KR20180059705A - High effective water treatment apparatus using membrane - Google Patents

Abstract

The present invention relates to an advanced water treatment apparatus using a submersible separation membrane for removing nitrogen and phosphorus. In particular, the present invention relates to an advanced water treatment apparatus in which a sludge thickener and a stabilization tank are installed in a front end of a bioreactor; and sludge is transferred to the sludge thickener and the stabilization tank from a membrane separation tank, wherein a coagulant is added to the transferred sludge, thereby improving sludge thickening and phosphorus removal efficiency in the sludge thickener, minimizing the size of the sludge thickener, and simplifying the structure thereof. In particular, after reducing the dissolved oxygen concentration in the transferred sludge brought into the bioreactor through the stabilization tank as much as possible, the sludge is brought into an anoxic tank; and by reasonably designing the flow of sludge and incoming water from the anoxic tank to the membrane separation tank, the advanced water treatment apparatus maintains the dissolved oxygen concentration to be uniform and maximizes the retention time in each tank to increase nitrogen and phosphorus treatment efficiency thereby.

Description

TECHNICAL FIELD [0001] The present invention relates to a high-efficiency water treatment apparatus using a membrane,

The present invention relates to an advanced water treatment apparatus using a separation membrane using an immersion separation membrane for removing nitrogen and phosphorus, and more particularly, to an advanced water treatment apparatus using an immersion separation membrane and a stabilization tank at the front end of a bioreactor, The concentration of sludge in the concentrating tank and the removal efficiency of phosphorus are improved by minimizing the size of the concentrating tank and simplifying the structure of the concentrating tank by injecting the coagulant into the conveying sludge and the dissolved oxygen concentration in the returning sludge flowing into the bioreactor through the stabilizing tank The flow rate of the influent and sludge from the anoxic tank to the membrane separation tank is rationally designed to maintain the concentration of dissolved oxygen constant and to maximize the residence time of each reaction tank to maximize the treatment efficiency of nitrogen and phosphorus Wherein the separation membrane It relates to an apparatus.

In recent years, there has been a growing interest in reuse of effluent water and treatment water. In addition to the removal of organic matter such as BOD by the secondary treatment facility of the conventional activated sludge process, removal of nutrients such as nitrogen and phosphorus is also required in the sewage treatment process .

As a result, the A2O process and the continuous batch reactor (SBR) have been used as advanced treatment processes with the function of removing nitrogen and phosphorus.

For example, the advanced water treatment apparatus to which the conventional A2O method is applied includes a screen, a flow rate adjusting tank, an anaerobic tank where phosphorus emission occurs, an anoxic tank where denitrification and organic matter removal occur, nitrification, phosphorus accumulation, And a sedimentation tank for solid-liquid separation of sludge. The nitrification liquid in the aeration tank is internally transported to the anoxic tank, and the sludge in the settling tank is transported outside in the anaerobic tank to maintain the optimum microorganism concentration in the tank. In addition, the SBR is continuously operated in a single reactor (SBR reactor) in accordance with the arrangement of the predetermined time, such as the inflow of wastewater, the outflow of treated water, and anaerobic, anoxic, aerobic and sedimentation processes.

 However, in such a conventional high-temperature water treatment apparatus, the quality of the treated water deteriorates as the sedimentation property of the sludge in the sedimentation tank becomes poor. Further, when the sedimentation property of the sludge in the sedimentation tank becomes poor, the microorganisms are mixed into the treated water and the quality of the treated water is degraded. Especially, during the winter when the water temperature drops, the quality of the treated water is unstable due to poor sedimentation property. Therefore, specialized management is required for influent load and water quality management.

To overcome this problem, a submerged membrane separation sewage elevation treatment process (MBR) has been proposed in which a membrane is immersed in an activated sludge aeration tank and a process for removing nitrogen and phosphorus is added in place of the settling tank.

This is because the treatment water is produced instead of the sedimentation tank by introducing the submerged separation membrane into the aerobic tank of the biological advanced treatment method, and there is no problem of deterioration of the treated water due to sludge floatation of the sedimentation tank as well as the settlement site because there is no sedimentation tank . In particular, MBR (membrane separation process) maintains the sludge concentration higher than that of the existing advanced treatment process and produces treated water through the membrane, which is advantageous in that the quality of treated water is good and stable.

3, the conventional membrane-separated high-altitude water treatment apparatus includes an anaerobic tank 10 for treating organic matter and phosphorus, a stabilization tank 20 for reducing dissolved oxygen, an anoxic tank 30 for denitrification, An aerobic tank 40 for removal and nitrification and excessive intake, and a membrane separation tank 50 for removal of organic matter and phosphorus and solid-liquid separation. The surplus sludge of the membrane separation aeration tank (50) is transported to the stabilization tank (20) in order to maintain the optimum microorganism concentration in the reaction tank. The nitrified liquid of the anoxic tank (30) is internally transported to the anaerobic tank (30).

However, in the conventional membrane-separation aeration tank, contamination is formed on the surface of the membrane during the solid-liquid separation through the suction type submerged separation membrane. Therefore, air is excessively injected by the blower B provided at the bottom of the membrane. Thus, when the dissolved oxygen concentration of the membrane separation and aeration tank is maintained higher than the concentration required for the biological reaction, and the sludge having such a high dissolved oxygen concentration is transported through the return line to the anoxic tank, .

That is, in order to minimize the membrane contamination during the process of producing the treated water through the submerged membrane, air is supplied in a larger amount than the amount of air required for the microorganisms, so that the concentration of dissolved oxygen in the aerobic tank is kept high. Accordingly, when the sludge having a high dissolved oxygen concentration in the membrane separation aeration tank is returned to the anoxic tank through the return line as it is, the oxygen concentration in the anoxic tank is increased and denitrification of the nitrate nitrogen is not caused, The nitrate nitrogen concentration that is not reacted also reduces the proliferation of the PAOs microorganisms used to remove phosphorus and consequently the removal efficiency of phosphorus.

In addition, the conventional MBR methods have a complicated structure in which the mixed liquid is returned to the anaerobic tank by the inner conveyance and then returned to the anaerobic tank because the conventional MBR process can not properly remove the dissolved oxygen from the stabilization tank.

Conventionally, in order to overcome such a problem, there is a case where a deaeration tank or a stabilization tank for reducing dissolved oxygen is installed before the sludge of the membrane separation aeration tank is transported to the anoxic tank, or the separation membrane tank and the oxic tank are separately operated. There is a disadvantage that the advantage of performing solid-liquid separation with an immersion type membrane in place of the settling tank is offset.

In addition, conventionally, a stabilizing tank or a deaeration tank is placed at the downstream end of the separation membrane, and the concentration of dissolved oxygen is reduced by staying for about 30 minutes to 1 hour. However, when the sludge is conveyed using an underwater pump as in the prior art, dissolved oxygen is dissolved in the return water by the impeller of the underwater pump, so that the dissolved oxygen concentration is somewhat present in the anoxic tank and the nitrogen is not effectively removed. In addition, the sludge is introduced into the anoxic tank in the state that the sludge is disassembled by the impeller of the underwater pump. Unlike the aeration tank, the anoxic tank has a slow growth rate and low reactivity, so that the better the state of the sludge to be transported, .

(0001) Korea Patent Registration No. 10-0920176 (Registered Date: 2009/09/28) (0002) Korea Patent Registration No. 10-1018587 (Registered on February 22, 2011)

SUMMARY OF THE INVENTION It is a primary object of the present invention to provide a separation membrane that reduces the concentration of dissolved oxygen in a carrier liquid flowing into an anoxic tank and an anaerobic tank to a maximum extent and improves treatment efficiency of nitrogen and phosphorus And to provide an advanced water treatment apparatus.

In addition, the present invention provides a method of adjusting the size of a thickener by setting the concentration tank and the stabilization tank at the front end of the bioreactor, adding the flocculant to the sludge conveyed to the concentration tank and the stabilization tank in the membrane separation tank, And to provide an advanced water treatment apparatus using a membrane that minimizes the structure and simplifies the structure.

In addition, the present invention is designed to optimize the flow of influent and sludge from the anoxic tank to the membrane separation tank so that the concentration of dissolved oxygen is kept constant to prevent interference between the microorganisms in each reaction tank and to maximize the residence time of each tank, And an object thereof is to provide an advanced water treatment apparatus using a separation membrane that maximizes treatment efficiency.

In addition, the present invention can reduce the construction cost by arranging the anaerobic tank at the downstream of the anaerobic tank so that the anaerobic tank can be naturally submerged after flowing into the anoxic tank through sludge transportation without carrying the inner tank, and the altitude And a water treatment apparatus.

It is another object of the present invention to provide an apparatus for high-altitude water treatment using a separation membrane that can appropriately dispose each reaction vessel to minimize the size and area of a site.

In order to achieve the object of the present invention, there is provided an apparatus for treating water using a separation membrane according to the present invention,

An anoxic tank, an anaerobic tank, an aeration tank, a membrane separation tank, and a discharge tank,

A stabilizer provided at the tip of the anoxic tank;

A thickening tank provided at the tip of the stabilization tank;

A flow rate adjusting tank provided at a front end of the thickener;

A transfer line installed between the membrane separation tank, the thickening tank and the stabilization tank for conveying the mixed liquid;

A coagulant injecting means provided in the return line for injecting a coagulant into the transport mixed liquid;

Dividing and feeding means provided in the conveying line for dividing and injecting the conveying mixed liquid into the thickening tank and the stabilizing tank,

A raw water supply line provided between the flow rate adjusting tank, the anoxic tank, and the anaerobic tank for dividing raw water;

A divided supply unit installed in the raw water supply line and dividedly injected into the anoxic tank and the anaerobic tank;

A connecting passage provided between the thickener and the stabilizer to form an upper portion of the stabilizer, wherein the upper portion of the diluent is introduced into the stabilizer;

And a plurality of connection passages disposed between the reaction vessels from the stabilization vessel to the membrane separation vessel and alternately installed at the upper and lower ends of the reaction vessels.

In the present invention, the coagulant dosing means comprises a line mixer installed in the return line and a flocculant tank connected to the line mixer to supply the flocculant.

The membrane-separated high-altitude water treatment apparatus includes a quadrangular reactor partitioned into four compartments,

A concentrating tank and a flow rate adjusting tank are disposed in the first compartment;

A stabilization tank, an anoxic tank and an anaerobic tank are disposed in the second compartment;

An aeration tank is arranged in the third compartment;

A membrane separation tank and a discharge tank are disposed in the fourth compartment.

The connection passages formed between the respective reaction tanks from the anoxic tank to the membrane separation tank are installed diagonally of each reaction tank.

According to the eleventh water treatment apparatus using the separation membrane of the present invention, the concentration tank and the stabilization tank are provided at the front end of the bioreactor to reduce the size of the concentration tank and to simplify the structure, and to minimize the concentration of dissolved oxygen in the transport sludge flowing into the anoxic tank There is an effect that can be made.

Further, the present invention provides a line mixer installed in a transfer line provided between a membrane separation tank, a thickening tank and a stabilization tank, and a coagulant is added to the thickening tank and the conveying sludge flowing into the stabilization tank to increase the coagulation efficiency and minimize contamination of the separation membrane by the coagulant There is an effect that can be.

Further, the present invention eliminates the need for a separate facility for effectively removing the concentration of phosphorus having a high reflux number and treating the reflux water by injecting the flocculant into the transportation sludge introduced into the concentration tank, thereby simplifying the structure of the concentration tank have.

In addition, since the stabilization tank is installed in the anterior part of the anoxic tank and dissolved oxygen is removed from the stabilization tank as much as possible, the dissolved oxygen concentration of the transport sludge can be reduced and the transportation sludge can be supplied There is an effect that can be.

In addition, the present invention is designed to optimize the flow of inflow water and sludge in each reaction tank, to maximize the residence time of inflow water and sludge in each reaction tank, to maintain the concentration of dissolved oxygen between each reaction tank constant There is an effect that can be.

BRIEF DESCRIPTION OF THE DRAWINGS FIG. 1 is a schematic cross-sectional view of an advanced water treatment apparatus using a separation membrane according to the present invention;
2 is a schematic plan view of an advanced water treatment apparatus using a separation membrane according to the present invention,
3 is a schematic cross-sectional view of an advanced water treatment apparatus using a separation membrane according to the prior art.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, preferred embodiments of an advanced water treatment apparatus using a separation membrane according to the present invention will be described in detail with reference to the accompanying drawings.

FIG. 1 is a schematic cross-sectional view showing an advanced water treatment apparatus using a separation membrane according to the present invention, and FIG. 2 is a schematic plan configuration diagram of an advanced water treatment apparatus using a separation membrane according to the present invention.

As shown in the drawing, an advanced water treatment apparatus 1 (hereinafter, referred to as an 'advanced water treatment apparatus') using a separation membrane according to the present invention includes a flow rate adjustment tank 2, a concentration tank 3, a stabilization tank 4, 5, an anaerobic tank 6, an aeration tank 7, a membrane separation tank 8, and a discharge tank 9.

The flow rate adjusting tank 2 injects wastewater into the tank, the thickener tank 3 stores excess sludge, and the stabilizer tank 4 reduces the concentration of dissolved oxygen in the transport sludge.

The anoxic tank 5 removes nitrogen components by a denitrification operation and the anaerobic tank 6 releases phosphorus and the aeration tank 7 removes nitrification, phosphorus intake and organic matter, Separates the mixed liquid from the sludge and the filtrate, and the effluent tank 9 stores the filtered water.

A transfer line 10 is provided between the membrane separation tank 9 and the thickening tank 3 or the stabilization tank 4 so that the mixed liquid of the membrane separation tank 9 is supplied to the thickening tank 3 and the stabilization tank 4 ).

The transfer line 10 is provided with a split supply unit 13 to inject the divided liquid into the concentration tank 3 and the stabilizer tank 4 at a predetermined ratio.

The transfer line (10) is provided with a coagulant injecting device for injecting a coagulant. Preferably, the coagulant injector comprises a line mixer 11 installed in the return line 10 and a flocculant tank 12 for supplying a flocculant to the line mixer 11.

A raw water supply line 29 for supplying raw water is provided between the flow rate adjusting tank 2 and the anoxic tank 5 or the anaerobic tank 6.

The supply line 31 is provided with a screen device 14 for removing contaminants.

The supply line 31 is provided with a split supply unit 16 and is divided into the anoxic tank 5 and the anaerobic tank 6 at a predetermined ratio.

In addition, the aeration tank (7) and the membrane separation tank (8) are provided with aeration device not shown. The flow rate adjusting tank 2, the anoxic tank 5, and the anaerobic tank 6 may be equipped with an agitator not shown. The membrane separation unit 9 is provided with a separation unit 17 and a suction pump 19. The membrane separation tank 9 is provided with a transfer pump 18 for transferring mixed liquid and a raw water pump 15 for supplying raw water to the flow rate regulating tank 2 is provided.

Thus, the invention is characterized in that the thickening tank (3) and the stabilization tank (4) are installed at the front end of the bioreactor.

It is possible to reduce the size of the thickening tank 3 and simplify the structure by providing the thickening tank 3 and the stabilization tank 4 at the front end of the bioreactor so that the concentration of dissolved oxygen in the transporting mixed liquid flowing into the non- .

The line mixer 11 is installed in the conveying line 10 provided between the membrane separation tank 8 and the thickening tank 3 and the stabilizing tank 4 so that the concentration tank 3 and the stabilization tank 4). ≪ / RTI >

Accordingly, the concentration efficiency of the concentration tank 3 can be increased, and the size of the concentration tank 3 can be minimized. In the conventional MBR method, the coagulant is introduced into the aeration tank or the membrane separation tank. This method not only decreases the efficiency of the coagulant, but also may affect the clogging of the separation membrane due to the excessive introduction of the coagulant. However, the present invention can increase the coagulation efficiency and minimize the contamination of the separation membrane by the coagulant by injecting the coagulant into the conveying water through the line mixer 11 provided in the conveying line 10 conveyed in the membrane separation tank 8.

Also, the supernatant of the thickener 3 is referred to as 'reflux water.' The reflux water contains phosphorus which is 2 to 4 times higher than the influent water due to re-release of phosphorus due to the anaerobic condition of the concentrate tank 3. Therefore, in the conventional MBR method, a pressurized floating tank or a coagulating sedimentation device is installed at the downstream of the concentration tank 3 to remove phosphorus in the reflux water, so that phosphorus is removed and then introduced into the bioreactor. However, since the surplus sludge into which the coagulant is added flows into the concentrating tank 3, the concentration of phosphorus having high reflux water can be effectively removed. That is, the coagulant introduced through the line mixer 11 chemically coagulates the phosphorus of the counter current and is precipitated and removed in the concentration tank 3.

Accordingly, the present invention can increase the concentration efficiency of the concentration tank 3, minimize the size of the concentration tank 3, reduce the sludge treatment cost, and eliminate the need for a separate facility to treat the reflux water. 3).

In addition, since the stabilization tank 4 is installed at the front end of the bioreactor and the dissolved oxygen is removed from the stabilization tank 4 as much as possible, it flows into the anoxic tank 5, so that the dissolved oxygen concentration of the transporting sludge can be reduced . In the conventional MBR method, since the amount of cleaning air for separating membrane cleaning is excessively supplied to the separating membrane tank 8 in excess of the amount of air required for organic matter and nitrification, the concentration of dissolved oxygen in the conveying water conveyed from the separating membrane tank 8 to the anoxic tank or anaerobic tank The denitrification efficiency in the anoxic tank (5) is lowered, and the nitrate nitrogen concentration unreacted in the anaerobic tank decreases the proliferation of the PAOs microorganisms used for removing phosphorus, resulting in a decrease in phosphorus removal efficiency. However, in the present invention, the stabilization tank 4 is installed at the front end of the anoxic tank 5, and the concentration of dissolved oxygen in the stabilization tank 4 is reduced. Then, the stabilized tank 4 is injected into the anoxic tank 5 in a natural- The concentration can be reduced to the maximum.

In addition, in the conventional MBR method, the stabilization tank or the deaeration tank is provided at the downstream end of the separation membrane, and the concentration of dissolved oxygen is reduced for a certain period of time, and the sludge of the stabilization tank is returned to the anoxic tank through internal transportation. Therefore, the dissolved oxygen is dissolved in the transported water during the movement through the return line, so that the dissolved oxygen concentration is somewhat present in the anoxic tank, and the nitrogen is not effectively removed. However, according to the present invention, the stabilization tank 4 is installed at the front end of the anoxic tank 5 so that the conveying sludge is introduced in a natural descent manner, thereby minimizing the concentration of dissolved oxygen and simplifying the structure.

Accordingly, the present invention can minimize the concentration of dissolved oxygen in the return water, stabilize the sludge, and minimize the capacity of the stabilization tank 4, which is the object of the stabilization tank 4.

Meanwhile, in the present invention, a connection passage is appropriately installed between each reaction tank to smooth the flow of influent water and sludge, and to maximize the residence time of inflow water and sludge in each reaction tank.

1, a connecting passage 21 is provided between the thickener 3 and the stabilizer 4 at the upper end of the reaction tank. Therefore, when the surplus sludge in the thickening tank 3 is equal to or higher than a certain level, the counterflow of the thickening tank 20 flows into the stabilization tank 4.

A T-shaped pipe 22 is installed between the stabilization tank 4 and the anoxic tank 5. [ The T-shaped pipe 22 allows the sludge at the lower end of the stabilization tank 4 to be discharged to the anoxic tank 5 through the upper part of the reaction tank, so that the stabilization tank 4 can be utilized as efficiently as possible.

The connection passages provided between the anoxic tank 5 and the membrane separation tank 8 are alternately installed at the upper and lower ends of the reaction tank to smooth the flow of influent water and sludge and to maximize the residence time of influent and sludge in each reaction tank do.

In addition, depending on the concentration of dissolved oxygen in each reaction tank, the connection channels provided between the reaction tanks are alternately arranged at the lower and upper ends of the reaction tank, so that the concentration of dissolved oxygen in each reaction tank is kept constant and the interference of microorganisms between the reaction tanks is minimized .

That is, the connection passage 23 between the anoxic tank 5 and the anaerobic tank 6 having a low dissolved oxygen concentration and the connection passage 25 between the aeration tank 7 and the membrane separation tank 8, Is formed at the lower end of the reaction tank so that the dissolved oxygen can move between the reaction vessels.

On the other hand, the connection passage 24 between the anaerobic tank 6 having a low concentration of dissolved oxygen and the aeration tank 7 having a high concentration of dissolved oxygen is installed at the top of the reaction tank so that dissolved oxygen can not move between the reaction tanks, So that the concentration of dissolved oxygen in the reaction vessel is kept constant and the interference of microorganisms between the reaction vessels is minimized.

2, the membrane-separated high-altitude water treatment apparatus 1 according to the present invention has a rectangular shape as a whole, and four compartments are defined from the inflow side to the outflow side.

In the first compartment, a thickening tank (3) and a flow rate adjusting tank (2) are arranged. The wastewater or sludge does not move between the flow rate adjusting tank (2) and the thickening tank (3). Subsequently, in the second compartment, the stabilization tank 4, the anoxic tank 5, and the anaerobic tank 6 are disposed. The number of reflux of the anaerobic tank (6) flows into the stabilization tank (6). The return sludge of the stabilization tank 6 flows into the anoxic tank 5. The mixture of the anoxic tank (5) is introduced into the anaerobic tank (6). At this time, the connection passages 21, 22, 23 and 24 provided between the reaction tanks are provided in the diagonal direction of the reaction tank so as to maximize the residence time of inflow water and sludge in each reaction tank.

And an aeration tank 7 is disposed in the third compartment. The mixture of the anaerobic tank (6) is introduced into the aeration tank (7). A membrane separation tank 8 and a discharge tank 9 are disposed in the fourth compartment. The mixture of the aeration tank (7) is introduced into the membrane separation tank (8). At this time, the connection passages 25 provided between the reaction vessels are installed diagonally of the reaction vessels to maximize the residence time of the influent water and the sludge in each reaction vessel.

The filtered water filtered in the separation unit (17) of the membrane separation tank (8) flows into the discharge tank (9) through a suction pump (19). The sludge which has not passed through the separation membrane unit 17 in the membrane separation tank 8 is conveyed to the thickening tank 3 and the stabilization tank 4 through the return line 10. The wastewater of the flow rate adjusting tank 2 is dividedly injected into the anoxic tank 5 and the anaerobic tank 6.

As described above, the membrane-separated high-altitude water treatment system 1 according to the present invention minimizes site area by compactly arranging each reaction tank, smoothes inflow water and sludge flow in each reaction tank, maximizes residence time, So that the concentration of oxygen can be kept constant.

Hereinafter, the operation of the membrane-separated high-altitude water treatment system according to the present invention will be described with reference to FIGS. 1 and 2. FIG.

First, the raw water, which is wastewater flowing from the outside, flows into the flow rate regulating tank 2.

The wastewater flowing into the flow rate adjusting tank 2 is supplied to the anoxic tank 5 and the anaerobic tank 6 by supplying the wastewater into the anaerobic tank 6 by operating the raw water pump 15 by detecting a certain level of the level switch. The split supply ratio can be adjusted according to the characteristics of the wastewater. That is, the anoxic tank 5 and the anaerobic tank 6 are connected to each other through the split supply means 16 provided in the raw water supply line 29 provided between the flow rate regulator 2, the anoxic tank 5 and the anaerobic tank 6, To supply the wastewater. At this time, the screen device 16 installed in the raw water supply line 29 removes fine contaminants contained in the wastewater.

The wastewater supplied to the anoxic tank (5) is mixed with the carrier liquid flowing in the stabilizer tank (4). In the anoxic tank 3, the nitrogen component is removed by the denitrification reaction. Denitrification refers to the action that nitrate nitrogen is reduced to nitrogen gas (N2) by microorganisms. When microorganisms lack oxygen, oxygen contained in nitric acid (NO3) is taken out and used. It is reduced to gas (N2) and released into the atmosphere.

This is because a large amount of nitrate nitrogen in the mixed solution of microorganisms supplied from the stabilization tank 1 and a small amount of nitrate nitrogen contained in the wastewater supplied from the wandering tank 1 are supplied to the anoxic tank 5 And is separated from the bound oxygen by denitrifying microorganisms in the reaction tank, and is converted into nitrogen gas (N2) and released into the atmosphere. At this time, the organic carbon source necessary for the denitrifying microorganisms to work is obtained from the organic substances in the mixed inflow of the organic substances in the inflow wastewater and the microorganisms introduced from the stabilization tank (4).

Then, the mixed liquid of the anoxic tank (5) is introduced into the anaerobic tank (6) and mixed with the wastewater to be divided and introduced in the flow rate regulating tank (2). In the anaerobic tank (6), phosphorus release occurs. That is, in the absence of oxygen, the microorganisms accumulate in the cell with PHB (Poly - Hydroxyl Butyrate), which is the intermediate form of the polymer. In order to obtain the necessary energy in this process, intracellular ATP (Adenosine di - phosphate) Is converted to ADP (adenosine triphosphate) and releases H2PO4-.

Subsequently, when the mixed liquid in the anaerobic tank 6 is at a certain level or higher, it flows into the aeration tank. The ammonia nitrogen (NH3-N) and nitrite nitrogen (NO2-N) components contained in the mixture introduced into the aeration tank 7 are nitrified in an aerobic state in the aeration tank 7, N) component, and the phosphorus component material is excessively absorbed and removed by the microorganisms in the aeration tank 7. In other words, the phosphorus-removing microorganisms in the aerobic condition reuse PHB as an electron donor to store phosphorus in the form of ATP in the body.

The nitrified mixture of the aeration tank (7) is introduced into the membrane separation tank (8). In the membrane separation tank 8, ammonia nitrogen (NH 3 -N) and nitrite nitrogen (NO 2 -N) components contained in the influent mixture are nitrified in an aerobic state in the membrane separation tank 8, Nitrogen (NO3-N) component. And the phosphorus component is excessively consumed by the microorganisms existing in the membrane separation tank 8.

When the organic pollutants and the phosphorus components are excessively consumed, only the suspended solids such as suspended solids and microorganisms are present in the membrane separation tank 8, which is separated into the treated water and the sludge by the separation membrane unit 17. The separation membrane unit (17) is connected to a suction pump (19) existing outside the membrane separation tank (8).

The suction pressure generated by the suction pump 19 causes the mixture in the outside of the separation membrane to flow into the separation membrane through the separation membrane cavity to cause solid-liquid separation. As a result, clean filtration water is sucked by the suction pump 19 .

During long-term operation of the submerged membrane separation advanced treatment facility, MLSS concentration, SS and phosphorus content in the membrane separation tank 8 are continuously increased. In order to maintain the proper concentration of MLSS in the membrane separation tank 8 and to remove the SS and phosphorus component materials, the sludge remaining solid-liquid separated by the membrane separation unit 17 in the membrane separation tank 8 has a certain level or more The concentrated liquid is divided and introduced into the thickening tank 3 and the stabilization tank 4 through the return line 10.

The conveying line 10 is provided with a line mixer 11 and a split feeder 13. The divided supply means 13 is provided with a valve in a pipe which is separated and conveyed to the thickening tank 3 and the stabilizing tank 4 so that the amount of conveyance can be adjusted.

The line mixer 11 stores a flocculant for flocculating and removing the phosphorus component in the flocculant tank 12 and removes the stored flocculant from the transfer pump To the line mixer (11).

Since the excess sludge containing the flocculant injected from the line mixer 11 installed in the conveying line 10 is conveyed to the thickening tank 3, the phosphorus contained in the sludge and the counter current water can be effectively settled and removed .

Then, the treated water is supplied to the upper end of the flow rate regulator 4 through the connecting passage 21 formed at the upper end of the thickener 3. The stabilization tank (4) keeps the conveyed sludge for a predetermined period to remove dissolved oxygen in the sludge and coagulate and remove unreacted phosphorus components.

The reaction sludge of the stabilization tank 4 flows into the upper portion of the anoxic tank 5 through the T-shaped pipe 22 installed in the reaction tank. The T-shaped pipe 22 allows the sludge at the lower end of the stabilization tank 4 to flow into the upper end of the anoxic tank 5, thereby making it possible to use the stabilization tank 4 efficiently.

As described above, the membrane-separation high-altitude water treatment apparatus 1 according to the present invention is characterized in that the concentrating tank 3 and the stabilizing tank 4 are provided in front of the bioreactor and the membrane separation tank 8, A line mixer 11 is installed in a conveying line 10 provided between the stabilizing tank 4 and the stabilizing tank 4 to administer the flocculant to the conveying sludge flowing into the thickening tank 3 and the stabilization tank 4.

This makes it possible to increase the concentration efficiency of the concentration tank 3, minimize the size of the concentration tank 3, reduce the sludge treatment cost, and eliminate the need for a separate facility for treating the counter current water. ) Is simplified.

In addition, since the stabilization tank 4 is installed at the front end of the bioreactor and the dissolved oxygen is removed from the stabilization tank 4 as much as possible and then flows into the anoxic tank 5, the dissolved oxygen concentration of the transporting sludge can be reduced , The concentration of dissolved oxygen in the stabilization tank 4 is reduced, and then the solution is injected into the anoxic tank 5 in a natural submerged manner, so that the dissolved oxygen concentration can be reduced to the maximum.

The embodiments of the present invention described above and shown in the drawings should not be construed as limiting the technical idea of the present invention. The scope of protection of the present invention is limited only by the matters described in the claims, and those skilled in the art will be able to modify the technical idea of the present invention in various forms. Accordingly, such improvements and modifications will fall within the scope of the present invention as long as they are obvious to those skilled in the art.

1: membrane separation altitude water treatment device 2: flow rate adjustment tank
3: Enrichment tank 4: Stabilization tank
5: Anoxic tank 6: Anaerobic tank
7: aeration tank 8: membrane separation tank
9: Discharging tank 10: Return line
11: line mixer 13: split feed means
14: Screen device 15: raw water pump
16: split supply means 17: separation membrane unit
18: suction pump 21, 23, 24, 25:
22: T-shaped piping 29: Feed water supply line

Claims (4)

An anoxic tank, an anaerobic tank, an aeration tank, a membrane separation tank, and a discharge tank,
A stabilizer provided at the tip of the anoxic tank;
A thickening tank provided at the tip of the stabilization tank;
A flow rate adjusting tank provided at a front end of the thickener;
A transfer line installed between the membrane separation tank, the thickening tank and the stabilization tank for conveying the mixed liquid;
A coagulant injecting means provided in the return line for injecting a coagulant into the transport mixed liquid;
Dividing and feeding means provided in the conveying line for dividing and injecting the conveying mixed liquid into the thickening tank and the stabilizing tank,
A raw water supply line provided between the flow rate adjusting tank, the anoxic tank, and the anaerobic tank for dividing raw water;
A divided supply unit installed in the raw water supply line and dividedly injected into the anoxic tank and the anaerobic tank;
A connecting passage provided between the thickener and the stabilizer to form an upper portion of the stabilizer, wherein the upper portion of the diluent is introduced into the stabilizer;
And a plurality of connection passages disposed between the reaction tanks from the stabilization tank to the membrane separation tank and alternately installed at the upper and lower ends of the reaction tanks.
The method according to claim 1,
Wherein the coagulant dosing means comprises a line mixer installed in the return line and a flocculant tank connected to the line mixer to supply a flocculant.
The method according to any one of claims 1 to 3,
The membrane-separated high-altitude water treatment apparatus includes a quadrangular reactor partitioned into four compartments,
A concentrating tank and a flow rate adjusting tank are disposed in the first compartment;
A stabilization tank, an anoxic tank and an anaerobic tank are disposed in the second compartment;
An aeration tank is arranged in the third compartment;
And a membrane separation tank and a discharge tank are disposed in the fourth compartment.
The method of claim 3,
Wherein the connection channels formed between the reaction vessels from the anoxic tank to the membrane separation tank are installed diagonally of the respective reaction vessels.

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