KR101772913B1 - Mobile apparatus for water treatment - Google Patents

Mobile apparatus for water treatment Download PDF

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Publication number
KR101772913B1
KR101772913B1 KR1020150180732A KR20150180732A KR101772913B1 KR 101772913 B1 KR101772913 B1 KR 101772913B1 KR 1020150180732 A KR1020150180732 A KR 1020150180732A KR 20150180732 A KR20150180732 A KR 20150180732A KR 101772913 B1 KR101772913 B1 KR 101772913B1
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South Korea
Prior art keywords
contaminated water
unit
water
space
processing unit
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KR1020150180732A
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Korean (ko)
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KR20170072502A (en
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김수홍
김가람
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(주)에스지알테크
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Publication of KR20170072502A publication Critical patent/KR20170072502A/en
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    • C02F9/005
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D21/00Separation of suspended solid particles from liquids by sedimentation
    • B01D21/24Feed or discharge mechanisms for settling tanks
    • B01D21/2433Discharge mechanisms for floating particles
    • B01D21/2438Discharge mechanisms for floating particles provided with scrapers on the liquid surface for removing floating particles
    • 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
    • B01D35/02Filters adapted for location in special places, e.g. pipe-lines, pumps, stop-cocks
    • 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
    • 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
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • 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
    • C02F1/38Treatment of water, waste water, or sewage by centrifugal separation
    • 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
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • 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
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/36Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
    • C02F2103/365Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/008Mobile apparatus and plants, e.g. mounted on a vehicle

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Analytical Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The present invention relates to a mobile water treatment apparatus having mobility and improved water treatment efficiency. A mobile water treatment apparatus according to an embodiment of the present invention includes a vehicle, a pretreatment unit, a separation unit, and an adsorption unit. Here, the vehicle has a mounting portion in which a first space is formed. The pretreatment unit is installed in the first space, and the contaminated water flows in from the outside and the air is mixed with the contaminated water. The separation part is installed in the first space, and separates the oil and sludge from the contaminated water flowing through the pretreatment part. The adsorption unit is installed in the first space, and adsorbs and removes the refractory material from the contaminated water flowing through the separation unit.

Description

[0001] MOBILE APPARATUS FOR WATER TREATMENT [0002]

The present invention relates to a mobile water treatment apparatus, and more particularly, to a mobile water treatment apparatus having mobility and improved water treatment efficiency.

In general, wastewater from the petrochemical industry, which accounts for the largest percentage of refractory materials, is generated in various processes and contains mainly hydrocarbon-type substances. There are dozens or more kinds of refractory materials existing in the wastewater, and there exist detectable concentrations of aromatic materials in the effluent of the wastewater treatment process and exist in the form of coloring matter or oil emulsion. .

In order to treat such refractory materials, separation using reverse osmosis (R / O), activated carbon adsorption, and removal method using an oxidizing agent such as Fenton have been proposed and applied. However, , And iron salt sludge generation. Since the treatment cost is high, it is diluted with a large amount of wastewater generated in the cooling water system and discharged.

In general, the emission of decomposable substances is minimized through processes such as pretreatment, biological treatment and post-treatment in consideration of economical efficiency and treatment efficiency. However, wastewater polluted mainly with oil decreases the activity of microorganisms, There are many difficulties in applying the treatment method.

In addition, in the case of activated carbon adsorption, which is known to have high removal efficiency, adsorption speed is slow and retention time is kept long, so excessive design of adsorption tower is pointed out as a problem.

In addition, the adsorbed activated carbon is reused in the field through regeneration treatment outside the treatment site using heat treatment, or chemical regeneration using steam backwashing and isopropanol.

However, since mass loss occurs during the regeneration process and the regeneration yield is as low as 70 ~ 85% of the initial adsorption amount, repeated use is almost impossible.

Further, since waste liquid generated during the chemical regeneration process must be disposed of separately, additional waste disposal costs may occur.

Therefore, although the adsorbent can be regenerated directly from the adsorption tower, there is no interruption of the wastewater treatment process due to the regeneration of the adsorbent, and even if the adsorbent is regenerated in some adsorption towers, a technique capable of implementing a continuous wastewater treatment process through other adsorption towers is required have.

On the other hand, the conventional water treatment facility is installed in a fixed place. However, the generation of polluted water is not limited to a specific place even if a river is taken as an example. Therefore, even if polluted water is generated, rapid water treatment is difficult. Therefore, there is a need for a method for enabling rapid water treatment in the case of contaminated water.

Korean Patent Publication No. 2011-0004142 (Jan. 13, 2011) Japanese Laid-Open Patent Publication No. 1994-178987 (Jun. 28, 1994)

In order to solve the above problems, a technical object of the present invention is to provide a mobile water treatment apparatus having mobility and improved water treatment efficiency.

According to an aspect of the present invention, there is provided a vehicle comprising: a vehicle having a mounting portion in which a first space is formed; A pretreatment unit installed in the first space to process the polluted water flowing in from the outside into the contaminated water to be mixed with air; A separating unit installed in the first space and separating oil and sludge from the polluted water flowing through the pretreatment unit; And a suction unit installed in the first space and adsorbing and removing the refractory material from the contaminated water flowing through the separation unit.

According to an embodiment of the present invention, the pretreatment unit may include a filter for filtering foreign substances from the polluted water flowing from the outside, a mixing tank for pressurizing and mixing the air supplied from the outside to the polluted water introduced through the filter, A pump for providing a pressure such that the contaminated water flows through the filter, the mixed tank and the dissolved air floating portion; and a pump for selectively compressing the mixed tank and the pump And an air compressor for supplying air.

According to an embodiment of the present invention, the separator may include a housing having a second space formed therein, and a second space provided at one side of the second space to receive the contaminated water discharged from the pre- And a second screen member provided in the second space and partitioned by the first screen member to separate the foreign matter from the contaminated water flowing through the first screen member And a second processing unit provided in the second space with the second screen unit by the second screen member, wherein the foreign matter from the contaminated water flowing through the second screen member is divided into third And a third processing unit provided in the second space and partitioned by the third processing unit so as to allow the foreign matter to be adsorbed and separated from the polluted water flowing over the partition wall And a fourth treatment unit provided with the first adsorbent.

In one embodiment of the present invention, the first processing unit is provided so as to penetrate through one side of the housing, and one end thereof is connected to the pre-processing unit to guide polluted water discharged from the pretreatment unit into the second space A cover part connected to the other end of the guide part in the second space and formed in a container shape in which the lower part is opened to guide the polluted water discharged through the guide part to be discharged to the lower part, And a vortex generating part formed in a spiral shape to generate a vortex.

According to an embodiment of the present invention, the second processing unit may include a first hill part having a concave upward projecting shape and having a first through hole formed at an upper end thereof, a second concave hole having a shape recessed downwardly, A first separating pack which is composed of a plurality of first plates repeatedly formed in a horizontal direction and which are stacked at predetermined intervals along a vertical direction to separate oil and sludge of polluted water, And a first skimmer which is provided to cross the housing at a water surface height of water and to remove the oil floating on the water surface of the contaminated water.

According to an embodiment of the present invention, the third processing unit may include a second hill having a shape protruding upward concave and having a third through-hole formed at an upper end thereof, a second hill having a shape recessed downward, A second separating pack which is composed of a plurality of second plates repeatedly formed in the horizontal direction and which are stacked at predetermined intervals along the vertical direction to separate oil and sludge of the contaminated water, And a second skimmer which is provided to cross the housing at a water surface height of water so as to remove the oil floating on the water surface of the contaminated water.

In an embodiment of the present invention, the fourth processing unit may include a receiving unit connected to the barrier rib to receive the polluted water flowing through the barrier ribs, a plurality of connecting members connected to the receiving unit, And a first adsorbent which is provided at a lower portion of the branch portion and allows the foreign substances to be adsorbed and separated from the polluted water falling over and falling down from the branch passage, .

In one embodiment of the present invention, a first outlet for a lower portion of the housing corresponding to the first processing unit is provided for discharging foreign matter separated from contaminated water, and a lower portion of the housing corresponding to the third processing unit A second outlet may be provided.

In one embodiment of the present invention, a high-pressure gas is supplied into the second space below the housing corresponding to the second processing unit and the third processing unit to clean the first and second separation packs For example.

In an embodiment of the present invention, a resupply unit for separating contaminated water and oil carried through the first skimmer provided in the second processing unit and the second skimmer provided in the third processing unit is provided outside the housing .

According to an embodiment of the present invention, the re-splitting unit may include a chamber provided outside the housing, and a second skimmer disposed at an outer portion of the housing to discharge polluted water and oil discharged from the first skimmer and the second skimmer into the chamber. A cylindrical shielding portion provided in a vertical direction inside the chamber and having a lower end portion connected to a bottom surface of the chamber; a cylindrical shielding portion formed below the shielding portion, A dam portion formed at an upper portion of the blocking portion to form a receiving space at an upper portion of the blocking portion, and a dam portion provided at a lower portion of the chamber and connected to the inside of the blocking portion, A third discharge port for discharging the inner process water; and a second discharge port provided on the front surface of the chamber so as to be connected to the accommodation space, Is introduced to block the overflow portion may have a fourth outlet port such that the oil is discharged to be accommodated in the accommodation space.

In an exemplary embodiment of the present invention, the adsorption unit may include an inlet port through which the polluted water passing through the separating unit flows, an upper portion of which is open, an outlet port through which the polluted water flowing into the inlet port is discharged, A lid part which is detachably attached to the upper part of the container part to open and close the upper part of the container part and an adsorption module which is provided inside the container part to adsorb the refractory material of the contaminated water flowing into the inlet part.

In one embodiment of the present invention, the lid portion has a plurality of slits formed on the outer circumferential surface at predetermined intervals along the circumferential direction and having a predetermined length along the radial direction, and the container portion is provided at an upper end portion of the container portion, A first flange having a support portion provided at a position corresponding to the slit along the slit; a rotation bar provided at the support portion and inserted into the slit while one end of the engagement shaft is engaged with the engagement shaft, And a tightening portion that is screwed to the other end portion and presses the lid portion in a state where the rotary bar is inserted into the slit to fix the lid portion to the container portion.

According to an embodiment of the present invention, the adsorption module may further include a receiving portion for receiving the second adsorbent, a second flange detachably coupled to the coupling rib protruding from the inside of the container portion, And a perforated plate provided at the upper and lower portions of the accommodating portion and having a plurality of through holes for allowing the contaminated water to move.

In one embodiment of the present invention, the adsorption unit includes a plurality of first adsorption units, a first pipe line connected to the main line for guiding the movement of the treated water through the separation unit and connected to the outlets of the plurality of adsorption units, A second pipe line connected to an inlet of one of the adsorption units of the adsorption unit and branched at a first pipe line portion connected to an outlet of the other adsorption unit and connected to an inlet of the other adsorption unit And may be arranged in series including the third piping line.

In one embodiment of the present invention, the plurality of adsorption units disposed in series may be provided, and each of the adsorption units arranged in series may be arranged in parallel with the main line branched.

According to an embodiment of the present invention, since the pretreatment unit, the separation unit, and the adsorption unit for treating the contaminated water are provided in the vehicle, it is possible to move to the area where the polluted water has been generated,

Also, according to an embodiment of the present invention, a plurality of adsorption units can be arranged in series, and the adsorption units arranged in series can be arranged in parallel. By arranging the adsorption portions in series and in parallel, it is possible to improve the treatment efficiency by continuously performing the regeneration of the adsorbent of some adsorption portions different from the breakage point while continuously processing the refractory materials through the different adsorption portions.

It should be understood that the effects of the present invention are not limited to the above effects and include all effects that can be deduced from the detailed description of the present invention or the configuration of the invention described in the claims.

1 is a front view illustrating a mobile water treatment apparatus according to an embodiment of the present invention.
2 is a plan view illustrating a mobile water treatment apparatus according to an embodiment of the present invention.
3 is a block diagram illustrating a mobile water treatment apparatus according to an embodiment of the present invention.
4 is a view illustrating an exemplary pretreatment unit of a mobile water treatment apparatus according to an embodiment of the present invention.
5 is a front view illustrating a separating unit of a mobile water treatment apparatus according to an embodiment of the present invention.
6 is a cross-sectional view illustrating a separation unit of a mobile water treatment apparatus according to an embodiment of the present invention.
7 is a plan view illustrating a separation unit of a mobile water treatment apparatus according to an embodiment of the present invention.
8 is a sectional view taken along the line AA in Fig.
FIG. 9 is a side view illustrating a separation unit of a mobile water treatment apparatus according to an embodiment of the present invention.
10 is a cross-sectional view illustrating a re-separation unit of a mobile water treatment apparatus according to an embodiment of the present invention.
11 is a view illustrating an adsorption unit of a mobile water treatment apparatus according to an embodiment of the present invention.
12 is a cross-sectional view illustrating an adsorption unit of a mobile water treatment apparatus according to an embodiment of the present invention.
13 is an exploded cross-sectional view illustrating an adsorption unit of a mobile water treatment apparatus according to an embodiment of the present invention.
FIG. 14 is an exemplary view showing an example of the arrangement of a suction portion of a mobile water treatment apparatus according to an embodiment of the present invention.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described with reference to the accompanying drawings. The present invention may, however, be embodied in many different forms and should not be construed as limited to the embodiments set forth herein. In order to clearly illustrate the present invention, parts not related to the description are omitted, and similar parts are denoted by like reference characters throughout the specification.

Throughout the specification, when a part is referred to as being "connected" to another part, it includes not only "directly connected" but also "indirectly connected" . Also, when an element is referred to as "comprising ", it means that it can include other elements, not excluding other elements unless specifically stated otherwise.

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

In an embodiment of the present invention, for convenience, water flowing into the water treatment unit based on the water treatment unit described above is expressed as 'polluted water', and water discharged and discharged from the water treatment unit can be expressed as 'treated water'. Therefore, in the water treatment process, the treated water that has been treated in the preceding water treatment section can be expressed as the contaminated water when it flows into the next water treatment section.

FIG. 1 is a front view illustrating a mobile water treatment apparatus according to an embodiment of the present invention, FIG. 2 is a plan view illustrating a mobile water treatment apparatus according to an embodiment of the present invention, FIG. Fig. 8 is a configuration diagram showing a mobile water treatment apparatus according to an example;

1 to 3, a mobile water treatment apparatus 100 according to an embodiment of the present invention includes a vehicle 110, a pretreatment unit 200, a separation unit 300, and an adsorption unit 800 .

Here, the vehicle 110 may have a mounting portion 120 in which a first space 121 is formed. The mounting part 120 can accommodate the pre-processing part 200, the separating part 300 and the suction part 800 in the first space 121. For example, A structure directly mounted on the vehicle 110 as a part of the vehicle 110 or a structure in which the vehicle 110 is manufactured separately such as a container or mounted on the vehicle 110 or a structure in which the vehicle 110 such as a trailer, As shown in FIG. According to the present invention, since the pretreatment unit 200, the separation unit 300, and the suction unit 800 for treating the contaminated water are provided in the vehicle, it is possible to move to the area where the contaminated water is generated, Do.

The pretreatment unit 200 may be installed in the first space 121 of the installation unit 120 and may be configured to introduce polluted water from the outside and to mix the polluted water with the air.

The separation unit 300 may be installed in the first space 121 of the installation unit 120 and may separate oil and sludge from the polluted water introduced through the pretreatment unit 200. The separator 300 can transfer oil and sludge separated from the contaminated water to different paths.

The adsorption unit 800 can be installed in the first space 121 of the installation unit 120 and can adsorb and remove the refractory material from the polluted water flowing through the separation unit 300. A plurality of adsorption units 800 may be arranged in series, and the adsorption unit 800 may increase throughput of the refractory materials through the tandem arrangement. In addition, the adsorption units 800 arranged in series can be arranged in parallel. Through the parallel arrangement, regeneration of the adsorbent of some adsorption units 800 different from the breakage points can be performed, It is possible to increase the treatment efficiency by continuously treating the decomposable substance.

A clean tank 710 and a filter pump 720 may be further provided between the separation unit 300 and the adsorption unit 800.

The clean tank 710 can receive the treated water through the separating unit 300 and can include a level switch (not shown) for adjusting the capacity of the treated water to be introduced.

The filter pump 720 may provide pressure to transfer the contaminated water received in the clean tank 710 to the adsorption unit 800. The filter pump 720 may further include a filter member (not shown) for filtering foreign substances to be removed from the incoming polluted water.

The mobile water treatment apparatus 100 may include a control unit 730 and the control unit 730 may include a pretreatment unit 200, a separation unit 300, a clean tank 710, a filter pump 720, Can be controlled.

4 is a view illustrating an exemplary pretreatment unit of a mobile water treatment apparatus according to an embodiment of the present invention.

4, the pretreatment unit 200 may include a filter 210, a mixing tank 220, a dissolved air floating unit 230, a pump 240, and an air compressor 250.

The filter 210 can filter foreign matter from the contaminated water flowing from the outside through the hose 201. The filter 210 may have a screen member 211 for filtering out contaminants from the contaminated water, and the screen member 211 may be formed to filter contaminants of a relatively large size. The screen member 211 may be formed as a perforated plate.

The mixing tank 220 can pressurize and mix the air supplied from outside with the polluted water flowing through the filter 210. [

In addition, the dissolved air floating portion 230 can generate bubbles in the contaminated water flowing from the mixing tank 220. The dissolved air floating portion 230 can generate a large amount of air bubbles in the contaminated water by using a dissolved air flotation (DAF) method.

The pump 240 may provide pressure to allow the contaminated water to flow through the filter 210, the mixing tank 220, and the dissolved air floating portion 230. The pump 240 may be provided between the filter 210 and the mixing tank 220.

The air compressor 250 can selectively supply compressed air to the pump 240 and the mixing tank 220. The mixed tank 220 can generate a large amount of air bubbles in the polluted water by using the compressed air supplied from the air compressor 250.

The pretreatment unit 200 may be fixedly coupled to the mounting unit 120 by the first support unit 130.

FIG. 5 is a front view illustrating a separating unit of a mobile water treatment apparatus according to an embodiment of the present invention, FIG. 6 is a cross-sectional view illustrating a separating unit of a mobile water treatment apparatus according to an embodiment of the present invention, FIG. 8 is a cross-sectional view taken along line AA of FIG. 6, and FIG. 9 is a side view illustrating a separating portion of a mobile water treatment apparatus according to an embodiment of the present invention. FIG. And FIG. 10 is a cross-sectional view illustrating a re-separation unit of a mobile water treatment apparatus according to an embodiment of the present invention.

5 to 10, the separating unit 300 includes a housing 301, a first processing unit 310, a second processing unit 320, a third processing unit 340, and a fourth processing unit 350 can do.

First, the housing 301 may form an outer shape of the separating part 300 and may be fixedly coupled to the mounting part 120 (see FIG. 1) by the second supporting part 140.

A second space 302 may be formed on the inner side of the housing 301. The second space 302 may refer to the entire inner space of the housing 301. The second space 302 may be divided according to the purpose of use so that the first to third processing units 310 to 350 may be provided. have.

The first processing unit 310 may be provided at one side of the second space 302, and the contaminated water may be introduced from the pretreatment unit 200 and the foreign matter of the contaminated water may be primarily separated.

To this end, the first processing unit 310 may have a guide unit 311 and a separation unit 312.

The guide portion 311 may be provided so as to penetrate through one side of the housing 301 and one end of the guide portion 311 located outside the housing 301 may be connected to the dissolved air floating portion 230 Can be connected. The guide portion 311 and the dissolved air floating portion 230 may be connected by a pipe 235 or the like.

The separation unit 312 may be provided at the other end of the guide unit 311 and may include a cover unit 313 and a vortex generation unit 314.

The cover portion 313 may be formed in a container shape in which a lower portion is opened, and may be connected to the other end portion of the guide portion 311. The treated water discharged from the dissolved air floating portion 230 can be introduced into the cover portion 313 through the guide portion 311 and discharged to the lower portion of the cover portion 313, 302, respectively.

The vortex generating part 314 may be provided in the axial direction of the cover part 313 on the inner side of the cover part 313 and may be formed in a spiral shape to generate a vortex.

At this time, heavy foreign matter sinks to the bottom of the first processing unit 310 due to the centrifugal force, and air bubbles, foam, light foreign matter, oil, The car can be separated.

The second processing unit 320 may have a first screen member 321, a first separation pack 323, and a first skimmer 331.

The first screen member 321 may be provided in the second space 302 perpendicularly to the flow direction of the polluted water. The first screen member 321 may be a plate having a plurality of perforations 322 formed therein. The second processing unit 320 may be partitioned from the first processing unit 310 by the first screen member 321.

The first separating pack 323 may include a plurality of first plates 324 stacked at predetermined intervals along the vertical direction.

The first plate 324 may have a first hill 325 protruding upward concavely and a first hill 326 recessed downward. A first hill 325 and a first hill 326 (326) may be repeatedly formed in the horizontal direction. A first through hole 327 may be formed in the upper end of the first hill 325 and a second through hole 328 may be formed in the first hill 326.

Accordingly, when the contaminated water passes through the first separation pack 323, the oil of the contaminated water floats to the water surface through the first through-hole 327, and the sludge is settled through the second through-hole 328 Can be separated secondarily. The sludge settling through the second through-hole 328 can be deposited on the bottom surface of the housing 301.

The first skimmer 331 may be provided to cross the housing 301 and may be provided at the water surface height of the contaminated water. The first opening 332 may be formed on the outer circumferential surface of the first skimmer 331 in the longitudinal direction. The oil floated on the water surface may flow into the first skimmer 331 through the first opening 332 so that the first skimmer 331 can remove the oil floating on the water surface.

The third processing unit 340 may have a second screen member 341, a second separation pack 342, and a second skimmer 335.

The second screen member 341 may be provided in the second space 302 perpendicularly to the flow direction of the polluted water. The second screen member 341 may be formed of a plate having a plurality of perforations (not shown), and may be formed in the same manner as the first screen member 321.

The third processing unit 340 may be partitioned from the second processing unit 320 by the second screen member 341.

The second separation pack 342 may include a plurality of second plates 343 stacked at predetermined intervals along the vertical direction.

The second plate 343 may have a second hill 344 protruding upward concavely and a second hill 345 recessed downward. The second hill 344 and the second hill The light guide plate 345 may be repeatedly formed in the horizontal direction. A third through hole 346 may be formed in the upper end of the second hill 344, and a fourth through hole may be formed in the second hill 345.

Accordingly, when the contaminated water passes through the second separation pack 342, the oil of the contaminated water rises to the water surface through the third through hole 346, and the sludge is settled through the fourth through hole 347 It can be separated three times. The sludge settling through the fourth through-hole 347 can be accumulated on the bottom surface of the housing 301.

The second plate 343 may be formed to have a larger area than the first plate 324 and may be stacked at a finer interval than the stacking interval of the first plates 324.

Accordingly, in the first separation pack 323, the primary separation of foreign matter can be achieved while reducing the flow resistance of the polluted water having a relatively large amount of oil and sludge. In addition, the second separation pack 342 can be provided with a second plate 343 having a wider area, so that secondary separation of foreign matter can be performed more effectively.

The second skimmer 335 may be provided to cross the housing 301 and may be provided at a height of the water surface of the contaminated water, more preferably, slightly lower than the water surface height of the contaminated water. A second opening 336 may be formed in the outer circumferential surface of the second skimmer 335 in the longitudinal direction. The oil floated on the water surface can flow into the second skimmer 335 through the second opening 336, through which the second skimmer 335 can take off the oil floating on the surface of the water.

The fourth processing unit 350 may be provided in the second space 302 by being partitioned by the partitioning wall 351 and the third processing unit 340 and the fourth processing unit 350 may be provided by dividing the branching unit 352 and the first adsorbent Lt; RTI ID = 0.0 > 358 < / RTI >

Here, the branching section 352 may have a receiving section 353 and a branching passage 354.

The receiving portion 353 may be formed in a container shape having an open upper portion and may be provided on one side of the barrier rib 351. An inclined plate 355 may be provided on one side of the partition 351 and a lower end of the inclined plate 355 may be positioned on the inner side of the receiving portion 353. [ Accordingly, the contaminated water flowing over the partition wall 351 flows along the swash plate 355 and can be received in the receiving part 353 and accommodated.

The branch passage 354 may be connected to the receiving portion 353 and may be provided in plural along the horizontal direction. The branch channel 354 may have a sidewall 356 and the sidewall 356 may have grooves 357 formed at regular intervals.

Accordingly, when the water level of the contaminated water received in the receiving portion 353 increases, the contaminated water in the receiving portion 353 moves through the branching flow path 354, overflows into the groove 357 of the side wall 356, . Here, since the branch flow paths 354 are provided in plural along the horizontal direction, the contaminated water is guided to move to a plurality of paths by the branch flow path 354, and the contaminated water overflowing in the grooves 357 flows into the fourth processing section 350) and can fall down.

The first adsorbent 358 may be provided below the branch portion 352 and may adsorb various foreign substances including oil from the polluted water.

An outlet 303 may be provided on the other side of the housing 301. The treated water that has been treated through the fourth treatment unit 350 may be discharged through the outlet 303.

A first exhaust port 304 may be provided in a lower portion of the housing 301 corresponding to the first processing unit 310. The foreign substances precipitated in the first processing unit 310 through the first exhaust port 304 may be exhausted .

The second exhaust port 305 may be provided in a lower portion of the housing 301 corresponding to the third processing unit 340. The foreign substances precipitated in the third processing unit 340 may be discharged through the second exhaust port 305 .

Width mechanisms 306 and 307 may be provided on the lower portion of the housing 301 corresponding to the second processing unit 320 and the third processing unit 340, respectively. Pressure gas can be supplied to the width mechanisms 306 and 307 and the supplied high-pressure gas can pass through the first separating pack 323 and the second separating pack 342 so that the first separating pack 323 and the second separating pack 342 So that the separation pack 342 can be cleaned.

The sludge separated from the first separation pack 323 and the second separation pack 342 by the high pressure gas introduced into the width mechanisms 306 and 307 flows to the bottom surface of the second processing unit 320 and the third processing unit 340 And the accumulated sludge can be discharged through the first outlet 304 and the second outlet 305.

A re-separation unit 360 may be provided outside the housing 301. The re-separation unit 360 includes a chamber 361, a guide pipe 362, a dam 363, a third outlet 368, And a fourth outlet (370).

The chamber 361 may form the outer shape of the housing 301 and may be provided outside the housing 301.

The guide tubes 362 may be provided on both sides of the chamber 361 in pairs. One end of the guide tube 362 may be connected to the first skimmer 331 and the second skimmer 335 and the other end may be connected to the chamber 361. The guide pipe 362 may be inclined so that the portion connected to the chamber 361 is lower than the portion connected to the skimmers 331 and 335. The oil and the contaminated water introduced into the skimmers 331 and 335, May be conveyed inwardly of the chamber 361 through the openings 362.

The dam portion 363 may have a blocking portion 364, an inflow hole 365, and a partition portion 366.

Here, the blocking portion 364 may be provided in the vertical direction inside the chamber 361. The blocking portion 364 may be formed in a cylindrical shape having an upper end and a lower end opened and a lower end thereof may be connected to a bottom surface 367 of the chamber 361.

The inflow hole 365 may be formed below the blocking portion 364 so that the contaminated water flowing into the chamber 361 flows into the blocking portion 364 through the inflow hole 365 . At this time, since the oil introduced into the chamber 361 floats on the water surface of the contaminated water, inflow through the inflow hole 365 can be prevented.

The third outlet 368 is provided in the lower portion of the chamber 361 and can be connected to the inside of the blocking portion 364 and the treated water flowing into the blocking portion 364 through the inlet hole 365, And may be discharged through outlet 368.

The partition 366 may be provided inside the upper portion of the blocking portion 364 and may have a receiving space 369 formed above the blocking portion 364. [ As the water level of the treated water flowing into the chamber 361 increases, the oil on the water surface may flow over the blocking portion 364 and the oil thus introduced may be introduced into the chamber 361 by the partitioning portion 366 And can be accommodated in a receiving space 369 formed in the upper part.

The fourth outlet 370 may be provided in the front surface 371 of the chamber 361 to be connected to the accommodation space 369 and the oil contained in the accommodation space 369 may be supplied through the fourth outlet 370 Can be discharged.

FIG. 11 is a view illustrating an adsorption unit of a mobile water treatment apparatus according to an embodiment of the present invention, FIG. 12 is a cross-sectional view illustrating an adsorption unit of a mobile water treatment apparatus according to an embodiment of the present invention, Sectional view illustrating a suction portion of a mobile water treatment apparatus according to an embodiment of the present invention.

11 to 13, the adsorption unit 800 may have a container unit 810, a lid unit 830, and an adsorption module 850.

The container portion 810 may include an inlet 811, an outlet 812, a first flange 813, a coupling portion 820, and a coupling rib 810 815).

The inlet port 811 may be formed below the container section 810 and the treated water passing through the inlet port 811 through the separation section 300 (see FIG. 3) may be introduced. The outlet port 812 may be formed on the upper side of the container portion 810 and the contaminated water on the inside of the container portion 810 may be discharged through the outlet port 812.

The first flange 813 may be provided at the upper end of the container portion 810.

The lid 830 may be detachable to open or close the upper portion of the container portion 810 and may have an outer diameter corresponding to the first flange 813. A plurality of slits 831 may be formed on the outer circumferential surface of the cover portion 830. The slits 831 may be formed to have a predetermined length along the radial direction at regular intervals along the circumferential direction.

In addition, the first flange 813 may have a support portion 814 provided at a position corresponding to the slit 831 along the circumferential direction.

The coupling portion 820 may have a coupling shaft 821, a rotation bar 822, and a tightening portion 823.

The coupling shaft 821 may be provided in the support portion 814 and one end of the rotation bar 822 may be coupled to the coupling shaft 821 to rotate. The rotation bar 822 can be inserted into the slit 831 by rotating around the engagement shaft 821. [ The throttle portion 823 can be screwed to the other end of the rotary bar 822. The rotary bar 822 can be screwed in the state where the rotary bar 822 is inserted into the slit 831 to press the lid portion 830, Through this, the lid portion 830 can be fixed to the container portion 810.

The engaging rib 815 may protrude from the inside of the container portion 810 and the engaging rib 815 may be provided horizontally on the inner circumferential surface of the container portion 810. A plurality of first coupling holes 316 may be formed in the coupling rib 815 along the circumferential direction.

The adsorption module 850 may have a receiving portion 851, a second flange 852, and a perforated plate 853.

The receiving portion 851 may receive the second adsorbent 854 on the inner side and the second flange 852 may be provided on the receiving portion 851. A second engagement hole 855 may be formed in the second flange 852 along the circumferential direction and a second engagement hole 855 may be formed to correspond to the first engagement hole 316.

The perforated plate 853 may be provided at the upper and lower portions of the receiving portion 851 and the perforated plate 853 may have a plurality of through holes 857 formed therein. A third coupling hole 858 corresponding to the second coupling hole 855 may be formed in the perforated plate 853 provided at the upper portion of the receiving portion 851.

The fastening member 856 is engaged with the third engaging hole 858, the second engaging hole 855 and the first engaging hole 316 in a state where the second flange 852 is placed on the upper portion of the engaging rib 815 The receiving portion 851 can be detachably attached to the inside of the container portion 810.

The contaminated water flowing into the inlet 811 can be introduced into the receiving portion 851 through the perforated plate 853 provided at the lower portion of the receiving portion 851, The refractory material of the polluted water can be adsorbed to the second adsorbent 854 while passing through the second adsorbent 854. The second adsorbent 854 may be a porous carbon nanomaterial and may be, for example, expanded graphite.

The treated water discharged through the perforated plate 853 provided in the upper portion of the receiving portion 851 may be discharged through the outlet 812 of the receiving portion 851.

In addition, an ozone water inlet 817 may be provided in a lower portion of the container portion 810. The ozone water can be injected into the ozone water inlet 817. The injected ozone water passes through the adsorption module 850 and the refractory material adsorbed on the second adsorbent 854 can be oxidized and removed. The ozone water having passed through the adsorption module 850 can be discharged to the ozone water drain port 832 formed in the lid part 830.

FIG. 14 is an exemplary view showing an example of the arrangement of a suction portion of a mobile water treatment apparatus according to an embodiment of the present invention. According to the embodiment of the present invention, a plurality of adsorption units may be provided. Hereinafter, for convenience of explanation, the case where two adsorption units are used will be described as an example.

14, a plurality of adsorption units may be provided and may be arranged in series (D1) including a first pipeline line 910, a second pipeline line 920, and a third pipeline line 930 .

The first piping line 910 may be connected to the main line ML for guiding the movement of the process water through the separator 300 (see FIG. 3), and may be connected to the outlet 951 of the first adsorption unit 950, And the outlet (961) of the second adsorption portion (960).

The second piping line 920 can connect the main line ML and the inlet 952 of the first adsorption unit 950 and the second piping line 920 can open and close the second piping line 920. [ A first valve 921 may be provided.

The first pipe 910 may include a second valve 911, a third valve 912 and a fourth valve 913 around an outlet 951 of the first adsorption unit 950, The fifth valve 914, the sixth valve 915 and the seventh valve 916 may be provided around the outlet port 961 of the second adsorption section 960. [

The third piping line 930 may be branched at a portion of the first piping line 910 connected to the outlet 961 of the second adsorption portion 960 and may be branched at the inlet 962 of the second adsorption portion 960 Can be connected. The third pipe line 930 may include an eighth valve 931 and the eighth valve 931 may perform the same function as the first valve 921.

When the second valve 911 and the fifth valve 914 are closed and the first valve 921 and the eighth valve 931 are opened, the polluted water moving through the main line ML flows into the second pipe line May be introduced into the inlet 952 of the first adsorption part 950 through the outlet 920 and may be discharged through the outlet 951 after the refractory contaminant is adsorbed. At this time, the third valve 912 and the fourth valve 913 are opened, and the process water discharged flows in the direction of the second adsorption unit 960 through the first pipe line 910.

The treated water traveling through the first piping line 910 moves along the third piping line 930 through the opened valve 831 and flows into the inlet port 962 of the second adsorption unit 960 And may be discharged to the outlet port 961 after the refractory pollutant is adsorbed. At this time, the sixth valve 915 and the seventh valve 916 are opened, and the treated water flows through the first piping line 910 and is connected to the hose 970 connected to the first piping line 910, Lt; / RTI >

On the other hand, when the adsorbent of the first adsorption portion 950 is different from the break point and the adsorbent of the second adsorption portion 960 is not different from the break point, the first valve 921 and the third valve 912 And the second valve 911 and the fourth valve 913 are opened to allow the treated water through the main line ML to flow directly through the first pipe line 910 to the inlet 962 of the second adsorption portion 960, As shown in FIG.

Similarly, when the adsorbent of the second adsorption portion 960 is different from the breakthrough point and the adsorbent of the first adsorption portion 950 does not reach the breakthrough point, the second valve 911, the sixth valve 915 And the eighth valve 931 so that the treated water that has been water-treated in the first adsorption portion 950 passes through the fifth valve 914 and the seventh valve 916 and passes through the first piping line 910 to the hose 970 ). ≪ / RTI >

As described above, according to the embodiment of the present invention, a plurality of adsorption units are provided, and each adsorption unit is arranged in series to selectively regenerate only the adsorption unit having adsorbents different in breaking point, and the adsorption unit, Can be used.

On the other hand, a plurality of adsorption units arranged in series may be provided. That is, a plurality of adsorption units may be arranged in series (D1, D2), and each series arrangement (D1, D2) may have the same structure. The adsorbing portions in the series arrangement (D1, D2) can be arranged in parallel by branching the main line (ML). That is, the main line ML can be branched (ML1, ML2) so that the process water can be supplied to the adsorption units in the respective series arrangements D1, D2. By arranging the adsorption sections in parallel, it is possible to operate the adsorption section in series arrangement or to use the adsorption section having the adsorbent that is not close to the breakthrough point more effectively.

In the foregoing, for convenience of description, one series arrangement has been described as having two adsorbents, but the number of adsorbents may be increased to three, four, etc. In this case, the above-described operational example can also be applied.

It will be understood by those skilled in the art that the foregoing description of the present invention is for illustrative purposes only and that those of ordinary skill in the art can readily understand that various changes and modifications may be made without departing from the spirit or essential characteristics of the present invention. will be. It is therefore to be understood that the above-described embodiments are illustrative in all aspects and not restrictive. For example, each component described as a single entity may be distributed and implemented, and components described as being distributed may also be implemented in a combined form.

The scope of the present invention is defined by the appended claims, and all changes or modifications derived from the meaning and scope of the claims and their equivalents should be construed as being included within the scope of the present invention.

100: Portable water treatment device
110: vehicle
120:
200:
300:
800:

Claims (16)

A vehicle having a mounting portion in which a first space is formed;
A pretreatment unit installed in the first space to process the polluted water flowing in from the outside into the contaminated water to be mixed with air;
A separating unit installed in the first space and separating oil and sludge from the polluted water flowing through the pretreatment unit; And
And a suction unit installed in the first space for adsorbing and removing the refractory material from the contaminated water flowing through the separator,
The separator
A housing having a second space formed therein,
A first processing unit provided at one side of the second space for introducing contaminants discharged from the pretreatment unit and primarily separating contaminants from the inflowed contaminated water,
A second processing unit provided in the second space and being partitioned from the first processing unit by a first screen member and including a first separating pack for secondarily separating foreign matter from the contaminated water flowing through the first screen member, Wow,
A third processing unit provided in the second space and being partitioned from the second processing unit by a second screen member and including a second separation pack for tertiary separation of foreign substances from the contaminated water flowing through the second screen member, Wow,
And a fourth adsorbent which is provided in the second space and is partitioned from the third treatment section and includes a first adsorbent for adsorbing and separating foreign matter from the polluted water flowing over the partition wall. Portable water treatment device.
The method according to claim 1,
The pre-
A filter for filtering foreign matter from the contaminated water flowing from the outside,
A mixing tank for pressurizing and mixing the air supplied from the outside to the contaminated water flowing through the filter,
A dissolved air floating portion for generating air bubbles in the contaminated water flowing from the mixing tank,
A pump for providing a pressure such that the contaminated water flows through the filter, the mixing tank, and the dissolved air floating portion;
And an air compressor for selectively supplying compressed air to the mixing tank and the pump.
delete The method according to claim 1,
The first processing unit
A guide part connected to the pretreatment part and guiding the contaminated water discharged from the pretreatment part to be introduced into the second space,
A cover part connected to the other end of the guide part in the second space and formed in a container shape opening the lower part and guiding the polluted water discharged through the guide part to be discharged to the lower part, And a vortex generating part formed in a spiral shape and generating a vortex.
The method according to claim 1,
The second processing unit
A first crest portion having a concave upward projecting shape and having a first through hole formed at an upper end thereof; a first crest portion having a shape recessed downwardly and formed with a second through hole at a lower end thereof repeatedly formed in a horizontal direction A first separating pack which is composed of a plurality of first plates stacked at predetermined intervals along a vertical direction to separate oil and sludge of contaminated water;
And a first skimmer provided across the housing at a water level of the contaminated water to remove oil floating on the water surface of the contaminated water.
The method according to claim 1,
The third processing unit
A second crest portion having a concave upward projecting shape and having a third through hole formed at an upper end thereof, a second crest portion having a recessed shape recessed downwardly and having a fourth through hole at a lower end thereof repeatedly formed in a horizontal direction A second separation pack which is composed of a plurality of second plates stacked at predetermined intervals along the vertical direction to separate oil and sludge of the contaminated water,
And a second skimmer provided across the housing at the water level of the contaminated water to remove oil floating on the water surface of the contaminated water.
The method according to claim 1,
The fourth processing unit
A plurality of branch ducts connected to the receiving unit and guiding the polluted water overflowing from the receiving unit into a plurality of paths, the branch duct being connected to the receiving unit, The branching portion,
And a first adsorbent provided below the branch portion and adapted to adsorb and separate foreign matter from the polluted water that overflows from the branch flow path.
The method according to claim 1,
A first outlet for a lower portion of the housing corresponding to the first processing portion is provided to discharge foreign matter separated from the contaminated water and a second outlet is provided at a lower portion of the housing corresponding to the third processing portion A water treatment device.
The method according to claim 1,
And a width mechanism for supplying high-pressure gas to the second space and cleaning the first and second separation packs is provided at a lower portion of the housing corresponding to the second processing unit and the third processing unit. Lt; / RTI >
The method according to claim 1,
On the outside of the housing
Wherein the first skimmer of the second processing unit and the second skimmer of the third processing unit are provided with a re-separation unit for separating the contaminated water and the oil carried by the second skimmer.
11. The method of claim 10,
The re-
A chamber provided outside the housing,
A pair of guide pipes provided on an outer side of the housing to guide the contaminated water and oil discharged from the first skimmer and the second skimmer to the chamber,
A cylindrical blocking portion provided in a vertical direction inside the chamber and having a lower end connected to a bottom surface of the chamber, an inflow hole formed below the blocking portion to allow contamination of the inside of the chamber into the blocking portion, A dam portion formed inside the upper portion of the blocking portion and configured to define a receiving space at an upper portion of the blocking portion,
A third discharge port provided at a lower portion of the chamber and connected to the inside of the shutoff portion to discharge treated water inside the shutoff portion,
And a fourth discharge port provided on a front surface of the chamber so as to be connected to the accommodation space and allowing the oil contained in the accommodation space to flow and flow through the blocking portion.
The method according to claim 1,
The adsorption unit
A container portion having an upper opening formed therein and having an inlet port through which the polluted water passing through the separating section flows and an outlet port formed through the upper portion and through which the polluted water introduced into the inlet port is discharged,
A lid part which is detachably attached to open and close the upper part of the container part,
And an adsorption module provided on the inside of the container to adsorb the refractory material of the contaminated water flowing into the inlet.
13. The method of claim 12,
The lid part has a plurality of slits formed on the outer circumferential surface at predetermined intervals along the circumferential direction and having a predetermined length along the radial direction,
The container
A first flange provided at an upper end of the container portion and having a support portion provided at a position corresponding to the slit along a circumferential direction;
A rotation bar which is inserted into the slit while one end of the rotation shaft is engaged with the coupling shaft and is screwed to the other end of the rotation bar, and the rotation bar is inserted into the slit, And a tightening portion for tightening the lid portion to the container portion by pressing the lid portion to the container portion.
13. The method of claim 12,
The adsorption module includes a receiving portion for receiving the second adsorbent,
A second flange detachably coupled to an engaging rib provided on an upper portion of the receptacle and protruding from the container;
And a perforated plate provided at the upper and lower portions of the receiving portion and having a plurality of through holes for allowing the contaminated water to move.
13. The method of claim 12,
A first pipeline line connected to a main line for guiding the movement of the treated water through the separator and connected to an outlet of the plurality of adsorption units,
A second pipe line connected to the main line and connected to an inlet of one of the adsorption units,
And a third piping line branched from a first piping line portion connected to an outlet of the other adsorption unit and connected to an inlet port of the other adsorption unit.
16. The method of claim 15,
Wherein a plurality of adsorption units arranged in series are provided, and each of the adsorption units arranged in series is branched in the main line.
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KR102281523B1 (en) * 2017-10-31 2021-07-23 한국산업기술시험원 Movable advanced oxidation process appratus
KR102154604B1 (en) * 2019-08-05 2020-09-11 (주)쓰리에스 Purifying and uncycling system for livestock wastewater
KR102643348B1 (en) * 2022-10-26 2024-03-08 (주)동명엔터프라이즈 Mobile automatic operation control system for urgent purification of chemical accident contaminated water
KR102593316B1 (en) * 2022-10-26 2023-10-26 (주)동명엔터프라이즈 Mobile control system for urgent purification of chemical accident contaminated water

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JP3045066B2 (en) * 1996-03-14 2000-05-22 日本電気株式会社 Compressed video editing device
JP2000176443A (en) * 1998-12-18 2000-06-27 Kubota Corp Operation control method and device of adsorption column
KR100301650B1 (en) * 1999-04-17 2001-09-22 김규홍 Apparatus for purifying the waste water using cone-type inclined plate
KR200303682Y1 (en) * 1999-05-29 2003-02-14 원종암 a filter for a bath

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Publication number Priority date Publication date Assignee Title
JP3045066B2 (en) * 1996-03-14 2000-05-22 日本電気株式会社 Compressed video editing device
JP2000176443A (en) * 1998-12-18 2000-06-27 Kubota Corp Operation control method and device of adsorption column
KR100301650B1 (en) * 1999-04-17 2001-09-22 김규홍 Apparatus for purifying the waste water using cone-type inclined plate
KR200303682Y1 (en) * 1999-05-29 2003-02-14 원종암 a filter for a bath

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