KR101581241B1 - Apparatus for treating rainwater and overflow water of confluent water drainage - Google Patents
Apparatus for treating rainwater and overflow water of confluent water drainage Download PDFInfo
- Publication number
- KR101581241B1 KR101581241B1 KR1020150098155A KR20150098155A KR101581241B1 KR 101581241 B1 KR101581241 B1 KR 101581241B1 KR 1020150098155 A KR1020150098155 A KR 1020150098155A KR 20150098155 A KR20150098155 A KR 20150098155A KR 101581241 B1 KR101581241 B1 KR 101581241B1
- Authority
- KR
- South Korea
- Prior art keywords
- water
- tank
- artificial floating
- filtration
- overflow
- Prior art date
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D24/00—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
- B01D24/02—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration
- B01D24/10—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof with the filter bed stationary during the filtration the filtering material being held in a closed container
- B01D24/16—Upward filtration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D24/00—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
- B01D24/46—Regenerating the filtering material in the filter
- B01D24/4605—Regenerating the filtering material in the filter by scrapers, brushes, nozzles or the like placed on the cake-side of the stationary filtering material and only contacting the external layer
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D24/00—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
- B01D24/46—Regenerating the filtering material in the filter
- B01D24/4631—Counter-current flushing, e.g. by air
- B01D24/4636—Counter-current flushing, e.g. by air with backwash shoes; with nozzles
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D24/00—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof
- B01D24/48—Filters comprising loose filtering material, i.e. filtering material without any binder between the individual particles or fibres thereof integrally combined with devices for controlling the filtration
- B01D24/4807—Handling the filter cake for purposes other than regenerating
- B01D24/4815—Handling the filter cake for purposes other than regenerating for washing
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D39/00—Filtering material for liquid or gaseous fluids
- B01D39/14—Other self-supporting filtering material ; Other filtering material
- B01D39/20—Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
- B01D39/2003—Glass or glassy material
-
- 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
-
- 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
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
-
- 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
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Geology (AREA)
- Inorganic Chemistry (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The present invention relates to an apparatus for high-speed processing of sewage water using a foamed artificial floating material having natural eco-friendliness and resource recyclability.
Accordingly, the technical point of the present invention is to rapidly improve pollutants in sewage water generated during rainfall to improve the quality of water rapidly. This is because the two-stage compartment (rapid reaction tank and slow reaction tank) type flocculation tank (Flocculation or coagulation) of contaminants such as various organic matters, suspended matters, coliform bacteria, etc. in the overflow water is highly concentrated. In the filtration tank which is a downstream process, an (LCD) glass or a waste glass bottle And the recycled multistage multi-layered artificial floating material is formed so as to be enclosed in the compartments, so that the overflow water flowing from the flocculation tank through the overflow water conveying pipe rises in the upward flow manner, and the artificial floating filter material is filtered at a high speed.
Description
The present invention provides a method for rapidly improving the quality of water by treating contaminants in the sewage water generated during rainfall at a high speed by using a two stage compartment (rapid reaction tank and slow reaction tank) flocculation tank having an agitation facility, (Flocculation or condensation) of contaminants such as various kinds of organic substances, suspended matters, coliforms, etc. in a filtration tank which is a post-production process. In the filtration tank, a (waste) LCD glass or a waste glass bottle, Wherein the flood water flowing from the flocculation tank through the overflow water conveying pipe is raised in an upward flow manner so that the artificial floating filter material is filtered at a high speed so as to be filtered at a high speed. Of High Speed Sewage Water Treatment System Using Foamed Artificial Floating Material will be.
In other words, the present invention can be applied to a method of treating rainfall water (high concentration of pollutants contained in roads, industrial areas, commercial areas and residential areas combined sewerage) So that the sewage water exceeding the treatment capacity of the sewage treatment plant can be treated at a high speed.
The pollutants affecting the water system are divided into point-source and non-point source.
In this case, the point source is a pollutant source such as domestic sewage or factory wastewater which can be expressed as a single point, and the pollutant movement path is clear and easy to process.
In addition, the nonpoint source is a pollution source that pollutants on the ground surface are washed away by rainwater during rainfall, and the pollution source is very difficult to treat due to the concentration of the outflow amount during rainfall.
Thus, in the case of non-point-pollution sources, pollution sources are distributed in a wide area, and various pollutants on the impervious surface are washed in the first-flush at the beginning of rainfall, And the width of the fluctuation of the flow rate with time is formed to have a very large characteristic.
In this case, in case of urban area or industrial complex, the possibility of containing toxic substances such as heavy metals is high, and a different approach from the conventional water treatment method is needed.
As a method of treating pollutants in the early stage, storage type, permeability, vegetation type, device type, and the like have been proposed.
At this time, the reservoir type removes the particulate pollutants by sedimentation, and the permeable type increases the underground penetration ability, thereby reducing the storm drainage and utilizing the underground soil as a filter.
As vegetation type, there are mainly vegetation channel and vegetation filtration as a pretreatment method, and the device type is installed in a pipeline, and it is applied to an urban area where rainwater flows out through pipelines. And can be classified into a vortex type, a sedimentation type, a filtration type, and the like.
Therefore, the apparatus type is predominantly composed of a vortex type method in which a vortex is formed by using a centrifugal force to precipitate a suspended substance, and a cartridge type filter filtration type method.
At this time, the conventional vortex type has a disadvantage in that the particulate matter is not easily removed when the vortex is not sufficiently generated, and the removal efficiency thereof is rapidly lowered.
In addition, since the vortex-type facility deposits particulate matter by the centrifugal force generated by the vortex, it is difficult to sufficiently remove the contaminant due to the limitation that the particulate matter can not be sufficiently removed.
And the vortex type facility is a facility that has a limit to remove the micro pollutant which occupies most of the particulate matter.
Accordingly, since the filtration type facility is difficult to precipitate rapidly like a vortex type facility, it has disadvantages that the required capacity and the required site of the apparatus are large and the filtration type is the surface filtration type, so that it can be easily clogged.
In other words, the rainfall runoff (overflow water) exceeding the normal treatment capacity (Q) of the sewage or sewage treatment plant contains a high concentration of pollutants accumulated in the sewage pipe and is discharged to the discharge water system without being appropriately treated in the mixed state with sewage There is a possibility of destroying the river ecosystem such as the Tanchon fish dwelling in August 2004 and the Nakdong River, Geumgang, Youngsan River, etc., which are closed waters where the discharge water is the estuary, have eutrophication and red tide, In the long term, it will have a negative impact on water resources management because it is difficult to adhere to the allowable outflow pollutant load of the total water quality system being implemented.
On the other hand, the sewage overflow is equivalent to about 3% to 6% of the sewage inflow in Cheongcheon, and the sewage overflow water load (Camp, 1963), which accounts for about 30% As shown in the following Table 1, at the early stage of rainfall, high concentrations of up to 30 times of the sewage concentration occurred in the river are discharged to the river by the water quality item.
1. EMC (Event Mean Concentration): Flow weighted average concentration
2. Study on the Basin Survey on the Outflow Pollution Load of Excellent Pipeline in the Sewer System of the Combined Sewer System in the Urban Area (2004. Environmental Management Corporation)
In order to deal with this, the Ministry of Environment revised the sewerage law in 2014, introduced the simplified public treatment facility system in Korea for the first time, and prepared the legal standard to treat the sewage water.
1. The water quality standard for sewage effluent shall apply only to the simplified public sewage treatment facility installed to treat the sewage that temporarily flows into the public sewage treatment facility having a sewage treatment capacity of 500㎥ or more per day.
2. The Minister of the Environment may set a relaxed standard for public sewage treatment facilities newly installed during the period from July 17, 2014 to December 31, 2018, rather than the quality standard of effluent water.
In other words, the water quality standard of the effluent water of the treatment facility is the waterside area of the water management area of the 4 rivers such as the water conservation area, the water quality protection special area, the Han river water, etc. and the Saemangeum business area. (BOD) of less than 60mg / L for the first time since July 17, 2014, and the biochemical oxygen demand (BOD) is gradually increased to less than 40mg / L from January 1, And the treatment standard for coliform bacteria was also applied.
According to the "Sewerage Facilities Standard (2005, Ministry of Environment)" as a treatment method for the reduction of sewage water pollutants in the past, the second treatment facility was constructed and processed in 1Q for appropriate treatment of sewage introduced during rainfall, Excess sewage is discharged after the simple sedimentation at the primary settlement site of the sewage treatment plant. In some sewage treatment plants, there is a problem in the water quality management during rainfall due to the untreated sewage water discharge through the emergency inflow prevention device installed at the inlet of the inlet And it is urgent to develop and apply excellent treatment technology that can comply with water quality standard of effluent water of public public treatment facility.
In this connection, the patent document 10-2009-0071017 discloses an overflow water treatment apparatus for treating pollutants contained in the overflow of the combined sewerage, comprising: an inflow section for introducing the overflow exceeding the subsequent treatment capacity of the sewage treatment process; A lower water treatment section provided at a lower portion of the treatment tank and having a sedimentation filter medium for filtering coarse contaminants in the flowing water flowing into the treatment tank; An upper water treatment unit provided at an upper portion of the water treatment unit and having a floating filter medium for filtering fine contaminants; a discharge unit for discharging the overflow water filtered through the upper water treatment unit; and an inverter for washing the lower water treatment unit and the upper water treatment unit And the like.
However, in the above-mentioned prior art, the filter material layer has two stages of the upper water treatment portion and the lower water treatment portion to complicate the device, and the backwashing speed becomes slow due to the two-stage water treatment portion, The cleaned contaminants are likely to pass completely through the lower water treatment section, so that there is a problem that the contaminants accumulate between the upper water treatment section and the lower water treatment section, and the inflow pipe is directly introduced from the lower part of the treatment tank, The sediment in the lower part of the treatment tank is easily swept away by the flow of influent water.
Disclosure of Invention Technical Problem [8] Accordingly, the present invention has been made keeping in mind the above problems occurring in the prior art, and an object of the present invention is to provide a method for rapidly improving the quality of water by treating contaminants in sewage water generated during rainfall at high speed, (Rapid reaction tank and slow reaction tank) type flocculation tank is formed to highly concentrate floc (flocculation or coagulation) of contaminants such as various organic matter, suspended matters and coliform bacteria in the overflow water. In the filtration tank, LCD glass or waste glass bottle, etc., is formed so that the recycled multi-layer multi-layered artificial floating material is formed as a compartment, so that the overflow water flowing from the flocculation tank through the overflow water transfer pipe rises in an upward flow manner, Wherein the foamed material has a natural eco-friendliness and resource recyclability. And an object of the present invention is to provide an apparatus for high-speed processing of sewage water using a studying filter medium.
In other words, the present invention can be applied to a method of treating rainfall water (high concentration of pollutants contained in roads, industrial areas, commercial areas and residential areas combined sewerage) The present invention has been made to solve the above-mentioned problems, and it is an object of the present invention to provide a sewage treatment system capable of quickly performing flocculation and filtration on sewage water discharged in a nearby river without any treatment.
In addition, the present invention is to develop a technology capable of complying with the water quality standards of effluent water of a public public treatment facility set forth in the Enforcement Regulations of the Sewerage Act enacted on July 17, 2014, Considering the physical properties of sediments with high specific gravity, the suspended particulate matter has a higher specific gravity than the existing sewage, and adopts an upflow type filtration method considering the collision and sedimentation mechanism between the multi-layer filter media filled with the filter media and the filter inlet particles. have.
(Lung) LCD glass is used as an artificial floating filter material. This is because the floating glass material layer is packed in the filtration tank, and the filtration is performed by using a straining process, a impaction and a sedimentation mechanism center Removal of solids and solids trapped in the filter medium removes contaminants from the air supplied from the bottom and transfers them to the drainage tank through the sludge drawer at the bottom. The process is then concentrated and dehydrated through the sludge tank in the existing process. And an ion disinfection facility capable of appropriately treating a coliform group contained in a large amount in a simple and high-speed operation.
In addition, the (lung) LCD glass artificial floating filter material of the present invention plays a key role in sewage water treatment, and it produces artificial floating filter media by using waste LCD panel generated from disposal of LCD household appliances as a raw material, Thereby improving the strength and durability of the floating filter media and contributing to the conservation of limited resources by recycling waste resources.
In order to achieve the above object, the high-speed processing apparatus of the present invention is provided with a
At this time, the
In addition, the
At this time, the overflow
The artificial floating
In this case, the
In addition, the
The disinfection
In addition, the
As described above, the present invention provides a two-stage compartment (rapid reaction tank and slow reaction tank) type flocculation tank having agitation facilities, which can prevent floc (flocculation or condensation) of contaminants such as various organic matter, suspended matters, coliform bacteria, And a recycling multi-stage multi-layered artificial floating filter medium is formed in the filtration tank, which is a second step process, to contain recycled LCD glass or waste glass bottle, etc., so that the overflow water flowing from the flocculation tank through the overflow water conveying pipe So that the artificial floating filter material can be filtered at a high speed.
In other words, the present invention can be applied to a method of treating rainfall water (high concentration of pollutants contained in roads, industrial areas, commercial areas and residential areas combined sewerage) So that the sewage water exceeding the treatment capacity of the sewage treatment plant at the time of rainfall can be treated at a high speed.
In addition, the present invention is to develop a technology capable of complying with the water quality standards of effluent water of a public public treatment facility set forth in the Enforcement Regulations of the Sewerage Act enacted on July 17, 2014, Considering the good physical properties of sediment with high specific gravity, the float has the effect of inducing the collision and sedimentation mechanism between the multi - layered filter media and the filter inlet particles.
(Lung) LCD glass is used as an artificial floating filter material. This is because the floating glass material layer is packed in the filtration tank, and the filtration is performed by using a straining process, a impaction and a sedimentation mechanism center Removal of solids and solids trapped in the filter medium removes contaminants from the air supplied from the bottom and transfers them to the drainage tank through the sludge drawer at the bottom. The process is then concentrated and dehydrated through the sludge tank in the existing process. An ion disinfection facility capable of appropriately treating E. coli contained in a large amount can be employed.
In addition, the (lung) LCD glass artificial floating filter material of the present invention plays a key role in sewage water treatment, and it produces artificial floating filter media by using waste LCD panel generated from disposal of LCD household appliances as a raw material, It is possible to improve the strength and durability of floating filter media and to contribute to preserving limited resources by recycling waste resources.
That is, according to the present invention, since the sewage treatment plant is constructed and operated by investing huge amount of money to the sewage treatment plant, the sewage treatment rate of the sewage treatment plant reaches to the advanced country level The problem of water pollution caused by sewage is greatly improved.
However, due to the inadequate disposal facilities, the high concentration sewage water generated from the combined sewer pipe at the time of rainfall destroys the aquatic ecosystem such as the water pollution caused by the discharged water area and the fish stubble and causes the cause of the waterborne infectious disease due to the pathogenic Escherichia coli As a part of measures to properly cope with the urgent reality of the waterfront environment in the waterfront area, which is a waterfront area of urban residents, and the national water quality system, The sewage related laws have been amended to introduce a simplified public treatment facility system.
Accordingly, the present invention contributes to provide economical and superior technology by using environment-friendly materials in the simplified public sewage treatment facility introduced for proper treatment of the sewage overflow generated during rainfall, It has the effect of contributing to the improvement of the water quality of rivers and lakes, which is a water area downstream of the sewage treatment plant.
FIG. 1 is a diagram illustrating an example of a high-throughput water treatment apparatus according to the present invention.
2 to 3 are side views of the flocculation tank according to the present invention,
4 is a side view of a filtration tank according to the present invention,
5 is an exemplary view showing a disinfection apparatus according to the present invention,
FIG. 6 is a process chart of the high-throughput water treatment apparatus according to the present invention,
FIG. 7 is a photograph showing an example of a case in which a high-throughput water treatment apparatus according to the present invention is applied,
8 is an illustration of an artificial floating material according to the present invention.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail below with reference to the accompanying drawings.
First, as shown in FIG. 1 to FIG. 8, the high-speed processing apparatus of the present invention is largely composed of an aggregation reaction tank and a filtration tank.
The
At this time, the
In this case, the
In other words, in the flocculation tank, the swirling water and the inorganic flocculant are rapidly mixed by using a rapid stirrer, and a rapid reaction tank for forming micro flocs and an auxiliary coagulant such as polymer are injected and mixed slowly using a stirrer to obtain floc ).
At this time, in the case of a small scale processing facility, the rapid reaction tank preferably has a function of rapidly mixing an inline mixer when necessary.
In addition, the medicine supply unit may include a facility for automatically inputting the medicine by the medicine pump after determining the amount of the flocculant and the auxiliary coagulant to be supplied in a proportional control manner according to the inflow amount of the overflow water and the inflow water quality concentration.
It is also possible to provide a mixing facility in which the auxiliary coagulant stock solution can be mixed with water at a certain ratio to form a polymer with an appropriate injection concentration.
It is preferable that such a chemical tank is formed so as to be able to store a quantity of medicine which can be used for about one month for each medicine.
The
At this time, the sludge settling portion is settled in the lower portion of the filtration tank by solid-liquid separation by the solid-liquid separation method, and then discharged to the outside at regular intervals using a pump during the filtration treatment, and a large amount of backwash water And a discharging device is provided so as to be discharged to the outside at a time.
At this time, the disinfection treatment water tank is connected to the rear end of the pipe through which the overflow water passes through the filter material through the overflow water pipe through the overflow water conveyance pipe, and the disinfection treatment device is formed on the pipe line, As shown in FIG.
At this time, the
That is, in the process of filtering the overflow water in the filtration tank, the CD artificial floatation material is lost to the upper part of the filtration tank due to the hydraulic pressure of the overflow water or the overflow water supplied in the filtration and backwashing process A screen is provided with a screen or the like so as to prevent the water from flowing out, and a stable water quality is ensured by controlling the outlet flow rate evenly.
In addition, when the LCD artificial floating material filled in the filtration tank is used for a long time, the float can be partially adsorbed on the filter material because the weight of the LCD artificial floating material becomes heavy due to adhesion of flocs and sinks There is a risk of being lost to the bottom of the filtration tank.
Therefore, a screen or a strainer is provided in the lower portion of the filter material to prevent the problem, thereby improving the above-mentioned problem.
The artificial floating
At this time, the artificial floating filter material is obtained by firing and firing the glass powder at a high temperature, so that it is possible to remarkably increase the filtration speed because the pores are abundant and the surface area is very wide.
That is, since the artificial floating filter material using the LCD glass can be filtrated in a state where it is floated in the filtration tank, it is possible to improve the economical efficiency by reducing the facility area by increasing the filtration speed, And the like.
The
At this time, the overflow
In other words, the perforated type overflow conveying pipe has a plurality of holes per predetermined interval, so that if the overflow is introduced into the filtration tank, it can be discharged to the LCD artificial floating material layer through the plurality of holes, Can be increased.
Also, it is preferable that the porous distribution end of the porous percolating water transfer pipe is formed in a cross shape at the lower end portion, that is, in the vicinity of the lower portion of the filtration tank, and is formed to be fixed to the sidewall of the filtration tank to prevent the separation by water pressure.
Thus, the bottom fixed type overflow conveying pipe is formed to minimize the turbulent flow when the overflow water enters the filtration tank through the pipe.
In addition, soil or flocs mixed in the overflow water are discharged through the perforations to induce rapid sedimentation, while sediments settling in the sedimentation part of the filtration tank are formed so as to be prevented from sweeping up.
In addition, the overflow water conveyance pipe is formed so as to prevent the backflow and the opening and closing of the vacuum cleaner.
That is, the overflow water conveying pipe of the present invention is formed such that the overflow water is passed through the holes of the perforated outer peripheral surface and partly flows into the LCD artificial floating material layer to be filtered, and the remaining part is conveyed to the lower part of the filtration tank, So as to minimize sedimentation effect by minimizing the flowability of flocs deposited at the bottom of the filtration tank due to influent overflow.
The
At this time, the
That is, if the operation time of the filtration tank becomes longer, the flow velocity of the overflow or the flow rate of the treated water is lowered as the contaminant collecting amount increases between the LCD artificial floating filter media, or the water level of the tank before the overflow is increased do.
In this case, the LCD artificial floating media should be backwashed to remove the contaminants trapped between the LCD artificial floating media.
In other words, when the flow rate or the water level sensed through the detection sensor for detecting the flow velocity or the water level reaches a predetermined set value, the supply of the overflow water supplied to the filtration tank is stopped by using the inflow- And the air and the backwash water are supplied to clean the LCD artificial floating material.
At this time, in order to backwash the LCD artificial floating material, the valve of the overflow water pipe is closed, air is blown through the air supply unit provided at the lower part of the filtration tank, the LCD artificial floating material flows, So that the pollutants are separated and discharged to the sludge discharge pipe under the filtration tank.
At this time, it is also possible to supply the treated water through the outlet pipe to the upper portion of the filtration tank, or to provide a separate backwash water supply device.
At this time, the air supply unit may include a blower for injecting air for cleaning the LCD artificial floating filter of the filtration tank and an air storage tank capable of storing air made in the blower, so that the air stored in the air storage tank can be supplied to the filtration tank equally It is preferable to provide a lattice type anagen pipe below the filtration tank underfeed portion.
In the embodiment of the present invention, the backwash water is supplied back through the outlet pipe as an example, but a separate backwash water supply device is provided.
The disinfection
The disinfection
In addition, the
That is, the disinfection apparatus is an ion sterilizing apparatus for disinfecting coliform bacteria accommodated in treated water that has been overflowed through a filtration tank. The disinfection and disinfection method of the present invention can reduce the risk of carcinogenesis caused by chlorine disinfection and disinfection by- THM generation and alternative disinfection technologies ozone and UV sterilization persistence problem, which is a disinfection method, is composed of an ion release unit and a control unit.
That is, copper (Cu) and silver (Ag) ions produced by the electrolysis of copper-silver (Cu-Ag) alloy having proven sterilizing power are supplied to the flow- (Cu) and silver (Ag) ions to release the copper (Cu) and silver (Ag) cations and to maintain the sterility of the remaining copper It is an integral structure connected to a channel that is attached to the negative charge area and destroys the cell structure and prevents the cell from absorbing or multiplying nutrients and performs the sterilizing function. It is composed of a cell type including an electrode for ion release, It has easy features.
At this time, the control unit of the disinfection device (ion sterilization device) is configured to control the amount of ion emission of the electrode by the voltage output proportional to the fluctuation of the flow rate by the current signal, the flow rate switch and the timer attached to the flowmeter.
In summary, according to the present invention, when rainwater effluent and sewage are mixed into a sewage treatment plant in a sewage pipeline during rainfall, the remaining sewage water excluding the sewage treated in the normal sewage (1Q) is filtered at high speed using LCD artificial floating media .
In the case of existing sewage treatment plants, it is considered that there is a limit that it is difficult to secure sufficient free space to install additional sewage water treatment facilities due to the saturation of the site for installation of the facilities. Therefore, the sewage effluent treatment facility requires a small footprint, And to develop a technology that can handle it.
Accordingly, the present invention compares the site area required for installing the first settling basin of the sewage treatment plant and the site area required for application of the present invention, which are presented in the above-mentioned sewerage facility standard, as shown in Table 3 below.
As shown in Table 3, when the present invention is applied to improve the primary settling basin installed in an existing sewage treatment plant, there is no need to reserve a spare site or it is possible to install a treatment facility by securing a minimum site It is necessary to carefully consider whether it is applicable in consideration of the on-site conditions because there are limitations such as the partial shutdown of the existing treatment facilities when the facilities are improved.
It will be understood by those skilled in the art that various changes in form and details may be made therein without departing from the spirit and scope of the present invention as defined by the appended claims and their equivalents. Of course, such modifications are within the scope of the claims.
100 ...
111 ...
120 ...
131 ...
150 ...
200 ...
220 ... artificial floating
231 ...
240 ... media
300 ... overflow
320 ... Porous distribution stage
400 ... Backwashing device
500 ... disinfection
520 ...
522 ...
540 ... backwash feeder
Claims (9)
The overflow water conveyance pipe 300 is formed such that a porous distribution stage 320 having a cross shape is formed under the filtration tank and the porous distribution stage 320 is fixed to the side wall of the filtration tank A high - speed treatment device for sewage effluent using foaming artificial floating media having natural eco - friendliness and resource recyclability.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020150098155A KR101581241B1 (en) | 2015-07-10 | 2015-07-10 | Apparatus for treating rainwater and overflow water of confluent water drainage |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1020150098155A KR101581241B1 (en) | 2015-07-10 | 2015-07-10 | Apparatus for treating rainwater and overflow water of confluent water drainage |
Publications (1)
Publication Number | Publication Date |
---|---|
KR101581241B1 true KR101581241B1 (en) | 2015-12-31 |
Family
ID=55129158
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1020150098155A KR101581241B1 (en) | 2015-07-10 | 2015-07-10 | Apparatus for treating rainwater and overflow water of confluent water drainage |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR101581241B1 (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106745976A (en) * | 2016-12-13 | 2017-05-31 | 江苏龙腾工程设计股份有限公司 | Novel rainwater is regulated and stored processing pond and its processing method of regulating and storing |
CN107522360A (en) * | 2017-09-18 | 2017-12-29 | 浙江问源环保科技股份有限公司 | A kind of sewage collecting and processing system for being discharged into river course |
CN110668700A (en) * | 2019-11-12 | 2020-01-10 | 上海超高环保科技股份有限公司 | Manufacturing method of high-temperature-resistant sintered filter plate by using waste glass |
CN116588997A (en) * | 2023-05-19 | 2023-08-15 | 苏州天瑞环境科技有限公司 | Wastewater treatment device |
CN116750853A (en) * | 2023-08-22 | 2023-09-15 | 山东北成环境工程有限公司 | Sewage preliminary screening filter equipment of organic wastewater treatment |
CN116789332A (en) * | 2023-08-24 | 2023-09-22 | 天津中环天元环境检测技术服务有限公司 | Mariculture wastewater treatment device |
CN117964021A (en) * | 2024-03-29 | 2024-05-03 | 兴泰建设集团有限公司 | V-shaped filter tank for sewage treatment |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100960015B1 (en) * | 2009-08-28 | 2010-05-28 | 주식회사 부강테크 | Waste water treatment apparatus for processing early rain effectively and the method thereof |
KR100978070B1 (en) * | 2010-06-18 | 2010-08-26 | 미라클워터 주식회사 | Filtraion apparatus having ss filtering type and backwash-water discharge type |
KR101231458B1 (en) | 2012-05-21 | 2013-02-07 | (주)세원이엔지 | Street inlet |
KR101288471B1 (en) | 2013-05-14 | 2013-07-26 | (주)세원이엔지 | First flush stormwater treatment apparatus |
KR20140132126A (en) * | 2013-05-07 | 2014-11-17 | 한국도로공사 | Bottom-up type upflow filter tank for waste water diposal of tunnel excavation |
KR101527005B1 (en) * | 2014-10-06 | 2015-06-09 | 주식회사 에코빅 | A pollutant purification apparatus |
-
2015
- 2015-07-10 KR KR1020150098155A patent/KR101581241B1/en active IP Right Grant
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100960015B1 (en) * | 2009-08-28 | 2010-05-28 | 주식회사 부강테크 | Waste water treatment apparatus for processing early rain effectively and the method thereof |
KR100978070B1 (en) * | 2010-06-18 | 2010-08-26 | 미라클워터 주식회사 | Filtraion apparatus having ss filtering type and backwash-water discharge type |
KR101231458B1 (en) | 2012-05-21 | 2013-02-07 | (주)세원이엔지 | Street inlet |
KR20140132126A (en) * | 2013-05-07 | 2014-11-17 | 한국도로공사 | Bottom-up type upflow filter tank for waste water diposal of tunnel excavation |
KR101288471B1 (en) | 2013-05-14 | 2013-07-26 | (주)세원이엔지 | First flush stormwater treatment apparatus |
KR101527005B1 (en) * | 2014-10-06 | 2015-06-09 | 주식회사 에코빅 | A pollutant purification apparatus |
Cited By (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106745976A (en) * | 2016-12-13 | 2017-05-31 | 江苏龙腾工程设计股份有限公司 | Novel rainwater is regulated and stored processing pond and its processing method of regulating and storing |
CN107522360A (en) * | 2017-09-18 | 2017-12-29 | 浙江问源环保科技股份有限公司 | A kind of sewage collecting and processing system for being discharged into river course |
CN107522360B (en) * | 2017-09-18 | 2024-02-02 | 浙江问源环保科技股份有限公司 | Sewage collection and treatment system discharged into river channel |
CN110668700A (en) * | 2019-11-12 | 2020-01-10 | 上海超高环保科技股份有限公司 | Manufacturing method of high-temperature-resistant sintered filter plate by using waste glass |
CN110668700B (en) * | 2019-11-12 | 2021-09-03 | 上海超高环保科技股份有限公司 | Manufacturing method of high-temperature-resistant sintered filter plate by using waste glass |
CN116588997A (en) * | 2023-05-19 | 2023-08-15 | 苏州天瑞环境科技有限公司 | Wastewater treatment device |
CN116750853A (en) * | 2023-08-22 | 2023-09-15 | 山东北成环境工程有限公司 | Sewage preliminary screening filter equipment of organic wastewater treatment |
CN116750853B (en) * | 2023-08-22 | 2024-01-26 | 山东北成环境工程有限公司 | Sewage preliminary screening filter equipment of organic wastewater treatment |
CN116789332A (en) * | 2023-08-24 | 2023-09-22 | 天津中环天元环境检测技术服务有限公司 | Mariculture wastewater treatment device |
CN116789332B (en) * | 2023-08-24 | 2023-11-07 | 天津中环天元环境检测技术服务有限公司 | Mariculture wastewater treatment device |
CN117964021A (en) * | 2024-03-29 | 2024-05-03 | 兴泰建设集团有限公司 | V-shaped filter tank for sewage treatment |
CN117964021B (en) * | 2024-03-29 | 2024-06-07 | 兴泰建设集团有限公司 | V-shaped filter tank for sewage treatment |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
KR101581241B1 (en) | Apparatus for treating rainwater and overflow water of confluent water drainage | |
KR101696189B1 (en) | Apparatus for treating rainwater and overflow water of confluent water drainage | |
US9908800B2 (en) | System and method for wastewater treatment | |
Bhargava | Physico-chemical waste water treatment technologies: an overview | |
AU2010291882B2 (en) | An apparatus and method for the treatment of water | |
CN104108830B (en) | Recycled water advanced treatment and reclaiming system | |
Bagundol et al. | Efficiency of slow sand filter in purifying well water | |
JP2004510566A (en) | Method and apparatus for treating wastewater | |
US4128477A (en) | Method for the treatment of sea discharged sewage | |
EP2707334B1 (en) | Biological treatment process and installation including air-lift and post-treatment in filter | |
KR20170074401A (en) | Advanced treatment apparatus to removing nitrogen and phosphorus from wastewater | |
CN208776538U (en) | A kind of domestic sewage processing system | |
JP2011110533A (en) | Upward filtration apparatus | |
Malik et al. | Low-cost municipal wastewater treatment options for use in Pakistan–a review | |
WO1999001385A1 (en) | Waste water treatment system | |
CN204058185U (en) | Integration ecological waste water treater | |
CN214781321U (en) | Novel rural sewage centralized treatment recycles device | |
Marloth | Wastewater and Water Utilities | |
JP5266436B2 (en) | Organic wastewater treatment method and apparatus | |
Wang et al. | Electroflotation | |
JP2002239570A (en) | Apparatus for recycling waste water | |
CA1036952A (en) | Process for the treatment and disposal of septic tank effluents | |
Knežević et al. | ANALYSIS OF TECHNICAL AND TECHNOLOGICAL PARAMETERS OF WASTE WATER TREATMENT PLANT FOR UP TO 15 000 EQUIVALENTS | |
Marloth | Water and Wastewater Utilities | |
Case | Applying ozone technology to treat urban runoff to Santa Monica Bay |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 20181219 Year of fee payment: 4 |
|
FPAY | Annual fee payment |
Payment date: 20191220 Year of fee payment: 5 |