the inner wall of the hole 422 and penetrates the hole 422.
ける こ と と な ]? 、 3 0° よ ]? 大き い と α に関係 く 拡散 It's 30 °, right?]?
せず、 中間孔 4 1 2 a の直径と略同 じ直径の流れにな るおそれ力 ¾>る。 Without this, there is a risk that the flow will be approximately the same as the diameter of the intermediate hole 4 1 2a.
ま た、 1° < ≤ 30° については、 ^ の値が 1°よ ]? 小 Also, for 1 ° <≤ 30 °, the value of ^ is 1 °]?
さ く ても 、 ま た、 30° よ ]9 大き く て も 微粒気泡の発生 Even if it is large, it is 30 degrees.
が非常に少 く な る。 Is very low.
a > と されたこ と は末広テ ー パ孔 4 2 2 の内壁に 末広テー パ噴出孔 4 1 2 b よ ]) の噴射空気が衝突 して 気泡を勃果的に発生させる。 This means that the blast air from the Suehiro taper orifice 4 12 b) collides against the inner wall of the Suehiro taper hole 4 22], and bubbles are generated erectly.
更に、 0 ≤ < Lの条件では末広テ ー パ孔 4 2 2 内 で流体が右ま たは左回 に旋回 しつつ流動するので、 こ の と き 水と空気と は攪拌されて、 空気が水中に溶融 Further, under the condition of 0 ≤ <L, the fluid flows while turning clockwise or counterclockwise in the divergent taper hole 422, and at this time, the water and the air are stirred, and the air is stirred. Melting in water
される こ と と な る。 従って、 孔 4 2 2 の入口において Will be done. Therefore, at the entrance of hole 4 2 2
流体の麿流が形成される。 A flow of fluid is formed.
次の 0 0 の条件も流体の層流形成に役 立ち 、 液体が液体室 4 2 1 内に充満 して噴出口 4 1 2 b の周囲力ゝ ら孔 4 2 2への平均 した水流が得 られる。 The following condition of 0 also contributes to the formation of a laminar flow of the fluid, and the liquid fills the liquid chamber 4 21 to obtain an average water flow to the hole 4 22 from the peripheral force of the ejection port 4 12 b. Can be
泡安定部 4 B は前記気泡発生部 4 A の末広テ -パ The bubble stabilizing section 4B is a Suehiro tape of the bubble generating section 4A.
孔 4 2 2 に連通 した外筒 4 3 0 と、 該外筒の内側に設 け られて、 前記末広テ -パ孔 4 2 2 か らの気泡混合水 の流入方向に対 し直角に流動方向を変更させる よ う な An outer cylinder 430 communicating with the hole 4222, and a flow direction perpendicular to the inflow direction of the bubble-mixed water from the divergent taper hole 422 provided inside the outer cylinder. To change
O PI O PI
W丄 ITリ Κ 第 1 変更部 4 4 0 、 第 2 変更部 4 5 0 、 第 3 変更 ¾ 4 6 0 力 ら な る 邪魔部材 と か ら な る。 W 丄 IT Κ The first change portion 440, the second change portion 450, and the third change ¾460 are composed of strong obstruction members.
即ち 、 気泡安定部 4 B において、 外筒 4 3 0 は水平 軸線を有 し、 流体流入方 向に沿 う 側壁 4 3 1 と 、 該側 壁 4 3 1 の流体流入側 に設け ら れた端壁 4 3 2 と か ら な J? 、 端壁 4 3 2 にはその中 心に液体の第 1 流入孔 4 3 2 a が設け られる。 第 1 変向部 4 4 0 は外筒 4 3 0 内上流側に おい て、 前記液体流入孔 4 3 2 a に対向す る 円形板状の横 ( 流体の流入方 向 に 対 し直角 を な す方 向 ) 部材 4 4 1 と 、 該横板材 4 4 1 の外縁の複数個所 に接 し、 該横部材 4 4 1 ¾ 前記端壁 4 3 2 に結着させ る 板状の縦 ( 流体の流入方 向 に 沿 う 方 向 ) 部材 4 4 2 と か ら な ]? 、 縦部材 4 4 2 と 端壁 4 3 2 と の 前記縦部 材 4 4 2 を除 く 隙間部分は液体の第 1 変向流路 と さ れ ている ( 第 6 図 ) 。 That is, in the bubble stabilizing section 4B, the outer cylinder 430 has a horizontal axis and has a side wall 431 along the fluid inflow direction, and an end provided on the fluid inflow side of the side wall 431. J from wall 4 3 2 The end wall 432 is provided with a first inflow hole 432a for liquid at the center thereof. The first diverting portion 4440 is located on the inner upstream side of the outer cylinder 4330 and has a circular plate-like side (which is perpendicular to the fluid inflow direction) facing the liquid inlet hole 432a. A plate-like vertical member (fluid of fluid) that is in contact with a member 441 and a plurality of portions of the outer edge of the horizontal plate member 441 and is bonded to the horizontal member 441 ¾ the end wall 432. In the direction along the inflow direction), the gap between the vertical member 4 42 and the end wall 4 32 between the vertical member 4 42 and the end member 4 42 is the first liquid. It is a turning channel (Fig. 6).
第 2 変更部 4 5 0 は外筒 4 3 0 の 中 間部に設け られ 前記外筒側壁 4 3 1 に沿 う-円筒状の縦部材 4 5 1 と 、 該縦部材 4 5 1 の上'流側端を外筒側壁に結合 させる第 1 横部材 4 5 2 と 、 前記縦部材 4 5 1 の 下流側端を 閉 塞する第 2 横部材 4 5 3 と か ら な る。 そ して、 前記縦 部材 4 5 1 には 周囲に苐 2 変向流路たる 多数の横方 向 孔 4 5 1 a が設け られ、 第 1 掼部材 4 5 2 にはその中 央に縦部材が密接内嵌さ れる 第 2 流入孔 4 5 2 a が開 口 されている 。 前記第 2 変向孔 4 5 1 a は前 記縦部材 4 5 1 の同一円 周上 4 個が等間隔かつ、 縦方向等間隔 に設け られてい ο The second changing portion 450 is provided at a middle portion of the outer cylinder 43 0, along the outer cylinder side wall 43 1 -a cylindrical vertical member 45 1, and an upper portion of the vertical member 45 1 The first horizontal member 452 connects the downstream end to the outer cylinder side wall, and the second horizontal member 453 closes the downstream end of the vertical member 451. The vertical member 45 1 is provided with a large number of horizontal holes 45 1 a, which are 変 2 diverting flow paths, in the periphery thereof, and the first vertical member 45 2 has a vertical member in the center thereof. The second inflow hole 452a into which the is closely fitted is opened. The second diverting hole 4 51 a is the vertical member 4 5 1 on the same circumference are provided at equal intervals and at equal intervals in the vertical direction ο
第 3 変向部 4 6 0 は外筒 4 3 0 内下流側において該 外筒内を仕切る第 1 横部材 4 6 1 2 横部材 4 6 2 と、 これら両横部材を連結する複数の扳状縦部材 4 6 3 と、 更に、 該縦部材 4 6 3 の中間に支持された 形 板状の第 3 横部材 4 6 4 とか ら な る そ して 、 前記第 1 積部材 4 6 1 にはその中心に第 5 m入孔 4 6 1 a が ま た、 第 2 横部材 4 6 2 の中心に液阵流出孔 4 6 2 a が設け られる。 前記第 3 横部材 4 6 4 の前後において 前記縦部材 4 6 4 を除 く 部分は第 3 変 R3流路と される 気泡混合水圧力調整タ ン ク 4 Cは、 下部に気泡混合 水出口 4 7 0 a ¾備えた鉛直軸線を も つ円筒形側壁 4 7 1 と弁付空気排出孔 4 7 2 a を有する頂壁 4 7 2 と 底壁 4 7 3 とか ら な る第 2 圧力調 たるタ ン ク本体 4 7 0 と、 その内部に設け られた前記気泡安定部 4 B か ら送入される気泡混合水を 受入れる導入管 4 8 0 と 更に、 該導入管 4 8 0 の下流部を aつた第 1 圧力調整 室 4 9 0 と を備えている。 The third turning part 460 is a first horizontal member 461 2 that partitions the inside of the outer cylinder on the inner and downstream side of the outer cylinder 430, and a plurality of ridges connecting these two horizontal members. The vertical member 463 and a plate-shaped third horizontal member 464 supported in the middle of the vertical member 463, and the first stacking member 461 At the center thereof, a 5 m inlet hole 461 a is provided, and at the center of the second horizontal member 462, a liquid outlet hole 462 a is provided. A portion other than the vertical member 464 before and after the third horizontal member 464 is a third variable R3 flow passage.The bubble mixed water pressure adjustment tank 4C has a bubble mixed water outlet 4 at the lower part. A second pressure regulating device consisting of a cylindrical side wall 4 7 1 having a vertical axis with 70 a ¾ and a top wall 4 7 2 having a valved air discharge hole 4 7 2 a and a bottom wall 4 7 3 The tank body 470, an inlet pipe 480 for receiving the bubble mixed water sent from the bubble stabilizer 4B provided therein, and a downstream part of the inlet pipe 480 are a And a first pressure regulating chamber 490.
導入管 4 8 0 は本体 4 7 0 の下部に設置され、 前記 気泡安定部 4 B の外筒 4 3 1 内下流側に開口する水平 円筒部 4 8 1 と 、 該水平円筒部 4 8 1 に連続し、 前記 第 1 圧力調整室 4 9 0 内に下向開口する鉛直円筒部 4 8 2 と よ ]) な る。 前記水平円筒部 4 8 1 と鉛直円筒部 The introduction pipe 480 is installed at the lower part of the main body 470, and is connected to a horizontal cylindrical section 481, which opens on the inner and downstream sides of the outer cylinder 431 of the bubble stabilizing section 4B. A vertical cylindrical portion 482 that opens downward into the first pressure regulating chamber 490]). The horizontal cylindrical part 4 8 1 and the vertical cylindrical part
ΟϊνίΡΙ 4 8 2 と は タ ン ク 内流路変向部分 と な る。 ΟϊνίΡΙ 482 is the part of the tank where the flow path is diverted.
第 1 圧力調整室 4 9 0 において、 前記鉛直円筒部 4 8 2 と 同心で、 かつ、 該円筒部 4 8 2 よ 大径の鉛直 円筒側壁 4 9 1 の 下端が 前記タ ン ク 本体 4 7 0 の底壁 4 7 3 に対 し水密 と され、 頂部は多数の噴射孔 4 9 2 a を有する 頂扳 4 9 2 で覆われる。 な お、 図 中 4 7 4 は圧力計取付用座で あ る。 In the first pressure regulating chamber 490, the lower end of the vertical cylindrical side wall 491 concentric with the vertical cylindrical portion 482 and having a larger diameter than the cylindrical portion 482 is formed in the tank main body 470. The bottom wall 473 is made watertight, and the top is covered with a top 492 having a large number of injection holes 492a. In the figure, 4 7 4 is a pressure gauge mounting seat.
以上 に おいて次 にそ の作動状態を説明す る 。 分離櫓 1 A におい て、 汚物が 混入さ れた 水は ポ ン プ圧力が加 え られて、 入口 1 1 a よ !) 櫓内の入口 側汚水域 1 a に 送入される。 該汚水域 1 a 内 の混入汚物の う ち大粒の も のは大 き な 浮力に よ っ て金網の 目 を通って浮上 し、 カ バ - 2 の下面付近に集合す る。 '一方、 浮力の弱い微 粒状汚物は金網 6 a 廇内 で他の微粒状汚物 と 結合 して 粗粒化さ れ、 浮力が増 して浮上する 。 カ バ - 2 の下面 付近に集合 した汚物は閭欠的に電磁弁 ( 図示外 ) が開 かれる こ と に よ ]? エ ル ボ 3 を経て圧送排出 さ れる。 The operation of the above will be described below. At the separation tower 1A, the water mixed with filth is subjected to pump pressure, and the inlet 11a! ) It is sent to the entrance side sewage area 1a in the tower. Of the contaminated waste in the sewage area 1a, large particles float through the wire mesh due to large buoyancy, and gather near the lower surface of the cover-2. 'On the other hand, fine filth with weak buoyancy is combined with other fine filth in the wire mesh 6a 廇 and coarsened, and the buoyancy increases and the levitation rises. The filth collected near the lower surface of the cover-2 is opened by a solenoid valve (not shown) openly.
しか して、 上記排出 に際 し、 エ ル ボ 3 、 特に カ バ ー 2 が下部を大 き く 開 口 し上部が小径 と な る よ う 縮径さ れてい る ため、 貯溜汚物は分離摴頂部全面積 に わたつ て圧 し出 される。 ま た、 こ の よ う な 形状の カ バ — の場 合、 分離樗が相当量煩いた と き で も 第 2 縮径部 2 b の 下部開口 に水面が到達 して汚物の代 に 水が圧 し 出さ れる懸念が な い。 この よ う に浄化された水は出 口側浄水域 1 b を経て 出口 l i b よ 排出さ れる。 この排出 に際 し粗粒化汚 物が排.出さ れな い よ う に浄水域 1 b 上方の金網 6 b は 汚物 過材の役 目 をする。 However, during the above-mentioned discharge, the accumulated waste is separated because the elbow 3, especially the cover 2, has been reduced in diameter so that the lower part is largely opened and the upper part is reduced in diameter. Extruded over the entire area of the top. Also, in the case of a cover having such a shape, even when the separating fission is considerably troublesome, the water surface reaches the lower opening of the second reduced diameter portion 2b, and water is used instead of dirt. There is no fear of being pushed out. The water thus purified is discharged from the outlet lib through the water purification area 1b on the outlet side. The wire mesh 6b above the water purification area 1b serves as a waste filter so that coarse-grained waste is not discharged during this discharge.
第 1 検出器 7 1 は、 カ バ - 2 の 下面付近に汚物が充満 し、 該汚物のため水面がお し下げ られ、 水 と 汚物 と の 界面が前記油量検出器 7 1 の位置ま で下った こ と を感 知 して污物排送 管の電磁弁を 開放させる 役 目 をする。 ま た、 第 2 油検出器 7 2 は界面が該器の設置高さ ま で 下った と き 、 前記電磁弁の開放を制御する の に役立つ この よ う に して界面は常時、 前記第 1 第 2 油検出器 7 1 , 7 2 の設置位置 と の間の高さ に維持さ れる。 The first detector 71 is filled with dirt near the lower surface of the cover 2, the water surface is lowered by the dirt, and the interface between water and the dirt reaches the position of the oil amount detector 71. It senses that it has dropped and opens the solenoid valve on the waste pipe. Also, the second oil detector 72 helps to control the opening of the solenoid valve when the interface is lowered to the installation height of the device, and thus the interface is always in contact with the first oil detector. It is maintained at a height between and the installation positions of the second oil detectors 71 and 72.
洗滌用空気管 8 は分離糟内の清掃時に空気を噴射さ せ、 糟内部お よ び前記汚物粗粒化部材 6 に付着する 油 成分に対 して気泡会合 を起させて油塊状 と し浮上させ るための も のであ る。 The cleaning air pipe 8 injects air at the time of cleaning the inside of the separation tank, and causes air bubbles to associate with the oil component adhering to the inside of the tank and the filth coarsening member 6 to form an oil mass and float. This is to make it happen.
本発明に よ る と 、 汚物粗粒化部材 6 と して金網、合成 樹脂網や金属、 合成樹脂織維体を ラ ン ダ ム に積層 した 網 目 状体層が使用される ので、 従来の板、パ ィ プ等の多 数を組合せ、 これに汚物を付着させて分離させていた 方式に比べて、 汚物の付着率が低 く 、 掃除が容易であ According to the present invention, the mesh-like body layer in which the wire mesh, the synthetic resin mesh, the metal, and the synthetic resin woven body are laminated at random is used as the filth coarsening member 6, so that the conventional method is used. Compared to a system in which a large number of plates, pipes, etc. are combined and sewage is adhered to them, the sewage adhesion rate is lower and cleaning is easier.
O o O o
次 に油分凝集装置 2 A の各混合容器 2 1 1 , 2 1 2 2 1 3 に おいて、 その入口 で、 夫々 の薬品が添加され る と 、 各薬品は夫々 の混合器内 におい て ジ グザ グ状に 流下する が、 こ の流下中 に液体 と よ く 混合され、 微細 油分 を フ ロ ッ ク 化する。 即 ち、 無機凝集剤混合器 2 1 1 に おいて液体にボ リ 塩化ア ル ミ が加え られる と 、 液 体中 の油分は凝集さ れ次 の ア ル 力 リ.凝集 剤混合器 2 1 2 では ; P H 6 . 5 〜 7 . 5 程度に調整さ れ、最終の高分子凝 集剤混合器 2 1 3 では、 散在微粒汚物を架橋作用に よ 前記 フ ロ ッ ク に凝集強化さ せる。 そ して次 の工程の 加圧浮上沈籙分離樗 におい て分離容易な 程度の適正 な 大 き さ の油塊が形成される。 Next, in each mixing vessel 2 11, 2 1 2 2 1 3 of the oil coagulation device 2 A, each chemical is added at the inlet. Then, each chemical flows down in a zigzag manner in each of the mixers, and is mixed well with the liquid in this downflow to block the fine oil. Immediately, when polychlorinated aluminum is added to the liquid in the inorganic coagulant mixer 211, the oil in the liquid is coagulated, and the next alloy is formed. Then, the pH is adjusted to about 6.5 to 7.5, and in the final polymer coagulant mixer 2 13, the scattered fine particles are coagulated and strengthened in the block by a crosslinking action. Then, in the next step, the pressure floatation sedimentation separation fission, an oil mass of an appropriate size that is easy to separate is formed.
ま た、 加圧浮上沈澱樗 3 A に おい て 、 フ ロ ッ ク 化 さ れた汚物が混入さ れた水は ポ ン プ圧力 を 加え られて汚 水入口 3 1 1 か ら 第 1 筒 3 1 0 内 に 送 ら れる が、 第 1 筒 内 には同時に気泡混合水発生機 Apよ ]9 気泡混合水導 管 3 5 0 を経て微粒気泡が混合された水が送入さ れる。 従って、 第 1 筒 内の汚物に気泡が付着 して汚物の浮力 が増大さ れ、 大径部 3 2 3 を 経て汚物導 出管 ·3 6 0 に 蓄積さ れる。 そ して、 前記汚物が除去さ れた残 ]? の 水 は第 2 筒 3 2 0 を 上か ら 下へ下降 し、 残留す る汚物の 重い も のは汚物沈緞窒 3 3 0 a に沈積される。 水は更 に進んで第 3 筒 3 3 0 を 下か ら 上へ通過 し第 4 筒 3 4 0 に入る。 第 4 筒 3 4 0 に進んだ水は炉過層 3 4 0 a を通って浄化 され、 下部に設け られた集水管 3 8 0 に 集水さ れ、 清淨水導出管 3 8 1 よ ]) 流出する。 In addition, in the pressurized flotation sediment Filo 3 A, the water mixed with the flocculed filth is subjected to a pump pressure, and from the sewage inlet 311 to the first cylinder 3. The water mixed with the fine bubbles is sent into the first cylinder through the bubble mixed water generator Ap at the same time. Therefore, air bubbles adhere to the waste in the first cylinder, the buoyancy of the waste is increased, and the waste is accumulated in the waste guide pipe · 360 through the large diameter portion 323. Then, the remaining water from which the dirt has been removed] flows down the second cylinder 320 from the top to the bottom, and the remaining heavy dirt is discharged into the waste sedimentation pipe 330a. Is deposited. The water proceeds further and passes through the third cylinder 340 from bottom to top and enters the fourth cylinder 340. The water that has proceeded to the fourth cylinder 340 is purified through the furnace superstructure 340a, collected in the water collecting pipe 380 provided at the lower part, and the clean water outlet pipe 381] ) leak.
O PI 汚物導出管 3 6 0 の直円筒部 3 6 1 , 第 1 縮怪都 3 6 2 およ び第 2 縮怪部 3 6 3 内に浮上集積されてい る 汚物は、 第 2 縮径部 3 6 3 の先端に設け られた電磁弁 C 図示せず ) が間欠開放さ れる と 水圧に よ ]5 お し出さ れる。 この際、 汚物導出管 3 6 0 は小径で しか も 、 汚 物の導出方向に 沿って更に小径と る る よ ぅ 縮径されて い る ため、 汚 #J導出管 3 6 0 か ら汚物 と 一緒に水が導 出さ れる こ と は な い。 この こ と は、 水処理装置が船な どに搭載された場合、該加圧浮上沈鷇樗 3 Aが船の揺れ に従って或る程度煩いた場合で も 適用される。 O PI The filth floating and accumulating in the straight cylindrical portion 361, the first shrinkage portion 362, and the second shrinkage portion 3663 of the waste discharge pipe 360 is reduced to the second reduced diameter portion 366. When the solenoid valve C (not shown) provided at the end of 3) is intermittently opened, it is discharged by water pressure] 5. At this time, although the dirt outflow pipe 360 has a small diameter, it is further reduced in diameter along the dirt outflow direction. Water is not led out together. This applies even when the water treatment apparatus is mounted on a ship or the like, even when the pressurized floating sinking filter 3A is bothered to some extent as the ship shakes.
第 1 油検出器 3 9 0 a は、 汚物導出管 3 6 0 内に汚 物が充満 し、 該汚物のため水面が圧 し下げ られ、 水 と 汚称 と の界面が 前記油量検出 器 3 9 0 a の位置ま で下 つた こ と を感知 して汚物導出管 3 6 0 の電磁弁を 開放 させる役 目 をする。 ま た、 第 2 油検出器 3 9 0 b は界 面が該器の設置高さ ま で下った と き は、 前記電磁弁の 開放を 制御するの に役立つ。 この よ う に して界面は常 時、 前記第 1 , 第 2 油換出器 3 9 0 a , 3 9 O b の設 置位置 と の間の高さ に維持される。 In the first oil detector 390a, the filth outlet pipe 360 is filled with filth, the water surface is reduced by the filth, and the interface between water and the filth is the oil amount detector 3a. It senses that it has fallen to the position of 90a and opens the solenoid valve of the waste discharge pipe 360. Also, the second oil detector 390b serves to control the opening of the solenoid valve when the interface drops to the installation height of the detector. In this way, the interface is always maintained at a height between the first and second oil changers 3900a and 39Ob.
第 4 筒 3 4 0 内 の泸過層 3 4 0 a 形成部材の洗浄に 際 し逆洗用水供給管 3 8 2 か ら 水が注入され、 逆洗用 水排出管 3 8 3 よ ]? 排出 される。 これ ら両管は常時に 閉止されてい る。 Water is injected from the backwash water supply pipe 382 when washing the formation member in the fourth cylinder 3400, and the backwash water discharge pipe 383 is discharged. Is done. Both pipes are always closed.
沈澱物排出管 3 7 0 は汚物沈澱室 3 3 0 a 内 に溜つ た沈澱物を排出する 際に 開放さ れる。 The sediment discharge pipe 370 collects in the waste sedimentation chamber 330a. Opened when discharging precipitated sediment.
上記実施例 におい て 、 第 1 筒 3 1 0 の 上端が汚物導 出管 3 6 0 の下部円 筒部 3 6 1 内 に位置さ れて も よ い ま た、 汚物導出管 3 6 0 は少 な く と も 一部分に 上狭縮 径部を も っていれば よ く 、 第 2 縮径部 3 6 3 は テ ー パ 付でな く 、 同径ェ ル ポ であっ て も よ い。 In the above embodiment, the upper end of the first cylinder 310 may be located in the lower cylindrical portion 361 of the waste guiding pipe 360, or the number of the waste discharging pipe 360 may be small. It is sufficient if at least a part has an upper narrowed diameter portion, and the second reduced diameter portion 363 does not have a taper and may be an elliptical diameter.
次に、 気体 ノ ズ ル 4 1 0 に加圧空気、 液体 ノ ズル 4 2 . 0 に加圧水 ( 空気 と 同圧力 ) が供給さ れる と 気泡発 生部 4 A において、 液体導入孔 4 2 0 a を 経て液体室 4 2 1 中 に流入す る 水は、 気体 ノ ズ ル 4 1 0 よ ]9 の噴 射空気に よ る末広 テ - パ 孔 4 2 2 内 に おけ る 気泡膨張 作用に よ って、 細かい気泡混合水 と さ れ、 気泡安定部 4 B に送 こ ま れる。 該気泡安定部 4 B 内 では矢示 F に従い第 1 変更部 4 4 0 , 第 2 変更部 4 5 0 , 第 3 変 更部 4 6 0 を経て次 の気泡混合水圧力調整タ ン ク 4 C 内 に送 られ る が、 これ ら 変更部に おい て 、 気泡混合水 は各邪魔部材に衝突 し方 向変向 を繰 返す こ と に よ 攪拌さ れて気泡結合が阻止さ れ、 気泡は益 .々 細粒化さ れる こ と に な る。 気泡混合水は更 に 次 の圧力調整タ ン ク 4 C 内の導入管 4 8 0 に入って変向が行われ、 ま た 第 1 圧力調整室 4 9 0 内 で脈動が防止されて調圧され 噴射孔 4 9 2 a か ら 徐 々 に噴射さ れる ため、 気泡が粗 粒化される こ と は な い。 圧力調整タ ン ク 4 C は次工程 へ送 ら れる 気泡 ¾合水の脈動防止に役立つ。 な お、 余 Next, when pressurized air is supplied to the gas nozzle 410 and pressurized water (at the same pressure as the air) is supplied to the liquid nozzle 42.0, the liquid inlet hole 420a is formed in the bubble generating section 4A. The water flowing into the liquid chamber 4 21 via the gas nozzle 4 is generated by the bubble expansion action in the divergent taper hole 4 22 by the jet air of the gas nozzle 4 10] 9. Then, the mixture is converted into fine bubble mixed water and sent to the bubble stabilizing section 4B. In the bubble stabilizing section 4B, the first bubble changing water pressure adjusting tank 4C passes through the first changing section 44, the second changing section 450, and the third changing section 460 according to the arrow F. In the change section, the bubble-mixed water collides with each of the obstructing members and repeats the direction change, so that the mixed water is stirred and the bubble-bonding is prevented. It will be finely divided. The bubble-mixed water enters the inlet pipe 480 in the next pressure adjusting tank 4 C and is deflected, and pulsation is prevented in the first pressure adjusting chamber 490 to regulate the pressure. Since the air is gradually injected from the injection holes 492a, the bubbles are not coarsened. The pressure adjustment tank 4C helps prevent pulsation of bubbles and mixed water sent to the next process. Nao
OMFI 剰空気は本体 4 7 0 の上部に溜 ]? 、 排出孔 4 7 2 a よ ]3 外部へ排出される ο OMFI Excess air accumulates in the upper part of the body 470], and the discharge hole 472a is discharged to the outside.
この よ う に して、 例えば 3 0 A と い う 微細な気泡を 持つ混合水が瞬時に生成され、 しかも 例えば 1 時間位 とい う 長時間にわた 気泡が消滅する こ と な く 安定に 保持される。 In this way, mixed water having fine bubbles, for example, 30 A, is instantaneously generated, and the bubbles are maintained stably without disappearing for a long time, for example, about one hour. You.
な お、 ま た、 図示省略されたが、 前記気泡発生部 4 A、 気泡安定部 4 B はそれ らの軸線を鉛直に向けても よ い。 この場合、 気泡安定部 4 B の上 ¾が圧力調整タ ン ク 4 C の底壁 4 7 3 の中心に接続され、 鉛直導入管 4 8 0 の上方に邪魔板が設け られ、 導入管 4 8 0 か ら の流体は邪魔板に当つて水平に変向されて第 1 調簦室 4 9 0 へ入る。 Although not shown, the bubble generating section 4A and the bubble stabilizing section 4B may have their axes oriented vertically. In this case, the upper side of the bubble stabilizing section 4B is connected to the center of the bottom wall 473 of the pressure adjusting tank 4C, and a baffle plate is provided above the vertical inlet pipe 480, and the inlet pipe 48 The fluid from 0 hits the baffle and is diverted horizontally and enters the first control room 490.
第 7 図は分離槽 1 Aの糟内が円筒状仕切板 4 0 で仕 切られ、 入口汚水域 1 と 出口浄水域 1 b とに分割さ れた他の実施例の横断面を示す。 該実施例では糟本体 1 の中央に設け られた汚水域 1 a の中心に入□ 1 1 a が、 ま た前記仕切板 4 0 の外周に形成された浄水域 1 b 内に複数の出口 1 1 b が設け られている O FIG. 7 shows a cross section of another embodiment in which the inside of the vessel of the separation tank 1A is partitioned by a cylindrical partition plate 40 and divided into an inlet sewage zone 1 and an outlet purification zone 1b. In this embodiment, a plurality of outlets 1 are inserted into a center of a sewage area 1a provided in the center of the casser body 1 and a plurality of outlets 1 in a water purification area 1b formed on the outer periphery of the partition plate 40. O with 1 b
ま た、 第 8 図は大量の汚水を処理可能と した 2 つの 樗本体 1 0 A , 1 0 B を有する分離櫓の実施例の一部 切欠側面図であ る。 即ち、 第 1 分 0 A と第 2 分 ί樗 1 0 B とは Z状に曲折された接続管 1 0 で違結さ れ、 第 1 分離楕 0 A の 中央下向に元口 1 0 a が、 ま 一 ΟΜΓΙ た第 2 分離樗 1 0 B の中 央上向 に先口 1 0 b が開 口 さ れる。 先口 1 0 b は帽状の泸過用金網 6 2 で包极さ れ てい る。 この実施例構造に よ る と 下隅部に設け られた 入口 1 1 a か ら汚水が導入される と 汚物は浮上 して金 網 6 1 を迪過する と き 粗大化される 。 ま た汚水は接続 管 1 0 を 経て第 2 分離櫓 1 0 B へ送 られ帽状金網 6 2 に よ って再び粗粒化作用が付与さ れる と と も に泸過さ れる。 浄化水は出 口 1 1 よ ]) 送 ]) 出 さ れる。 前記金 6 1 , 6 2 に よ 粗粒化 された汚物は浮力が付さ れ 縮径邰 2 0 , 2 0 に溜め られ、 エ ル ボ状排出管 3 0 , 3 0 を経て夫 々 圧送排出 さ れ る。 縮径部 2 , 2 0 は第 8 図に示す如 く 段付 でな く て も よ い。 ま た、 排出管 3FIG. 8 is a partially cut-away side view of an embodiment of a separation tower having two main bodies 10 A and 10 B capable of treating a large amount of sewage. That is, the 1st minute 0A and the 2nd minute filament 10B are connected by the connecting pipe 10 bent in a Z shape, and the original port 10a is located downward at the center of the first separation ellipse 0A. 、 The opening 10b is opened in the upward direction of the center of the second separated fission 10B. The front end 10 b is covered with a cap-shaped wire mesh 62. According to the structure of this embodiment, when sewage is introduced from the inlet 11a provided in the lower corner, the sewage rises and becomes coarse when passing through the wire netting 61. The sewage is sent to the second separation tower 10B via the connecting pipe 10 and is again passed through the cap-shaped wire netting 62 so that the coarse-graining action is imparted thereto. Purified water is available at outlet 1 1. The filth coarsened by the golds 61 and 62 is given buoyancy and collected in reduced diameters 邰 20 and 20, and is pumped and discharged through elbow-shaped discharge pipes 30 and 30, respectively. It is done. The reduced diameter portions 2 and 20 may not be stepped as shown in FIG. Also, discharge pipe 3
, 3 0 は上方への汚物噴流が直線状 に噴 き あが る の を 阻止す ,る よ う な 曲管であれば必 らず し も 縮径されてい く て も よ い。 , 30 is a curved pipe that can prevent the upward flow of filth jets from blowing up in a straight line.
お、 本装置に け る 試験例を あ げる と 、 処理水 2 0 0 0 tZ日 の場合、 汚物除去率約 9 9 %以上 ( 海水か ら真水 も 造水可能 ) 、 据付面積約 6 0 vf . 処理時間約 1 5 〜 2 0 分で あ ]3 、 ラ ン ニ ン グ コ ス ト も 従来の も の の約 1/¾ と つた。 According to the test example of this equipment, when the treated water is 200 tZ days, the filth removal rate is about 9.9% or more (can produce fresh water from seawater), and the installation area is about 60%. vf. Processing time is about 15 to 20 minutes] 3, and the running cost is about 1 / ¾ of that of the conventional one.
W IrO W IrO
Claims
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CA000444818A CA1244823A (en) | 1983-01-07 | 1984-01-06 | Thiazole derivatives |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57/21918820212 | 1982-02-12 | ||
| JP57021918A JPS6054120B2 (en) | 1982-02-12 | 1982-02-12 | water treatment equipment |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO1983002769A1 true WO1983002769A1 (en) | 1983-08-18 |
Family
ID=12068454
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/JP1983/000038 Ceased WO1983002769A1 (en) | 1982-02-12 | 1983-02-07 | Water treatment apparatus |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JPS6054120B2 (en) |
| KR (1) | KR840003217A (en) |
| WO (1) | WO1983002769A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE4038605A1 (en) * | 1990-09-10 | 1992-09-17 | Rohe Gmbh A | Procedure and device for cleaning vehicle washing water - comprise adding flocculant and water is agitated to form foam which carries dirt particles to upper outlet while water is drawn from base of chamber |
| DE4038606A1 (en) * | 1990-09-10 | 1992-09-17 | Rohe Gmbh A | Cleaning vehicle washing water - using equipment comprising foam-maker, flotation sepn. tank and liquefier and foam thickener consisting of tank with conical floor and roof |
| CN114433371A (en) * | 2020-11-05 | 2022-05-06 | 广东美的白色家电技术创新中心有限公司 | Cyclone separator |
Families Citing this family (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6415193A (en) * | 1987-07-08 | 1989-01-19 | Fuji Electric Co Ltd | Method and device for treatment of waste washing water from electrostatic precipitator |
| JPH0685892B2 (en) * | 1987-11-13 | 1994-11-02 | 富士電機株式会社 | Cleaning method for electrostatic precipitator |
| JPH05136728A (en) * | 1991-11-13 | 1993-06-01 | Matsushita Electric Ind Co Ltd | Portable telephone set |
| KR100323852B1 (en) * | 1999-06-28 | 2002-02-07 | 홍유표 | Clearing system of a foul solution and irresoluble solution |
| KR100330493B1 (en) * | 1999-11-20 | 2002-04-09 | 주대성 | An Intake Water Purifying System |
| KR100383802B1 (en) * | 2000-12-13 | 2003-05-12 | 정병욱 | Apparatus for clarifying raw water |
| AU2003212146A1 (en) | 2002-03-13 | 2003-09-22 | The University Of British Columbia | High dynamic range display devices |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4996559A (en) * | 1972-12-13 | 1974-09-12 |
-
1982
- 1982-02-12 JP JP57021918A patent/JPS6054120B2/en not_active Expired
-
1983
- 1983-01-27 KR KR1019830000324A patent/KR840003217A/en not_active Abandoned
- 1983-02-07 WO PCT/JP1983/000038 patent/WO1983002769A1/en not_active Ceased
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4996559A (en) * | 1972-12-13 | 1974-09-12 |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE4038605A1 (en) * | 1990-09-10 | 1992-09-17 | Rohe Gmbh A | Procedure and device for cleaning vehicle washing water - comprise adding flocculant and water is agitated to form foam which carries dirt particles to upper outlet while water is drawn from base of chamber |
| DE4038606A1 (en) * | 1990-09-10 | 1992-09-17 | Rohe Gmbh A | Cleaning vehicle washing water - using equipment comprising foam-maker, flotation sepn. tank and liquefier and foam thickener consisting of tank with conical floor and roof |
| CN114433371A (en) * | 2020-11-05 | 2022-05-06 | 广东美的白色家电技术创新中心有限公司 | Cyclone separator |
| CN114433371B (en) * | 2020-11-05 | 2024-03-22 | 广东美的白色家电技术创新中心有限公司 | Cyclone separator |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58139783A (en) | 1983-08-19 |
| JPS6054120B2 (en) | 1985-11-28 |
| KR840003217A (en) | 1984-08-20 |
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Designated state(s): AT DE GB US |
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| AL | Designated countries for regional patents |
Designated state(s): FR |