JP4568528B2 - Water treatment equipment - Google Patents

Description

  The present invention relates to the treatment of wastewater such as sewage, industrial wastewater, and human waste, and more particularly to a water treatment apparatus using a carrier that holds activated sludge.

  Conventionally, the activated sludge method has been widely used in water treatment. However, since a high activated sludge concentration cannot be maintained, the treatment time is long and there is a problem in the stability of treatment against load fluctuations. In addition, it has been required to remove nutrients such as nitrogen and phosphorus that cause eutrophication in closed waters.

  On the other hand, in Japan's sewage treatment facilities, there is already no space for expansion, and it is difficult to acquire land for expansion, and it will be possible to use existing facilities for more advanced water treatment. Is required.

  On the other hand, with the improvement of the performance of carrier materials capable of holding microorganisms and activated sludge, water treatment apparatuses using these carriers have been developed.

  For example, in Japanese Patent No. 3285252 and Japanese Patent Application Laid-Open No. 2002-263687, a water treatment apparatus by biological treatment of organic wastewater by a nitrification denitrification method having an aerobic tank and an oxygen-free tank containing a microorganism-immobilized carrier is disclosed. Has been.

  In such a water treatment apparatus, the microorganism-immobilized carrier is held only in the aerobic tank, but the microorganism-immobilized carrier flows down the aerobic tank together with the water to be treated, and the carrier concentration at the end of the aerobic tank increases. There is a problem that a carrier concentration distribution is generated in the tank. Further, in order to hold the microorganism-immobilized carrier in the aerobic tank, it is necessary to provide a carrier separation screen on the outflow side of the aerobic tank. Although the effluent from the aerobic tank is transferred to the anoxic tank as a nitrification solution, the conventional microorganism-immobilized carrier can be used only in the aerobic treatment and is not suitable for denitrification in the anoxic tank. It could not be transferred to the tank.

  In order to solve this problem, in the invention described in Japanese Patent No. 3285252, a carrier separator is provided in the return line from the gas-liquid mixing and transferring means at the end of the aerobic tank, and the solid-liquid is separated in the middle. The immobilization carrier is returned to the tip of the aerobic tank, and the aerobic tank effluent is transferred to the anaerobic tank. For this transfer, an air lift pump or the like is used. However, due to the flow rate of the treated water and the screen structure, the microorganism-immobilized carrier contacts the carrier separation screen on the downstream side of the gas-liquid mixing and transferring means. The screen is closed along with wear and other impurities, and the activated sludge mixed liquid flows out from above the carrier separation screen or deforms the carrier separation screen due to the difference in water level before and after the screen.

  In the invention described in Japanese Patent Application Laid-Open No. 2002-263687, the nitrification liquid is transferred downstream of the screen, and a water level sensor is provided before and after the screen to adjust the circulation amount of the digestive juice. Prevents overflow of activated sludge liquid and carrier outflow. However, in this case, in order to adjust the distribution of the carrier, it is necessary to separately provide a carrier returning means.

  Furthermore, when refurbishing the air diffuser installed inside the aerobic tank in order to maintain the activity of the microorganism-immobilized carrier, it is necessary to pause the aerobic tank and empty the inside. On the other hand, in the invention described in Japanese Patent No. 3285252, a means for transferring the microorganism-immobilized carrier is provided in another series of devices arranged in parallel to cope with this problem. The transfer line of the microorganism-immobilized carrier is complicated.

  On the other hand, an anaerobic, anaerobic, and aerobic water treatment apparatus that performs anaerobic treatment, oxygen-free treatment, and aerobic treatment in one reaction tank has been developed. Such a water treatment apparatus comprises a first solid-liquid separation means (first sedimentation basin), a reaction tank, and a second solid-liquid separation means (final sedimentation basin). The reaction tanks are anaerobic tank, anoxic tank and aerobic tank. The configuration is divided into three.

  First, influent wastewater is firstly solid-liquid separated in a settling basin, and the separated liquid is introduced into an anaerobic tank. In the anaerobic tank, the returned sludge returned from the final settling basin through a return sludge pipe is contacted with the separated liquid. The At this time, the phosphorus accumulating bacteria contained in the returned sludge take in the soluble BOD (mainly volatile organic acid) in the inflow wastewater and simultaneously release the phosphorus accumulated in the cells.

  Next, the effluent water from the anaerobic tank is introduced into the anoxic tank, and in the anoxic tank, a mixed liquid containing oxidized nitrogen oxidized in the aerobic tank is circulated. Touched. Thereby, the denitrifying bacteria contained in the sludge performs denitrification using the BOD in the inflow wastewater, and the oxidized nitrogen is removed as nitrogen gas.

  Furthermore, the effluent from the anaerobic tank is introduced into the aerobic tank, and BOD in the inflow wastewater is oxidatively decomposed under aerobic conditions, and ammonia nitrogen and organic nitrogen are nitrified by nitrifying bacteria contained in the sludge. The phosphorus is re-uptaked excessively by the phosphorus accumulating bacteria and removed from the liquid phase.

  The outflow water from the aerobic tank is introduced into the final sedimentation basin and separated into solid and liquid into treated water and sludge. The treated water is discharged after disinfection, and the sludge is partially returned to the anaerobic tank through the return sludge pipe. In addition, a part of the sludge is treated as surplus sludge in the sludge treatment process, or once transferred to the first sedimentation basin and treated in the sludge treatment process together with the initial sedimentation sludge.

  In an anaerobic / anoxic / aerobic water treatment system, the phosphorus release of phosphorus accumulating bacteria in the anaerobic tank becomes unstable due to fluctuations in the drainage water quality, and sufficient phosphorus removal is achieved in the aerobic tank. There was a problem that was not possible. On the other hand, in Japanese Patent Application Laid-Open No. 11-156387 disclosed by the present applicants and the like, the sludge condition in which the first settling sludge from the first settling basin is introduced without introducing the separated water from the first settling basin into the anaerobic tank. The acid fermentation broth containing volatile organic acid (VFA) obtained in the peptizer is introduced and brought into contact with the returned sludge introduced from the final sedimentation basin to remove the influence of the inflow wastewater in the anaerobic tank.

  In the water treatment apparatus described in Japanese Patent Application Laid-Open No. 11-156387, organic substances and nitrogen in the inflow wastewater are increased by using a microorganism-immobilized carrier to increase the amount of microorganisms retained for reducing the reaction tank volume. Are removed stably and efficiently. That is, the total MLSS concentration in the anaerobic tank and aerobic tank related to nitrification / denitrification (concentration of the activated sludge in these tanks) is maintained at least twice as compared with the case where the microorganism-immobilized support is not used. In addition, sufficient sludge retention time (SRT) is ensured to improve processing efficiency.

Japanese Patent No. 3285252

JP 2002-263687 A

JP-A-11-156387

  The present invention can cope with an increase in the amount of load water in an existing sewage treatment facility without the need to add an existing treatment facility such as expansion of a biological treatment tank or final sedimentation basin, and without increasing the load on the final sedimentation basin. And it aims at providing the water treatment apparatus which can prevent bulking.

  Specifically, the carrier carrying activated sludge and microorganisms is prevented from flowing into the final sedimentation basin, the load on the final sedimentation basin is not increased, the generation of excess sludge is suppressed, and further, the treatment A water treatment apparatus capable of reducing time and stabilizing treatment is provided.

  In addition, the present invention provides equipment capable of removing BOD, removing nitrogen, and removing phosphorus as needed without expanding existing equipment.

The present invention relates to a water treatment apparatus which has a suction port on the downstream side and a discharge port on the upstream side and is provided with a return pipe for returning the carrier, and which treats waste water using the carrier. In particular, in the present invention, a plurality of air blowing holes provided around the return pipe , a gas distributor forming an air reservoir around the air blowing holes, and air connected to the gas distributor with flue to supply equipped et be, vent valve is provided in the return pipe.

The bioreactor is preferably a aerobic tank provided with a carrier separator.

The biological reaction tank is preferably composed of an aerobic tank equipped with a carrier separator and an oxygen- free tank.

The biological reaction tank preferably includes an anaerobic tank .

The biological reaction tank preferably includes an organic substance addition tube .

  In the water treatment apparatus according to the present invention, the activated sludge can be made high in concentration, so that the capacity of the reaction tank required by the activated sludge circulation modified method is reduced to half. That is, BOD and nitrogen can be removed in half the residence time compared with the activated sludge circulation modified method.

  Since the carrier that holds the activated sludge stays only in the reaction tank, the activated sludge can be concentrated at a high concentration without increasing the load on the final settling basin. Can be used.

  By introducing the carrier, the activated sludge can be kept at a high concentration in the reaction tank, and the SS load is reduced, so that the sedimentation property of the sludge can be stabilized.

  Airlift circulation is used for returning the carrier mixture, and the cost associated with the circulation pump can be reduced.

  Although management of sludge is important in nitrification, since nitrifying bacteria can be held on a carrier, maintenance management becomes easy, and a high nitrogen removal rate can be obtained at a predetermined residence time even at a low water temperature regardless of the sludge residence time. Furthermore, even if the nitrogen load is high at high water temperature, a high nitrogen removal rate can be obtained. Therefore, high nitrogen load processing became possible.

  A combination of an anaerobic tank, an anaerobic tank using a carrier, and an aerobic tank has the same size as the installation area of the existing standard activated sludge process. This can be applied to an existing processing apparatus without changing the structure of the processing facility, and the processing facility can be reduced in capacity and space. Furthermore, a high nitrogen and phosphorus removal rate can be obtained while eliminating the need for methanol and chemicals during denitrification and dephosphorization.

  In one embodiment of the present invention, since the air supply pipe is not provided in the return pipe, the diameter of the return pipe can be reduced, and the equipment cost can be reduced. Further, when the discharge port is submerged, the head can be reduced, so that the pumping efficiency can be improved and the operating cost can be reduced.

  FIG. 1 is a flowchart showing a first embodiment of a water treatment apparatus according to the present invention. Throughout the drawings, the same or corresponding parts are denoted by the same reference numerals, and redundant description is omitted. In addition, the carrier (16) is partially illustrated for the sake of explanation, and most of the illustration is omitted to the extent that the presence can be understood. In addition, the flow of water and the like is indicated by arrows throughout the entire diagram.

  As is apparent from FIG. 1, the first mode is constituted by a biological reaction tank (2) consisting only of an aerobic tank (5).

  In addition to the sedimentation basin, the first sedimentation basin (first solid-liquid separation means) (1) may employ a separation device using a membrane or a filtration device using a filter medium. The separated liquid separated in the first sedimentation basin (1) is introduced into the aerobic tank (5) through the transfer pipe (13), and the sludge from the first sedimentation basin (1) and the returned sludge from the last sedimentation liquid are removed. Introduce by pipeline.

The sludge in the first sedimentation basin (1) may be added after removing the residue through the rotor mat. The electric control valve is controlled so that the concentration of the introduced sludge becomes the set concentration, and the input amount of the first settling basin (1) is controlled. For example, 80 to 90 m ³ / day of first settling sludge from the first settling basin (1) is charged at around 22000 m ³ / day. The sludge from the first sedimentation basin (1) is introduced, but the sludge from the first sedimentation basin (1) is guided to a sludge tempering tank (not shown), and the sludge fermentation product or the supernatant water after sludge fermentation is used. An easily decomposable organic substance may be added.

  The carrier (16) holds microorganisms. This carrier (16) is mainly made of a three-dimensional polyurethane having a side or a diameter of 5 to 30 mm, but if the biodegradability is extremely low, such as polyester or polypropylene, and is excellent in corrosion resistance and durability, The material is arbitrary. Natural materials such as activated carbon may also be used. Moreover, the shape and the size are arbitrary as long as it has a function of flowing in the tank by aeration or stirring and retaining microorganisms. The microorganisms may be held in a manner that the microorganisms are adhered and fixed to the surface or inside of the carrier (16), or the microorganisms may be comprehensively fixed with a carrier material. Furthermore, the material of the carrier (16) can be any of an inorganic substance and an organic substance.

  A return pipe (10) that circulates the liquid mixture of the aerobic tank (5) and the carrier (16) from the end to the tip of the aerobic tank (5) is provided. The return pipe (10) includes an air lift part (31) and a horizontal pulling part (32), and an air supply pipe and a gas distributor (14) are provided. A suction port (15) for taking the mixed liquid and the carrier (16) into the return pipe (10) is provided at the bottom of the tank. The return pipe (10) is provided with a plurality of holes (25 mm) for blowing air as a gas disperser (14), and an air reservoir is provided to make air blowing uniform. The positions of the holes are provided around the same surface regardless of whether the cut end of the tube is a corner or the cut end of the tube is a circle. In order to increase the discharge amount, it is desirable that the gas disperser (14) is provided as low as possible. It is desirable that the suction port of the return pipe (10) is configured to be substantially downward from 45 °. In addition, the hole diameter of the air blowing port of a gas disperser (14) changes with transfer amounts.

  Return pipe (10) The air vent valve is provided above the water surface. This is to prevent pulsation, but it is also possible to force the pulsation and close the sludge of the carrier (16) by closing the air vent valve.

  The transfer portion of the return pipe (10) may be provided in water or above the water surface. The shape may be a pipe line, but the taper may be about 1/100 as an open water path provided above the water surface. By returning the mixed liquid containing the carrier (16) through the open channel, separation and accumulation of water and the carrier (16) can be prevented. In addition, confirmation of the circulation amount of the mixed liquid and the carrier (16) is easy because it is easy to measure the flow velocity and the water depth in the open channel. Furthermore, the acclimatization period can be shortened by introducing the carrier (16) and water rapidly by introducing it into the open channel when the carrier is initially introduced.

  At the end of the aerobic tank (5), a carrier separator (for example, a punching plate) (17) is used as means for separating the effluent from the carrier (16) and the aerobic tank (5). Processing is preferably performed with a hole diameter of 3 to 20 mm and a hole area ratio that can maintain the strength of the punching plate (17). The thickness of the punching plate (17) is preferably 1 to 5 mm.

  The punching plate (17) is provided vertically at the end of the aerobic tank (5), but may be inclined depending on the shape of the tank. Generally, it is provided at right angles to the direction in which the treated water flows, but at the end of the aerobic tank (5), it passes through a punching plate installed at the end of the aerobic tank (5) in a U-shape. May be.

  The size and pitch of the holes of the punching plate (17) are determined by factors such as the size of the carrier (16). However, in order for the carrier (16) of the aerobic tank (5) to flow smoothly, the passing speed of the effluent passing through the aperture of the punching plate (17) is usually 0.3-3 cm / It is preferable to set to sec.

  As the carrier separator (17) at the end of the aerobic tank, a carrier can be separated by providing a bar screen or a water collecting pipe. However, the carrier (16) wears heavily because the carrier (16) bites into the bar. However, since the punching plate has no protrusion on the inside and has a low coefficient of friction, the carrier contact side is smooth and wear of the carrier (16) can be prevented. The carrier separator (17) is not limited to this, and any carrier separator (17) may be used as long as the carrier (16) has little wear and can be separated.

  By providing such a carrier separator (17), it is possible to prevent the carrier (16) from being worn, and to prevent the head difference between the front and the rear of the carrier separator (17) from being blocked by impurities. The carrier (16) and activated sludge are not led to the final sedimentation basin (9).

  Further, a cleaning air diffuser (19) is provided in the lower part on the upstream side of the carrier separator (17) so as to create an aeration zone parallel to the carrier separator. This creates an upward flow along the carrier separator (17). Therefore, the carrier (16) that has approached the carrier separator (17) by the flow in the direction of flowing water moves while scraping off foreign matter and scum adhering to the carrier separator (17) while floating. It is possible to prevent the head difference between the front and rear separators (17). A defoaming device may be provided in the vicinity of the carrier separator (17).

  The aerobic tank (5) is provided with an air diffusion facility (8) in parallel with the direction in which the treated water flows. The diffuser facility (8) is optional as long as it can aerate the treated water in the aerobic tank (5). As the air diffusion facility (8), it is recommended to use a fine bubble diffusion cylinder, but an air diffusion plate or the like can also be used. When using a fine bubble diffuser cylinder, a cap with a hole is attached so that the carrier (16) does not enter the diffuser (8).

  The air diffuser (8) has a large pressure loss and changes (increases) over time. Therefore, the air distribution with the existing air diffuser cannot be achieved simply by installing a new air diffuser fixed at the bottom. There is. Therefore, as shown in FIG. 5, a movable type is adopted so that the height of the header pipe can be adjusted. By making it movable, it can be lifted, and it becomes easy to replace the diffuser facility (8). Thereby, replacement | exchange of aeration equipment (8) can be performed easily, without extracting a support | carrier (16) and emptying an aerobic tank (5).

  In the aerobic tank (5), aeration is performed by the aeration equipment (8), and aerobic treatment is performed, whereby oxidative decomposition of BOD and nitrification of nitrogen components by nitrifying bacteria are performed. About 5 to 50% of the carrier (16) is charged per tank volume. Since the activated sludge retention concentration in the aerobic tank (5) is improved by introducing the carrier (16), the removal efficiency of BOD is improved. Furthermore, since the inside of the carrier (16) is in an oxygen-free state, nitrogen can be removed by aerobic tank denitrification of the carrier (16). Thus, by circulating the mixed liquid containing the carrier (16) from the aerobic tank (5) to the oxygen-free tank (described later), the carrier (16) is increased by 10 to 30%. Nitrogen can be removed. That is, the circulation amount can be reduced to obtain the same nitrogen removal amount, and the power cost can be reduced. Further, even when only the aerobic tank (5) in which the carrier (16) is charged is operated, about 25% of nitrogen can be removed when the carrier (16) is not charged. For example, of 50% of nitrogen removal, 25% can be removed as excess sludge and 25% can be removed by aerobic tank denitrification. In addition, with the above-described configuration, there is no bias in the distribution of the carrier (16) in the aerobic tank (5), and water treatment with minimal wear of the carrier (16) is possible. Furthermore, since the carrier (16) stays only in the reaction tank, the activated sludge can be made high in concentration without increasing the load on the final sedimentation tank (9). Thereby, it becomes possible to suppress the generation amount of surplus sludge to the same extent as the standard activated sludge method, and the extension of the final sedimentation basin (9) becomes unnecessary.

  FIG. 2 shows a second embodiment of the water treatment apparatus of the present invention. The biological reaction tank (2) in the second embodiment includes an anoxic tank (4) and an aerobic tank (5).

  In this embodiment, the anoxic tank (4) and the aerobic tank (5) are separated by a partition. The treated water in the oxygen-free tank (4) flows into the aerobic tank (5) from the upper part of the partition. This makes it possible to separate the state of the anaerobic tank (4) and the state of the aerobic tank (5).

  The oxygen-free tank (4) is provided with a stirrer (7) for generating an oxygen-free stirring state. The number of blades of the stirrer (7) in the anaerobic tank (4) is 4 or more because it is necessary to suppress the rotation speed of stirring, but it can be operated at about 3 to 10 rpm, and the anaerobic tank (4) There is no limitation on the number of sheets as long as the carrier (16) can be made to flow by generating a flow therein. You may attach the blade | wing for suppressing foaming to the upper part of a stirrer (7). In order to prevent the carrier (16) from being worn or damaged, the blades preferably have rounded corners. In order to prevent wear of the carrier (16) and oxygen dissolution, the stirrer (7) must be operable at 3 to 15 rpm.

  In the second embodiment, the separation liquid from the first sedimentation basin (1) is introduced into the anoxic tank (4) through the transfer pipe (13). The first settling sludge from the first settling basin (1) is introduced into the anoxic tank (4) through the transfer pipe (13) through the sludge screen (11) (for example, rotor mat). The mixed solution in the aerobic tank (5) is circulated to the anoxic tank (4) through the return pipe (10) together with the carrier (16). Other configurations are the same as those in the first embodiment.

  In the anaerobic tank (4), the separation liquid from the first sedimentation tank (1) flows in, and the nitrification liquid containing the carrier (16) from the aerobic tank (5) is circulated by the return pipe (10). The denitrifying bacteria contained in the activated sludge under the oxygen-free stirring condition by the stirrer (7) in the oxygen-free tank (4) uses the organic matter (BOD) of the waste water and the first settling sludge. Then, the circulating oxygen nitrogen is denitrified and removed as nitrogen gas.

  In the anaerobic tank (4), the control operation by the oxidation-reduction potential ORP is desirable. In this case, an oxygen sensor (4) is maintained in an oxygen-free state by installing an ORP sensor (not shown) and controlling the amount of input sludge, the amount of separated liquid, and the amount of circulating water based on the measured values. Is possible. In the anaerobic tank (4), it is preferable to operate at an oxidation-reduction potential ORP of about 0 to -300 mV.

  The mixed liquid containing the denitrified carrier (16) is introduced into the aerobic tank (5) and subjected to the aerobic treatment described above. In the second aspect, by adding the carrier (16) to the anaerobic tank (4) and the aerobic tank (5), a high nitrogen load operation capable of improving both the nitrification rate and the denitrification rate becomes possible. In particular, since the nitrifying bacteria are fixed to the carrier (16), the sludge residence time of the nitrifying bacteria having a slow growth rate can be easily managed. In addition, it is the same as the first embodiment in that the carrier (16) is not biased in the reaction tank and the wear of the carrier (16) can be suppressed.

  FIG. 3 shows a third embodiment of the water treatment apparatus of the present invention. The biological reaction tank (2) in the third aspect includes an anaerobic tank (3), an oxygen-free tank (4), and an aerobic tank (5). Other configurations are the same as those in the first and second aspects.

  In this aspect, the anaerobic tank (3) and the anaerobic tank (4) and the anoxic tank (4) and the aerobic tank (5) are separated by a partition. An opening is provided in the upper part of the partition between the anaerobic tank (3) and the anaerobic tank (4). The opening is provided in the upper part by flowing the scum and adjusting the level by dropping the corners, so that the carrier (16) is submerged and the anaerobic tank (4) is changed from the anaerobic tank (4) by the flow rate fluctuation ( This is to prevent backflow in 3). Further, the treated water in the anaerobic tank (4) flows into the aerobic tank (5) from the upper part of the partition, so that the anoxic state and the aerobic state can be separated.

  The anaerobic tank (3) is provided with a stirrer (6) for generating an anaerobic stirring state. The stirrer (6) may be any stirrer that can be operated to prevent oxygen from being dissolved.

  In the third aspect, the separation liquid from the first sedimentation basin (1) and the initial sedimentation sludge from the first sedimentation basin (1) through the sludge screen are passed through the transfer pipe (13), respectively, in the anaerobic tank (3) and / Or introduced into the anoxic tank (4). The mixed solution in the aerobic tank (5) is circulated to the anoxic tank (4) through the return pipe (10) together with the carrier (16). Other configurations are the same as those in the first and second aspects.

  The first settling sludge from the first settling basin (1) is introduced into the anaerobic tank (3) and the anoxic tank (4) through the transfer pipe (13) and used as an organic substance. Thereby, in the anaerobic tank (3), the separated substance from the first sedimentation basin and the organic matter from the first sedimentation sludge are used for the phosphorus release of the phosphorus accumulating bacteria. In the anaerobic tank (4), denitrifying bacteria use this organic matter to perform denitrification. Thereby, the phosphorus discharge | release in an anaerobic process and the organic matter shortage with respect to the denitrification in an oxygen-free process can be solved at low cost by using the first settling sludge in the existing equipment, without providing an acid fermentation tank separately.

  In the anaerobic tank (3), the separation liquid from the first sedimentation basin (1) flows in and the first sedimentation sludge from the first sedimentation basin (1) through the sludge screen is introduced. Here, the phosphorus accumulating bacteria are the energy obtained by hydrolyzing the polyphosphoric acid stored in the microbial bodies under the anaerobic stirring condition by the stirrer (6), and the organic substances in the microbial bodies are stored in the microbial bodies. take in. That is, the phosphorus accumulated in the cells is reliably released. Furthermore, under repeated aerobic / anaerobic conditions, phosphate is excessively taken up into cells under aerobic conditions and stored in the form of polyphosphate. Moreover, in this anaerobic tank (3), since filamentous bacteria can be inactivated, floating sludge with good sedimentation can be obtained. Thereby, bulking can be prevented.

  Also in the anaerobic tank (3), the control operation by the redox potential ORP is desirable. In this case, by installing an ORP sensor (not shown) and controlling the amount of introduced sludge and the amount of separated liquid based on the measured values, the inside of the tank can be maintained in an anaerobic state. In the anaerobic tank (3), it is generally preferable to operate at an oxidation-reduction potential ORP of -200 to -500 mV.

  The anaerobic mixed liquid is introduced into the anaerobic tank (4) and the above-described denitrification treatment is performed, and the denitrified mixed liquid is introduced into the aerobic tank (5) and the above-described aerobic characteristics. Processing is performed.

  In the third aspect, by adding the carrier (16) to the anaerobic tank (4) and the aerobic tank (5), a high nitrogen load operation capable of improving both the nitrification rate and the denitrification rate becomes possible. . In particular, since the nitrifying bacteria are fixed to the carrier (16), the sludge residence time of the nitrifying bacteria having a slow growth rate can be easily managed. In addition, it is the same as the first embodiment in that the carrier (16) is not biased in the reaction tank and the wear of the carrier (16) can be suppressed.

  Furthermore, it is possible to efficiently remove nitrogen and phosphorus without requiring additional facilities and not only increasing the amount of treated water but also adding methanol for denitrification and chemicals for dephosphorization. . In addition, using existing equipment, it is possible to remove nitrogen and phosphorus simultaneously with removal of BOD and SS corresponding to the increase in load treated water, and there are restrictions on the site, and closed water areas where phosphorus removal is necessary It is useful in the treatment plant that discharges to

[Example 1]
As shown in FIG. 1, the biological reaction tank (2) was applied to the removal of organic matter and nitrogen by using a water treatment device comprising an aerobic tank (5).

  A carrier separator (punching plate) (17) was provided at the downstream end of the aerobic tank of the existing processing facility. Furthermore, the return pipe (10) provided with the gas disperser (14) and the air feed pipe (12) was provided.

  The carrier separator (punching plate) (17) had a thickness of 2 mm, a hole diameter of 8 mmφ, and a hole area ratio of 40%. The passing speed through the aperture was 1.4 cm / sec.

  As shown in FIG. 5, the header pipe of the air diffuser (8) is connected to the two riser pipes (21) joined by the knee joint (20) and connected to the upper lift diffuser body (22). And further connected to a blower (not shown). The air from the blower is sent to the header pipe 8 of the diffuser through these riser pipes (21) and the like. The lift diffuser body (22) and knee joint (20) are provided with hinges at two locations, and the header pipe is lifted by pulling while rotating the lift diffuser body (22) and knee joint (20). Is possible.

  As shown in FIGS. 4 and 7, the return pipe (10) provided with the gas disperser (14) has a pipe diameter sufficient for the carrier (16) to flow. As shown in FIG. 4, the return pipe air lift part (31) includes a suction port (15) and a gas distributor (14). The return pipe air lift part (31) was installed on the upstream side of the carrier separator (punching plate) (17). The carrier (16) and the mixed solution suction port (15) provided in the lower part of the tank were conical and the suction port (15) was 45 ° with respect to the horizontal. The suction port (15) is connected to the vertical pipe line of the return pipe. A gas distributor (14) was provided on the bottom side of the vertical pipe. The vertical pipe was connected by an elbow on the water surface, and the return pipe (10) was extended from the end of the aerobic tank (5) to the tip, and provided with a discharge port (25) connected to the elbow. Further, a cleaning air diffuser (19) is provided at the lower part on the upstream side of the carrier separator (punching plate) (17). The suction port (15) can also be connected to the return pipe horizontal pulling portion (32) on the upstream side of the screen as shown in FIGS. The shape of the suction port (15) is not limited to the conical shape, and it is sufficient that the suction is easy.

  A polyurethane sponge having a size of 15 × 12 × 12 mm was used as the carrier (16). The input rate of the carrier (16) was 20% in terms of the tank volume ratio, and the return rate of the carrier mixed solution was changed depending on the removal rate.

  The water treatment apparatus having the biological reaction tank (2) having the above configuration was continuously operated for one year. The treatment target was urban sewage.

  As a result, the activated sludge could be maintained at a high concentration in the biological reaction tank, so that the SS load was reduced and the sedimentation property of the sludge was stabilized. Therefore, the floating sludge concentration was 1000 to 2000 mg / L, but the total activated sludge concentration including the activated sludge retained on the carrier (16) was 3000 to 4500 mg / L.

  By adding the carrier (16) to the aerobic tank (5), the activated sludge retention concentration in the aerobic tank (5) is improved, the BOD removal rate is improved, and the removal rate is 95% or more. It was. Furthermore, the aerobic tank denitrification by the carrier (16) became possible, and a nitrogen removal rate of 30 to 50% was obtained on average.

  Further, since the air lift circulation is used for returning the carrier mixed liquid, the cost for the circulation pump is reduced. Further, the distribution of the carrier (16) in the aerobic tank (5) is not biased, the carrier (16) is not clogged with the carrier separator (punching plate) (17), and the wear of the carrier (16) is also 1 % Or less.

  In the vicinity of the suction port (15), the carrier (16) and dust may be clogged in the punching plate by the cleaning air diffuser (19) provided in the lower part of the upstream side of the carrier separator (punching plate) (17). Therefore, the carrier (16) stayed only in the biological reaction tank and did not overflow the carrier separator (punching plate) (17). Furthermore, since the activated sludge is retained in the carrier (16), the load on the final sedimentation basin (9) is not increased, and therefore no problem has occurred in the treatment with the existing final sedimentation basin (9). Furthermore, the amount of surplus sludge generation was similar to that of conventional standard activated sludge.

[Example 2]
As shown in FIG. 2, the biological reaction tank (2) is divided into the anaerobic tank (4) and the aerobic tank (5) with respect to the existing processing facility, and the anaerobic tank (4) Except for the provision of 7), a water treatment device having the same configuration as in Example 1 was installed, including the carrier (16) and its charging rate.

  By the return pipe (10), the carrier (16) and the mixed liquid are returned from the end of the aerobic tank (5) to the tip of the anaerobic tank (4). The carrier (16) and the treated water can move from the anoxic tank (4) to the aerobic tank (5) by overflow.

The water treatment apparatus having the biological reaction tank (2) having the above configuration was continuously operated for one year. The treatment target was urban sewage. The nitrogen load was 0.2 kg / m ³ · day.

  As a result, the activated sludge can be kept at a high concentration in the biological reaction tank and can be operated without being biased. From these things, SS load fell and the sedimentation property of sludge was stabilized. Therefore, the floating sludge concentration was 1000 to 2000 mg / L, but the total activated sludge concentration including the activated sludge retained on the carrier (16) was 3000 to 4500 mg / L.

  Oxidized nitrogen in the mixed solution returned to the anaerobic tank (4) is reduced by denitrifying bacteria in the carrier (16) and floating sludge using the organic matter in the inflowing water and the organic matter adhering to the sludge as a hydrogen donor. Treated as nitrogen gas. The oxygen-free tank (4) was set to a redox potential ORP of −150 mV.

  In nitrification, sludge management is important, but nitrifying bacteria can be retained on the carrier (16). Therefore, in the conventional activated sludge circulation modified method, in order to achieve a nitrogen removal rate of 70% or more, a residence time of 16 hours is required. In contrast to the time required, a nitrogen removal rate of 70% or more was obtained at a water temperature of 12 ° C. with a residence time of 8 hours, and it became unnecessary to pay attention to the sludge residence time.

When the sludge retention time is 4 to 5 days at a water temperature of 25 ° C., the number of nitric acid bacteria in the suspended sludge is 2.4 × 10 ² MPN / mL, and the carrier-attached sludge is 9.0 × 10 ² MPN / mL. The sludge residence time of 15 to 20 days was maintained on the carrier (16).

Further, a nitrogen removal rate of 70% or more was obtained even at a water temperature of 20 ° C., a suspended sludge concentration of 2000 mg / L, and a nitrogen load of 0.26 kg / m ³ · day. Further, the removal rate of BOD was 95% or more.

  In this way, continuous operation was performed, but there was no bias in the distribution of the carrier (16) in the anaerobic tank (4) and the aerobic tank (5), and the wear of the carrier (16) was 1%. It was the following. Furthermore, the outflow of the carrier (16) and activated sludge to the final sedimentation basin (9) was also suppressed.

  Also, by adding the carrier (16) to both the anaerobic tank (4) and the aerobic tank (5), a high nitrogen load operation can be performed for the purpose of improving both the nitrification rate and the denitrification rate. It became. Furthermore, since the nitrifying bacteria are fixed to the carrier (16), the sludge residence time of the nitrifying bacteria having a slow growth rate can be easily managed.

[Example 3]
As shown in FIG. 3, the biological reaction tank (2) is divided into the anaerobic tank (3), the anaerobic tank (4), and the aerobic tank (5) with respect to the existing processing facility, and the anaerobic tank (3). And a water treatment device having the same configuration as in Example 1, including the carrier (16) and its charging rate, except that the anaerobic tank (4) is provided with the stirrers (6) and (7), respectively. installed.

  By the return pipe (10), the carrier (16) and the mixed liquid are returned from the end of the aerobic tank (5) to the tip of the anaerobic tank (4). The treated water flows from the anaerobic tank (3) into the anaerobic tank (4) due to overflow, and the carrier (16) and the treated water move from the anaerobic tank (4) to the aerobic tank (5) due to overflow. To do.

  The water treatment apparatus having the biological reaction tank (2) having the above configuration was continuously operated for one year. The treatment target was urban sewage.

  As a result, the activated sludge could be kept at a high concentration in the biological reaction tank, so that the SS load was reduced and the sedimentation property of the sludge was stabilized. Therefore, the floating sludge concentration was 1000 to 2000 mg / L, but the total activated sludge concentration including the activated sludge retained on the carrier (16) was 3000 to 4500 mg / L. In addition, the sludge holding amount of a support | carrier (16) is the range of 5-20 g / L normally.

First, the effluent from the settling basin (1) flows into the anaerobic tank (3), and in the anaerobic tank (3), in the presence of organic matter, the anaerobic state activates normal phosphate (PO ₄ − After releasing P), in the aerobic tank (5), more of the released normal phosphate phosphorus is taken into the activated sludge microorganisms, and the sludge is discharged out of the system. In addition, the anaerobic tank (3) was set to -250 mV oxidation-reduction potential ORP.

  Oxidized nitrogen in the mixed solution returned to the anoxic tank (4) is caused by denitrifying bacteria in the carrier (16) or floating sludge using organic matter in the inflowing water or organic matter adhering to the sludge as a hydrogen donor. Reduced and treated as nitrogen gas.

  This makes it possible to remove nitrogen and phosphorus at the same size as the installation area of the standard activated sludge method that has already been installed, and denitrification without significantly changing the structure of the biological reaction tank (2). And a water treatment apparatus capable of dephosphorization.

  The water quality of the initial sedimentation effluent was, on average, 30 mg-N / L nitrogen, 3.5 mg-P / L phosphorus, 7 mg / L BOD, but when the residence time was 8 hours and the water temperature was 14 ° C, the quality of the treated water Obtained 9 mg-N / L of nitrogen, 0.4 mg-P / L of phosphorus and 7 mg / L of BOD on average, without the need for addition of methanol for denitrification or addition of chemicals for phosphorus removal, A removal rate of 70% or more of nitrogen and 80% or more of phosphorus could be obtained.

  Normally, the separation liquid from the first settling basin and the first settling sludge flow into the anaerobic tank. However, when the oxidation-reduction potential ORP of the anaerobic tank rises (for example, in rainy weather), In some cases, the separation liquid and the initial settling sludge are allowed to flow, and when the oxidation-reduction potential ORP of the anoxic tank rises or the organic matter source is insufficient, the initial settling sludge enters the anoxic tank. May be thrown in. By measuring the oxidation-reduction potential ORP, it is recommended to keep the anaerobic tank at approximately −200 to −500 mV and the anaerobic tank at approximately 0 to −300 mV.

  In this way, continuous operation was performed, but there was no bias in the distribution of the carrier (16) in the anaerobic tank (4) and the aerobic tank (5), and the wear of the carrier (16) was 1% or less. Met. Furthermore, the outflow of the carrier (16) and activated sludge to the final sedimentation basin (9) was also suppressed.

The installation position of the discharge port discharge port (25) may be near the top and bottom of the water surface. The shape of the discharge port (25) protruding from the water surface is shown in FIGS. The shape in which the discharge port (25) is below the water surface is shown in FIGS. The shape in which the discharge port (25) is the same as the water surface is shown in FIG. Further, the position of the discharge port may follow either the water level as shown in FIG. 12, or may be fixed depending on the shape of the tank, the form of inflow, or the like. The shape of the discharge port (25) may be either a trumpet shape or a cylindrical shape as long as the mixed liquid of the carrier and the activated sludge is smoothly circulated and discharged.

  A plurality of biological reaction tanks may be a combination of an aerobic tank and an anaerobic tank, an aerobic tank, an anaerobic tank, and an anaerobic tank, depending on the type of treatment. The present invention is used when a carrier is used even in the combination and it is necessary to move the carrier.

Air is supplied from the air supply pipe (12) to the air return section (31) of the return pipe (10) of the gas distributor to obtain the air lift effect. However, as shown in FIGS. A hole (14) was formed around the return pipe (10) so that air was evenly supplied to the pipe (10), and a gas distributor (14) was provided so that air could be collected around the hole (14). By providing the position of the gas distributor (14) at a deeper depth of the return pipe (10), the amount of air supply can be reduced, and the maintenance cost can be reduced.

Draft tube As shown in FIG. 16, the draft tube is provided in the anaerobic tank, and the inflowing water and the return sludge are guided into the draft tube, so that the energy for stirring can be reduced by using the return energy of the sludge. The return sludge introduced into the draft tube may be guided to the upper part of the draft tube, but depending on the structure, it may be guided to the lower part of the draft tube. In addition, when returning sludge is introduced into a square anaerobic tank, it is also possible to reduce the energy by returning the sludge to the corner so that a swirling flow occurs. Moreover, the energy for stirring can be reduced by providing the draft tube in the oxygen-free tank and providing the discharge port of the return pipe at the top of the draft tube. The shape of the draft tube can be selected according to the shape of the tank. For example, a blade can be attached to the outside of the draft tube so that it can rotate with a little energy, or the position of the draft tube can be adjusted with a chain.

Organic substance addition pipe As shown in Fig. 6, an organic substance addition pipe is provided in the biological reaction tank (2), so that the phosphorus of the phosphorus accumulating bacteria can be released sufficiently. It is structured to add chemicals such as extraction sludge from the tank, organic acid from the sludge fermentation tank, and sodium acetate.

  It should be noted that the stirring blades of the anaerobic tank have the blades angled to prevent the carrier from being worn.

  The shape of the carrier separator (17) may be a combination of inclined plates (27) as shown in FIGS. 9 and 10 in addition to providing a punching plate as a screen. Further, a combination of the inclined plate (27) and a screen such as a punching plate may be used in combination. Furthermore, by aeration on the upstream side of the carrier separator, the carrier separator can always be kept free from clogging.

  As shown in FIG. 8, when the outflow side of the anaerobic tank and the aerobic tank are close to each other, the horizontal pulling portion of the return pipe may be small, the cost for installing the return pipe can be reduced, and the pipe line is short. Minute maintenance is easy.

[Example 4]
The diameter of the return pipe is 350 mm, the diameter of the air supply pipe is 150 mm, the diameter of the hole opened in the return pipe is 25 mm (number of 8 pieces), the diameter of the gas disperser is 500 mm, the height of the gas disperser is 200 mm, the inundation depth is 2400 mm, With the water treatment device of the present invention having a combination of tanks shown in FIG. 6 at a rate of 3.0 m ³ / min and an air supply rate of 4.5 m ³ / min, mixed water of a carrier and activated sludge is transferred from an aerobic tank to an anoxic tank. When returned, good operation was possible without the carrier staying downstream.

[Example 5]
The apparatus of FIG. 2 can be used as a processing apparatus mainly for removing nitrogen during fine weather, and can be a primary processing apparatus for 3Q during rainy weather. That is, nitrification and BOD removal are performed in the aerobic tank (5) as shown in Example 2 during clear weather, and denitrification is performed in the anaerobic tank (4), but the amount of treated water increases during rainy weather, so aerobic. The residence time in the tank (5) and the oxygen-free tank (4) is shortened and the activated sludge flows out. However, since the carrier (16) is put in, the suspended matter is removed, that is, as a primary treatment tank. Function can be retained. Furthermore, when the weather is fine, even when the water temperature is low in winter, it is possible to secure the biomass for organic matter removal and nitrifying bacteria for nitrogen removal.

  Moreover, SS provided in the filtration tank can be reduced to 50 mg / L or less by providing a filtration tank after the precipitation tank. Moreover, the sludge of a sedimentation tank with good sedimentation can be returned, and the sludge that is difficult to settle is treated in a filtration tank. In addition, by using a floating body drainage machine that uses a siphon tube to drain the sedimentation tank and filtration tank, a floating body is used without using a drive unit in the water. The sludge can be efficiently precipitated using this.

  Furthermore, phosphorus can be removed by adding a flocculant to the filtration tank.

[Example 6]
Using the apparatus of FIG. 8, the biological reaction tank (2) was treated as an anaerobic tank (4) and an aerobic tank (5). The return pipe (10) was provided with a suction port (15) in the aerobic tank (5) and a discharge port (25) in the anaerobic tank (4). Nitrogen removal was a good treatment.

  Furthermore, in addition to providing the anaerobic tank (4) and the aerobic tank (5) as the biological reaction tank (2), biological dephosphorization could be performed by providing an anaerobic tank.

It is a 1st aspect of this invention, and is a conceptual flowchart which shows the water treatment apparatus of the biological reaction tank which consists only of an aerobic tank. It is a conceptual flow figure which is the 2nd aspect of this invention, and shows the water treatment apparatus of the biological reaction tank which consists of an anaerobic tank and an aerobic tank. It is a conceptual flow figure which is the 3rd aspect of this invention, and shows the water treatment apparatus of the biological reaction tank which consists of an anaerobic tank, an oxygen-free tank, and an aerobic tank. It is the schematic which shows a return pipe airlift part, the air diffuser for washing | cleaning, and a carrier separator. It is the schematic which shows the use condition and lifting state of a diffuser. It is a conceptual flow figure which is the 4th aspect of this invention, and shows the water treatment apparatus of the biological reaction tank which consists of an anaerobic tank, an oxygen-free tank, and an aerobic tank. It is a conceptual flow figure which is the 5th aspect of this invention, and shows the water treatment apparatus of the biological reaction tank which consists only of an aerobic tank. It is a conceptual flow figure which is the 6th aspect of this invention, and shows the water treatment apparatus of the biological reaction tank which consists of an anaerobic tank and an aerobic tank. It is the schematic which showed one Example of the carrier separator. It is the schematic which showed one Example of the carrier separator. It is the schematic which showed one Example of the discharge outlet. It is the schematic which showed one Example of the discharge outlet. It is the schematic which showed the gas disperser of the return pipe air lift part. It is the schematic which showed the gas disperser of the return pipe air lift part. It is the schematic which showed the gas disperser of the return pipe air lift part. It is the conceptual flow figure which provided the draft tube in the anaerobic tank of the water treatment apparatus of the biological reaction tank which consists of an anaerobic tank, an oxygen-free tank, and an aerobic tank.

Explanation of symbols

DESCRIPTION OF SYMBOLS 1 First sedimentation tank 2 Biological reaction tank 3 Anaerobic tank 4 Anoxic tank 5 Aerobic tank 6, 7 Stirrer 8 Aeration equipment 9 Final sedimentation tank 10 Return pipe 11 Sludge screen 12 Air feed pipe 13 Transfer pipe 14 Gas disperser 15 Suction port 16 Carrier 17, 26, 29 Carrier separator (punching plate)
19 Aeration equipment for cleaning 20 Knee joint 21 Riser pipe 22 Lift diffuser body 24 Organic substance addition pipe 25 Discharge port 27 Inclined plate 28 Water passage 30 Floating 31 Return pipe air lift part 32 Return pipe horizontal pulling part 33 Draft tube

Claims (5)

In a biological reaction tank having a return pipe for returning a carrier having a suction port on the downstream side and a discharge port on the upstream side, in a water treatment apparatus for treating waste water using the carrier, the periphery of the return pipe A plurality of air blowing holes provided in the air, a gas distributor that forms an air reservoir around the air blowing holes, and an air supply pipe that is connected to the gas distributor and supplies air, and the return pipe Is a water treatment apparatus provided with an air vent valve . The said biological reaction tank is an aerobic tank provided with the support | carrier separator, The water treatment apparatus of Claim 1 characterized by the above-mentioned. The biological reactor, the water treatment apparatus according to claim 1, characterized in that comprising the aerobic tank and the anoxic tank having a carrier separator. The said biological reaction tank is equipped with an anaerobic tank, The water treatment apparatus in any one of Claims 1-3 characterized by the above-mentioned. The said biological reaction tank is equipped with an organic substance addition pipe | tube, The water treatment apparatus in any one of Claims 1-4 characterized by the above-mentioned.

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