KR101580556B1 - Turbidity of hot water emiting from power plant reducing system - Google Patents
Turbidity of hot water emiting from power plant reducing system Download PDFInfo
- 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
- Prior art date
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 143
- 238000001914 filtration Methods 0.000 claims abstract description 203
- 239000013535 sea water Substances 0.000 claims abstract description 103
- 239000002351 wastewater Substances 0.000 claims abstract description 7
- 238000004062 sedimentation Methods 0.000 claims description 36
- 238000000034 method Methods 0.000 claims description 17
- 239000000463 material Substances 0.000 claims description 13
- 238000012937 correction Methods 0.000 claims description 12
- 239000002245 particle Substances 0.000 claims description 10
- 238000012546 transfer Methods 0.000 claims description 8
- 230000006872 improvement Effects 0.000 claims description 6
- 238000005452 bending Methods 0.000 claims description 5
- 230000001174 ascending effect Effects 0.000 claims description 4
- 238000004140 cleaning Methods 0.000 claims description 4
- 230000003247 decreasing effect Effects 0.000 claims description 4
- 239000000706 filtrate Substances 0.000 claims description 4
- 239000012530 fluid Substances 0.000 claims description 4
- 239000011521 glass Substances 0.000 claims description 4
- 238000007599 discharging Methods 0.000 claims description 2
- 238000005192 partition Methods 0.000 claims description 2
- 239000007921 spray Substances 0.000 claims description 2
- 239000013049 sediment Substances 0.000 claims 1
- 230000000630 rising effect Effects 0.000 abstract description 3
- 238000005406 washing Methods 0.000 abstract description 2
- 230000008021 deposition Effects 0.000 abstract 3
- 238000010521 absorption reaction Methods 0.000 abstract 1
- 230000002441 reversible effect Effects 0.000 description 14
- 230000008569 process Effects 0.000 description 7
- 239000000498 cooling water Substances 0.000 description 5
- 230000002265 prevention Effects 0.000 description 5
- 238000011001 backwashing Methods 0.000 description 4
- 238000011010 flushing procedure Methods 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 239000002826 coolant Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000005484 gravity Effects 0.000 description 3
- 238000002347 injection Methods 0.000 description 3
- 239000007924 injection Substances 0.000 description 3
- 239000004576 sand Substances 0.000 description 3
- 230000009471 action Effects 0.000 description 2
- 239000004927 clay Substances 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 238000010248 power generation Methods 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 235000014443 Pyrus communis Nutrition 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 210000001520 comb Anatomy 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 230000009191 jumping Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
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- 230000003449 preventive effect Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000032258 transport Effects 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
- C02F1/004—Processes for the treatment of water whereby the filtration technique is of importance using large scale industrial sized filters
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D33/00—Filters with filtering elements which move during the filtering operation
- B01D33/04—Filters with filtering elements which move during the filtering operation with filtering bands or the like supported on cylinders which are impervious for filtering
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D35/00—Filtering 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
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/11—Turbidity
Abstract
Description
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
A
The
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
The
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
The
In the
The second point is the
The
At this time, as an effect generated by filtering the seawater by the
The
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
The first entry of the seawater in the
At this time, the lower end of the
Therefore, since the
The seawater discharged from the
The filtering
The unit mesh size of the
Meanwhile, in the basic embodiment of the present invention, the
Therefore, in the basic embodiment, the mud particles passing through the
At this time, when the mud particles starting to accumulate at the lower end of the
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
Also, preferably, the
The
If the amount of the mud accumulated in the lower part of the
In addition, an
There may be a mud remaining in the
In the present invention, the mud of the inner wall of the
In the basic embodiment of the
This is because if the
Therefore, if the
In this case, if the
Particularly preferably, the mud which is caught by the
The
The inside of the
At this time, the first inlet of the seawater is the
The seawater flowing into the
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
The
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
As shown in FIG. 6, the
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
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
The
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
The backwashing process will be described later.
4, the seawater injected into the
When the seawater pressure in the
The filtered seawater that fills the inside of the
4, a filtered
By forming the
As described above, the seawater enters the
At this time, the water surface of the seawater filling the inside of the
When the seawater is supplied to the customer for the predetermined period of time, the mud is accumulated in the
As the inner pressure of the
When the seawater ascending through the
The seawater is injected into the
At this time, if the external pump is no longer activated, the seawater supplied to the
Herein, the force to reverse the flow of the seawater in the
The seawater flows backward from the
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
The sea water inside the
The air sucked into the
When air is sucked into the
Since the siphon operation can be stopped by the
The height of the lower end of the
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
Here, it is determined whether the seawater should pass through the second filtration device according to the measurement of the
If the
At this time, the three-
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
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 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 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.
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 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.
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 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 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:
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.
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 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.
Priority Applications (1)
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KR1020150080992A KR101580556B1 (en) | 2015-06-09 | 2015-06-09 | Turbidity of hot water emiting from power plant reducing system |
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KR1020150080992A KR101580556B1 (en) | 2015-06-09 | 2015-06-09 | Turbidity of hot water emiting from power plant reducing system |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101621295B1 (en) | 2016-01-13 | 2016-05-17 | 한일종합기계 주식회사 | A wastewater power plant cargo equipment sprinkling systems |
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KR100877309B1 (en) * | 2008-03-07 | 2009-01-07 | 주식회사 대금지오웰 | Cyclone settling apparatus and wheel washing machine utilizing thereof |
KR100897258B1 (en) * | 2008-11-05 | 2009-05-15 | 대일산업(주) | Draining unit for purifying the non-point pollution source in rainwater |
KR101173214B1 (en) * | 2012-02-23 | 2012-08-20 | 녹스 코리아(주) | Nonpower treatment device for drinkable water and waste water |
KR101494296B1 (en) * | 2014-08-01 | 2015-02-17 | 주식회사 가온텍 | A Non-power Automatic Back-washing Type Equipment for Decreasing Non-point Pollution of First Flush |
KR101516726B1 (en) | 2013-11-22 | 2015-05-04 | 이전웅 | Up-flow gravity continuous filter |
-
2015
- 2015-06-09 KR KR1020150080992A patent/KR101580556B1/en active IP Right Grant
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100877309B1 (en) * | 2008-03-07 | 2009-01-07 | 주식회사 대금지오웰 | Cyclone settling apparatus and wheel washing machine utilizing thereof |
KR100897258B1 (en) * | 2008-11-05 | 2009-05-15 | 대일산업(주) | Draining unit for purifying the non-point pollution source in rainwater |
KR101173214B1 (en) * | 2012-02-23 | 2012-08-20 | 녹스 코리아(주) | Nonpower treatment device for drinkable water and waste water |
KR101516726B1 (en) | 2013-11-22 | 2015-05-04 | 이전웅 | Up-flow gravity continuous filter |
KR101494296B1 (en) * | 2014-08-01 | 2015-02-17 | 주식회사 가온텍 | A Non-power Automatic Back-washing Type Equipment for Decreasing Non-point Pollution of First Flush |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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KR101621295B1 (en) | 2016-01-13 | 2016-05-17 | 한일종합기계 주식회사 | A wastewater power plant cargo equipment sprinkling systems |
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