WO2007055500A1 - The sewerage disposal facility of stable - Google Patents
The sewerage disposal facility of stable Download PDFInfo
- Publication number
- WO2007055500A1 WO2007055500A1 PCT/KR2006/004606 KR2006004606W WO2007055500A1 WO 2007055500 A1 WO2007055500 A1 WO 2007055500A1 KR 2006004606 W KR2006004606 W KR 2006004606W WO 2007055500 A1 WO2007055500 A1 WO 2007055500A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- tank
- effluent
- micro
- pipe
- solid
- Prior art date
Links
- 239000007787 solid Substances 0.000 claims abstract description 91
- 239000007788 liquid Substances 0.000 claims abstract description 59
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 43
- 238000005273 aeration Methods 0.000 claims abstract description 39
- 244000144972 livestock Species 0.000 claims abstract description 24
- 238000007667 floating Methods 0.000 claims abstract description 21
- 238000000926 separation method Methods 0.000 claims abstract description 16
- 239000013049 sediment Substances 0.000 claims abstract description 15
- 238000000855 fermentation Methods 0.000 claims description 3
- 230000004151 fermentation Effects 0.000 claims description 2
- 238000009434 installation Methods 0.000 claims 1
- 238000004062 sedimentation Methods 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 29
- 229910052760 oxygen Inorganic materials 0.000 abstract description 9
- 239000001301 oxygen Substances 0.000 abstract description 9
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 8
- 230000008030 elimination Effects 0.000 abstract 1
- 238000003379 elimination reaction Methods 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 23
- 244000005700 microbiome Species 0.000 description 18
- 230000001376 precipitating effect Effects 0.000 description 18
- BPYKTIZUTYGOLE-IFADSCNNSA-N Bilirubin Chemical compound N1C(=O)C(C)=C(C=C)\C1=C\C1=C(C)C(CCC(O)=O)=C(CC2=C(C(C)=C(\C=C/3C(=C(C=C)C(=O)N\3)C)N2)CCC(O)=O)N1 BPYKTIZUTYGOLE-IFADSCNNSA-N 0.000 description 14
- 230000003647 oxidation Effects 0.000 description 7
- 238000007254 oxidation reaction Methods 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 239000003344 environmental pollutant Substances 0.000 description 5
- 229940088597 hormone Drugs 0.000 description 5
- 239000005556 hormone Substances 0.000 description 5
- 231100000719 pollutant Toxicity 0.000 description 5
- 239000008213 purified water Substances 0.000 description 5
- 210000002700 urine Anatomy 0.000 description 5
- 239000000356 contaminant Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 210000003608 fece Anatomy 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 235000013618 yogurt Nutrition 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000006864 oxidative decomposition reaction Methods 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 238000003825 pressing Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 241000282887 Suidae Species 0.000 description 1
- 239000010828 animal waste Substances 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 150000002926 oxygen Chemical class 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000005086 pumping Methods 0.000 description 1
- 239000010453 quartz Substances 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
-
- 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
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/10—Packings; Fillings; Grids
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/74—Treatment of water, waste water, or sewage by oxidation with air
-
- 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
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/305—Endocrine disruptive agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/36—Organic compounds containing halogen
- C02F2101/363—PCB's; PCP's
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/22—Nature of the water, waste water, sewage or sludge to be treated from the processing of animals, e.g. poultry, fish, or parts thereof
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/18—Removal of treatment agents after treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Definitions
- Figure 1 is a simple figure of this invention used to treat effluent discharged from intensive livestock industries
- Figure 2 is the status figure of this invention of used to treat effluent discharged from intensive livestock industries.
- Figure 3 shows a simple figure of this invention with of the aid aeration tank to treat effluent discharged from intensive livestock industries.
- Figure 4 shows a simple figure of this invention added to a fermentation tank to treat effluent discharged from intensive livestock industries.
- Figure 5 shows a figure this invention using examples of media to treat effluent discharged from intensive livestock industries
- Figure 6 shows a simple figure of this invention using an example of a micro-bubble generator to treat effluent discharged from intensive livestock industries.
- Figure 7 is figure of this invention removing solid substances to treat effluent discharged from intensive livestock industries.
- the aid air spring tank 71 The aid micro-bubble generator
- the aid connecting tube 71b The aid control valve
- This invention relates to treatment of effluent discharged from intensive livestock industries.
- the effluent consists of mostly solid substances in high concentrations, such as excrement, thereby preventing the growth of microorganism. This precludes the application of ordinary treatment method using microorganisms.
- effluent discharged from hogs, being excrement and urine has BOD of 15,000-20,000 ⁇ m
- the effluent consists mostly of solid substances with minimal oxygen content. Consequently without treatment, micro-organisms can not survive; treatment of solid matter takes considerable time.
- Hog wastes are the hardest to treat among all farm animal wastes, as it contains a fine sludge, making separation of solids and liquids difficult.
- the pressure floatation method is expensive to build, difficult operate, has high operating costs and causes public nuisance due to large amounts of noise generating by an air blower during oxidation and after separation of solids and liquid.
- the present invention aims to solve the problems arising from the current effluent disposal methods by pumping micro-bubbles with diameter 1-50 jam to effluent in order to separate solids from the liquid, and then treatment of the liquid.
- the invention further aims to treat liquid separated from floating solids by aeration and to enhance the effectiveness of treatment methods using the micro-bubble and hollow media.
- This invention relates to the treatment of effluent discharged from intensive livestock industries.
- This invention will first separate solids from the effluent by use of micro-bubble generator and then treat the remaining liquid.
- the invention breaks polluting hormones and the animal excrement bilirubin by providing micro-bubble containing ozone to the aeration tank.
- an ultraviolet lamp will break down any residual ozone.
- the structure of this invention is as follows: the effluent is pumped inside; the first micro-bubble generator connected to an air blower and installed on the lower part; at one end of the of the discharge pipe is the solid/liquid separation tank; the other end of the discharge pipe is connected to the central pipe, which carries the discharge from the solid/liquid separation tank to inside of the invention, this is located on the interior where an exit tube of the solid/liquid separation tank is installed.
- disposal water ended precipitating process flows to the inside in which thousands of media are packed in below of the aeration tank installed the second micro-bubble generator connected to the air blower, ⁇ 64>
- the disposal water of the aeration tank flows to the inside, installed in bellow the third micro-bubble generator connected to the ozonizer and the entry of ozone tank which micro-bubble containing ozone provided inside.
- Aerated disposal water in ozone tank flows inside, where installed ultraviolet lamp, and consists of ultraviolet tank installed the exit of the purified water on one side. Disposal water of the aeration tank flows to the inside.
- the effluent providing piped 1) consist of one exit pipe is connected to the solid liquid separating tank(l ⁇ ), or each pipe of disposal effluent can be connected to the solid liquid separating tank(l ⁇ ).
- the first micro-bubble generator(12) provides micro-bubble from bottom to the top of the solid liquid separating tank(l ⁇ ) due to transfer floating solid of the effluent(lOO) to the surface.
- the first micro-bubble generator(12) consists of the motor(12c), the im ⁇ eller(12d), the rotating axis(12e), the spraying nozzle and slit formed slit wall(12g) as shown on the figure 6 together with ' micro- bubble solving equipment' which Korean patent No.10-0465755 by applicant of this invention.
- the number of impeller(12d) is not limited as two, it can be as one , three and so on.
- ⁇ 75> Also, even not showing as figure but it can be consist of together with 'micro-bubble solving equipment' which Korean patent No.10- 0465755 by applicant of this invention.
- the floated floating solidOO) can be removed by hand work, or if prepared ,send to the fermenting tank(80) connected to the solid liquid separating tank(l ⁇ ) as shown on figure 4.
- solid removing equipment(14) installed the solid removing equipment(14) at top of the solid liquid separating tank(l ⁇ ), floating solid can be flown to the fermenting tank using the solid removing equipment(14) ⁇ 81>
- the solid removing equipment(14) consists of motor(14a), rotating roller(14b), belt(14c) connectable to the rotating roller(14b),the wing(14d) removing the solid are installed to the belt(14c)and which can be used.
- the precipitating tank(20) as shown on the figure 2 became slope at bottom of the wall, installed centric pipe emptied in middle and is connected , and its effluent discharge pipe(13) is connected to the centric pipe(21).
- slope shaped hunch can be installed inside of the precipitating tank(20).
- the purpose of the sediment tank(20) formed like above is that after separating liquid and solid from liquid solid separating tank(l ⁇ ) if the solid left in the disposal effluent(lOO) making ppt and eliminating entirely.
- the centric pipe(21) is installed in the middle of sediment tank(20)and the first treated effluent(lOO) from the liquid solid tank (10) flows to the centric pipe(21), the first treated effluent (100) in the centric pipe flows to the low part from which flows to outside of the centric pi ⁇ e(21) and make it elevate to upper part and make the solid precipitating easily.
- the lower part of the centric pipe(21) is not located on the bottom of the sediment tank(20) but apart some.
- the filter(23a) is installed at the exit of sediment tank(23) to prevent the flowing solid (90) goes to the next step.
- the aeration tank(30), one of essential part of this invention, is connected to the exit of sediment tank(23) that the disposal effluent(lOO) finished precipitating process is going to flow to the inside.
- the second micro bubble generator(32) is the same structure, and form the first micro bubble generator(12).
- the media (31) is empty of inside of small body which discard bottle or container can be used; the plastic yogurt bottle is the best.
- ⁇ 105> In this time, to escalate the activity of the microorganism make hole(31a) on the bottom of the yogurt bottle so that the micro-bubble providing more.
- This configuration is that from the second micro bubble generator (32)produce the bubble diameter 1-5 im, and this bubble escalate through the media(31) and provide the air to the microorganism residing in the media(31).
- the ozone treatment > tank(40) is that the disposal effluent(100)aerated firstly in the aeration tank(30) flow inside , and installed the third micro-bubble generator(41) with aeration tank(30).
- the third micro-bubble generator(41) can be used that the same as the first micro-bubble generator(41) explained as above. ⁇ 117> In this time ,due to the third micro-bubble generator(41) connected to the ozonizer(42) from which produce micro-bubble containing ozone and provide to the inside of ozone treatment tank(40).
- the ozonizer(42) can be used with the equipment prescribed on the applicant of this invention registered the Korean No.10-0509813' the equipment of resolving ozone into water as high efficiently and the method to use it.
- the reason for providing the micro-bubble containing ozone to inside of the ozone treatment tank(40) is that beside simply purify the effluent(lOO) and decompose the substance like bilirubin and various environmental hormone in feces and urine of intensive livestock industries.
- several of the aid aeration tank (70) can be installed between the aeration tank(30) and the ozone treatment tank(40) as showing on the figure 4.
- the aid aeration tank(70) like these can be formed one room or more according to the exit speed and quantity of the disposal effluent (100).
- the media(31) and the aid micro -bubble generator(71) are installed as the same as the aeration tank(30).
- the aid micro-bubble generator(71) is connected to the ventilator (60), at one side of the aid aeration tank(70) the exit of aid aeration tank is formed to discharge the aerated disposal water.
- the ventilator( ⁇ ) and the aid micro -bubble generator (71) are connected through the aid connecting pipe(71a), installing the aid controlling valve(71b) at one side of the aid connecting pipe(71a) is effective.
- the ultraviolet wave is 253-255nm so that decompose the left ozone and pollutants and better to install two of the quartz ultraviolet lamp(51) which produce 253.7nm ultraviolet ray.
- the treatment facility of intensive livestock industries effluent can be constructed with variety shape like concrete structure or tank beside tank structure.
- the first micro-bubble generator(12) and the ventilator( ⁇ ) ' are connected to the first connecting pipe(12a), the second micro-bubble generator(32) and the ventilator( ⁇ O) to the second connecting pipe(32a), the third micro-bubble generator(41) and the ventilator(60)connecting through the third connecting pipe(41a), and on each connecting pipe installed each control valve ie, the first connecting pipe(12a) to the first control valve(12b), the second connecting pipe(32a) to the second control valve(32b), and the connecting pipe(41a) to the third control valve(41b), thus supplying air can be controlled.
- the supplying air can be controlled by the control valve of supplying pi ⁇ e(22b) installed to the air supplying pi ⁇ e(22a) connected to the ventilator(60).
- SUBSTITOTE SHEET (RULE 26) supplies from lower to the upper part of the solid liquid separating tank (10).
- the aeration tank has the first aeration process through media(31) and micro-bubble produced from the second micro-bubble generator (32) installed inside and purified by contact oxidation.
- the ultraviolet lamp(51) is installed at ultraviolet treatment tank, this ultraviolet lamp(51) decompose the ozone contained in the treated effluent flown from the ozone treatment tank(40).
- ⁇ 152> Instead used big ventilator in contact oxidation method, using small ventilator almost noiseless treatment facility can be provided.
- ⁇ 153> Using the micro-bubble generator able to dissolve high concentration ozone in water, owing to dissolve high concentration ozone in treated effluent, the treatment method by ozone is provided.
- ⁇ 154> Especially, provided ozone able to decompose pcb and environmental hormone effectively.
- the facility is simple, because of dissolving micro-bubble diameter 1-50 [M in disposal water the quantity of dissolved oxygen is high therefore the efficiency of treatment is high up.
Abstract
This invention relates to the treatment of effluent discharged from intensive livestock industries. This invention consists of,effluent passing through its interior, the first micro-bubble generator that is connected with the ventilator and installed on its lower part; a solid/liquid separation tank installed on one side of the effluent discharge pipe; a central pipe installed on the other side of this and allows the liquid effluent from the solid/liquid separation tank to flow back to the interior; a return pipe that is installed on the interior of the center pipe, one end of which is connected to the solid/liquid separation tank, the other end is connected with a pipe supplying air connected to a ventilator, which is then connected to the sediment tank; the aeration tank houses the second micro-bubble generator, which is connected to the ventilator on the lower part, this is connected to the sediment tank housing numerous media; the ozone treatment tank houses the third micro-bubble generator, which is connected to the ozonizer and the effluent from the aeration tank is then discharged into the ultraviolet tank, which has an ultraviolet lamp installed on its interior. By use of micro-bubbles to enhance the elimination rate of floating solids, and media to supply ozone rich oxygen, this invention aims to provide a highly effective method of treating effluent discharged from livestock intensive industries.
Description
[Title of Invention]
The Sewerage Disposal facility of Stable
[Summary Explanation of figure]
<1> Figure 1 is a simple figure of this invention used to treat effluent discharged from intensive livestock industries
<2>Figure 2 is the status figure of this invention of used to treat effluent discharged from intensive livestock industries.
<3> Figure 3 shows a simple figure of this invention with of the aid aeration tank to treat effluent discharged from intensive livestock industries.
<4> Figure 4 shows a simple figure of this invention added to a fermentation tank to treat effluent discharged from intensive livestock industries.
<5> Figure 5 shows a figure this invention using examples of media to treat effluent discharged from intensive livestock industries
<6> Figure 6 shows a simple figure of this invention using an example of a micro-bubble generator to treat effluent discharged from intensive livestock industries.
<7> Figure 7 is figure of this invention removing solid substances to treat effluent discharged from intensive livestock industries.
<8> Detailed description of important items .
<9> 10: Solid/Liquid separation tank 11: Effluent supplying pipe
<10> 12:The first micro bubble generator. 12a : The first connecting pipe
<11> 12b : The first control valve 12c :The motor
<12> 12d : The impeller: 12e : The rotation axis
<13> 12f : The spraying nozzle 12g : The slit of separating wall
<14> 13: The effluent discharge pipe
14 : The removal equipment of solids <15> 14a : electric motor 14b '• Rotating roller <16> 14c : Belt 14d : Wing
<17> 15 : Solids exit 20 : Precipitation tank <17> 15 : Solids exit 20 : Precipitation tank <18> 21 : Centric tube 22 : Return pipe
<19> 22a : Air supplying pipe 22b : Control valve of supplying pipe <20> 23 : Exit of precipitate tank 23a : Filter <21> : Air spring tank 31 : Media
<22> 31a : Hole 32 : The second micro -bubble generator <23> 32A : The second connecting tube
32b : The second control valve <24> 33 : Box 34 : Exit of air spring tank
<25> 40 : Ozone entry tank 41: The third micro-bubble generator <26> 41a : The third connecting tube 41b : The third control valve <27> 42 : Ozonizer 43 : Ozone entry tank exit
<28> 50 : Ultraviolet tank 51 : Ultraviolet lamp
<29> 52 : The exit of treated water 60 : Ventilator
<30> 70 : The aid air spring tank 71 : The aid micro-bubble generator
<31> 71a ". The aid connecting tube 71b : The aid control valve
<32> 72 : The exit of the aid air spring tank 80 : The fermenting tank
<33> 90 : The floating solid material 100 : The effluent
<34> 110 : The separator 12
[Detailed explanation of the Invention]
[Purpose of the Invention]
[Technical area of this invention and the Prior Art in this Area]
<35> This invention relates to treatment of effluent discharged from intensive livestock industries.
<36> The effluent discharged from intensive livestock industries is a mixture of excrement and urine.
<37> The effluent consists of mostly solid substances in high concentrations, such as excrement, thereby preventing the growth of microorganism. This precludes the application of ordinary treatment method using microorganisms.
<38> For an instance, effluent discharged from hogs, being excrement and urine has BOD of 15,000-20,000ρρm,
<39> The effluent consists mostly of solid substances with minimal oxygen content. Consequently without treatment, micro-organisms can not survive; treatment of solid matter takes considerable time.
<40> Therefore, a more efficient way to treat the liquid after it has separated from solids is to apply the oxidation method through contact with microorganisms.
<41> Hog wastes are the hardest to treat among all farm animal wastes, as it contains a fine sludge, making separation of solids and liquids difficult.
<42> Presently, centrifuge, filter-pressing, pressure floating methods are used to separate solids and liquids. However, under the current centrifuge method, solids under a certain size still cannot be separated entirely.
<43> The filter-pressing method is complicated and expensive in both facility and labour required; despite this it cannot separate solid substances below a certain size.
<44> The pressure floatation method is expensive to build, difficult operate, has high operating costs and causes public nuisance due to large amounts of noise generating by an air blower during oxidation and after separation of solids and liquid.
<45> The technology related to this invention purifies effluent using microorganism, "The treatment system of effluent" (Korean patent No.
10-0226213) using media to allow microorganisms to habit invented by applicant of this invention.
<46> Although the media in the above methods make use of aerobic microorganisms, problems arise due to their complicated systems of re- washing of media, returning of sludge and ventilator.
<47> To resolve this problem, "The aerobic treatment method of effluent and treatment tank " (The Korean patent No.10-0409056) using aeration device in water(120) and separator (110) for effluent treatment was invented by the Applicant of this invention.
<48> The existing methods contain a problem of low purifying effect due to aeration in a single treatment tank.
<49> the existing methods contain a further a problem in that there are no steps for the separation of floating solid substances in effluent, or its method is ineffective.
[The technological aim of the invention]
<50> The present invention aims to solve the problems arising from the current effluent disposal methods by pumping micro-bubbles with diameter 1-50 jam to effluent in order to separate solids from the liquid, and then treatment of the liquid.
<51> The invention further aims to treat liquid separated from floating solids by aeration and to enhance the effectiveness of treatment methods using the micro-bubble and hollow media.
<52> Further, by supplying ozone containing micro-bubbles to the aeration tank, another aim is to break down polluting hormones as well as other substances found in animal excrements.
<53> The effluent treatment process will be made more effective by using an ultraviolet lamp which will be used to break down residual ozone
<54> Noise pollution will be kept to a minimum through use of a small capacity air pump.
[Composition of Invention]
<55> This invention relates to the treatment of effluent discharged from intensive livestock industries.
<56> This invention will first separate solids from the effluent by use of micro-bubble generator and then treat the remaining liquid.
<57> The liquid will then be treated by using media and micro-bubbles.
<58> The invention breaks polluting hormones and the animal excrement bilirubin by providing micro-bubble containing ozone to the aeration tank.
<59> Furthermore, an ultraviolet lamp will break down any residual ozone.
<60> The structure of this invention is as follows: the effluent is pumped inside; the first micro-bubble generator connected to an air blower and installed on the lower part; at one end of the of the discharge pipe is the solid/liquid separation tank; the other end of the discharge pipe is connected to the central pipe, which carries the discharge from the solid/liquid separation tank to inside of the invention, this is located on the interior where an exit tube of the solid/liquid separation tank is installed.
<61> In the middle of inside installed center pipe, the other side of the exit pipe of disposal effluent connected to the center pipe disposal water of the solid liquid separating tank flows to the inside through the center pipe, inside of the center pipe installed returning pipe which of one side connected to the solid liquid separating tank.
<62> On the other side of the returning pipe connected to the air blower the precipitate in bellow make returning to the solid liquid separating tank like thus precipitating tank.
<63> Connected to the precipitating tank, disposal water ended precipitating process flows to the inside in which thousands of media are packed in below of the aeration tank installed the second micro-bubble generator connected to the air blower,
<64> The disposal water of the aeration tank flows to the inside, installed in bellow the third micro-bubble generator connected to the ozonizer and the entry of ozone tank which micro-bubble containing ozone provided inside.
<65> Aerated disposal water in ozone tank flows inside, where installed ultraviolet lamp, and consists of ultraviolet tank installed the exit of the purified water on one side. Disposal water of the aeration tank flows to the inside.
<66> The technical aspects of this invention are described further on the attached diagram .
<67> The diagram is attached only as an explanatory aid for the invention, and its intrinsic worth is not limited to merely what is contained in the diagram.
<68> The effluent(lOO) of intensive livestock industry flows to the inside of the solid/liquid separation tank(lθ), in which the ventilation mechanism (60) is connected to the first micro-bubble generator (12) on the lower part of it, also installed on the lower part one end of the effluent discharge pipe. (13)
<69> As shown in Figure 2, the ventilator(60) is connected to outside ,the ventilator (60) and the first micro-bubble generator(12) are connected through the first connecting pipe(12a).
<70> Just, through the first connecting pipe(12a) the air from ventilator provides to the first micro-bubble generator (12)
<71> To flow the effluent(lOO) into the inside, preparing collecting pipe or collecting tank to collect the effluent(lOO) from intensive livestock industries then the effluent providing piped 1) consist of one exit pipe is connected to the solid liquid separating tank(lθ), or each pipe of disposal effluent can be connected to the solid liquid separating tank(lθ).
<72> The first micro-bubble generator(12) provides micro-bubble from bottom to the top of the solid liquid separating tank(lθ) due to transfer floating solid of the effluent(lOO) to the surface.
<73> The first micro-bubble generator(12) consists of the motor(12c), the imρeller(12d), the rotating axis(12e), the spraying nozzle and slit formed slit wall(12g) as shown on the figure 6 together with ' micro- bubble solving equipment' which Korean patent No.10-0465755 by applicant of this invention.
<74> In this time, the number of impeller(12d) is not limited as two, it can be as one , three and so on.
<75> Also, even not showing as figure but it can be consist of together with 'micro-bubble solving equipment' which Korean patent No.10- 0465755 by applicant of this invention.
<76> Normally the effluent(lOO) of hog farm excretes together with feces and urine and its floating solidOO) is 18,000-20,000mg/ 1 .
<77> In this time, passing the micro-bubble diameter l~50 //m through the first micro-bubble generator (12) described above, the floating solid adapted to the micro-bubble and make it floating.
<78> The floated floating solidOO) can be removed by hand work, or if prepared ,send to the fermenting tank(80) connected to the solid liquid separating tank(lθ) as shown on figure 4.
<79> The methods of sending the floating solid (90) to the fermenting tank(80) are by hand work or have flow the floating solid (90) naturally to the fermenting tank(80)which built next to the solid liquid separating tank(10)and make the open wall between the fermenting tank(80) and the solid liquid separating tank(lθ).
<80> Also, installed the solid removing equipment(14) at top of the solid liquid separating tank(lθ), floating solid can be flown to the fermenting tank using the solid removing equipment(14)
<81> The solid removing equipment(14) consists of motor(14a), rotating roller(14b), belt(14c) connectable to the rotating roller(14b),the wing(14d) removing the solid are installed to the belt(14c)and which can be used.
<82>also, making the solid exit(15) at the upper part of the solid liquid separating tank(lθ) and removed solid to the wing(14d) can be eliminated through the solid exit(15).
<83> The precipitating tank(20), one of essential part of this invention, installed the next to the solid liquid separating tank(lθ), is built to get the first treated effluent(lOO) from the solid liquid separating tank(lθ) through effluent discharge pipe(13).
<84> In this time, the precipitating tank(20) as shown on the figure 2 became slope at bottom of the wall, installed centric pipe emptied in middle and is connected , and its effluent discharge pipe(13) is connected to the centric pipe(21).
<85> To precipitate the solid at the center of the precipitating tank(20) slope shaped hunch can be installed inside of the precipitating tank(20).
<86> Just, the effluent(lOO) of the solid liquid separating tank(10 )became to flow inside of the precipitating tank(20) through the centric pipe(21), but it makes to gather in the middle.
<87> The reason for installing one side of the effluent discharge pipe(13) to the lower part of solid liquid separating tank(lθ) and the other side connects to the centric pipe (21) of the precipitating tank(20) is that the first treated effluent (100) have sent to the precipitating tank(20) due to contain small quantity of solid after separated solid and liquid in the solid liquid separating tank(lθ).
<88> Inside of the centric pipe of the precipitating tank(20) installed the returning pipe(22) through which the solid of the precipitating tank(20) return to the solid liquid separating tank(lθ).
<89> The returning pipe(22) installed up to the bottom of the precipitating tank(20) in the centric pipe, the upper part of the returning pipe(22) connected to the upper part of solid liquid separating tank(lθ).
<90> And, the returning pipe(22), at the lower part of it, connected to the blower(22a) which connected to the ventilator(βθ)
<91> Just, the air from ventilator (60) through air pipe(22a) is provided to the lower part of the returning pipe (22) and moved to the upper part of the returning pipe(22), in this time the precipitate return together to the solid liquid separating tank.
<92> This is the principle of the air pump, blowing air to the lower part of the pipe filled with liquid ,the air goes to the upper part, at same time the part of pipe with mixed air and liquid become lower pressure than the
bottom part of liquid so that the liquid not containing air push the liquid containing air which has lower pressure .
<93> The purpose of the sediment tank(20) formed like above is that after separating liquid and solid from liquid solid separating tank(lθ) if the solid left in the disposal effluent(lOO) making ppt and eliminating entirely.
<94> The centric pipe(21) is installed in the middle of sediment tank(20)and the first treated effluent(lOO) from the liquid solid tank (10) flows to the centric pipe(21), the first treated effluent (100) in the centric pipe flows to the low part from which flows to outside of the centric piρe(21) and make it elevate to upper part and make the solid precipitating easily.
<95> Therefore, the lower part of the centric pipe(21) is not located on the bottom of the sediment tank(20) but apart some.
<96> The exit of sediment tank(23) is formed at the upper part of the sediment tank for treated effluent(lOO) finished precipitating process to flow to the next step.
<97> The filter(23a) is installed at the exit of sediment tank(23) to prevent the flowing solid (90) goes to the next step.
<98>The aeration tank(30), one of essential part of this invention, is connected to the exit of sediment tank(23) that the disposal effluent(lOO) finished precipitating process is going to flow to the inside.
<99> The thousands of media are filled the inside of aeration tank(30) of which at the lower part installed the second micro bubble generator(32) connected to the ventilator(60).
<100> the second micro bubble generator(32) is the same structure, and form the first micro bubble generator(12).
<101> The way filling thousands of media at the inside of aeration tank(30) is various.
<102> As showing on the figure, after forming the shape(33) of the iron net, stainless net or pvc net, the media put into the shape(33) or put into inside the square shape(33) formed with pore upper and lower part of it .
<103> In this time, it is better to install the shape(33) at the place of 50cm from the aeration tank(30) and the upper of the shape(33) is going to be at 30cm below of water.
<104> The media (31) is empty of inside of small body which discard bottle or container can be used; the plastic yogurt bottle is the best.
<105> In this time, to escalate the activity of the microorganism make hole(31a) on the bottom of the yogurt bottle so that the micro-bubble providing more.
<106> This configuration is that from the second micro bubble generator (32)produce the bubble diameter 1-5 im, and this bubble escalate through the media(31) and provide the air to the microorganism residing in the media(31).
<107> The aeration tank(30) formed like this, purifies the contaminant in treated effluent(lOO) separated the solid from the sediment tank(20) by microorganism through contact oxidation aeration.
<108> In this time, from the second micro bubble generator(32) provide oxygen by the bubble, the microorganism purifies the disposal water using this oxygen.
<109> It is better that the media are filled with indifferently when the media(31) formed ρore(31a) at bottom stands strait the micro- bubble goes through inside much, then much oxygen provide , so that the aerobic microorganism can live vividly and this microorganism oxidate the contaminants, so that effluent(lOO) become purified.
<110> Also, in the media(31) layed as side the oxygen cannot be provided therefore anaerobic microorganism live inside of the media(31), by the
anaerobic fermentation the contaminant in the effluent(lOO) become purified.
<111> In the media stands leaning as 45° ,30°, 15°, the middle of aerobic and anaerobic microorganism live and that can purify the effluent(lOO).
<112> Like this, using as media(31) formed hole(31a) at bottom of yogurt bottle, so this media installed indifferently that whole range of microorganism with aerobic, anaerobic and middle of both live together, then the ability of treatment is much upgrade.
<113> These various microorganism is occurring naturally, or put them prior in the media(31) and install that later to grow microorganism .
<114> And also, at one side of the aeration tank(30) the exit of aeration tank(34) is formed to discharge the disposal effluent(lOO).
<115> One of the essential part of this invention, the ozone treatment >tank(40) is that the disposal effluent(100)aerated firstly in the aeration tank(30) flow inside , and installed the third micro-bubble generator(41) with aeration tank(30).
<116> The third micro-bubble generator(41) can be used that the same as the first micro-bubble generator(41) explained as above.
<117> In this time ,due to the third micro-bubble generator(41) connected to the ozonizer(42) from which produce micro-bubble containing ozone and provide to the inside of ozone treatment tank(40).
<118> In the ozone treatment tank(40) the bilirubin( yellowish red color) and PCB in the disposal effluent(lOO) flowed from aeration tank(30) are decomposed by oxidation.
<119) Due to discharge the treated effluent(lOO) decomposed bilirubin and pvc by oxidation ,the exit of ozone treatment tank(43) is formed on one side of the inner part of ozone treatment tank(40).
<120> The ozonizer(42)can be used with the equipment prescribed on the applicant of this invention registered the Korean No.10-0509813' the equipment of resolving ozone into water as high efficiently and the method to use it.
<121> Also, these ozonizer(42) known as publicly precise description is omitted.
<122> Through these ozonizer(42) and the third micro-bubble generator(41) provides micro-bubble to inside of ozone treatment tank(40),for instance of which ozone 5-15 vol.% oxygen 85-95 vol.% can be used.
<123> The reason for providing the micro-bubble containing ozone to inside of the ozone treatment tank(40) is that beside simply purify the effluent(lOO) and decompose the substance like bilirubin and various environmental hormone in feces and urine of intensive livestock industries.
<124> In this time , several of the aid aeration tank (70) can be installed between the aeration tank(30) and the ozone treatment tank(40) as showing on the figure 4.
<125> This is that if the house of intensive livestock industries big enough, the speed of flowing and exiting of treated effluent(lOO) into the aeration tank(30) become fast, in this case due to the insufficient aeration make difficult of purifying the disposal water.
<126> Therefore, the aid aeration tank(70) like these can be formed one room or more according to the exit speed and quantity of the disposal effluent (100).
<127> At the inside of the aid aeration tank(70) ,the media(31) and the aid micro -bubble generator(71) are installed as the same as the aeration tank(30).
<128> Also, the aid micro-bubble generator(71) is connected to the ventilator (60), at one side of the aid aeration tank(70) the exit of aid aeration tank is formed to discharge the aerated disposal water.
<129> And , the ventilator(βθ) and the aid micro -bubble generator (71) are connected through the aid connecting pipe(71a), installing the aid controlling valve(71b) at one side of the aid connecting pipe(71a) is effective.
<130> One of essential part of this invention, the ultraviolet treatment tank(50) inside of which flown the disposal effluent(lOO) finishing decompose process of bilirubin and environmental hormone in the ozone treatment tank(40) and installed ultraviolet lamp(51) which sterilize the treated effluent(lOO) and decompose the left ozone in the treated effluent(lOO).
<131> And on one side installed the exit(52) of the purified water finishing the treatment process.
<132> In this time, the ultraviolet wave is 253-255nm so that decompose the left ozone and pollutants and better to install two of the quartz ultraviolet lamp(51) which produce 253.7nm ultraviolet ray.
<133> If the wave for decomposing ozone and the wave for pollutants are different several ultraviolet lamp(51) generating different rays can be installed.
<134> And on one side of the ultraviolet treatment tank (50) installed the exit(52) of the purified water to discharge the disposal effluent(lOO) finishing treatment process.
<135> Like above, the treatment facility of intensive livestock industries effluent can be constructed with variety shape like concrete structure or tank beside tank structure.
<136> Also, the first micro-bubble generator(12) and the ventilator(βθ)' are connected to the first connecting pipe(12a), the second micro-bubble generator(32) and the ventilator(ΘO) to the second connecting pipe(32a), the third micro-bubble generator(41) and the ventilator(60)connecting through the third connecting pipe(41a), and on each connecting pipe installed each control valve ie, the first connecting pipe(12a) to the first control valve(12b), the second connecting pipe(32a) to the second control valve(32b), and the connecting pipe(41a) to the third control valve(41b), thus supplying air can be controlled.
<137> And the supplying air can be controlled by the control valve of supplying piρe(22b) installed to the air supplying piρe(22a) connected to the ventilator(60).
<138> Like this ,it is better that the first micro-bubble generator(12) ,the second micro-bubble generator(32),the third micro-bubble generator(41) and the air supplying pipe(22a) are connecting to the one ventilator. But it is not limited but can be connected to each ventilator(βθ). <139> Following is the explanation of this invention structured like above.
<140> Seeing the process of the treatment of intensive livestock industries effluent, first the effluent(lOO) including urine and feces flow to the solid liquid separating tank (10).
<141> When the effluent(lOO) was flown into the solid liquid separating tank (10), moving the first micro-bubble generator(12) and micro-bubble
20
SUBSTITOTE SHEET (RULE 26)
supplies from lower to the upper part of the solid liquid separating tank (10).
<142> In this process the floating solid(90)in the effluent (100) combine with micro-bubble gathers on the upper part, the gathered floating solid (90) send to the fermenting tank(80) through solid removing tool(14) or by hand work.
<143> Or as describing above, made the upper wall lowered between the solid liquid separating tank (10) and the fermenting tank(80) the floating solid(90) mounting on the wall eliminates naturally into the fermenting tank. (80).
<144> The disposal effluent(lOO) in the solid liquid separating tank (10) moves to the sediment tank(20) through the exit of disposal water(13), precipitating the remained solid in the sediment tank(20) through the returning pipe the precipitated floating solid transfer again to the solid liquid separating tank (10) and the disposal water finished precipitating process flows to the aeration tank(30).
<145> The aeration tank has the first aeration process through media(31) and micro-bubble produced from the second micro-bubble generator (32) installed inside and purified by contact oxidation.
<146> Once aerated treated effluent(lOO) flows to the ozone treatment tank, (40)
because the third micro-bubble generator (41)and the ozonizer(42) are installed at the ozone treatment tank (40) in which bilirubin and pollutants are processed to oxidative decomposition by oxygen containing ozone.
<147> The treated effluent(lOO) finished oxidative decomposition of bilirubin and pollutants in the ozone treatment tank(40) flows into the ultraviolet treatment tank(50).
<148> The ultraviolet lamp(51) is installed at ultraviolet treatment tank, this ultraviolet lamp(51) decompose the ozone contained in the treated effluent flown from the ozone treatment tank(40).
<149>Also, by using the wave of the ultraviolet lamp(51) the remained pollutants can be sterilized.
<150> The purified water finished the process of sterilizing and ozone decomposing discharge through the exit of purified water.(52)
[ The effect of the invention]
<151> According to this invention , providing micro -bubble diameter 1- 50 IM to the floating solid in disposal water the floating solid can be decomposed easily in the effluent.
<152> Instead used big ventilator in contact oxidation method, using small ventilator almost noiseless treatment facility can be provided.
<153> Using the micro-bubble generator able to dissolve high concentration ozone in water, owing to dissolve high concentration ozone in treated effluent, the treatment method by ozone is provided.
<154> Especially, provided ozone able to decompose pcb and environmental hormone effectively.
<155> Also, the facility is simple, because of dissolving micro-bubble diameter 1-50 [M in disposal water the quantity of dissolved oxygen is high therefore the efficiency of treatment is high up.
<156> And purifying by aeration the disposal water separated floating solid , using the media with empty space inside and micro-bubble, the efficiency of treatment is high up.
<157> The treatment facility of high efficacy be provided that using the ultraviolet lamp decomposes the remained ozone.
Claims
[claim 1]
In relation to this invention to treat effluent discharged from intensive livestock industries, the effluent produced by intensive livestock industries is passed through to the interior of the invention; the first micro-bubble generator is connected to the ventilator on the lower part; the solids separation tank installed on one side; the interior of the invention, where the central pipe is installed on the other side of where the effluent discharge pipe is connected to the center pipe; liquid from the solid liquid separation tank flows inwards through the center pipe; the return pipe connects to one side of the center pipe; connected to the other side of this return pipe is the solid/liquid separation tank; the air supply pipe is connected with the ventilator that is connected on one side, allowing for the return of solids after it has separated from the liquid effluent through sedimentation in the sediment tank;
Connection to the sediment tank allows liquid effluent to flow back to the interior after the sediment has settled; there are numerous media found in the interior; the aeration tank is connected to the second micro-bubble generator and the ventilator; the effluent from the aeration tank flows back inside; installed on the lower part is the third micro-bubble generator which is connected with an ozone generator; the ozone treatment tank allowing supply of the ozone containing micro-bubble back into the interior; the aerated effluent flows back into the interior, where an ultraviolet lamp is also installed, the ultraviolet treatment tank which is located on one side the exit where the treated liquid is discharged; the scope of the claim for the invention to treat effluent discharged from intensive livestock industries, which consists of but not is limited to the above.
[claim 2]
In relation to claim 1,
This invention to treat effluent discharged from intensive livestock industries, allows floating solids to pass through a fermentation tank that is connected to the solid/liquid separation tank.
[claim 3]
In relation to claim 1,
This invention to treat effluent discharged from intensive livestock industries, allows several stages of aeration due to the installation of several assisting media between the aeration tank and the ozone treatment tank.
[claim 4 ]
In claim l,This invention to treat effluent discharged from intensive livestock industries, contains a mechanism for removal of solids from the upper part of the solids separation tank.
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KR10-2005-0107790 | 2005-11-11 | ||
KR20050107790A KR100665664B1 (en) | 2005-11-11 | 2005-11-11 | The sewage disposal facility of stable |
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WO2007055500A1 true WO2007055500A1 (en) | 2007-05-18 |
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PCT/KR2006/004606 WO2007055500A1 (en) | 2005-11-11 | 2006-11-06 | The sewerage disposal facility of stable |
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WO (1) | WO2007055500A1 (en) |
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KR200447584Y1 (en) * | 2009-08-14 | 2010-02-10 | 김남순 | Movable Sewage Treatment Toilet |
KR101599797B1 (en) * | 2014-10-16 | 2016-03-04 | 주식회사 동부환경 | Water treatment method for sewage disposal tank |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5466367A (en) * | 1994-04-06 | 1995-11-14 | Environmental Restoration Services, Inc. | Industrial waste water treatment |
KR20020030764A (en) * | 2002-03-28 | 2002-04-25 | 서영진 | Wastewater treatment and Composting method of domestic animals feces and urine |
KR20020039283A (en) * | 2002-04-06 | 2002-05-25 | 서영진 | Treated method of a nightsoil |
KR20030065092A (en) * | 2002-01-29 | 2003-08-06 | 엄태경 | The procces and apparatus of Livestock wastewater treatment. |
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KR20030037196A (en) * | 2001-11-02 | 2003-05-12 | 정팔진 | Ionized gas, coagulation-precipitation, zeolite and activated carbon system and method for treating livestock wastewater |
KR100621792B1 (en) * | 2005-01-19 | 2006-09-13 | 주식회사 젠트로 | Livestock Wastewater Treating System |
-
2005
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Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5466367A (en) * | 1994-04-06 | 1995-11-14 | Environmental Restoration Services, Inc. | Industrial waste water treatment |
KR20030065092A (en) * | 2002-01-29 | 2003-08-06 | 엄태경 | The procces and apparatus of Livestock wastewater treatment. |
KR20020030764A (en) * | 2002-03-28 | 2002-04-25 | 서영진 | Wastewater treatment and Composting method of domestic animals feces and urine |
KR20020039283A (en) * | 2002-04-06 | 2002-05-25 | 서영진 | Treated method of a nightsoil |
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