KR101580556B1 - Turbidity of hot water emiting from power plant reducing system - Google Patents

Turbidity of hot water emiting from power plant reducing system Download PDF

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Publication number
KR101580556B1
KR101580556B1 KR1020150080992A KR20150080992A KR101580556B1 KR 101580556 B1 KR101580556 B1 KR 101580556B1 KR 1020150080992 A KR1020150080992 A KR 1020150080992A KR 20150080992 A KR20150080992 A KR 20150080992A KR 101580556 B1 KR101580556 B1 KR 101580556B1
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South Korea
Prior art keywords
filtration
tank
pipe
water
seawater
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KR1020150080992A
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Korean (ko)
Inventor
심수섭
이영남
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에너지관리기술(주)
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • C02F1/004Processes for the treatment of water whereby the filtration technique is of importance using large scale industrial sized filters
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D33/00Filters with filtering elements which move during the filtering operation
    • B01D33/04Filters with filtering elements which move during the filtering operation with filtering bands or the like supported on cylinders which are impervious for filtering
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D35/00Filtering devices having features not specifically covered by groups B01D24/00 - B01D33/00, or for applications not specifically covered by groups B01D24/00 - B01D33/00; Auxiliary devices for filtration; Filter housing constructions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/08Seawater, e.g. for desalination
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/11Turbidity

Abstract

Provided is a system for reducing turbidity of hot water emitted from a power plant maximizing quantity and quality of filtered seawater, by comprising a first filtering device (100) including a water collecting tank (101) where sea water is flowed in, a strainer (102), an absorption pipe (106), and a filtering chamber (104); a second filtering device (200) including a natural deposition tank (210) having multiple strainers (212a, 212b, 212c), a filtering water tank where the sea water is discharged from the natural deposition tank (210), a mud deposition tank (230), a venturi pipe (240), and a spray-washing pipe (242); and a third filtering device (300) including a countercurrent filtering tank (310), a wedge wire screen, filters (323a, 323b, 323c), a rising pipe (341) and a descending pipe (342) connecting an upper water tank (301), a lower water tank (303), a countercurrent pipe (343) connecting a filter tank (302) and a waste water tank (360), and a countercurrent stopping pipe (345).

Description

Technical Field [0001] The present invention relates to a turbidity improving system,

The present invention relates to a system for improving the turbidity of a ship water tank, and more particularly, to a turbine system for improving the turbidity of a power plant by using a multistage device to filter fine particles including mud contained in seawater discharged as a coolant in a power plant using seawater as a coolant And to a system for making use of pear hot water as a water temperature regulating water for a farm or a heat pump or water for cogeneration.

Generally, thermal power or nuclear power plants use seawater as cooling water.

At this time, the seawater used as the cooling water is taken from the deep sea because the temperature is low, and the collected seawater is used as a coolant for condensing the steam discharged from the end of the steam turbine in the cycle apparatus of the power plant.

On the other hand, gypsum, which is the seawater discharged after being used as cooling water in the power plant, is discharged at a high temperature, so it is often used for control of water temperature in the winter season in the surrounding farms. In addition, since the temperature of the hot water is high, in order to use the heat energy contained in the hot water, various heat pumps and hot water discharged from the power generation water are used in the cogeneration facilities.

However, since the sewage water discharged from the power plant is seawater collected from the deep sea water, a lot of clay components may be introduced depending on the condition of seawater, causing problems in various facilities using the sewage water, increasing the heat resistance, When the hot water is used, there is a problem that the turbidity of the fish farm is increased, which adversely affects fish farming.

In order to solve these problems, conventionally developed sewage water filtration apparatuses are classified into gravity filtration type and rapid filtration type.

The gravity filtration type is advantageous in reducing the quality of the filtrate and reducing the operation cost, but has a disadvantage in that the area occupied by the filtration device is too large. The rapid filtration type is advantageous in producing a large amount of filtrate in a short time, There is a drawback in that the maintenance effort of maintenance is relatively large.

On the other hand, in the conventional gravity filtration type or rapid filtration type, when the seawater containing a large amount of clay is filtered, the backwashing process must be performed frequently, so that the filtration efficiency is remarkably decreased and the problem that the filtration filter is damaged quickly due to backwash there was.

Therefore, it is required to have a flushing water filtration system in which the flushing water discharged from the power generation water can be filtered at a high efficiency while the filtration can be thoroughly performed, and the utilization of flushing water can be increased.

Patent Registration No. 10-1516726 (Registration date: May 24, 2015)

SUMMARY OF THE INVENTION Accordingly, the present invention has been made keeping in mind the above problems occurring in the prior art, and it is an object of the present invention to provide a filtration system capable of selecting a filtration step necessary for the amount of mud contained in the waste water of a power plant by multi-stage filtration, Water turbidity improving system capable of improving the turbidity of the flushing water with high efficiency.

In order to achieve the above object, the present invention provides a system for improving the turbidity of a water tank of a power plant, comprising a water collecting tank (101) into which seawater is discharged after being used as cooling water in a power plant, a strainer And a filtration chamber 104 which surrounds one end of the suction pipe 106 and a suction pipe 106 having one end disposed inside the water collecting tank 101 and the other end outside the water collecting tank 101, A filtration device 100,

A natural sedimentation tank 210 in which a plurality of filtration nets 212a, 212b and 212c through which the seawater discharged from the first filtration apparatus 100 are sequentially passed is installed inside and the bottom of the natural sedimentation tank 210 is opened; A mud sedimentation tank 230 connected to the bottom of the natural sedimentation tank 210 and decreasing stepwise as the horizontal cross-sectional area is lowered, a venturi pipe 230 connected to the lower end of the mud sedimentation tank 230, A second filtration device 200 composed of an injection cleaning pipe 242 branched from the venturi pipe 241 and leading into the mud sedimentation tank 230,

The filtration filter unit 302 and the lower water tank 303 are divided into an upper water tank 301, a lower filtration tank 302 and a lower water tank 303 in order from the upper part of the water tank, A wedge wire screen 321 inserted into the bottom of the filtration filter tank 302 in a plurality of rows and spaced apart from each other with the columns being inserted at different heights, Filtration filter materials 323a, 323b and 232c which are stacked on the bottom of the filtration filter tank 302 and made up of particles of different sizes and a rising pipe 323b which connects the upper water tank 301 and the lower water tank 303 A bending point S is formed between one end and the other end as a pipe connecting the filtration filter tank 302 and the waste water tank 360. The height of the bending point S A reverse water pipe 343 which is higher than the reciprocal filtration tank 310 and an upper filtration tank 301 branched from the upper end of the reverse water pipe 343, And a third filtration unit 300 composed of an inverse correction tube 345 which is introduced into the first filtration tank 345.

The present invention has the following effects.

First, the degree of improvement of the turbidity of the hot water is remarkably high by performing the three filtration steps, and the intermediate filtration step can be omitted by a simple operation depending on the state of the hot water, so that the filtration of the hot water can be performed quickly and efficiently.

Second, by applying the wedge wire type screen drum to the final filtration tank, the conventional PE Disc Plate filter is less durable due to the impact caused by the impact for a long period of use, and the problem of periodic nozzle filter inspection is solved.

Third, when the turbidity is high due to the high amount of mud contained in the hot water, the mud can be quickly removed by using the dust collecting tank and the venturi pipe, thereby supplying the intermediate filtered water to the final filtration tank.

Fourth, since the hot water is heavier than ordinary water, the height of the siphon tube is adjusted to be close to the height of the filtrate water discharge pipe, so that the reverse process is smoothly performed.

BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a diagram of an overall system of the present invention,
2 is a view showing a first filtration apparatus in the present invention,
3 is a view showing a second filtration apparatus according to the present invention,
4 is a view showing a third filtration apparatus in the present invention,
FIG. 5 is a plan view and a front view showing an arrangement of a wedge wire screen applied to a third filtration apparatus in the present invention,
6 is a front view and an inner plan view of one wedge wire screen according to the present invention,
7 is an enlarged view of a front view of Fig. 6,

Hereinafter, the present invention will be described in detail with reference to the accompanying drawings.

First, a basic embodiment of a turbine water purifying system according to the present invention will be briefly described. Next, the first to third filtration devices and the additional construction will be described in detail, and finally, the entire filtration process will be described .

First, the overall configuration of the present invention will be briefly described with reference to Figs. 1 to 4. Fig.

As shown in FIG. 1, the system for improving the turbine water temperature according to the present invention comprises a first filtration device, a second filtration device, and a third filtration device.

2, the first filtration apparatus 100 includes a water collection tank 101 into which seawater is discharged after being used as cooling water in a power plant, a strainer 102 installed at a point where seawater flows into the water collection tank 101, A suction pipe 106 having one end disposed inside the water collecting tank 101 and having the other end disposed outside the water collecting tank 101 and a filtration chamber 104 surrounding the one end of the suction pipe 106. [

The second filtration apparatus 200 includes a plurality of filtration nets 212a, 212b, and 212c through which the seawater discharged from the first filtration apparatus 100 is sequentially passed, as shown in FIG. 3, A sedimentation tank 210, a filtration water tank 220 in which seawater discharged from the natural sedimentation tank 210 is stored, a mud sedimentation tank 230 connected to the bottom of the natural sedimentation tank 210 and decreasing stepwise as the horizontal cross- A venturi pipe 241 connected to the lower end of the mud settling tank 230 and a jet washing pipe 242 branching from the venturi pipe 241 and leading into the mud settling tank 230.

The third filtration apparatus 300 is divided into an upper water tank 301, a filtration filter tank 302 and a lower water tank 303 in order from the upper part of the water tank connected to the second filtration apparatus 200, A reciprocal filtration tank 310 in which seawater is supplied to the filtration filter tank 302 from the filtration filter tank 200 and a plurality of columns arranged in the bottom of the filtration filter tank 302, A wedge wire screen 321 that is differently inserted into the upper water tank 301 and a filter filter material 323a, 323b, and 232c that are stacked on the bottom of the filter filter tank 302 and made of particles of different sizes, An ascending pipe 341 and a descending pipe 342 for connecting the filtering filter tank 302 and the waste water tank 360 to each other and a bent point S is formed between one end and the other end, The height of the inflection point S is higher than that of the reciprocating filtration tank 310 and the height of the inflow pipe 343 at the upper end of the back water pipe 343 Air filtration tank consists of an upper station modified tube 345 is drawn by 301. The

Thus, the basic structure and the connection relationship of the present invention have been described.

Hereinafter, the interaction between each configuration and the configuration will be described in detail.

The first filtration apparatus 100 is as shown in Fig.

The first filtration apparatus 100 is a first filtration apparatus to which sewage water discharged from a power plant meets, and performs a primary filtration.

In the first filtration apparatus 100, filtration occurs at two points. The first point is the inflow port of the seawater in which the strainer 102 is installed in the process of entering the water tank 101 into the water tank 101.

The second point is the filtration chamber 104 through which seawater exits to the outside of the catchment 101.

The filtration chamber 104 surrounds one end of the suction pipe 106, so that the seawater sucked into the suction pipe can not pass through. At this time, relatively large lumps or large particles among the mud components contained in the seawater are caught by the outer wall of the filter net making up the filtration chamber 104 and can not enter the filtration chamber 104.

At this time, as an effect generated by filtering the seawater by the filtration chamber 104, besides supplying the basically filtered seawater to the second or third filtration apparatuses 200 and 300, it also protects the blade of the pump that transports the seawater. Specifically, the pump to be protected is the first pump 402 to be described later.

The first pump 402 is preferably connected to the end of both ends of the suction pipe 106 exposed to the outside of the water collecting tank 101. The seawater discharged from the first pump (402) is transferred to the second filtration apparatus (200) or the third filtration apparatus (300) through the first conveyance pipe (400).

The connection between the pump and the piping between each filtration device itself is a well-known technology, so there is no need to mention it.

The present invention is characterized in that the first conveying pipe in the present invention is not directly connected to the second filtering device 200 but directly connects the first pump 402 and the third filtering device 300, The details will be described later in detail.

The first entry of the seawater in the second filtration apparatus 200 is the lower end of the branch supply pipe 403 branched from the first transfer pipe 400 and introduced into the natural sedimentation tank 210 as shown in FIG. .

At this time, the lower end of the branch supply pipe 403 is preferably provided with the anti-scattering box 214. The shatterproof box 214 is to prevent seawater from being scattered too far and jumping over the filter nets 212a, 212b, and 212c.

Therefore, since the scattering prevention box 214 is primarily intended to prevent scattering rather than filtration, the material of the scattering prevention box may be composed of combs arranged at intervals much larger than the unit mesh sizes of the filtering nets 212a, 212b and 212c.

The seawater discharged from the scattering prevention box 214 initially falls into the mud sedimentation tank 230 under the natural sedimentation tank 210. The seawater discharged from the scattering prevention box 214 passes through the filtration nets 212a, 212b and 212c in order to enter the filtration water tank 220 from the time when the mud sedimentation tank 230 almost reaches the sea water.

The filtering nets 212a, 212b, and 212c are shown as three in FIG. 3, but are not necessarily limited to three.

The unit mesh size of the filtering nets 212a, 212b, and 212c is preferably gradually smaller as the distance from the scatter preventive box 214 increases. Thus, seawater is gradually filtered from large particles to small particles.

Meanwhile, in the basic embodiment of the present invention, the filtering nets 212a, 212b and 212c are vertically erected and the bottom of the natural sedimentation tank 210 is opened.

Therefore, in the basic embodiment, the mud particles passing through the filtering nets 212a, 212b, and 212c through the seawater and not passing through the filtering nets 212a, 212b, and 212c are precipitated downward, It starts.

At this time, when the mud particles starting to accumulate at the lower end of the mud sedimentation tank 230 are gathered and accumulated to a certain area, the venturi pipe 241 is operated to instantaneously remove the mud lumps and discharge them to the sea.

Here, the venturi pipe 241 may be a well-known compression pump, though not shown, for the operation of the venturi pipe 241 as a pipe for forming a bottleneck section in which the cross-sectional area is rapidly narrowed and then rapidly expanded.

At this time, one end of the venturi pipe 241 is connected to the first conveyance pipe 400 to receive the seawater, and the fluid to be injected at a high speed into the venturi pipe 240 for removing the mud in the mud sedimentation tank 230 Is the seawater transferred through the first conveyance pipe (400).

Also, preferably, the site glass 251 may be installed below the mud sedimentation tank 230 as shown in FIG.

The sight glass 251 is provided at an upper end of an observation window for observing a state where the mud is accumulated in the mud sedimentation tank 230 so that it is necessary to operate the venturi pipe 240 according to the inner state of the mud sedimentation tank 230 It provides data for judging whether or not

If the amount of the mud accumulated in the lower part of the mud settling tank 230 exceeds a certain level, the mud may not easily be discharged even when the venturi pipe 240 is operated, so that the mud in the mud settling tank 230 This is because the accumulation situation must be observed.

In addition, an injection cleaning pipe 242 branched from the venturi pipe 240 is provided at a certain portion of the venturi pipe 240.

There may be a mud remaining in the mud settling tank 230 after the mud settling vessel 230 is discharged by the operation of the venturi pipe 240 and the remaining mud may be removed so that the re- So that it does not become entangled with the inner wall of the base 230.

In the present invention, the mud of the inner wall of the mud settling tank 230 can be easily removed by providing the spray cleaning pipe 242.

In the basic embodiment of the filter banks 212a, 212b and 212c described above, the filter banks 212a, 212b and 212c are arranged in the vertical direction. Preferably, however, the filter banks 212a, 212b and 212c Is inclined so as to be inclined toward the sea water flow direction.

This is because if the filtration nets 212a, 212b and 212c are vertically erected, the natural sedimentation tank 210 can be lowered directly below the filtration nets 212a, 212b and 212c. In this case, some of the seawater descending to the lower part may flow back to the filter water tank 220 closer to the filtration tank 220, because the filtration efficiency may be lowered since the mud is not filtered except for natural sedimentation .

Therefore, if the filter nets 212a, 212b, and 212c are inclined as shown in FIG. 3 in the sea water flow direction, the filtration efficiency can be further increased.

In this case, if the bottom filtration nets 213a, 213b, and 213c are formed on the bottom between the filtration nets 212a, 212b, and 212c, the reverse flow of the seawater is reversed while the filtration efficiency is higher.

Particularly preferably, the mud which is caught by the bottom filter nets 213a, 213b and 213c and does not fall off when the bottom filtering nets 213a, 213b and 213c are hinged to the filtering nets 212a, 212b and 212c .

The third filtration apparatus 300 is a filtration apparatus in which foreign matter after filtration can be automatically discharged from a filtration tank by using a siphon principle.

The inside of the reciprocating filtration tank 310 is divided into an upper water tank 301, a filtration filter tank 302 and a lower water tank 303 from the upper part.

At this time, the first inlet of the seawater is the filtration filter tank 302 positioned at the middle height.

The seawater flowing into the filtration filter tank 302 is filtered by two filtration means.

The first filtration means is filtration filter material (323a, 323b, 323c) filled in the filtration filter vessel (302), and the remaining filtration means is a wedge wire screen (321).

The wedge wire screen 321 is disposed at the interface between the filtration filter tank 302 and the lower water tank 303 below the wedge wire screen 321 so that the seawater flows through the filtration filter materials 323a, 323b, and 232c stacked on the bottom of the filtration filter tank 302, Lt; / RTI >

The filtration filter materials 323a, 323b and 323c are composed of the lowest fine sand layer 323c, the intermediate sand layer 323b and the uppermost coarse sand layer 323a, as shown in FIG.

The filtration filter material is arranged in a small particle size along the sedimentation direction of the seawater, so that the seawater is filtered stepwise.

The seawater filtered by the filtration filter materials 323a, 323b, and 232c is finally filtered by the wedge wire screen 321 and flows into the lower water tank 303.

As shown in FIG. 6, the wedge wire screen 321 is a filter in which a drum is formed in an upper portion and a water pipe is formed in a lower portion.

6 is a cross-sectional view of the left front view taken along the connecting line of A and B on the right side of FIG. 5B.

6, the wedge forming frame is formed along the outer circumferential surface. At this time, the wedge is installed on the outer circumferential surface, but the sharp blade portion of the end is directed toward the inner center, so that the mud particles or other foreign matter are prevented from entering the outer circumferential surface.

In particular, when the arrangement of the wedge wire screen 321 is arranged as shown in Fig. 5, the filtration efficiency can be dramatically improved.

That is, the wedge wire screens 321 are arranged in parallel with each other, and the wedge wire screens 321 are arranged in a state in which the plurality of wedge wire screens 321 are arranged side by side, ) Can all be used for filtration.

In addition, in order for the wedge wire screen 321 to be in contact with more seawater at one time, the installation height of the wedge wire screen 321 is different from that of the adjacent wirings in the heat of the wedge wire screen 321, Or the wedge wire screen 321 can be completely eliminated.

The wedge wire screen 321 has an effect of remarkably improving the durability in comparison with the conventional PE plate screen in backwashing process in particular.

As the backwashing process will be described later, the direction of the sea water flows in the opposite direction to the filtering direction, so that the sea water exits from the center to the outer circumferential surface when viewed from the right section of FIG.

At this time, the seawater rises together with the foreign matter while shaking off foreign matters on the outer circumferential surface of the wedge wire screen 321. Here, since the seawater comes into contact with the wedge shape, there is no fear that the wedge wire screen 321 is damaged due to the collision of strong seawater.

The backwashing process will be described later.

4, the seawater injected into the filter filter tank 302 is filtered by the filter filter materials 323a, 323b, and 323c and then passes through the wedge wire screen 321, And enters the water tank 303.

When the seawater pressure in the lower water tank 303 is gradually increased as the filtered seawater fills the inside of the lower water tank 303, the seawater in the lower water tank 303 rises along the uprising pipe 341 and flows into the upper water tank 304 .

The filtered seawater that fills the inside of the upper water tank 304 is supplied to a customer who needs filtered seawater.

4, a filtered water discharge pipe 314 for discharging the filtered seawater to the filtered water consumer is connected to the upper water tank 301 and surrounds the end of the filtered water discharge pipe 314 in the upper water tank 301 And an overflow chamber 311 having an open upper portion can be formed.

By forming the overflow chamber 311, a certain water level is maintained in the upper water tank 301.

As described above, the seawater enters the filtration filter tank 302, is filtered by the filtration filter tank 302 and then flows into the lower water tank 303 to fill the interior of the lower water tank 303, When the internal pressure is increased, the water flows into the upper water tank 301 through the uprising pipe 341 connecting the lower water tank 303 and the upper water tank 301.

At this time, the water surface of the seawater filling the inside of the upper water tank 301 is gradually increased along the uprising pipe 341 to overflow into the overflow chamber 311, and the seawater is taken in the filtered water discharge pipe 314, Is supplied.

When the seawater is supplied to the customer for the predetermined period of time, the mud is accumulated in the filtration filter tank 302 due to the filtration, and the inside of the filtration filter tank 302 is gradually filled with the mud.

As the inner pressure of the filtration filter tank 302 increases as the mud is filled in the filtration filter tank 302, the seawater in the filtration filter tank 302 does not descend to the lower water tank 303, (343).

When the seawater ascending through the backwater pipe 343 passes the bending point S of the backwater pipe 343, the inside of the backwater pipe 343 is completely filled with seawater and is no longer filled with the filter filter vessel 302 The water in the filtration filter tank 302 is continuously sucked in without any internal pressure increase.

The seawater is injected into the filtration filter tank 302 by the force of the pump provided outside the reciprocating filtration tank 310 until the bending point S of the backwater pipe 343 is reached, (S) point, the reverse water pipe (343) continues to draw in the seawater even if no seawater is injected by the force of the pump.

At this time, if the external pump is no longer activated, the seawater supplied to the filtration filter tank 302 is not supplied from the outside but the seawater in the lower tank 303 below the filtration filter tank 302 flows backward, And is introduced into the filter tank 302.

Herein, the force to reverse the flow of the seawater in the lower water tank 303 to the filtration filter tank 302 is a downward pipe connecting the upper water tank 301 and the lower water tank 303 due to the pressure of the seawater filled in the upper water tank 301 342 in the lower water tank 303 due to seawater flowing down through the lower water tank 303.

The seawater flows backward from the lower water tank 303 to the filtration filter tank 302 so that the wedge wire screen 321 and the filter filter materials 323a, 323b, And is discharged to the waste water tank 360 together with the seawater along the reverse water pipe 343.

This allows the mud to be released automatically by filtration, without the need for a separate mud or other foreign material discharge device.

However, once the mud or other foreign substances deposited in the filtration filter tank 302 is discharged, the filtration should proceed again. At this time, the inverse correction tube 345 stops the inhalation action of the backwater tube 343 so that the filtration can proceed again.

The sea water inside the upper water tank 301 is returned to the lower water tank 303 along the downfalling pipe 342 and the water level inside the upper water tank 301 gradually decreases and becomes lower than the lower end of the reverse correction branch pipe 345 Air is sucked into the inverse correction tube 345 from the end of the inverse correction tube 345.

The air sucked into the inverse correction tube 345 rises to the point where the reverse correction tube 345 and the reverse water pipe 343 meet, and the air is sucked into the reverse water pipe 343.

When air is sucked into the backwater pipe 343, an empty space filled with air is formed at the inflection point S of the backwater pipe 343 to stop suction by the backwater pipe 343. That is, the siphon action is interrupted.

Since the siphon operation can be stopped by the inverse correction tube 345, the reverse water amount by the siphon can be adjusted by adjusting the height of the lower end of the inverse correction tube 345.

The height of the lower end of the inverse correction tube 345 is determined by the capacity of the filtration filter tank 302 in the present invention.

This explains the process of removing the foreign matter accumulated during the final filtration process and the filtration process of the seawater.

On the other hand, in the present invention, the amount of mud contained in the seawater flowing into the first filtration apparatus for filtration is not constant, so it is necessary to take flexible measures according to the mud content of the seawater.

That is, when the amount of mud contained in seawater is large, it is necessary to operate all of the first to third filtration apparatuses in a phased manner, while in the case where the amount of mud is not large, a second filtration apparatus So that the sea water does not pass through.

Here, the second filtration device can be formed as a separate component by characterizing the transfer part through which the seawater is transferred so that the seawater can pass through without passing through the seawater.

1 to 4, the transfer unit includes a first pump 402 installed at the other end of the suction pipe 106 of the first filtration apparatus 100, a first pump 402 and a filtration filter tank 302 A branch feed pipe 403 branching from the first feed pipe 400 and leading into the natural sedimentation tank 210 and a turbidity sensor (not shown) installed in the first feed pipe 400. The first feed pipe 400, A second conveyance pipe 430 for connecting the filtration water tank 220 and the first conveyance pipe 400 to the first conveyance pipe 430 and the second conveyance pipe 430 for connecting seawater of the filtration water tank 220 to the first conveyance pipe 430, A second pump 406 for transferring the turbidity measured by the turbidity sensor 424 to the conveyance pipe 400 and a turbidity sensor 424 provided at a position where the branch pipe 403 branches from the first conveyance pipe 400, The branch feed pipe 403 is shut off and the first feed pipe 400 and the filtration filter tank 302 are opened to open the branch feed pipe 403 and the first feed pipe 400, (30 And a three-way valve (421) for shutting off between the two valves (4).

Here, it is determined whether the seawater should pass through the second filtration device according to the measurement of the turbidity sensor 424 shown in Fig.

If the turbidity sensor 424 exceeds a certain limit, the seawater is passed through the second filtration device so that the mud is removed at a time in a short time because the seawater contains a lot of mud.

At this time, the three-way valve 421 shown in Fig. 3 is used to change the path of the seawater flow. Although not the three-way valve 421 shown in FIG. 3, the control of the fluid flow is not a conventional technique, and the adoption of other applicable known techniques is not excluded.

Therefore, in the present invention, by controlling the flow of the seawater in a flexible manner according to the state of the seawater, the efficiency of the seawater filtration can be maximized, and the quality of the seawater filtered through the stepwise filtration can be remarkably improved.

It will be apparent to those skilled in the art that various modifications and variations can be made in the present invention without departing from the spirit or scope of the inventions. It will be apparent to those of ordinary skill in the art.

F1, F2, F3, F4: Wedge wire screen column S: Flexure
100: first filtration device 101: water collecting tank
102: Strainer 104: Filtration chamber
106: suction pipe 112: partition wall
114: overflow window 200: second filtration device
210: Natural sedimentation tank (210) 212a, 212b, 212c:
213a, 213b, 213c: floor filter network 214: scattering prevention box
220: filtration tank 221: second suction pipe
230: Mud settling tank 240: Venturi tube
242: jet wash pipe 243: bottleneck section
251: Sight glass 300: Third filtration device
301: Upper water tank 302: Filtration filter tank
303: Lower water tank 304: Sea water injection pipe
310: reciprocal filtration tank 311: overflow chamber
314: Filtration water discharge pipe 321: Wedge wire screen
322: bottoms of filtration filter bases 323a, 323b, 323c:
341: rising pipe 342: falling pipe
343: reverse water pipe 344: guide plate
345: Reverse correction tube 355: Air discharge tube
360: waste water tank 400: first transfer pipe
402: first pump 403: branch supply pipe
406: Second pump 421: Three-way valve
424: turbidity sensor 430: second conveyance pipe

Claims (11)

A strainer 102 installed at a point where seawater flows into the water collecting tank 101 and a strainer 102 installed at one end inside the water collecting tank 101 and connected to the water collecting tank 101 A first filtration device (100) comprising a suction pipe (106) in which the other end is disposed outside the suction pipe (101) and a filtration chamber (104) surrounding one end of the suction pipe (106);
A natural sedimentation tank 210 in which a plurality of filtration nets 212a, 212b and 212c through which the seawater discharged from the first filtration apparatus 100 are sequentially passed is installed inside and the bottom of the natural sedimentation tank 210 is opened; A mud sedimentation tank 230 connected to the bottom of the natural sedimentation tank 210 and decreasing stepwise as the horizontal cross-sectional area is lowered, a venturi pipe 230 connected to the lower end of the mud sedimentation tank 230, A second filtration apparatus 200 comprising a spray cleaning pipe 242 branching from the venturi pipe 240 and entering the mud sedimentation tank 230;
The filtration filter unit 302 and the lower water tank 303 are divided into an upper water tank 301, a lower filtration tank 302 and a lower water tank 303 in order from the upper part of the water tank, A wedge wire screen 321 inserted into the bottom of the filtration filter tank 302 in a plurality of rows and spaced apart from each other with the columns being inserted at different heights, Filtration filter materials 323a, 323b and 232c which are stacked on the bottom 322 of the filtration filter tank 302 and composed of particles of different sizes and an upper water tank 301 and a lower water tank 303 A bending point S is formed between one end and the other end as a tube connecting the uprising pipe 341 and the downfalling pipe 342 and the filter filter tank 302 and the waste water tank 360, The height of the backwater tube 343 is higher than that of the reciprocal filtration tank 310 and the height of the upper water tank 30 And a third filtering device 300 comprising an inverse correction tube 345 which is inserted into the first filtering device 300,
An outlet 221 through which the seawater can pass through the filtration water tank 220 is formed in the wall of the natural sedimentation tank 210 at a point where the filtration water tank 220 and the natural sedimentation tank 210 face each other in the second filtration apparatus 200 The mesh sizes of the filter nets 212a, 212b and 212c are arranged such that the mesh sizes of the filter nets 212a, 212b and 212c are set such that the mesh sizes of the filter nets 212a, 212b and 212c are Wherein the filtration nets (212a, 212b, 212c) are stepwise reduced as they are further away from the branch supply pipe (403), and the filtration nets (212a, 212b, 212c) are inclined to tilt toward the outlet Turbidity water turbidity improvement system.
The method according to claim 1,
The first filtration apparatus 100 is provided with a partition wall 112 for separating the lower portion of the space for installing the strainer 102 and the space for installing the seawater suction pipe 106 inside the water collecting tank 101, Characteristics of a seawater-based power plant turbine water turbidity improvement system.
The method according to claim 1,
Wherein the first filtration apparatus (100) is formed with an overflow window (114) at one point in the upper part of the water collecting tank (101).
The method according to claim 1,
The second filtration apparatus (200) further includes a sight glass (251) installed at a lower end of the mud sedimentation tank (230) and having a window for observing the amount of mud sediment.
delete The method according to claim 1,
And bottom filtering nets (213a, 213b, 213c) formed of a mesh having the same size as the mesh size of the filter net disposed on the side of the branch supply pipe (403) are disposed on the bottom surface between the filtering nets (212a, 212b, 212c) Power plant ship water turbidity improvement system
The method according to claim 6,
The bottom filtration nets 213a, 213b and 213c are hinged to any one of the filtration nets 212a, 212b and 212c adjacent to the bottom filtration nets 213a, 213b and 213c and can be opened into the mud sedimentation tank 230 Turbidity improvement system of power plant.
The method according to claim 1,
The third filtration apparatus 300 includes an ascending check valve installed in the uprising pipe 341 to allow only the flow of the ascending fluid to pass therethrough and a descending check valve installed in the descending pipe 342 to allow only the flow of the descending fluid to pass therethrough Wherein the turbidity improving system further comprises:
The method according to claim 1,
A first pump 402 installed at the other end of the suction pipe 106 of the first filtration apparatus 100, a first transfer pipe 400 connecting the first pump 402 and the filter filter tank 302, A branching pipe 403 branching from the first transfer pipe 400 and leading into the natural sedimentation tank 210, a turbidity sensor 424 installed in the first transfer pipe 400, a filtration water tank 220, A second conveyance pipe 430 connected to the first conveyance pipe 400 and a second pump installed in the second conveyance pipe 430 to convey the seawater of the filtration water tank 220 to the first conveyance pipe 400, And the first feed pipe 403 and the branch pipe 403 are branched from the first feed pipe 400. When the turbidity measured by the turbidity sensor 424 is lower than the tolerance, A three-way valve (not shown) for opening the branch supply pipe 403 and shutting off the first transfer pipe 400 and the seawater injector 304 when the turbidity is higher than an allowable value, 421) Eojineun conveyance; plant-fold water turbidity improved system according to claim 1, further comprising a.
The method according to claim 1,
And a guide plate 344 is attached to the end of the end portion disposed inside the filtration filter tank 302 in the backwater pipe 343 to prevent the filtration filter materials 323a, 323b and 232c from being introduced. Hot water turbidity improvement system.
The method according to claim 1,
The upper water tank 301 is connected to a filtered water discharge pipe 314 for discharging the filtered water to the consumer of filtrate water and an overflow chamber 311 surrounding the end of the filtered water discharge pipe 314 and having an open upper portion is disposed in the upper water tank 301 And the turbidity of the turbine is reduced.
KR1020150080992A 2015-06-09 2015-06-09 Turbidity of hot water emiting from power plant reducing system KR101580556B1 (en)

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