CN108249690A - Pasture waste water treatment system - Google Patents
Pasture waste water treatment system Download PDFInfo
- Publication number
- CN108249690A CN108249690A CN201611240046.6A CN201611240046A CN108249690A CN 108249690 A CN108249690 A CN 108249690A CN 201611240046 A CN201611240046 A CN 201611240046A CN 108249690 A CN108249690 A CN 108249690A
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- China
- Prior art keywords
- waste water
- treatment system
- chamber
- water treatment
- dephosphorization
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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- 238000004065 wastewater treatment Methods 0.000 title claims abstract description 155
- 238000006243 chemical reaction Methods 0.000 claims abstract description 359
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 285
- 238000005189 flocculation Methods 0.000 claims abstract description 40
- 230000016615 flocculation Effects 0.000 claims abstract description 40
- 238000000034 method Methods 0.000 claims abstract description 39
- 230000008569 process Effects 0.000 claims abstract description 37
- 239000003513 alkali Substances 0.000 claims abstract description 20
- 239000003054 catalyst Substances 0.000 claims abstract description 19
- 239000007800 oxidant agent Substances 0.000 claims abstract description 18
- 230000001590 oxidative effect Effects 0.000 claims abstract description 18
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 10
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 8
- 238000001556 precipitation Methods 0.000 claims description 205
- 239000010802 sludge Substances 0.000 claims description 199
- 238000007872 degassing Methods 0.000 claims description 180
- 239000002351 wastewater Substances 0.000 claims description 151
- 239000007789 gas Substances 0.000 claims description 126
- 238000000855 fermentation Methods 0.000 claims description 97
- 238000005192 partition Methods 0.000 claims description 75
- 238000005273 aeration Methods 0.000 claims description 68
- 238000003756 stirring Methods 0.000 claims description 45
- 238000000926 separation method Methods 0.000 claims description 38
- 238000004062 sedimentation Methods 0.000 claims description 31
- 239000002244 precipitate Substances 0.000 claims description 27
- 238000005276 aerator Methods 0.000 claims description 24
- 230000008676 import Effects 0.000 claims description 24
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 22
- 239000002253 acid Substances 0.000 claims description 17
- 239000003795 chemical substances by application Substances 0.000 claims description 16
- 239000004576 sand Substances 0.000 claims description 16
- 238000005345 coagulation Methods 0.000 claims description 15
- 230000015271 coagulation Effects 0.000 claims description 15
- 229910052698 phosphorus Inorganic materials 0.000 claims description 13
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 12
- 230000003647 oxidation Effects 0.000 claims description 12
- 238000007254 oxidation reaction Methods 0.000 claims description 12
- 239000011574 phosphorus Substances 0.000 claims description 12
- 229910021529 ammonia Inorganic materials 0.000 claims description 11
- 230000001376 precipitating effect Effects 0.000 claims description 11
- 239000000701 coagulant Substances 0.000 claims description 10
- 239000007788 liquid Substances 0.000 claims description 8
- 238000010992 reflux Methods 0.000 claims description 8
- 238000009287 sand filtration Methods 0.000 claims description 8
- 239000013049 sediment Substances 0.000 claims description 7
- 229910019142 PO4 Inorganic materials 0.000 claims description 6
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims description 6
- 239000010452 phosphate Substances 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 4
- 230000001112 coagulating effect Effects 0.000 claims description 4
- 239000002699 waste material Substances 0.000 claims description 3
- 229910052757 nitrogen Inorganic materials 0.000 claims description 2
- 238000005086 pumping Methods 0.000 claims description 2
- 238000005265 energy consumption Methods 0.000 abstract description 8
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 abstract description 5
- 238000011084 recovery Methods 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 4
- 230000000694 effects Effects 0.000 description 22
- 238000010586 diagram Methods 0.000 description 20
- 238000007599 discharging Methods 0.000 description 13
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 12
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 9
- 238000005516 engineering process Methods 0.000 description 9
- 239000001301 oxygen Substances 0.000 description 9
- 229910052760 oxygen Inorganic materials 0.000 description 9
- 238000002156 mixing Methods 0.000 description 8
- 239000000203 mixture Substances 0.000 description 7
- 238000007667 floating Methods 0.000 description 6
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 5
- CKMXBZGNNVIXHC-UHFFFAOYSA-L ammonium magnesium phosphate hexahydrate Chemical compound [NH4+].O.O.O.O.O.O.[Mg+2].[O-]P([O-])([O-])=O CKMXBZGNNVIXHC-UHFFFAOYSA-L 0.000 description 5
- 230000015556 catabolic process Effects 0.000 description 5
- 238000006731 degradation reaction Methods 0.000 description 5
- 235000019441 ethanol Nutrition 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 4
- 230000004151 fermentation Effects 0.000 description 4
- 239000003337 fertilizer Substances 0.000 description 4
- 238000005188 flotation Methods 0.000 description 4
- 239000000047 product Substances 0.000 description 4
- 239000007787 solid Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- ZZSNKZQZMQGXPY-UHFFFAOYSA-N Ethyl cellulose Chemical group CCOCC1OC(OC)C(OCC)C(OCC)C1OC1C(O)C(O)C(OC)C(CO)O1 ZZSNKZQZMQGXPY-UHFFFAOYSA-N 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 238000011010 flushing procedure Methods 0.000 description 3
- 239000013505 freshwater Substances 0.000 description 3
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 2
- 238000006065 biodegradation reaction Methods 0.000 description 2
- 230000003139 buffering effect Effects 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000001913 cellulose Substances 0.000 description 2
- 229920002678 cellulose Polymers 0.000 description 2
- 239000006185 dispersion Substances 0.000 description 2
- 230000003628 erosive effect Effects 0.000 description 2
- 239000011790 ferrous sulphate Substances 0.000 description 2
- 235000003891 ferrous sulphate Nutrition 0.000 description 2
- 239000003205 fragrance Substances 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 239000011261 inert gas Substances 0.000 description 2
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 2
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 2
- 239000011777 magnesium Substances 0.000 description 2
- 239000002957 persistent organic pollutant Substances 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- 229920000742 Cotton Polymers 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 206010016825 Flushing Diseases 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- MXZRMHIULZDAKC-UHFFFAOYSA-L ammonium magnesium phosphate Chemical compound [NH4+].[Mg+2].[O-]P([O-])([O-])=O MXZRMHIULZDAKC-UHFFFAOYSA-L 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- -1 biogas Inorganic materials 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000001506 calcium phosphate Substances 0.000 description 1
- 229910000389 calcium phosphate Inorganic materials 0.000 description 1
- 235000011010 calcium phosphates Nutrition 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000012512 characterization method Methods 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000001727 in vivo Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 1
- RUTXIHLAWFEWGM-UHFFFAOYSA-H iron(3+) sulfate Chemical compound [Fe+3].[Fe+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O RUTXIHLAWFEWGM-UHFFFAOYSA-H 0.000 description 1
- 229910000360 iron(III) sulfate Inorganic materials 0.000 description 1
- 239000006210 lotion Substances 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 239000008267 milk Substances 0.000 description 1
- 210000004080 milk Anatomy 0.000 description 1
- 235000013336 milk Nutrition 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000032696 parturition Effects 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000008247 solid mixture Substances 0.000 description 1
- 229910052567 struvite Inorganic materials 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 230000002459 sustained effect Effects 0.000 description 1
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 description 1
- AAKBLFQBZDFKMP-UHFFFAOYSA-H trimagnesium azane diphosphate Chemical compound N.[Mg+2].[Mg+2].[Mg+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O AAKBLFQBZDFKMP-UHFFFAOYSA-H 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
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
-
- 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
- C02F3/28—Anaerobic digestion processes
- C02F3/2813—Anaerobic digestion processes using anaerobic contact processes
-
- 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
- C02F3/28—Anaerobic digestion processes
- C02F3/2866—Particular arrangements for anaerobic reactors
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- 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
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- 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
- C02F1/722—Oxidation by peroxides
-
- 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
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- 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
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/026—Fenton's reagent
-
- 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
-
- 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
- C02F3/30—Aerobic and anaerobic processes
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Microbiology (AREA)
- Organic Chemistry (AREA)
- Biodiversity & Conservation Biology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Physical Water Treatments (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention discloses a kind of pasture waste water treatment systems, the pasture waste water treatment system is included along the sequentially connected pretreatment system in waste water treatment process direction, COD and denitrogenation processing system and advanced treatment system, wherein, the advanced treatment system is included along the sequentially connected Fenton's reaction device in the waste water treatment process direction and active carbon filter, the Fenton's reaction device includes Fenton's reaction pond, there is the Fenton's reaction chamber being sequentially communicated along the waste water treatment process direction in the Fenton's reaction pond, PH adjusts back chamber, devolatilizing chamber and Fenton flocculation chamber, there is the Fenton's reaction chamber acid to add mouth, catalyst adds mouth and oxidant adds mouth, there is the PH readjustments chamber alkali to add mouth, the Fenton flocculation chamber has flocculant concentration mouth.Pasture waste water treatment system according to embodiments of the present invention has many advantages, such as that processing capacity is strong, utilized conducive to energy recovery and environmental protection, can reduce water consumption and energy consumption.
Description
Technical field
The present invention relates to environmental technology field, in particular to a kind of pasture waste water treatment system.
Background technology
Pasture waste water mostlys come from cowshed and Nai Ting ground flushings workshop section, and water consumption is big, COD in waste water, nitrogen, phosphorus, solid
Body suspended matter and salinity are higher, and hard-degraded substance is more, and intractability is high.Pasture waste water treatment system processing in the relevant technologies
Ability is poor, and waste water is longer in the temporary pool residence time, causes energy waste and environmental pollution, and water consumption and energy consumption are higher.
Invention content
The present invention is directed to solve one of above-mentioned technical problem in the relevant technologies at least to a certain extent.For this purpose, this hair
Bright to propose a kind of pasture waste water treatment system, which there is processing capacity to utilize by force, conducive to energy recovery
With environmental protection, can reduce water consumption and energy consumption, the advantages that.
To achieve the above object, a kind of pasture waste water treatment system is proposed according to an embodiment of the invention, and the pasture is given up
Water treatment system is included along the sequentially connected pretreatment system in waste water treatment process direction, COD and denitrogenation processing system and depth
Processing system is spent, wherein, the advanced treatment system includes Fenton's reaction device, and the Fenton's reaction device includes Fenton's reaction
Pond has the Fenton's reaction chamber being sequentially communicated along the waste water treatment process direction, PH readjustments chamber, de- in the Fenton's reaction pond
Air cavity and Fenton flocculation chamber, the Fenton's reaction chamber is with acid adds mouth, catalyst adds mouth and oxidant adds mouth, the PH
There is readjustment chamber alkali to add mouth, and the Fenton flocculation chamber has flocculant concentration mouth.
Pasture waste water treatment system according to embodiments of the present invention is utilized by force, conducive to energy recovery with processing capacity and ring
Border protection can reduce the advantages that water consumption and energy consumption.
In addition, pasture waste water treatment system according to embodiments of the present invention can also have following additional technical characteristic：
According to one embodiment of present invention, the pretreatment system includes successively connecting along the waste water treatment process direction
Setting pot, solid-liquid separator and the adjusting tank connect.
According to one embodiment of present invention, the setting pot is equipped with pretreatment mud scraper.
According to one embodiment of present invention, it is connected with confession between the adjusting tank and the COD and denitrogenation processing system
Material pump.
According to one embodiment of present invention, the COD and denitrogenation processing system are included along the waste water treatment process side
To sequentially connected anaerobic fermentation reaction unit, high load aeration tank, denitrification reactor and dephosphorizing reactor.
According to one embodiment of present invention, the anaerobic fermentation reaction unit include anaerobic fermentation tank body, stripping tube and
Air supply pipe, the anaerobic fermentation tank body is interior to have anaerobic reaction room, and the anaerobic reaction room has waste water inlet, water outlet and row
Gas port, the stripping tube are located in the anaerobic reaction room, and the upper end of the stripping tube has gas outlet and the stripping tube
Lower end has air inlet, and the air supply pipe is connected with the air inlet of the stripping tube, is used for for being supplied into the stripping tube
The gas of air lift.
According to one embodiment of present invention, the lower end of the stripping tube is adjacent to the bottom of the anaerobic reaction room and described
The upper end of stripping tube extends to the top of the anaerobic reaction room, and the water outlet is located at the top of the anaerobic reaction room and height
In the upper end of the stripping tube.
According to one embodiment of present invention, the upper surface of the stripping tube is opened wide to form the gas outlet, the gas
The lower face for carrying pipe is opened wide to form the air inlet.
According to one embodiment of present invention, the stripping tube include the straight pipe that vertically extends and with it is described straight
The segmental arc that the upper end of pipeline section is connected, the angle between the opening direction and vertically downward direction of the gas outlet are more than or equal to
Zero degree and less than 180 degree.
According to one embodiment of present invention, the segmental arc is inverted U-shaped, the opening direction of the gas outlet vertically to
Under.
According to one embodiment of present invention, the stripping tube is multiple and is arranged at intervals in the horizontal plane.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Precipitate separator, the precipitation
Separator is located in the anaerobic reaction room and above the stripping tube, and the precipitation separator has and the water outlet
The connected separator water outlet and water outlet is connected with the high load aeration tank.
According to one embodiment of present invention, the precipitation separator includes：It is heavy to be formed with degassing in the babinet for babinet
Shallow lake chamber, it is described degassing precipitation chamber bottom have sludge outlet, it is described degassing precipitation chamber lower part cross-sectional area along on to
Under direction be gradually reduced；Partition board, the partition board are located at the top of the degassing precipitation chamber, and the partition board precipitates the degassing
The top of chamber is separated into degassing district and settling zone, the bottom of the degassing district connected with the bottom of the settling zone so as to waste water from
The anaerobic reaction room overflows in the degassing district and then is flowed in the settling zone from the bottom of the degassing district；Precipitation is oblique
Plate, the precipitation inclined plate are located in the settling zone；Downflow weir, the downflow weir is located in the settling zone and the downflow weir
Form the overflow launder with the separator water outlet.
According to one embodiment of present invention, the upper edge for the box portion for limiting the degassing district with the partition board is less than
The upper edge of the partition board and limited with the partition board settling zone box portion upper edge.
According to one embodiment of present invention, the babinet is cuboid, the first longitudinal side wall of the lower part of the babinet
Lower end extends downward beyond the lower end of the second longitudinal side wall of the lower part of the babinet, and the lower end of first longitudinal side wall with it is described
The lower end of second longitudinal side wall is overlapped in the up-down direction.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Precipitate separator, the precipitation
Separator is located at that the anaerobic fermentation tank is external and the water outlet passes through the precipitation separator and the high load aeration tank
It is connected, the precipitation separator includes：Babinet, forms degassing precipitation chamber in the babinet, the degassing precipitation chamber have import,
Separator water outlet and sludge outlet, the import are connected with the water outlet, the separator water outlet and the high load capacity
Aeration tank is connected, and the lower part of the degassing precipitation chamber is formed as cross-sectional area is gradually reduced along direction from the top down at least one
A conical cavity, the sludge outlet are formed in the bottom of the conical cavity；Precipitation inclined plate, the precipitation inclined plate are located at the degassing
Precipitate intracavitary；Downflow weir, the downflow weir are located to be formed in the degassing precipitation intracavitary and the downflow weir and be detached with described
The overflow launder of device water outlet connection.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Sinker, the sinker connect
It is connected between the import of water outlet and the degassing precipitation chamber of the anaerobic reaction room.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：For that will go out from the sludge
The sludge of mouth discharge returns to the indoor mud return line of the anaerobic reaction, one end of the mud return line and the anaerobism
Reative cell connects, and the sludge outlet is connected with the mud return line by sludge discharge pipe, is set on the mud return line
There is sludge reflux pump.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Water sealed tank, the anaerobic fermentation
The top of tank body is equipped with safe gas port, and the safe gas port is connected with the water sealed tank.
According to one embodiment of present invention, the denitrification reactor include the anaerobic ammonia oxidation reactor that is connected to each other and
Anoxic/Aerobic reaction tank.
According to one embodiment of present invention, the dephosphorizing reactor includes：Coagulation reaction tank, in the coagulation reaction tank
The dephosphorization flocculation chamber being connected with the dephosphorization reaction chamber being connected with the denitrification reactor and with the dephosphorization reaction chamber, it is described to remove
Phosphorus reaction intracavitary is equipped with the fast blender of dephosphorization and dephosphorization flocculation intracavitary is equipped with the slow blender of dephosphorization；Dephosphorization sedimentation basin, it is described
Dephosphorization sedimentation basin is connected respectively with dephosphorization flocculation chamber and the advanced treatment system, and dephosphorization is equipped in the dephosphorization sedimentation basin
Tilted plate separator and dephosphorization mud scraper.
According to one embodiment of present invention, the dephosphorizing reactor further includes：Coagulant solution tank, the coagulant are molten
Flow container is connected with the dephosphorization reaction chamber；Phosphate eliminating flocculant tank, the phosphate eliminating flocculant tank are connected with dephosphorization flocculation chamber.
According to one embodiment of present invention, the COD and denitrogenation processing system are included along the waste water treatment process side
To sequentially connected anaerobic fermentation reaction unit, waste water dephosphorization reaction unit and denitrification reactor.
According to one embodiment of present invention, the anaerobic fermentation reaction unit include anaerobic fermentation tank body, stripping tube and
Air supply pipe, the anaerobic fermentation tank body is interior to have anaerobic reaction room, and the anaerobic reaction room has waste water inlet, water outlet and row
Gas port, the stripping tube are located in the anaerobic reaction room, and the upper end of the stripping tube has gas outlet and the stripping tube
Lower end has air inlet, and the air supply pipe is connected with the air inlet of the stripping tube, is used for for being supplied into the stripping tube
The gas of air lift；The waste water dephosphorization reaction unit includes dephosphorization reacting tank body, aerator and degassing precipitation separator, described
There is dephosphorization reative cell, the dephosphorization reative cell has water inlet and dephosphorization agent adding mouth, the aeration in dephosphorization reacting tank body
Device is located in the dephosphorization reative cell, and the degassing precipitation separator is located in the dephosphorization reative cell and positioned at the aeration
Above device, for detaching gas and water and sludge.
According to one embodiment of present invention, the lower end of the stripping tube is adjacent to the bottom of the anaerobic reaction room and described
The upper end of stripping tube extends to the top of the anaerobic reaction room, and the water outlet is located at the top of the anaerobic reaction room and height
In the upper end of the stripping tube.
According to one embodiment of present invention, the upper surface of the stripping tube is opened wide to form the gas outlet, the gas
The lower face for carrying pipe is opened wide to form the air inlet.
According to one embodiment of present invention, the stripping tube include the straight pipe that vertically extends and with it is described straight
The segmental arc that the upper end of pipeline section is connected, the angle between the opening direction and vertically downward direction of the gas outlet are more than or equal to
Zero degree and less than 180 degree.
According to one embodiment of present invention, the segmental arc is inverted U-shaped, the opening direction of the gas outlet vertically to
Under.
According to one embodiment of present invention, the stripping tube is multiple and is arranged at intervals in the horizontal plane.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Precipitate separator, the precipitation
Separator is located in the anaerobic reaction room and above the stripping tube, and the precipitation separator has and the water outlet
The connected separator water outlet and water outlet is connected with the water inlet of the waste water dephosphorization reaction unit.
According to one embodiment of present invention, the precipitation separator includes：It is heavy to be formed with degassing in the babinet for babinet
Shallow lake chamber, it is described degassing precipitation chamber bottom have sludge outlet, it is described degassing precipitation chamber lower part cross-sectional area along on to
Under direction be gradually reduced；Partition board, the partition board are located at the top of the degassing precipitation chamber, and the partition board precipitates the degassing
The top of chamber is separated into degassing district and settling zone, the bottom of the degassing district connected with the bottom of the settling zone so as to waste water from
The anaerobic reaction room overflows in the degassing district and then is flowed in the settling zone from the bottom of the degassing district；Precipitation is oblique
Plate, the precipitation inclined plate are located in the settling zone；Downflow weir, the downflow weir is located in the settling zone and the downflow weir
Form the overflow launder with the separator water outlet.
According to one embodiment of present invention, the upper edge for the box portion for limiting the degassing district with the partition board is less than
The upper edge of the partition board and limited with the partition board settling zone box portion upper edge.
According to one embodiment of present invention, the babinet is cuboid, the first longitudinal side wall of the lower part of the babinet
Lower end extends downward beyond the lower end of the second longitudinal side wall of the lower part of the babinet, and the lower end of first longitudinal side wall with it is described
The lower end of second longitudinal side wall is overlapped in the up-down direction.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Precipitate separator, the precipitation
Separator is located at that the anaerobic fermentation tank is external and the water outlet is reacted by the precipitation separator with the waste water dephosphorization
Device is connected, and the precipitation separator includes：Babinet, the babinet is interior to form degassing precipitation chamber, and the degassing, which precipitates chamber, to be had
Import, separator water outlet and sludge outlet, the import are connected with the water outlet, and the separator water outlet gives up with described
Water dephosphorization reaction unit is connected, and the lower part of the degassing precipitation chamber is formed as cross-sectional area and is gradually reduced along direction from the top down
At least one conical cavity, the sludge outlet is formed in the bottom of the conical cavity；Precipitation inclined plate, the precipitation inclined plate are located at
The degassing precipitation intracavitary；Downflow weir, the downflow weir be located at it is described degassing precipitation intracavitary and the downflow weir in be formed with
The overflow launder of the separator water outlet connection.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Sinker, the sinker connect
It is connected between the import of water outlet and the degassing precipitation chamber of the anaerobic reaction room.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：For that will go out from the sludge
The sludge of mouth discharge returns to the indoor mud return line of the anaerobic reaction, one end of the mud return line and the anaerobism
Reative cell connects, and the sludge outlet is connected with the mud return line by sludge discharge pipe, is set on the mud return line
There is sludge reflux pump.
According to one embodiment of present invention, the anaerobic fermentation reaction unit further includes：Water sealed tank, the anaerobic fermentation
The top of tank body is equipped with safe gas port, and the safe gas port is connected with the water sealed tank.
According to one embodiment of present invention, the aerator has spaced multiple aeration heads or aeration tube.
According to one embodiment of present invention, the waste water dephosphorization reaction unit further includes：Multiple guide shells, it is each described
The top and bottom of guide shell are opened wide, and multiple aeration heads or aeration tube stretch into respectively from the lower end of multiple guide shells
Multiple guide shells.
According to one embodiment of present invention, waste water dephosphorization reaction unit further includes：Be located in the dephosphorization reative cell and
Water distributor below the aerator, the water distributor are connected with the water inlet.
According to one embodiment of present invention, multiple water distribution mouths that the water distributor has interval setting and Open Side Down.
According to one embodiment of present invention, the dephosphorization reative cell has the row positioned at the dephosphorization reacting tank body lower part
Material mouth.
According to one embodiment of present invention, waste water dephosphorization reaction unit further includes：Cyclone, the cyclone have rotation
The import of stream device, mud mouth and cyclone outlet, the cyclone inlets are connected with the discharge gate, and the cyclone outlet passes through
Return pipe is connected with the dephosphorization reative cell.
According to one embodiment of present invention, the waste water dephosphorization reaction unit further includes：Pump and the desliming being connected with pump
Device, the clear liquid after desliming device removing sludge return to the dephosphorization reative cell.
According to one embodiment of present invention, the waste water dephosphorization reaction unit further includes：It pumps and pumps what is be connected with described
Settler, the stillness of night after the settler precipitates return to the dephosphorization reative cell.
According to one embodiment of present invention, the degassing precipitation separator includes：Separator body, the separator sheet
Degassing mud chamber is formed in vivo, and there is sludge to arrange mouth, the horizontal stroke of the lower part of the degassing precipitation chamber for the bottom of the degassing precipitation chamber
Sectional area is gradually reduced along direction from the top down；Baffle, the baffle are located at the top of the degassing mud chamber, the baffle
The top of the degassing mud chamber is separated into devolatilizing chamber and precipitation chamber, the bottom of the devolatilizing chamber and the bottom of the precipitation chamber
Connection is overflowed in the devolatilizing chamber from the dephosphorization reative cell so as to waste water and then is flowed to from the bottom of the devolatilizing chamber described
Precipitate intracavitary；Inclined settling plate tilts sediment tube, and the inclined settling plate or inclination sediment tube are located at the precipitation intracavitary；Go out
Water downflow weir, the effluent overflow weir water is located at the precipitation intracavitary and the effluent overflow weir water is formed to have and be connected with denitrification reactor
The water outlet overflow launder of logical separation outlet.
According to one embodiment of present invention, the upper of the separator body part of the devolatilizing chamber is limited with the baffle
The upper edge of the separator body part of the precipitation chamber is limited along the upper edge less than the baffle and with the baffle.
According to one embodiment of present invention, the cross section of the separator body is rectangle.
According to one embodiment of present invention, the lower end of the first longitudinal side wall of the lower part of the separator body extends downwardly
More than the lower end of the second longitudinal side wall of the lower part of the separator body, and the lower end of first longitudinal side wall is indulged with described second
The lower end of side wall is overlapped in the up-down direction.
According to one embodiment of present invention, the waste water dephosphorization reaction unit further includes：It is located at the dephosphorization retort
The aeration pump or Aeration fan being connected outside body and with the aerator, the water inlet are connected with waste water control valve.
According to one embodiment of present invention, the top of the dephosphorization reacting tank body is equipped with head cover, the dephosphorization agent addition
Mouth is located on the head cover.
According to one embodiment of present invention, the denitrification reactor include the anaerobic ammonia oxidation reactor that is connected to each other and
Anoxic/Aerobic reaction tank.
According to one embodiment of present invention, the COD and denitrogenation processing system further include coagulation reaction device, described mixed
Solidifying reaction unit is connected between the denitrification reactor and the advanced treatment system, and the coagulation reaction device has along institute
State coagulating basin, flocculation basin and sedimentation basin that waste water treatment process direction is sequentially communicated.
According to one embodiment of present invention, the Fenton's reaction pond is equipped with first connected with the Fenton's reaction chamber
Stir air intake；And/or the Fenton's reaction intracavitary is equipped with the first Fenton blender.
According to one embodiment of present invention, the Fenton's reaction pond is equipped with second connected with PH readjustment chambers and stirs
Mix air intake；And/or the PH readjustments intracavitary is equipped with the second Fenton blender.
According to one embodiment of present invention, the Fenton's reaction pond is equipped with the third stirring connected with the devolatilizing chamber
Air intake；And/or third Fenton blender is equipped in the devolatilizing chamber.
According to one embodiment of present invention, the Fenton's reaction pond is equipped with the third stirring connected with the devolatilizing chamber
Air intake, the advanced waste treatment system further include：Air delivery pipe is stirred, the stirring air delivery pipe is by described the
Three stirring air intakes are stretched into the devolatilizing chamber.
According to one embodiment of present invention, the Fenton flocculation intracavitary is equipped with the 4th Fenton blender；And/or the sweet smell
The reaction tank that pauses is equipped with the 4th stirring air intake connected with Fenton flocculation chamber.
According to one embodiment of present invention, the advanced treatment system further includes：Acid adds pipe, the acid add pipe with
The acid adds mouth connection；Catalyst adds pipe, and the catalyst, which adds pipe and adds mouth with the catalyst, to be connected；Oxidant is thrown
Add pipe, the oxidant, which adds pipe and adds mouth with the oxidant, to be connected；Alkali adds pipe, and the alkali adds pipe and added with the alkali
Mouth connection；Flocculant concentration pipe, the flocculant concentration pipe are connected with the flocculant concentration mouth.
According to one embodiment of present invention, it is equipped in the Fenton's reaction pond and separates the Fenton's reaction chamber and the PH
The first partition of chamber is adjusted back, separate the second partition of PH readjustment chamber and the devolatilizing chamber and separates the devolatilizing chamber and described
The bottom wall phase of the lower end and the Fenton's reaction pond of the third partition board of Fenton flocculation chamber, the first partition and the third partition board
Even, the lower end of the second partition is spaced apart with the bottom wall in the Fenton's reaction pond and upper end is higher than the upper end of the first partition
With the upper end of the third partition board.
According to one embodiment of present invention, the Fenton's reaction device further includes Fenton sedimentation basin, the Fenton's reaction
Pond is sequentially communicated with the Fenton sedimentation basin along the waste water treatment process direction.
According to one embodiment of present invention, the advanced treatment system further includes：Continuous sand filter, the continuous filter sand
Device is connected with the Fenton sedimentation basin, and the continuous filter sand utensil has compressed air inlet and sand filtration to rinse water out, the sand
Filter is rinsed water out and is connected with the Fenton's reaction chamber in the Fenton's reaction pond or the Fenton sedimentation basin.
According to one embodiment of present invention, the pasture waste water treatment system further includes and the pretreatment system, institute
State the reuse pipe that at least one of COD and denitrogenation processing system and advanced treatment system are connected.
Description of the drawings
Fig. 1 is the structure diagram of pasture waste water treatment system according to embodiments of the present invention.
Fig. 2 is the structural representation of the anaerobic fermentation reaction unit of pasture waste water treatment system according to embodiments of the present invention
Figure.
Fig. 3 is the structure diagram according to the pasture waste water treatment system of the first alternative embodiment of the invention.
Fig. 4 is the knot according to the anaerobic fermentation reaction unit of the pasture waste water treatment system of the first alternative embodiment of the invention
Structure schematic diagram.
Fig. 5 is according to the heavy of the anaerobic fermentation reaction unit of the pasture waste water treatment system of first alternative embodiment of the invention
Shallow lake cyclone separator arrangement schematic diagram.
Fig. 6 is the structure diagram according to the pasture waste water treatment system of the second alternative embodiment of the invention.
Fig. 7 is the knot according to the anaerobic fermentation reaction unit of the pasture waste water treatment system of the second alternative embodiment of the invention
Structure schematic diagram.
Fig. 8 is the structure diagram according to the pasture waste water treatment system of third alternative embodiment of the present invention.
Fig. 9 is the knot according to the anaerobic fermentation reaction unit of the pasture waste water treatment system of third alternative embodiment of the present invention
Structure schematic diagram.
Figure 10 is the structure diagram according to the pasture waste water treatment system of the 4th alternative embodiment of the invention.
Figure 11 is the anaerobic fermentation reaction unit according to the pasture waste water treatment system of the 4th alternative embodiment of the invention
Structure diagram.
Figure 12 is the waste water dephosphorization reaction unit according to the pasture waste water treatment system of the 4th alternative embodiment of the invention
Structure diagram.
Figure 13 is the waste water dephosphorization reaction unit according to the pasture waste water treatment system of the 4th alternative embodiment of the invention
Degassing precipitation cyclone separator arrangement schematic diagram.
Figure 14 is the structure diagram according to the pasture waste water treatment system of the 5th alternative embodiment of the invention.
Figure 15 is the anaerobic fermentation reaction unit according to the pasture waste water treatment system of the 5th alternative embodiment of the invention
Structure diagram.
Figure 16 is the anaerobic fermentation reaction unit according to the pasture waste water treatment system of the 5th alternative embodiment of the invention
Precipitate cyclone separator arrangement schematic diagram.
Figure 17 is the structure diagram according to the pasture waste water treatment system of the 6th alternative embodiment of the invention.
Figure 18 is the anaerobic fermentation reaction unit according to the pasture waste water treatment system of the 6th alternative embodiment of the invention
Structure diagram.
Figure 19 is the structure diagram according to the pasture waste water treatment system of the 7th alternative embodiment of the invention.
Figure 20 is the anaerobic fermentation reaction unit according to the pasture waste water treatment system of the 7th alternative embodiment of the invention
Structure diagram.
Figure 21 is the structure diagram of the advanced treatment system of pasture waste water treatment system according to embodiments of the present invention.
Figure 22 is that the structure of the advanced treatment system of pasture waste water treatment system in accordance with another embodiment of the present invention is shown
It is intended to.
Reference numeral：
Pasture waste water treatment system 1,
Pretreatment system 70, COD and denitrogenation processing system 80, anaerobic fermentation reaction unit 10, waste water dephosphorization reaction unit
20th, high load aeration tank 30, denitrification reactor 40, dephosphorizing reactor 50, advanced treatment system 60,
Setting pot 71, solid-liquid separator 72, adjust tank 73, pretreatment mud scraper 74, charging pump 75,
Anaerobic fermentation tank body 100, anaerobic reaction room 110, waste water inlet 111, water outlet 112, exhaust outlet 113, substitute
Mouthfuls 114, mud discharging mouth 115, mud discharging valve and/or mud discharging pump 116, charging pump 117, gas control valve 118,
Stripping tube 200, straight pipe 210, air inlet 211, segmental arc 220, gas outlet 221,
Air supply pipe 300,
Precipitate separator 400, babinet 410, degassing precipitation chamber 411, sludge outlet 412, separator water outlet 413, first
Longitudinal side wall 414, the second longitudinal side wall 415, import 416, partition board 420, degassing district 421, settling zone 422, precipitation inclined plate 430, overflow
Weir 440, overflow launder 441,
Sinker 500,
Mud return line 600, sludge reflux pump 610,
Sludge discharge pipe 700,
Water sealed tank 800,
Anaerobic ammonia oxidation reactor 2100, Anoxic/Aerobic reaction tank 2200,
Coagulation reaction tank 3100, dephosphorization reaction chamber 3110, dephosphorization flocculation chamber 3120, the fast blender 3111 of dephosphorization, dephosphorization are slow
Blender 3112, dephosphorization sedimentation basin 3200, dephosphorization tilted plate separator 3210, dephosphorization mud scraper 3220, coagulant solution tank 3300,
Phosphate eliminating flocculant tank 3400,
Dephosphorization reacting tank body 1100, dephosphorization reative cell 1110, water inlet 1111, dephosphorization agent adding mouth 1112, discharge gate
1113rd, waste water control valve 1114, head cover 1115, blow-off valve 1116,
Aerator 1200, aeration head or aeration tube 1210,
Degassing precipitation separator 1300, separator body 1310, degassing mud chamber 1311, devolatilizing chamber 1312, precipitation chamber
1313rd, sludge row mouth 1314, the first longitudinal side wall 1315, the second longitudinal side wall 1316, baffle 1320, inclined settling plate or inclination precipitation
Pipe 1330, effluent overflow weir water 1340, water outlet overflow launder 1341, separation outlet 1342,
Guide shell 1400,
Water distributor 1500, water distribution mouth 1510,
Cyclone 1600, cyclone inlets 1610, mud mouth 1620, cyclone outlet 1630, return pipe 1640,
Aeration pump or Aeration fan 1700,
Fenton's reaction device 4100, active carbon filter 3000,
Fenton's reaction pond 4110, Fenton's reaction chamber 4111, PH readjustment chamber 4115, devolatilizing chamber 4116, Fenton flocculation chamber 4112,
Acid adds mouth 4121, catalyst adds mouth 4122, oxidant adds mouth 4123, alkali adds mouth 4124, flocculant concentration mouth 4126,
First Fenton blender 4113, the second Fenton blender 4117, third Fenton blender 4118, the 4th Fenton blender 4114,
Third stirring air intake 4127, stirring air delivery pipe 4128, first partition 4141, second partition 4142, third partition board
4143、
Fenton sedimentation basin 4130, Fenton mud scraper 4132,
Acid adds pipe 4131, catalyst adds pipe 4132, oxidant adds pipe 4133, alkali adds pipe 4134, flocculant is thrown
Add pipe 4136,
Continuous sand filter 4200, compressed air inlet 4201, sand filtration rinse water out 4202,
Reuse pipe 2000.
Specific embodiment
The embodiment of the present invention is described below in detail, the example of the embodiment is shown in the drawings, wherein from beginning to end
Same or similar label represents same or similar element or the element with same or like function.Below with reference to attached
The embodiment of figure description is exemplary, it is intended to for explaining the present invention, and is not considered as limiting the invention.
Pasture waste water treatment process in the relevant technologies is by the waste water desilting of generation, and cleaning up excrement is guided to temporary with after sieving
The pool temporarily stores, then the waste water in the temporary pool is introduced into pasture waste water treatment system and is handled.Because wastewater treatment difficulty
Greatly, the processing capacity of pasture waste water treatment system is limited, and residence time of the waste water on the temporary pool is very long, often at 10 days or more,
Most biochemical substance is consumed naturally in the temporary pool, and the gases such as hydrogen, biogas, hydrogen sulfide of generation directly discharge
Into air, the significant wastage of the energy is caused, also results in the pollution of exhaust gas in pasture.
Simultaneously because biochemical substance is consumed naturally in the temporary pool in waste water, the degree difficult to degrade of waste water continues to increase
Add, waste water treatment system treatable water in pasture is less and less, and the wastewater flow rate on the temporary pool continues to increase, pool capacity more dig more
Greatly, an endless loop is ultimately caused.
It naturally volatilizees with the waste water on the temporary pool, the salinity in waste water gradually rises, and the degree difficult to degrade of waste water continues
Increase, the value of reuse also reduces, and further increases the dosage of fresh water, and the water rate for improving pasture is used.
If the waste water in the temporary pool introduces biochemical system, since biochemical system needs to maintain certain water temperature, due to that can give birth to
The consumption of compound matter, the heat generated in biochemical treatment of wastewater can not meet wanting for pasture waste water treatment system biochemistry
It asks, has further resulted in the energy consumption of pasture waste water treatment system.
In view of the pasture wastewater processing technology situation in the relevant technologies, it is strong, sharp that the present invention proposes a kind of processing capacity
It is utilized in energy recovery and environmental protection, the pasture waste water treatment system 1 of water consumption and energy consumption can be reduced.
Below with reference to the accompanying drawings pasture waste water treatment system 1 according to embodiments of the present invention is described.
As shown in Fig. 1-Figure 22, pasture waste water treatment system 1 according to embodiments of the present invention is included along waste water treatment process
The sequentially connected pretreatment system 70 in direction, COD and denitrogenation processing system 80 and advanced treatment system 60.
As shown in figure 21 and figure, advanced treatment system 60 according to embodiments of the present invention includes the waste water treatment process
The sequentially connected Fenton's reaction device 4100 in direction and active carbon filter 3000.
Fenton's reaction device 4100 includes the Fenton's reaction pond 4110 being sequentially communicated along waste water treatment process direction and Fenton
Sedimentation basin 4130.There is the Fenton's reaction chamber being sequentially communicated along the waste water treatment process direction in Fenton's reaction pond 4110
4111st, PH adjust back chamber 4115, devolatilizing chamber 4116 and Fenton flocculation chamber 4112, wherein, PH readjustment chamber 4115 in PH refer to hydrogen from
Sub- concentration, the acid-base value of ie in solution.Wherein, Fenton's reaction chamber 4111 is with acid adds mouth 4121, catalyst adds 4122 and of mouth
Oxidant adds mouth 4123, and there is PH readjustment chambers 4115 alkali to add mouth 4124, and Fenton flocculation chamber 4112 has flocculant concentration mouth
4126。
In other words, acid adds mouth 4121, catalyst adds mouth 4122 and oxidant adds mouth 4123 and Fenton's reaction chamber
4111 connections, for launching sour (such as sulfuric acid), catalyst (such as ferrous sulfate) and oxidation to Fenton's reaction chamber 4111 respectively
Agent (such as hydrogen peroxide).Alkali adds mouth 4124 and is connected with PH readjustment chambers 4115, for launching alkali to PH readjustment chambers 4115.Flocculant
It adds mouth 4126 to connect with Fenton flocculation chamber 4112, for launching flocculant to Fenton flocculation chamber 4112.
It needs exist for being appreciated that, acid adds mouth 4121, catalyst adds mouth 4122, oxidant adds mouth 4123, alkali is thrown
Add mouth 4124, flocculant concentration mouth 4126 that can be arranged on Fenton's reaction pond 4110；It can also make Fenton's reaction pond 4110
Upper surface is opened wide, and acid is made to add mouth 4121, catalyst adds mouth 4122, oxidant adds mouth 4123, alkali adds mouth 4124, wadding
Solidifying agent adds mouth 4126 and is suspended in 4110 top of Fenton's reaction pond.
It will be appreciated by those skilled in the art that ground is, waste water treatment process direction refers to, in whole works of wastewater treatment
In sequence, along the ordering of each process, waste water is from the first procedure sequentially into the flow direction of last procedure.
Below with reference to the accompanying drawings the wastewater treatment process of pasture waste water treatment system 1 according to embodiments of the present invention is described.
Waste water enters pretreatment system 70, and pretreatment system 70 removes the suspended matter in waste water, and to sandstone and water quality water
It measures into row buffering, waste water enters COD and denitrogenation processing system 80 later, removes the COD (organic pollution) in waste water and denitrogenation,
Last waste water enters advanced treatment system 60, and further removing can not biodegradable organic pollution in waste water.
Pasture waste water treatment system 1 according to embodiments of the present invention by setting pretreatment system 70, utilizes pretreatment system
The 70 temporary storage for mobile agent pools of uniting solve the problem of that waste water goes oil removal sandstone and water quality and quantity to buffer, and pasture waste water treatment system 1
Entirety ability is strong, and waste water is less than 1 day in the residence time of pretreatment system 70, farthest remains giving birth to for waste water
The property changed and energy recoverable rate.The biogas of generation is not only for itself heat supply of pasture waste water treatment system 1, and can supply
The heat supply of on-site is herded, achievees the effect that energy recovery utilizes, and is ever-increasing temporarily due to not needing to residence time and volume
The pool is deposited, land area is small, has saved occupation of land, has eliminated peculiar smell, reduces the dosage of pasture fresh water and whole energy consumption.
Also, by setting active carbon filter 3000 after Fenton's reaction device 4100, in Fenton's reaction device 4100
Waste water in COD carbon dioxide and water are oxidized under certain pH condition after, into active carbon filter 3000, utilize work
Property charcoal absorption Fenton's reaction after the remaining COD of waste water, even if the concentration of COD difficult to degrade is higher in waste water, remain able to reach
To processing requirement.Below with reference to the accompanying drawings pasture waste water treatment system 1 according to the specific embodiment of the invention is described.
As shown in Fig. 1-Figure 22, pasture waste water treatment system 1 according to embodiments of the present invention is included along waste water treatment process
The sequentially connected pretreatment system 70 in direction, COD and denitrogenation processing system 80 and advanced treatment system 60.
In some specific embodiments of the present invention, as shown in Fig. 1,3,6,8,10,14,17 and 19, pretreatment system 70
Including along the sequentially connected setting pot 71 in the waste water treatment process direction, solid-liquid separator 72 and adjust tank 73.Setting pot 71
It is equipped with pretreatment mud scraper 74, the suspended matter for precipitating, in filtered wastewater.Solid-liquid separator 72 is used to remove in waste water
Solid.Tank 73 is adjusted for regulating pondage and pH value, and adjusts to be connected between tank 73 and COD and denitrogenation processing system 80 and be used for
Control feeds to the charging pump 75 of the water of COD and denitrogenation processing system 80.Pretreatment system 70 can replace the temporary pool as a result,
Suspended matter in quick removal waste water, and to sandstone and water quality and quantity into row buffering.
In some specific embodiments of the present invention, as shown in Fig. 1-Fig. 9, COD and denitrogenation processing system 80 are included along useless
It is anti-that water treatment technology direction is sequentially connected anaerobic fermentation reaction unit 10, high load aeration tank 30, denitrification reactor 40 and dephosphorization
Answer device 50.
Wherein, anaerobic fermentation reaction unit 10 includes anaerobic fermentation tank body 100, stripping tube 200 and air supply pipe 300.Anaerobism
There is anaerobic reaction room 110, anaerobic reaction room 110 has waste water inlet 111, water outlet 112 and exhaust outlet in fermentation tank 100
113.200 pipe of stripping tube is located in anaerobic reaction room 110, and the upper end of stripping tube 200 has a gas outlet 221, and stripping tube 200
Lower end has air inlet 211.Air supply pipe 300 is connected with the air inlet 211 of stripping tube 200, is used for being supplied into stripping tube 200
In the gas of air lift.The gas for being used for air lift can be oxygen-depleted gas or inert gas, preferably biogas.
Below with reference to the accompanying drawings COD according to embodiments of the present invention and the wastewater treatment process of denitrogenation processing system 80 are described.
Waste water enters anaerobic reaction room 110 by waste water inlet 111, and air supply pipe 300 is supplied to stripping tube 200, anaerobic reaction
Anaerobic environment is formed in room 110, meanwhile, stripping tube 200 plays stirring by exporting lift gas into anaerobic reaction room 110
The effect of waste water and anaerobic sludge, as a result, the waste water in anaerobic reaction room 110 mixed rapidly with anaerobic sludge, waste water and anaerobism
The intense contact of sludge makes the organic pollutant degradation in waste water, and extra gas is by 113 row of exhaust outlet in anaerobic reaction room 110
Go out, anaerobic reaction room 110 is flowed out by water outlet 112 through anaerobic fermentation purified waste water and enter high load aeration tank 30, give up
Water further carries out aerobic biodegradation in high load aeration tank 30, and the waste water after aerobic biodegradation is transported to denitrogenation
Reactor 40 carries out denitrogenation, and the waste water after denitrogenation enters dephosphorizing reactor 50 and carries out dephosphorization.
By setting along the sequentially connected anaerobic fermentation reaction unit 10 in waste water treatment process direction, high load aeration tank
30th, denitrification reactor 40 and dephosphorizing reactor 50, can will be in cellulose alcohol wastewater with reference to advanced treatment system 60
COD is handled to below 100mg/L.
Also, by setting stripping tube 200 and air supply pipe 300 in anaerobic fermentation reaction unit 10, gas supply can be utilized
Pipe 300 provides gas into stripping tube 200, and can utilize stripping tube 200 into anaerobic reaction room 110 output gas into promoting the circulation of qi
It carries, the gas exported by stripping tube 200 can stir the mixture of the waste water and anaerobic sludge in anaerobic reaction room 110, make to give up
Water and anaerobic sludge contact fully, rapidly, and stirring range is big, mixing effect is good, can greatly improve COD treatment effects.
On the other hand, by setting stripping tube 200, can cancel motor that air floating structure and air floating structure need to be equipped with and
Agitating element simplifies the structure of anaerobic fermentation reaction unit 10, reduces the cost of anaerobic fermentation reaction unit 10.
In addition, eliminating motor and cleaning element that flotation cell and flotation cell need to be equipped with, anaerobism hair is further simplified
The structure of ferment reaction unit 10, and further reduced the cost of anaerobic fermentation reaction unit 10.
In some specific examples of the present invention, advantageously, as shown in Fig. 2, Fig. 4, Fig. 7 and Fig. 9, under stripping tube 200
The bottom of the neighbouring anaerobic reaction room 110 in end, and the upper end of stripping tube 200 extends to the top of anaerobic reaction room 110, water outlet
112 are located at the top of anaerobic reaction room 110 and higher than the upper end of stripping tube 200.The gas that air supply pipe 300 provides passes through stripping tube
200, the top of anaerobic reaction room 110 is transported to by the bottom of anaerobic reaction room 110, and export with to detesting from gas outlet 221
Waste water and anaerobic sludge mixture in oxygen reative cell 110 are stirred, as a result, not only can be in order to which air supply pipe 300 is to air lift
Gas in pipe 200 is provided, and the stirring range and mixing effect of stripping tube 200 can be further improved, and by stripping tube 200
The gas of output will not interfere the water outlet of water outlet 112.
Optionally, as shown in Fig. 2, Fig. 4, Fig. 5 and Fig. 9, the upper surface of stripping tube 200 is opened wide to form gas outlet 221, gas
The lower face for carrying pipe 200 is opened wide to form air inlet 211, can increase air inlet 211 and gas outlet 221 to greatest extent in this way
Valid circulation area, so as to improve the output quantity of gas in 200 unit interval of stripping tube.
In some specific embodiments according to the present invention, as shown in Fig. 2, Fig. 4, Fig. 7 and Fig. 8, stripping tube 200 includes straight
Pipeline section 210 and segmental arc 220.Straight pipe 210 vertically extends, and segmental arc 220 is connected with the upper end of straight pipe 210, goes out
Angle α between the opening direction and vertically downward direction of gas port 221 is more than or equal to zero degree and less than 180 degree, i.e. 0 °≤α ＜
180°。
Preferably, as shown in figures 4 and 9, segmental arc 220 is inverted U-shaped, and the opening direction of gas outlet 221 changes straight down
Yan Zhi, α=0 °.Waste water is stirred downwards from the top of anaerobic reaction room 110 by the gas that stripping tube 200 exports in this way and anaerobism is dirty
The mixture of mud further improves stirring range and mixing effect, so as to further improve anaerobic fermentation reaction unit 10
COD treatment effects.
The severe degree and speed mixed to further improve waste water with anaerobic sludge, stripping tube 200 can be
It is multiple, air supply pipe 300 can one or more and in anaerobic reaction room 110 bottom levels set, multiple stripping tubes 200 are in water
It is arranged at intervals in plane and lower end is connected with same air supply pipe 300 or is connected respectively with multiple air supply pipes 300.
In some specific examples of the present invention, as shown in figure 4, anaerobic fermentation reaction unit 10 further includes precipitation separator
400, precipitation separator 400 is located in anaerobic reaction room 110 and positioned at 200 top of stripping tube, and precipitation separator 400 has with going out
The connected separator water outlet 413 in the mouth of a river 112, water outlet 112 are connected with high load aeration tank 30.It is purified through anaerobic fermentation
In waste water outflow to precipitation separator 400, thus gas is detached with water and anaerobic sludge, and the gas after separation is by exhaust outlet 113
Discharge, then, water is detached with anaerobic sludge, and the anaerobic sludge after separation is returned from precipitation separator 400 in anaerobic reaction room 110
It recycles, the separator water outlet 413 after separation is transported to water outlet 112, and discharge anaerobic reaction room 110 is simultaneously delivered to
High load aeration tank 30.
Gas, water and anaerobic sludge are first isolated thus, it is possible to be utilized in anaerobic reaction room 110 and precipitate separator 400,
Product after separation is respectively delivered to different regions again, improves the pure of water outlet.
Specifically, as shown in figure 5, precipitation separator 400 includes babinet 410, partition board 420, precipitation inclined plate 430 and overflow
Weir 440.
Degassing precipitation chamber 411 is formed in babinet 410, the bottom of degassing precipitation chamber 411 has sludge outlet 412, degassing
The cross-sectional area for precipitating the lower part of chamber 411 is gradually reduced along direction from the top down.Partition board 420 is located at degassing precipitation chamber 411
The top for the precipitation chamber 411 that deaerates is separated into degassing district 421 and settling zone 422 by top, partition board 420, the bottom of degassing district 421 with
The bottom of settling zone 422 is connected so that waste water is overflowed to from anaerobic reaction room 110 in degassing district 421 and then from degassing district 421
Bottom is flowed in settling zone 422.Precipitation inclined plate 430 is located in settling zone 422.Downflow weir 440 is located in settling zone 422 and overflow
Weir 440 forms the overflow launder 441 with separator water outlet 413.
Separation process of the precipitation separator 400 to water, gas and anaerobic sludge is described below with reference to Fig. 3.
Gas-entrained and anaerobic sludge in water after anaerobic sludge is degraded, gas-entrained and anaerobic sludge water overflow is extremely
The degassing district 421 of degassing precipitation chamber 411, wherein gas are escaped from degassing district 421, are discharged by exhaust outlet 113, complete gas point
From.The water of entrainment anaerobic sludge after being detached with gas flows to settling zone 422 by the bottom of degassing district 421, at this time anaerobic sludge
The guiding of the inner wall of 411 lower tilt of chamber is sunk and precipitated in degassing to precipitation down toward sludge outlet 412, by 412 row of sludge outlet
Go out to precipitate separator 400 and enter anaerobic reaction room 110, continue on for wastewater degradation, in degassing precipitation chamber 411 and anaerobic sludge
In water overflow to the overflow launder 441 of downflow weir 440 after separation, and discharged successively by separator water outlet 413 and water outlet 112
Anaerobic reaction room 110 carries out subsequent processing.During anaerobic sludge rises with water, anaerobic sludge settles on precipitation inclined plate 430
And 411 bottom of degassing precipitation chamber is slipped to, anaerobic sludge is contributed to be separated from water, so far, completes water, anaerobic sludge and gas
Separation.
Advantageously, as shown in figure 5, limiting the upper edge of the babinet 410 of degassing district 421 less than partition board 420 with partition board 420
Upper edge and limited with partition board 420 settling zone 422 410 part of babinet upper edge.In other words, babinet 410 limit it is de-
The upper edge of the part in gas area 421, less than the part upper edge for limiting settling zone 422 of babinet 410, and it is upper less than partition board 420
Edge.The upper edge of downflow weir 440 can be concordant with the upper edge of the part for limiting degassing district 421 of babinet 410 or higher than babinet 410
The part for limiting degassing district 421 upper edge, and the upper edge of downflow weir 440 limits settling zone 422 less than babinet 410
Part upper edge and partition board 420 upper edge.The water in degassing district 421 be thus it can be prevented that from top overflow to settling zone 422,
Ensure that the water in degassing district 421 flow to settling zone 422, and then be sufficiently separated anaerobic sludge, and sink from 421 bottom of degassing district
Water in shallow lake area 422 is by overflow to overflow launder 441, avoiding in the water in overflow launder 441 and carrying anaerobic sludge secretly.
Optionally, as shown in figure 5, babinet 410 is cuboid, the lower end of the first longitudinal side wall 414 of the lower part of babinet 410 to
Under extend beyond babinet 410 lower part the second longitudinal side wall 415 lower end, and the lower end of the first longitudinal side wall 414 and the second longitudinal side
The lower end of wall 415 is overlapped in the up-down direction.It is possible thereby to the anaerobic sludge in anaerobic reaction room 110 is advantageously avoided to pass through dirt
Mud outlet 412 enters in the degassing precipitation chamber 411 of precipitation separator 400.
For example, in four longitudinal side walls of babinet 410, two longer longitudinal side walls of length are respectively in the horizontal direction
The lower end of one longitudinal side wall 414 and the second longitudinal side wall 415, the lower end of the first longitudinal side wall 414 and the second longitudinal side wall 415 is relative to first
The upper end of longitudinal side wall 414 and the upper end of the second longitudinal side wall 415 are mutually adjacent, and the lower end of the first longitudinal side wall 414 is located at the second longitudinal side
The lower section of the lower end of wall 415, and the projection of the lower end of the first longitudinal side wall 414 and the lower end of the second longitudinal side wall 415 in the horizontal plane
Overlapping, gap between the lower end of the first longitudinal side wall 414 and the lower end of the second longitudinal side wall 415 form sludge outlet 412, and thus one
Aspect can be anti-by the smooth return anaerobism of sludge outlet 412 after can ensureing the anaerobic sludge precipitation in degassing precipitation chamber 411
Answer room 110, and on the other hand the structure of the sludge outlet 412 can stop anaerobic sludge in anaerobic reaction room 110 from sludge
Outlet 412 enters degassing precipitation chamber 411, ensures the anaerobic sludge separating effect of precipitation separator 400.
In some specific embodiments of the present invention, as shown in figures 7 and 9, it is heavy that anaerobic fermentation reaction unit 10 further includes
Shallow lake separator 400, precipitation separator 400 are located at outside anaerobic fermentation tank body 100, and water outlet 112 is by precipitating separator 400 and height
Rate aeration pond 30 is connected, and precipitates separator 400 and include babinet 410, precipitation inclined plate 430 and downflow weir 440.
Degassing precipitation chamber 411 is formed in babinet 410, degassing precipitation chamber 411 has import 416,413 and of separator water outlet
Sludge outlet 412, import 416 are connected with the water outlet 112 of anaerobic reaction room 110, and separator water outlet 413 is aerated with high load capacity
Pond 30 is connected, and at least one conical cavity is formed at the lower part of degassing precipitation chamber 411, and the cross-sectional area of each conical cavity is along from the top down
Direction be gradually reduced, sludge outlet 412 is formed in the bottom of the conical cavity.Precipitation inclined plate 430 is located at degassing precipitation chamber 411
It is interior.Downflow weir 440 is located in degassing precipitation chamber 411, and be formed in downflow weir 440 connect with separator water outlet 413 it is excessive
Flow weir 440.
Below with reference to separation process of Fig. 4 and Fig. 5 description precipitation separators 400 to water, gas and anaerobic sludge.
Gas-entrained and anaerobic sludge in the water flowed out by the water outlet 112 of anaerobic reaction room 110, gas-entrained and anaerobism
The water of sludge enters degassing precipitation chamber 411 by import 416, and wherein gas escapes from ullage and discharges degassing precipitation chamber
411, complete gas separation.Water entrainment anaerobic sludge after being detached with gas, wherein anaerobic sludge precipitation sink and sink in degassing
The guiding of the inner wall of 411 lower taper chamber of shallow lake chamber discharges degassing precipitation chamber 411 down toward sludge outlet 412, by sludge outlet 412,
In overflow launder 441 of the water overflow to downflow weir 440 after being detached in degassing precipitation chamber 411 with anaerobic sludge, and by separator
The discharge degassing precipitation chamber 411 of water outlet 413, carries out subsequent processing.During anaerobic sludge rises with water, anaerobic sludge is precipitating
The conical cavity of 411 bottom of degassing precipitation chamber is settled and be slipped on inclined plate 430, and anaerobic sludge is contributed to be separated from water, it is so far, complete
The separation of Cheng Shui, anaerobic sludge and gas.
Thus, it is possible to gas, water and anaerobic sludge are first isolated using precipitating separator 400 outside anaerobic reaction room 110,
Product after separation is respectively delivered to different regions again, improves the pure of water outlet.
Further, as shown in figures 7 and 9, anaerobic fermentation reaction unit 10 further includes sinker 500, and sinker 500 connects
It is connected between the import 416 of water outlet 112 and degassing precipitation chamber 411 of anaerobic reaction room 110.Sinker can be utilized in this way
The energy of water that 500 consumption and dispersion are flowed out by anaerobic fermentation tank body 100, prevents from or mitigates to be flowed out by anaerobic fermentation tank body 100
Water to precipitate separator 400 erosion damage.
Advantageously, as shown in figures 7 and 9, anaerobic fermentation reaction unit 10 further includes mud return line 600, sludge reflux
One end of pipe 600 is connected with anaerobic reaction room 110, degassing precipitation chamber 411 sludge outlet 412 by sludge discharge pipe 700 with
Mud return line 600 is connected, and mud return line 600 is equipped with sludge reflux pump 610, and the anaerobism discharged from sludge outlet 412 is dirty
Mud can pass sequentially through sludge discharge pipe 700 and mud return line 800 returns to anaerobic reaction room 110, so as to be recycled.
Optionally, for external precipitation separator 400, hydrocyclone may be used or external air-floating apparatus replaces.
In some specific examples of the present invention, as shown in figure 9, the lower part of anaerobic reaction room 110 has mud discharging mouth
115, mud discharging mouth 115 is connected with mud discharging valve and/or mud discharging pump 116, extra anaerobism in anaerobic reaction room 110
Sludge can discharge anaerobic reaction room 110 by mud discharging mouth 115.
Optionally, as shown in figures 7 and 9, waste water inlet 111 is connected with charging pump 117, to control whether to anaerobic reaction
110 transport wastewater of room and the wastewater flow rate conveyed to anaerobic reaction room 110.As depicted in figs. 1 and 2, air supply pipe 300 is equipped with position
In the gas control valve 118 outside anaerobic reaction room 110, to control whether to supply to stripping tube 200 and the confession to stripping tube 200
Tolerance.
Further, the water inlet pipe at waste water inlet 111 can be connected with water distributor or water distribution is opened up on water inlet pipe
Hole.
Advantageously, as shown in Fig. 2, Fig. 4, Fig. 7 and Fig. 8, anaerobic fermentation reaction unit 10 further includes water sealed tank 800, anaerobism
The top of fermentation tank 100 is equipped with safe gas port 114, and safe gas port 114 is connected with water sealed tank 800.It is possible thereby to utilize water seal
Tank 800 completely cuts off air, maintains the pressure of anaerobic reaction room 110, and can play the role of back-fire relief, and additionally biogas can be played
Certain clean-up effect.
Alternatively it is also possible to water sealed tank 800 is replaced using safety valve.
In some specific embodiments of the present invention, as shown in Fig. 1, Fig. 3, Fig. 6 and Fig. 8, denitrification reactor 40 includes edge
The sequentially connected anaerobic ammonia oxidation reactor 2100 in waste water treatment process direction and Anoxic/Aerobic reaction tank 2200.Wherein, anaerobism
Ammonia oxidation reactor 2100 is connected with high load aeration tank 30, and Anoxic/Aerobic reaction tank 2200 is connected with dephosphorizing reactor 50, by
The waste water that high load aeration tank 30 flows out carries out followed by anaerobic ammonia oxidation reactor 2100 and Anoxic/Aerobic reaction tank 2200
Denitrogenation processing.
In some specific examples of the present invention, as shown in Fig. 1, Fig. 3, Fig. 6 and Fig. 8, dephosphorizing reactor 50 includes coagulation
Reaction tank 3100 and dephosphorization sedimentation basin 3200.
Have in coagulation reaction tank 3100 the dephosphorization reaction chamber 3110 that is connected with denitrification reactor 40 and with dephosphorization reaction chamber
3110 connected dephosphorization flocculation chambers 3120, dephosphorization reaction chamber 3110 is interior to be equipped with the fast blender 3111 of dephosphorization and dephosphorization flocculation chamber 3120
It is interior to be equipped with the slow blender 3112 of dephosphorization.It needs exist for being appreciated that, the fast blender 3111 of dephosphorization and the slow blender 3112 of dephosphorization
Speed is that in contrast, i.e., the rotating speed of the fast blender 3111 of dephosphorization is higher than the rotating speed of the slow blender 3112 of dephosphorization.Dephosphorization sedimentation basin
3200 are connected respectively with dephosphorization flocculation chamber 3120 and advanced treatment system 60, and dephosphorization sloping plate deposition is equipped in dephosphorization sedimentation basin 3200
Device 3210 and dephosphorization mud scraper 3220.The waste water flowed out by denitrification reactor 40 is wadded a quilt with cotton followed by dephosphorization reaction chamber 3110, dephosphorization
Solidifying chamber 3120 and dephosphorization sedimentation basin 3200, and carry out dephosphorization, flocculation and solid-liquor separation.
Optionally, as shown in Fig. 1, Fig. 3, Fig. 6 and Fig. 8, dephosphorizing reactor 50 further includes coagulant solution tank 3300 and removes
Phosphorus flocculant tank 3400.Coagulant solution tank 3300 is connected with dephosphorization reaction chamber 3110, for being supplied to dephosphorization reaction chamber 3110
Coagulant (such as ferric sulfate) solution is to carry out dephosphorization.Phosphate eliminating flocculant tank 3400 and dephosphorization flocculation chamber 3120 are connected, for
Dephosphorization flocculation chamber 3120 supplies flocculant.
Those skilled in the art it will be understood that coagulant solution tank 3300 or for store it is other can
Make the NaOH solution tank NaOH of the chemical substance of calcium phosphate precipitation, such as polyaluminium sulfate NaOH solution tank NaOH.
In some specific embodiments of the present invention, as seen from figs. 10-20, COD and denitrogenation processing system 80 are included along useless
The sequentially connected anaerobic fermentation reaction unit 10 in water treatment technology direction, waste water dephosphorization reaction unit 20 and denitrification reactor 40.
Wherein, anaerobic fermentation reaction unit 10 includes anaerobic fermentation tank body 100, stripping tube 200 and air supply pipe 300.Anaerobism
There is anaerobic reaction room 110, anaerobic reaction room 110 has waste water inlet 111, water outlet 112 and exhaust outlet in fermentation tank 100
113.200 pipe of stripping tube is located in anaerobic reaction room 110, and the upper end of stripping tube 200 has a gas outlet 221, and stripping tube 200
Lower end has air inlet 211.Air supply pipe 300 is connected with the air inlet 211 of stripping tube 200, is used for being supplied into stripping tube 200
In the gas of air lift.The gas for being used for air lift can be oxygen-depleted gas or inert gas, preferably biogas.
Waste water dephosphorization reaction unit 20 includes dephosphorization reacting tank body 1100, aerator 1200 and degassing precipitation separator
1300.There is dephosphorization reative cell 1110, dephosphorization reative cell 1110 has water inlet 1111 and dephosphorization in dephosphorization reacting tank body 1100
Agent adding mouth 1112.Aerator 1200 is located in dephosphorization reative cell 1110.Degassing precipitation separator 1300 is located at except phosphorus reaction
In room 1110, and the precipitation separator 1300 that deaerates is located at 1200 top of aerator, and degassing precipitates separator 1300 for detaching
Gas and water and sludge.
Below with reference to the accompanying drawings COD according to embodiments of the present invention and the wastewater treatment process of denitrogenation processing system 80 are described.
Waste water enters anaerobic reaction room 110 by waste water inlet 111, and air supply pipe 300 is supplied to stripping tube 200, anaerobic reaction
Anaerobic environment is formed in room 110, meanwhile, stripping tube 200 plays stirring by exporting lift gas into anaerobic reaction room 110
The effect of waste water and anaerobic sludge, as a result, the waste water in anaerobic reaction room 110 mixed rapidly with anaerobic sludge, waste water and anaerobism
The intense contact of sludge makes the organic pollutant degradation in waste water, and extra gas is by 113 row of exhaust outlet in anaerobic reaction room 110
Go out, anaerobic reaction room 110 is flowed out by water outlet 112, and dephosphorization is entered by water inlet 1111 through anaerobic fermentation purified waste water
Reative cell 1110 adds dephosphorization agent (such as magnesia) into dephosphorization reative cell 1110 by dephosphorization agent adding mouth 1112, aeration
Device 1200 supplies oxygen aeration into dephosphorization reative cell 1110, and aerobic environment is formed in dephosphorization reative cell 1110, meanwhile, aerator
The air of 1200 supplies plays the role of stirring waste water, thus the waste water in dephosphorization reative cell 1110 and aerobic sludge and dephosphorization agent
Rapid mixing removes the biochemical organic matter of deliquescent colloidal state in waste water and carries out dephosphorization, it is reacted after waste water overflow
It flows in degassing precipitation separator 1300, thus gas, water and aerobic sludge separation, the gas after separation is by dephosphorization reative cell
1110 top discharge, then, water is detached with aerobic sludge, and the aerobic sludge after separation is returned from degassing precipitation separator 1300
It is recycled in dephosphorization reative cell 1110, the water overflow after being detached with aerobic sludge goes out degassing precipitation separator 1300, and discharge removes
Phosphorus reaction room 1110 is delivered to denitrification reactor 40 and carries out denitrogenation.
It is filled by setting along the sequentially connected anaerobic fermentation reaction unit 10 in waste water treatment process direction, waste water dephosphorization reaction
20 and denitrification reactor 40 are put, with reference to advanced treatment system 60, the COD processing in cellulose alcohol wastewater can be arrived
Below 100mg/L.
Also, by setting stripping tube 200 and air supply pipe 300 in anaerobic fermentation reaction unit 10, gas supply can be utilized
Pipe 300 provides gas into stripping tube 200, and can utilize stripping tube 200 into anaerobic reaction room 110 output gas into promoting the circulation of qi
It carries, the gas exported by stripping tube 200 can stir the mixture of the waste water and anaerobic sludge in anaerobic reaction room 110, make to give up
Water and anaerobic sludge contact fully, rapidly, and stirring range is big, mixing effect is good, can greatly improve COD treatment effects.Separately
On the one hand, by setting stripping tube 200, motor and agitating element that air floating structure and air floating structure need to be equipped with can be cancelled,
The structure of anaerobic fermentation reaction unit 10 is simplified, reduces the cost of anaerobic fermentation reaction unit 10.In addition, according to the present invention
The anaerobic fermentation reaction unit 10 of embodiment eliminates the motor and cleaning element that flotation cell and flotation cell need to be equipped with, further
The structure of anaerobic fermentation reaction unit 10 is simplified, and further reduced the cost of anaerobic fermentation reaction unit 10.
In addition, by setting dephosphorization agent adding mouth 1112 on dephosphorization reacting tank body 1100, and in dephosphorization reative cell 1110
Interior setting aerator 1200, is integrated with aeration and phosphorus removal functional, it is possible thereby to instead of cellulose ethyl alcohol pasture wastewater treatment
The respective required equipment of high load capacity aeration process and dephosphorization process in system, so as to simplification cellulose ethyl alcohol pasture wastewater treatment
The structure of system reduces the cost of cellulose ethyl alcohol pasture waste water treatment system, and COD high treating effects.
In some specific examples of the present invention, as shown in Figure 11, Figure 15, Figure 18 and Figure 20, the lower end of stripping tube 200 is adjacent
The bottom of nearly anaerobic reaction room 110, and the upper end of stripping tube 200 extends to the top of anaerobic reaction room 110, water outlet 112 is set
On the top of anaerobic reaction room 110 and higher than the upper end of stripping tube 200.The gas that air supply pipe 300 provides by stripping tube 200,
The top of anaerobic reaction room 110 is transported to by the bottom of anaerobic reaction room 110, and is exported from gas outlet 221 with anti-to anaerobism
Waste water and the anaerobic sludge mixture in room 110 is answered to be stirred, it as a result, not only can be in order to which air supply pipe 300 be to stripping tube 200
Interior offer gas, and the stirring range and mixing effect of stripping tube 200 can be further improved, and exported by stripping tube 200
Gas will not interfere the water outlet of water outlet 112.
Optionally, as shown in Figure 11, Figure 15, Figure 16 and Figure 20, the upper surface of stripping tube 200 is opened wide to form gas outlet
221, the lower face of stripping tube 200 is opened wide to form air inlet 211, can be increased air inlet 211 to greatest extent in this way and be gone out
The valid circulation area of gas port 221, so as to improve the output quantity of gas in 200 unit interval of stripping tube.
In some specific embodiments according to the present invention, as shown in Figure 11, Figure 15, Figure 18 and Figure 20, stripping tube 200 wraps
Include straight pipe 210 and segmental arc 220.Straight pipe 210 vertically extends, the upper end phase of segmental arc 220 and straight pipe 210
Even, the angle α between the opening direction and vertically downward direction of gas outlet 221 is more than or equal to zero degree and is less than 180 degree, i.e., 0 °
180 ° of≤α ＜.
Preferably, as shown in Figure 15 and Figure 20, segmental arc 220 is inverted U-shaped, the opening direction of gas outlet 221 straight down,
In other words, α=0 °.Waste water and anaerobism are stirred downwards from the top of anaerobic reaction room 110 by the gas that stripping tube 200 exports in this way
The mixture of sludge further improves stirring range and mixing effect, so as to further improve anaerobic fermentation reaction unit 10
COD treatment effects.
The severe degree and speed mixed to further improve waste water with anaerobic sludge, stripping tube 200 can be
It is multiple, air supply pipe 300 can one or more and in anaerobic reaction room 110 bottom levels set, multiple stripping tubes 200 are in water
It is arranged at intervals in plane and lower end is connected with same air supply pipe 300 or is connected respectively with multiple air supply pipes 300.
In some specific examples of the present invention, as shown in figure 15, anaerobic fermentation reaction unit 10 further includes precipitation separation
Device 400, precipitation separator 400 are located in anaerobic reaction room 110 and positioned at 200 tops of stripping tube, precipitation separator 400 have with
The connected separator water outlet 413 of water outlet 112, water outlet 112 are connected with the water inlet 1111 of waste water dephosphorization reaction unit 20.
Through in the purified waste water outflow of anaerobic fermentation to precipitation separator 400, thus gas is detached with water and anaerobic sludge, after separation
Gas discharged by exhaust outlet 113, then, water is detached with anaerobic sludge, the anaerobic sludge after separation from precipitation separator 400 return
It returns in anaerobic reaction room 110 and recycles, the separator water outlet 413 after separation is transported to water outlet 112, discharges anaerobism
Reative cell 110 is simultaneously delivered to waste water dephosphorization reaction unit 20.
Gas, water and anaerobic sludge are first isolated thus, it is possible to be utilized in anaerobic reaction room 110 and precipitate separator 400,
Product after separation is respectively delivered to different regions again, improves the pure of water outlet.
Specifically, as shown in figure 16, precipitation separator 400 includes babinet 410, partition board 420, precipitation inclined plate 430 and overflows
Flow weir 440.
Degassing precipitation chamber 411 is formed in babinet 410, the bottom of degassing precipitation chamber 411 has sludge outlet 412, degassing
The cross-sectional area for precipitating the lower part of chamber 411 is gradually reduced along direction from the top down.Partition board 420 is located at degassing precipitation chamber 411
The top for the precipitation chamber 411 that deaerates is separated into degassing district 421 and settling zone 422 by top, partition board 420, the bottom of degassing district 421 with
The bottom of settling zone 422 is connected so that waste water is overflowed to from anaerobic reaction room 110 in degassing district 421 and then from degassing district 421
Bottom is flowed in settling zone 422.Precipitation inclined plate 430 is located in settling zone 422.Downflow weir 440 is located in settling zone 422 and overflow
Weir 440 forms the overflow launder 441 with separator water outlet 413.
Separation process of the precipitation separator 400 to water, gas and anaerobic sludge is described below with reference to Figure 16.
Gas-entrained and anaerobic sludge in water after anaerobic sludge is degraded, gas-entrained and anaerobic sludge water overflow is extremely
The degassing district 421 of degassing precipitation chamber 411, wherein gas are escaped from degassing district 421, are discharged by exhaust outlet 113, complete gas point
From.The water of entrainment anaerobic sludge after being detached with gas flows to settling zone 422 by the bottom of degassing district 421, at this time anaerobic sludge
The guiding of the inner wall of 411 lower tilt of chamber is sunk and precipitated in degassing to precipitation down toward sludge outlet 412, by 412 row of sludge outlet
Go out to precipitate separator 400 and enter anaerobic reaction room 110, continue on for wastewater degradation, in degassing precipitation chamber 411 and anaerobic sludge
In water overflow to the overflow launder 441 of downflow weir 440 after separation, and discharged successively by separator water outlet 413 and water outlet 112
Anaerobic reaction room 110 carries out subsequent processing.During anaerobic sludge rises with water, anaerobic sludge settles on precipitation inclined plate 430
And 411 bottom of degassing precipitation chamber is slipped to, anaerobic sludge is contributed to be separated from water, so far, completes water, anaerobic sludge and gas
Separation.
Advantageously, as shown in figure 16, the upper edge that the babinet 410 of degassing district 421 is limited with partition board 420 is less than partition board 420
Upper edge and limited with partition board 420 settling zone 422 410 part of babinet upper edge.In other words, babinet 410 limits
The upper edge of the part of degassing district 421, less than the part upper edge for limiting settling zone 422 of babinet 410, and less than partition board 420
Upper edge.The upper edge of downflow weir 440 can be concordant with the upper edge of the part for limiting degassing district 421 of babinet 410 or higher than babinet
The upper edge of 410 part for limiting degassing district 421, and the upper edge of downflow weir 440 limits settling zone less than babinet 410
422 part upper edge and the upper edge of partition board 420.It thus it can be prevented that the water in degassing district 421 from top overflow to settling zone
422, ensure that the water in degassing district 421 flow to settling zone 422, and then be sufficiently separated anaerobic sludge from 421 bottom of degassing district, and
And the water in settling zone 422 is by overflow to overflow launder 441, avoiding in the water in overflow launder 441 and carrying anaerobic sludge secretly.
Optionally, as shown in figure 16, babinet 410 be cuboid, the lower end of the first longitudinal side wall 414 of the lower part of babinet 410
The lower end of the second longitudinal side wall 415 of the lower part of babinet 410 is extended downward beyond, and the lower end of the first longitudinal side wall 414 is indulged with second
The lower end of side wall 415 is overlapped in the up-down direction.It is possible thereby to the anaerobic sludge in anaerobic reaction room 110 is advantageously avoided to pass through
Sludge outlet 412 enters in the degassing precipitation chamber 411 of precipitation separator 400.
For example, in four longitudinal side walls of babinet 410, two longer longitudinal side walls of length are respectively in the horizontal direction
The lower end of one longitudinal side wall 414 and the second longitudinal side wall 415, the lower end of the first longitudinal side wall 414 and the second longitudinal side wall 415 is relative to first
The upper end of longitudinal side wall 414 and the upper end of the second longitudinal side wall 415 are mutually adjacent, and the lower end of the first longitudinal side wall 414 is located at the second longitudinal side
The lower section of the lower end of wall 415, and the projection of the lower end of the first longitudinal side wall 414 and the lower end of the second longitudinal side wall 415 in the horizontal plane
Overlapping, gap between the lower end of the first longitudinal side wall 414 and the lower end of the second longitudinal side wall 415 form sludge outlet 412, and thus one
Aspect can be anti-by the smooth return anaerobism of sludge outlet 412 after can ensureing the anaerobic sludge precipitation in degassing precipitation chamber 411
Answer room 110, and on the other hand the structure of the sludge outlet 412 can stop anaerobic sludge in anaerobic reaction room 110 from sludge
Outlet 412 enters degassing precipitation chamber 411, ensures the anaerobic sludge separating effect of precipitation separator 400.
In some specific embodiments of the present invention, as shown in Figure 18 and Figure 20, anaerobic fermentation reaction unit 10 further includes
Precipitate separator 400, precipitation separator 400 be located at outside anaerobic fermentation tank body 100, water outlet 112 by precipitate separator 400 with
The water inlet 1111 of waste water dephosphorization reaction unit 20 is connected.It precipitates separator 400 and includes babinet 410, precipitation inclined plate 430 and overflow
Weir 440.
Degassing precipitation chamber 411 is formed in babinet 410, degassing precipitation chamber 411 has import 416,413 and of separator water outlet
Sludge outlet 412, import 416 are connected with the water outlet 112 of anaerobic reaction room 110, and separator water outlet 413 and waste water dephosphorization are anti-
The water inlet 1111 of device 20 is answered to be connected, at least one conical cavity, the horizontal stroke of each conical cavity are formed at the lower part of degassing precipitation chamber 411
Sectional area is gradually reduced along direction from the top down, and sludge outlet 412 is formed in the bottom of the conical cavity.Precipitation inclined plate 430
It is located in degassing precipitation chamber 411.Downflow weir 440 is located in degassing precipitation chamber 411, and is formed in downflow weir 440 and separator
The downflow weir 440 that water outlet 413 connects.
Below with reference to separation process of Figure 18 and Figure 20 description precipitation separators 400 to water, gas and anaerobic sludge.
Gas-entrained and anaerobic sludge in the water flowed out by the water outlet 112 of anaerobic reaction room 110, gas-entrained and anaerobism
The water of sludge enters degassing precipitation chamber 411 by import 416, and wherein gas escapes from ullage and discharges degassing precipitation chamber
411, complete gas separation.Water entrainment anaerobic sludge after being detached with gas, wherein anaerobic sludge precipitation sink and sink in degassing
The guiding of the inner wall of 411 lower taper chamber of shallow lake chamber discharges degassing precipitation chamber 411 down toward sludge outlet 412, by sludge outlet 412,
In overflow launder 441 of the water overflow to downflow weir 440 after being detached in degassing precipitation chamber 411 with anaerobic sludge, and by separator
The discharge degassing precipitation chamber 411 of water outlet 413, carries out subsequent processing.During anaerobic sludge rises with water, anaerobic sludge is precipitating
The conical cavity of 411 bottom of degassing precipitation chamber is settled and be slipped on inclined plate 430, and anaerobic sludge is contributed to be separated from water, it is so far, complete
The separation of Cheng Shui, anaerobic sludge and gas.
Thus, it is possible to gas, water and anaerobic sludge are first isolated using precipitating separator 400 outside anaerobic reaction room 110,
Product after separation is respectively delivered to different regions again, improves the pure of water outlet.
Further, as shown in Figure 18 and Figure 20, anaerobic fermentation reaction unit 10 further includes sinker 500, sinker 500
It is connected between the import 416 of water outlet 112 and degassing precipitation chamber 411 of anaerobic reaction room 110.Sinker can be utilized in this way
The energy of water that 500 consumption and dispersion are flowed out by anaerobic fermentation tank body 100, prevents from or mitigates to be flowed out by anaerobic fermentation tank body 100
Water to precipitate separator 400 erosion damage.
Advantageously, as shown in Figure 18 and Figure 20, anaerobic fermentation reaction unit 10 further includes mud return line 600, and sludge returns
One end of flow tube 600 is connected with anaerobic reaction room 110, and the sludge outlet 412 of degassing precipitation chamber 411 passes through sludge discharge pipe 700
It is connected with mud return line 600, mud return line 600 is equipped with sludge reflux pump 610, the anaerobism discharged from sludge outlet 412
Sludge can pass sequentially through sludge discharge pipe 700 and mud return line 800 returns to anaerobic reaction room 110, so as to be recycled.
Optionally, for external precipitation separator 400, hydrocyclone may be used or external air-floating apparatus replaces.
In some specific examples of the present invention, as shown in figure 20, the lower part of anaerobic reaction room 110 has mud discharging mouth
115, mud discharging mouth 115 is connected with mud discharging valve and/or mud discharging pump 116, extra anaerobism in anaerobic reaction room 110
Sludge can discharge anaerobic reaction room 110 by mud discharging mouth 115.
Optionally, as shown in Figure 18 and Figure 20, waste water inlet 111 is connected with charging pump 117, anti-to anaerobism to control whether
Answer 110 transport wastewater of room and the wastewater flow rate conveyed to anaerobic reaction room 110.As depicted in figs. 1 and 2, air supply pipe 300 is equipped with
Gas control valve 118 outside anaerobic reaction room 110, to control whether to supply to stripping tube 200 and to stripping tube 200
Air demand.
Further, the water inlet pipe at waste water inlet 111 can be connected with water distributor or water distribution is opened up on water inlet pipe
Hole.
Advantageously, as shown in Fig. 2, Fig. 6, Fig. 9 and Figure 11, anaerobic fermentation reaction unit 10 further includes water sealed tank 800, anaerobism
The top of fermentation tank 100 is equipped with safe gas port 114, and safe gas port 114 is connected with water sealed tank 800.It is possible thereby to utilize water seal
Tank 800 completely cuts off air, maintains the pressure of anaerobic reaction room 110, and can play the role of back-fire relief, and additionally biogas can be played
Certain clean-up effect.
Alternatively it is also possible to water sealed tank 800 is replaced using safety valve.
In some specific embodiments of the present invention, as shown in figure 12, waste water dephosphorization reaction unit 20 further includes aeration pump
Or Aeration fan 1700, aeration pump or Aeration fan 1700 be located at 1100 outside of dephosphorization reacting tank body and with 1200 phase of aerator
Even, with to 1200 pumped air of aerator.In some embodiments, aerator 1200 is for blast aeration and including being aerated wind
Pipe and the aeration plate or aeration tube mounted on aeration air hose end, aeration pump or Aeration fan 1700 are by being aerated air hose by air
Aeration tube or aeration plate are transported to, aeration tube or aeration plate will be in air aerations to dephosphorization reative cell 1110.
Optionally, aerator 1200 can be jetting type aerator, in the case, without being located at dephosphorization retort
The aeration pump or Aeration fan 1700 of 1100 outside of body, jetting type aerator utilize jetting type hydraulic blow formula air diffusion dress
It puts and draws air into dephosphorization reative cell 1110, such as the ejector being located in dephosphorization reative cell 1110 is anti-with reference to dephosphorization is located at
Answer the jet pump outside tank body 1100.
Advantageously, as shown in figure 12, water inlet 1111 is connected with the waste water control valve outside dephosphorization reacting tank body 1100
1114, to control whether to 1110 transport wastewater of dephosphorization reative cell and the wastewater flow rate conveyed to dephosphorization reative cell 1110.
As shown in figure 12, dephosphorization reative cell 1110 is smoothly put into for convenience of dephosphorization agent and other impurity etc. is avoided to enter and is removed
Phosphorus reaction room 1110, while play heat preservation and reduce the effect of heating energy consumption, the top of dephosphorization reacting tank body 1100 is equipped with head cover
1115, dephosphorization agent adding mouth 1112 is located on head cover 1115.
In some specific embodiments of the present invention, as shown in figure 12, aerator 1200 has multiple aeration heads or exposure
Tracheae 1210, multiple aeration heads or aeration tube 1210 are arranged at intervals in dephosphorization reative cell 1110, and aerator 1200 is by more
A aeration head or aeration tube 1210 improve the even results of oxygen supply and become reconciled to waste water to 1110 uniform aeration of dephosphorization reative cell
The uniform stirring effect of oxygen sludge.
Further, as shown in figure 12, waste water dephosphorization reaction unit 20 further includes multiple guide shells 1400, guide shell 1400
Quantity it is corresponding with the quantity of aeration head or aeration tube 1210, the top and bottom of each guide shell 1400 are opened wide, multiple exposures
Gas head or aeration tube 1210 stretch into multiple guide shells 1400 from the lower end of multiple guide shells 1400 respectively.Thus, it is possible to using more
A guide shell 1400 plays guide functions, so as to further make waste water in dephosphorization reative cell 1110 and aerobic sludge abundant
Contact, aerobic sludge are in suspended state, the exposure level of waste water and aerobic sludge are improved, so as to improve waste water treatment efficiency.
With reference to the design of guide shell, Mg (OH) 2 lotion is added under optimum reaction condition, generates ammonia magnesium phosphate
(MgNH4PO4.6H2O is commonly called as guanite) crystallizes.Under such circumstances, a part of COD can also pass through the dissolving in waste water
Oxygen is removed, and forms new biomass and carbon dioxide.
Optionally, as shown in figure 12, waste water dephosphorization reaction unit 20 further includes water distributor 1500, and water distributor 1500, which is located at, to be removed
In phosphorus reaction room 1110 and positioned at 1200 lower section of aerator, water distributor 1500 is connected with water inlet 1111, and water distributor 1500
With the multiple water distribution mouths 1510 being arranged at intervals and Open Side Down.Waste water enters water distributor 1500 by water inlet 1111, and by cloth
Multiple water distribution mouths 1510 of hydrophone 1500 are uniformly dispersed to dephosphorization reative cell 1110.
In some specific examples of the present invention, as shown in figure 12, waste water dephosphorization reaction unit 20 further includes cyclone
1600, dephosphorization reative cell 1110 has the discharge gate 1113 positioned at 1100 lower part of dephosphorization reacting tank body, and cyclone 1600 has rotation
Device import 1610, mud mouth 1620 and cyclone outlet 1630 are flowed, cyclone inlets 1610 are connected with discharge gate 1113 and eddy flow
Blow-off valve 1116 is connected between device import 1610 and discharge gate 1113, cyclone outlet 1630 passes through return pipe 1640 and dephosphorization
Reative cell 1110 is connected.
Discharge gate 1113,1116 and of blow-off valve can be passed through successively by being deposited on the liquid-solid mixture of 1110 bottom of dephosphorization reative cell
Cyclone inlets 1610 enter cyclone 1600 and are detached in cyclone 1600, and the water after separation passes sequentially through cyclone
Outlet 1630 and return pipe 1640 return to dephosphorization reative cell 1110, and the solid (such as ammonium magnesium phosphate) after detaching is by mud mouth 1620
Birds droppings pond is delivered to, can be used as fertilizer.
With reference to the design of cyclone, to detach struvite crystals and activated sludge and water, to improve the pure of guanite
It spends and is used as fertilizer application.
Compared to traditional dephosphorization apparatus, such as compared with the device for adding molysite, the dephosphorization reaction unit of the embodiment of the present invention
Cost is lower, and the multiple purposes of set of device (except ammonia nitrogen and COD), the guanite of generation does not cause secondary pollution not only, still
It is sustained N, the fertilizer of P, Mg.Guanite particle is separated by cyclone from device, and quality meets such as European Union
Fertilizer relevant criterion.
In some specific embodiments of the present invention, waste water dephosphorization reaction unit 20 further includes pump and with pumping the desliming being connected
Device, the clear liquid after desliming device removing sludge is back to dephosphorization reative cell 1110 is stated, so as to improve the utilization rate of waste water.
Optionally, settler replacement may be used in the desliming device, i.e., waste water dephosphorization reaction unit 20 further includes pump
The settler being connected is pumped with described, the stillness of night after the settler precipitates returns to dephosphorization reative cell 1110.
In some specific examples of the present invention, as shown in Figure 12 and Figure 13,.Degassing precipitation separator 1300 includes separation
Device ontology 1310, baffle 1320, inclined settling plate tilt sediment tube 1330 and effluent overflow weir water 1340.
Degassing mud chamber 1311 is formed in separator body 1310, there is sludge to arrange mouth for the bottom of degassing mud chamber 1311
1314, the cross-sectional area of the lower part for the mud chamber 1311 that deaerates is gradually reduced along direction from the top down.Baffle 1320 is located at degassing
The top for the mud chamber 1311 that deaerates is separated into devolatilizing chamber 1312 and precipitation chamber 1313 by the top of mud chamber 1311, baffle 1320,
The bottom of devolatilizing chamber 1312 is connected with precipitating the bottom of chamber 1313 so that waste water overflows to devolatilizing chamber from dephosphorization reative cell 1110
It is flowed in precipitation chamber 1313 in 1312 and then from the bottom of devolatilizing chamber 1312.It is heavy that inclined settling plate or inclination sediment tube 1330 are located at
In shallow lake chamber 1313.Effluent overflow weir water 1340 is located in precipitation chamber 1313 and the formation of effluent overflow weir water 1340 is had and denitrification reactor
The water outlet overflow launder 1341 of the separation outlet 1342 of 40 connections.
Below with reference to separation of Figure 12 and Figure 13 description degassing precipitation separators 1300 to water, gas and aerobic sludge
Journey.
Gas-entrained and aerobic sludge in water after aerobic sludge is degraded, gas-entrained and aerobic sludge water overflow is extremely
The devolatilizing chamber 1312 of degassing mud chamber 1311, wherein gas are escaped from devolatilizing chamber 1312, are arranged by the top of dephosphorization reative cell 1110
Go out, complete gas separation.The water of entrainment aerobic sludge after being detached with gas precipitates chamber by the bottom flow direction of devolatilizing chamber 1312
1313, aerobic sludge precipitates sinking at this time and the guiding of the inner wall in degassing 1311 lower tilt of mud chamber arranges mouth down toward sludge
1314, degassing precipitation separator 1300 is discharged by sludge row's mouth 1314 and enters dephosphorization reative cell 1110, continues on for wastewater degradation,
In water outlet overflow launder 1341 of the water overflow to effluent overflow weir water 1340 after being detached in degassing mud chamber 1311 with aerobic sludge,
And be expelled to outside dephosphorization reative cell 1110 by separation outlet 1342, carry out subsequent processing.It is good during aerobic sludge rises with water
Oxygen sludge settles on inclined settling plate or inclination sediment tube 1330 and is slipped to degassing 1311 bottom of mud chamber, contributes to aerobic
Sludge is separated from water, and so far, completes the separation of water, aerobic sludge and gas.
Advantageously, as shown in figure 13, the upper edge that the separator body 1310 of devolatilizing chamber 1312 is limited with baffle 1320 is low
In baffle 1320 upper edge and with baffle 1320 limit precipitation chamber 1313 1310 part of separator body upper edge.Change speech
It, the upper edge of the part for limiting devolatilizing chamber 1312 of separator body 1310 is heavy less than limiting for separator body 1310
The part upper edge of shallow lake chamber 1313, and less than the upper edge of baffle 1320.The upper edge of effluent overflow weir water 1340 can be with separator body
The upper edge of 1310 part for limiting devolatilizing chamber 1312 is concordant or limits devolatilizing chamber 1312 higher than separator body 1310
Part upper edge, and the upper edge of effluent overflow weir water 1340 less than separator body 1310 limit precipitation chamber 1313 portion
Divide upper edge and the upper edge of baffle 1320.The water in devolatilizing chamber 1312 be thus it can be prevented that from top overflow to precipitation chamber 1313,
Ensure that the water in devolatilizing chamber 1312 flow to precipitation chamber 1313, and then be sufficiently separated aerobic sludge from 1312 bottom of devolatilizing chamber, and
And the water in precipitation chamber 1313 is by overflow to water outlet overflow launder 1341, avoiding and being carried secretly in the water in water outlet overflow launder 1341
Aerobic sludge.
Optionally, as shown in figure 13, the cross section of separator body 1310 is rectangle, such as cuboid, separator sheet
The lower end of first longitudinal side wall 1315 of the lower part of body 1310 extends downward beyond the second longitudinal side of the lower part of separator body 1310
The lower end of wall 1316, and the lower end of the first longitudinal side wall 1315 and the lower end of the second longitudinal side wall 1316 are be overlapped in the up-down direction.By
This can advantageously be avoided the aerobic sludge in dephosphorization reative cell 1110 from arranging mouth 1314 into degassing precipitation separator by sludge
In 1300 degassing mud chamber 1311.
For example, in four longitudinal side walls of separator body 1310, two longer longitudinal side walls of length in the horizontal direction
Respectively the first longitudinal side wall 1315 and the second longitudinal side wall 1316, under the lower end of the first longitudinal side wall 1315 and the second longitudinal side wall 1316
End is mutually adjacent relative to the upper end of the first longitudinal side wall 1315 and the upper end of the second longitudinal side wall 1316, under the first longitudinal side wall 1315
End is located at the lower section of the lower end of the second longitudinal side wall 1316, and the lower end of the first longitudinal side wall 1315 and the lower end of the second longitudinal side wall 1316
Projection overlapping in the horizontal plane, the gap between the lower end of the first longitudinal side wall 1315 and the lower end of the second longitudinal side wall 1316 are formed
Sludge arranges mouth 1314, can pass through sludge after the aerobic sludge precipitation in mud chamber 1311 that thus on the one hand can ensure to deaerate
It arranges mouth 1314 and smoothly returns to dephosphorization reative cell 1110, and on the other hand the structure of sludge row mouth 1314 can stop except phosphorus reaction
Aerobic sludge in room 1110 enters degassing mud chamber 1311 from sludge row's mouth 1314, ensures the good of degassing precipitation separator 1300
Oxygen sludge separating effect.
In some specific embodiments of the present invention, as shown in Figure 10, Figure 14, Figure 17 and Figure 20, denitrification reactor 40 wraps
It includes along the sequentially connected anaerobic ammonia oxidation reactor 2100 in waste water treatment process direction and Anoxic/Aerobic reaction tank 2200.Wherein,
Anaerobic ammonia oxidation reactor 2100 is connected with waste water dephosphorization reaction unit 20, Anoxic/Aerobic reaction tank 2200 and advanced treatment system
60 are connected, and the waste water flowed out by waste water dephosphorization reaction unit 20 is anti-followed by anaerobic ammonia oxidation reactor 2100 and Anoxic/Aerobic
Pond 2200 is answered to carry out denitrogenation processing.
In some specific examples of the present invention, pasture waste water treatment system 1 further includes coagulation reaction device, the coagulation
Reaction unit is connected between denitrification reactor 40 and advanced treatment system 60, and the coagulation reaction device has along the waste water
Coagulating basin, flocculation basin and the sedimentation basin that treatment process direction is sequentially communicated, dosing coagulant in coagulating basin add wadding in flocculation basin
Solidifying agent, sedimentation basin is for the precipitation separation that deaerates.
In in some specific implementations of the present invention, as shown in figure 21 and figure, first is equipped in Fenton's reaction chamber 4111
Fenton blender 4113.And/or Fenton's reaction pond 4110 is equipped with the first stirring air connected with Fenton's reaction chamber 4111 and enters
Mouth (not shown) is stirred with being passed through air to Fenton's reaction chamber 4111 living.
The second Fenton blender 4117 is equipped in PH readjustment chambers 4115.And/or Fenton's reaction pond 4110 is equipped with and is returned with PH
The second stirring air intake (not shown) that chamber 4115 connects is adjusted, is stirred with being passed through air to PH readjustment chambers 4115.
Third Fenton blender 4118 (as shown in figure 21) is equipped in devolatilizing chamber 4116, third Fenton blender 4118 turns
Speed is higher than the rotating speed of the 4th Fenton blender 4114.And/or Fenton's reaction pond 4110 is equipped with the connected with devolatilizing chamber 4116
Three stirring air intakes 4127 (as shown in figure 22), are stirred with being passed through air to devolatilizing chamber 4116.
The 4th Fenton blender 4114 is equipped in Fenton flocculation chamber 4112.And/or Fenton's reaction pond 4110 is equipped with and sweet smell
The 4th stirring air intake (not shown) that the flocculation chamber 4112 that pauses connects, to be passed through air progress to Fenton flocculation chamber 4112
Stirring.
Fenton mud scraper 4132 is equipped in Fenton sedimentation basin 4130.
In other words, it is each in Fenton's reaction chamber 4111, PH readjustments chamber 4115, devolatilizing chamber 4116 and Fenton flocculation chamber 4112
It is a, blender stirring may be used, compressed air can also be used to stir, blender and compressed air can also be used simultaneously
Stirring.Wherein, the rotating speed of the first Fenton blender 4113, the rotating speed of the second Fenton blender 4117, third Fenton blender
4118 rotating speed is respectively higher than the rotating speed of the 4th Fenton blender 4114,
It is possible thereby to pass through the first Fenton blender 4113, the second Fenton blender 4117, third Fenton blender 4118
Waste water is stirred with the 4th Fenton blender 4114, so as to improve abolishment treatment effeciency, and can be gone using Fenton mud scraper 4132
Except the sludge in Fenton sedimentation basin 4130.
Wherein, as shown in figure 21, it is equipped on Fenton's reaction pond 4110 in the embodiment of third stirring air intake 4127,
Advanced treatment system 60 further includes stirring air delivery pipe 4128, and stirring air delivery pipe 4128 stirs air intake by third
4127 stretch into devolatilizing chamber 4116, for example, the lower end of stirring air delivery pipe 4128 can extend into the bottom of devolatilizing chamber 4116,
So as to improve mixing effect.Certainly, the first stirring air intake, the second stirring air intake, the 4th stirring air intake also may be used
To set corresponding stirring air delivery pipe.
The present invention some specific examples in, as shown in figure 21 and figure, for the ease of it is various add object add with
And the setting and connection of advanced treatment system 60, advanced treatment system 60 further include that acid adds pipe 4131, catalyst adds pipe
4132nd, oxidant adds pipe 4133, alkali adds pipe 4134 and flocculant concentration pipe 4136.
Acid, which adds pipe 4131 and adds mouth 4121 with acid, to be connected, for conveying sulfuric acid.Catalyst adds pipe 4132 and catalyst
It adds mouth 4122 to connect, for conveying ferrous sulfate.Oxidant, which adds pipe 4133 and adds mouth 4123 with oxidant, to be connected, for defeated
Send hydrogen peroxide.Alkali, which adds pipe 4134 and adds mouth 4124 with alkali, to be connected, for conveying alkali.Flocculant concentration pipe 4136 is thrown with flocculant
Mouth 4126 is added to connect, for conveying flocculant.
In some specific embodiments of the present invention, as shown in figure 21 and figure, first is equipped in Fenton's reaction pond 4110
Partition board 4141, second partition 4142 and third partition board 4143.
First partition 4141 separates Fenton's reaction chamber 4111 and PH readjustment chambers 4115, and second partition 4142 separates PH readjustment chambers
4115 and devolatilizing chamber 4116, third partition board 4143 separates devolatilizing chamber 4116 and Fenton flocculation chamber 4112.First partition 4141 and
The lower end of three partition boards 4143 is connected with the bottom wall in Fenton's reaction pond 4110, lower end and the Fenton's reaction pond 4110 of second partition 4142
Bottom wall be spaced apart, and the upper end of second partition 4142 higher than first partition 4141 upper end and third partition board 4143 upper end.
Waste water in Fenton's reaction chamber 4111 adjusts back chamber 4115 by the upper end overflow of first partition 4141 to PH, and PH is adjusted back in chamber 4115
Waste water flow to devolatilizing chamber 4116 by the lower end of second partition 4142, the waste water in devolatilizing chamber 4116 by third partition board 4143 upper end
Overflow to Fenton flocculate chamber 4112.
In some specific examples of the present invention, as shown in figure 21 and figure, advanced treatment system 60 further includes continuous sand
Filter 4200.
Continuous sand filter 4200 is connected between Fenton sedimentation basin 4130 and active carbon filter 3000, continuous sand filter
4200 have compressed air inlet 4201 and sand filtration flushing water out 4202, and water out 4202 and Fenton's reaction pond are rinsed in sand filtration
4110 Fenton's reaction chamber 4111 or Fenton sedimentation basin 4130 connects.The water that Fenton sedimentation basin 4130 flows out enters continuous sand filter
4200, compressed air enters continuous sand filter 4200 to be carried out to the water in continuous sand filter 4200 by compressed air inlet 4201
Filter sand removes the solid suspension in water removal, improves the degree of purity of the water of outflow, and sand filtration flushing water rinses water out by sand filtration
4202 return to the Fenton's reaction chamber 4111 in Fenton's reaction pond 4110 or Fenton sedimentation basin 4130.
In some specific examples of the present invention, as shown in Fig. 1,3,6,8,10,14,17 and 19, pasture wastewater treatment system
System 1 further includes reuse pipe 2000, reuse pipe 2000 and pretreatment system 70, COD and denitrogenation processing system 80 and advanced treating
At least one of system 60 is connected.Waste water can be from pretreatment system 70, COD and denitrogenation processing system 80 and advanced treating
Ground is rinsed at least one of system 60 reuse to cowshed and the milk Room, make the wastewater treatment capacity of pasture waste water treatment system 1 with
The fresh water amount that daily workshop is come maintains an equal level.
Preferably, reuse pipe 2000 respectively with adjust the water outlet of tank 73, waste water dephosphorization reaction unit 20 water outlet or
The water outlet of high load aeration tank 30, the water outlet of denitrification reactor 40, the water outlet of continuous sand filter 4200 and activated carbon mistake
The water outlet of filter 3000 is connected.
In the description of the present invention, it is to be understood that term " " center ", " longitudinal direction ", " transverse direction ", " length ", " width ",
" thickness ", " on ", " under ", "front", "rear", "left", "right", " vertical ", " level ", " top ", " bottom " " interior ", " outer ", " up time
The orientation or position relationship of the instructions such as needle ", " counterclockwise " are based on orientation shown in the drawings or position relationship, are for only for ease of
The description present invention and simplified description rather than instruction imply that signified device or element must be with specific orientation, Yi Te
Fixed azimuth configuration and operation, therefore be not considered as limiting the invention.
In addition, term " first ", " second " are only used for description purpose, and it is not intended that instruction or hint relative importance
Or the implicit quantity for indicating indicated technical characteristic.Define " first " as a result, the feature of " second " can be expressed or
Implicitly include one or more this feature.In the description of the present invention, " multiple " are meant that at least two, such as two
It is a, three etc., unless otherwise specifically defined.
In the present invention unless specifically defined or limited otherwise, term " installation ", " connected ", " connection ", " fixation " etc.
Term should be interpreted broadly, for example, it may be being fixedly connected or being detachably connected or integral；Can be that machinery connects
It connects or is electrically connected；It can be directly connected, can also be indirectly connected by intermediary, can be in two elements
The connection in portion or the interaction relationship of two elements.It for the ordinary skill in the art, can be according to specific feelings
Condition understands the concrete meaning of above-mentioned term in the present invention.
In the present invention unless specifically defined or limited otherwise, fisrt feature second feature it " on " or it " under "
It can be in direct contact including the first and second features, it is not to be in direct contact but pass through it that can also include the first and second features
Between other characterisation contact.Moreover, fisrt feature second feature " on ", " top " and " above " including first spy
Sign is right over second feature and oblique upper or is merely representative of fisrt feature level height higher than second feature.Fisrt feature exists
Second feature " under ", " lower section " and " following " immediately below second feature and obliquely downward or be merely representative of including fisrt feature
Fisrt feature level height is less than second feature.
In the description of this specification, reference term " one embodiment ", " example ", " is specifically shown " some embodiments "
The description of example " or " some examples " etc. means specific features, structure, material or the spy for combining the embodiment or example description
Point is contained at least one embodiment of the present invention or example.In the present specification, schematic expression of the above terms are not
It must be directed to identical embodiment or example.Moreover, particular features, structures, materials, or characteristics described can be in office
What combined in an appropriate manner in one or more embodiments or example.In addition, those skilled in the art can say this
Different embodiments or examples described in bright book are engaged and are combined.
Although the embodiments of the present invention has been shown and described above, it is to be understood that above-described embodiment is example
Property, it is impossible to limitation of the present invention is interpreted as, those of ordinary skill in the art within the scope of the invention can be to above-mentioned
Embodiment is changed, changes, replacing and modification.
Claims (63)
1. a kind of pasture waste water treatment system, which is characterized in that including along the sequentially connected pretreatment in waste water treatment process direction
System, COD and denitrogenation processing system and advanced treatment system,
Wherein, the advanced treatment system is included along the sequentially connected Fenton's reaction device in the waste water treatment process direction and work
Property carbon filter, the Fenton's reaction device includes Fenton's reaction pond, with along the wastewater treatment in the Fenton's reaction pond
Fenton's reaction chamber, PH readjustments chamber, devolatilizing chamber and Fenton flocculation chamber, the Fenton's reaction chamber that process orientation is sequentially communicated have acid
Add mouth, catalyst adds mouth and oxidant adds mouth, there is the PH readjustments chamber alkali to add mouth, and the Fenton flocculation chamber has
Flocculant concentration mouth.
2. pasture waste water treatment system according to claim 1, which is characterized in that the pretreatment system is included along described
The sequentially connected setting pot in waste water treatment process direction, solid-liquid separator and adjusting tank.
3. pasture waste water treatment system according to claim 2, which is characterized in that the setting pot is equipped with pretreatment and scrapes
Mud machine.
4. pasture waste water treatment system according to claim 2, which is characterized in that described to adjust tank and the COD and take off
Charging pump is connected between nitrogen processing system.
5. the pasture waste water treatment system according to any one of claim 1-4, which is characterized in that the COD and denitrogenation
Processing system includes along the sequentially connected anaerobic fermentation reaction unit in the waste water treatment process direction, high load aeration tank, takes off
Analysis and dephosphorizing reactor.
6. pasture waste water treatment system according to claim 5, which is characterized in that the anaerobic fermentation reaction unit includes
Anaerobic fermentation tank body, stripping tube and air supply pipe, the anaerobic fermentation tank body is interior to have anaerobic reaction room, the anaerobic reaction room tool
There are waste water inlet, water outlet and exhaust outlet, the stripping tube is located in the anaerobic reaction room, and the upper end of the stripping tube has
Gas outlet and the lower end of the stripping tube have air inlet, and the air supply pipe is connected with the air inlet of the stripping tube, for
Supply is used for the gas of air lift in the stripping tube.
7. pasture waste water treatment system according to claim 6, which is characterized in that the lower end of the stripping tube is neighbouring described
The bottom of anaerobic reaction room and the upper end of the stripping tube extend to the top of the anaerobic reaction room, and the water outlet is located at institute
State the top of anaerobic reaction room and higher than the upper end of the stripping tube.
8. the pasture waste water treatment system described according to claim 6 or 7, which is characterized in that the upper surface of the stripping tube opens
It opens to form the gas outlet, the lower face of the stripping tube is opened wide to form the air inlet.
9. pasture waste water treatment system according to claim 8, which is characterized in that the stripping tube is included vertically
The straight pipe of extension and the segmental arc being connected with the upper end of the straight pipe, the opening direction of the gas outlet with straight down
Angle between direction is more than or equal to zero degree and less than 180 degree.
10. pasture waste water treatment system according to claim 9, which is characterized in that the segmental arc is described to be inverted U-shaped
The opening direction of gas outlet is straight down.
11. the pasture waste water treatment system according to any one of claim 6-10, which is characterized in that the stripping tube is
It is multiple and be arranged at intervals in the horizontal plane.
12. the pasture waste water treatment system according to any one of claim 6-11, which is characterized in that the anaerobic fermentation
Reaction unit further includes：Separator is precipitated, the precipitation separator is located in the anaerobic reaction room and positioned at the stripping tube
Top, the precipitation separator is with the separator water outlet and the water outlet and the high load capacity being connected with the water outlet
Aeration tank is connected.
13. pasture waste water treatment system according to claim 12, which is characterized in that the precipitation separator includes：
Babinet, degassing precipitation chamber is formed in the babinet, and the bottom of the degassing precipitation chamber has sludge outlet, the degassing
The cross-sectional area for precipitating the lower part of chamber is gradually reduced along direction from the top down；
Partition board, the partition board are located at the top of the degassing precipitation chamber, and the top that the degassing is precipitated chamber by the partition board separates
Into degassing district and settling zone, the bottom of the degassing district is connected with the bottom of the settling zone so that waste water is from the anaerobic reaction
Room overflows in the degassing district and then is flowed in the settling zone from the bottom of the degassing district；
Precipitation inclined plate, the precipitation inclined plate are located in the settling zone；
Downflow weir, the downflow weir is located in the settling zone and the downflow weir forms overflowing with the separator water outlet
Chute.
14. pasture waste water treatment system according to claim 13, which is characterized in that limited with the partition board described de-
The upper edge of the box portion in gas area is less than the upper edge of the partition board and the chest portion of the settling zone is limited with the partition board
The upper edge divided.
15. pasture waste water treatment system according to claim 14, which is characterized in that the babinet is cuboid, described
The lower end of first longitudinal side wall of the lower part of babinet extends downward beyond the lower end of the second longitudinal side wall of the lower part of the babinet, and institute
Lower end and the lower end of second longitudinal side wall for stating the first longitudinal side wall are be overlapped in the up-down direction.
16. the pasture waste water treatment system according to any one of claim 6-11, which is characterized in that the anaerobic fermentation
Reaction unit further includes：Precipitate separator, the precipitation separator is located at that the anaerobic fermentation tank is external and the water outlet leads to
It crosses the precipitation separator with the high load aeration tank to be connected, the precipitation separator includes：
Babinet, the babinet is interior to form degassing precipitation chamber, and the degassing precipitates chamber, and there is import, separator water outlet and sludge to go out
Mouthful, the import is connected with the water outlet, and the separator water outlet is connected with the high load aeration tank, and the degassing is heavy
The lower part of shallow lake chamber is formed as at least one conical cavity that cross-sectional area is gradually reduced along direction from the top down, the sludge outlet
It is formed in the bottom of the conical cavity；
Precipitation inclined plate, the precipitation inclined plate are located at the degassing precipitation intracavitary；
Downflow weir, the downflow weir are located to be formed in the degassing precipitation intracavitary and the downflow weir and be discharged with the separator
The overflow launder of mouth connection.
17. pasture waste water treatment system according to claim 16, which is characterized in that the anaerobic fermentation reaction unit is also
Including：Sinker, the sinker are connected between the import of water outlet and the degassing precipitation chamber of the anaerobic reaction room.
18. pasture waste water treatment system according to claim 16, which is characterized in that the anaerobic fermentation reaction unit is also
Including：
Sludge for will be discharged from the sludge outlet returns to the indoor mud return line of the anaerobic reaction, the sludge
One end of return duct is connected with the anaerobic reaction room, and the sludge outlet passes through sludge discharge pipe and the mud return line phase
Even, the mud return line is equipped with sludge reflux pump.
19. the pasture waste water treatment system according to any one of claim 6-18, which is characterized in that the anaerobic fermentation
Reaction unit further includes：Water sealed tank, the top of the anaerobic fermentation tank body are equipped with safe gas port, the safe gas port and the water
Sealed cans are connected.
20. the pasture waste water treatment system according to claim requires any one of 5-19, which is characterized in that the denitrogenation
Reactor includes the anaerobic ammonia oxidation reactor being connected to each other and Anoxic/Aerobic reaction tank.
21. the pasture waste water treatment system according to claim requires any one of 5-19, which is characterized in that the dephosphorization
Reactor includes：
Coagulation reaction tank, the coagulation reaction tank is interior to be had the dephosphorization reaction chamber being connected with the denitrification reactor and is removed with described
The dephosphorization flocculation chamber that phosphorus reaction chamber is connected, the dephosphorization reaction chamber is interior to be set equipped with the fast blender of dephosphorization and dephosphorization flocculation intracavitary
There is the slow blender of dephosphorization；
Dephosphorization sedimentation basin, the dephosphorization sedimentation basin is connected respectively with dephosphorization flocculation chamber and the advanced treatment system, described
Dephosphorization tilted plate separator and dephosphorization mud scraper are equipped in dephosphorization sedimentation basin.
22. according to the pasture waste water treatment system described in claim requirement 21, which is characterized in that the dephosphorizing reactor also wraps
It includes：
Coagulant solution tank, the coagulant solution tank are connected with the dephosphorization reaction chamber；
Phosphate eliminating flocculant tank, the phosphate eliminating flocculant tank are connected with dephosphorization flocculation chamber.
23. the pasture waste water treatment system according to any one of claim 1-4, which is characterized in that the COD and denitrogenation
Processing system is included along the sequentially connected anaerobic fermentation reaction unit in the waste water treatment process direction, waste water dephosphorization reaction unit
And denitrification reactor.
24. pasture waste water treatment system according to claim 23, which is characterized in that the anaerobic fermentation reaction unit packet
Anaerobic fermentation tank body, stripping tube and air supply pipe are included, there is anaerobic reaction room, the anaerobic reaction room in the anaerobic fermentation tank body
With waste water inlet, water outlet and exhaust outlet, the stripping tube is located in the anaerobic reaction room, the upper end tool of the stripping tube
There are gas outlet and the lower end of the stripping tube that there is air inlet, the air supply pipe is connected with the air inlet of the stripping tube, is used for
Into the stripping tube, supply is used for the gas of air lift；
It is anti-that the waste water dephosphorization reaction unit includes dephosphorization reacting tank body, aerator and degassing precipitation separator, the dephosphorization
Answering has dephosphorization reative cell in tank body, the dephosphorization reative cell has water inlet and dephosphorization agent adding mouth, and the aerator is set
In the dephosphorization reative cell, the degassing precipitation separator is located in the dephosphorization reative cell and on the aerator
Side, for detaching gas and water and sludge.
25. pasture waste water treatment system according to claim 24, which is characterized in that the lower end of the stripping tube is adjacent to institute
The upper end for stating the bottom of anaerobic reaction room and the stripping tube extends to the top of the anaerobic reaction room, and the water outlet is located at
The top of the anaerobic reaction room and the upper end for being higher than the stripping tube.
26. the pasture waste water treatment system according to claim 24 or 25, which is characterized in that the upper surface of the stripping tube
It opens wide to form the gas outlet, the lower face of the stripping tube is opened wide to form the air inlet.
27. pasture waste water treatment system according to claim 26, which is characterized in that the stripping tube is included along vertical side
Straight pipe to extension and the segmental arc being connected with the upper end of the straight pipe, the opening direction of the gas outlet with straight down
Direction between angle be more than or equal to zero degree and less than 180 degree.
28. pasture waste water treatment system according to claim 27, which is characterized in that the segmental arc is described to be inverted U-shaped
The opening direction of gas outlet is straight down.
29. the pasture waste water treatment system according to any one of claim 24-28, which is characterized in that the stripping tube
It is multiple and be arranged at intervals in the horizontal plane.
30. the pasture waste water treatment system according to any one of claim 24-29, which is characterized in that the anaerobism hair
Ferment reaction unit further includes：Separator is precipitated, the precipitation separator is located in the anaerobic reaction room and positioned at the air lift
Above pipe, the precipitation separator is with the separator water outlet and the water outlet and the waste water being connected with the water outlet
The water inlet of dephosphorization reaction unit is connected.
31. pasture waste water treatment system according to claim 30, which is characterized in that the precipitation separator includes：
Babinet, degassing precipitation chamber is formed in the babinet, and the bottom of the degassing precipitation chamber has sludge outlet, the degassing
The cross-sectional area for precipitating the lower part of chamber is gradually reduced along direction from the top down；
Partition board, the partition board are located at the top of the degassing precipitation chamber, and the top that the degassing is precipitated chamber by the partition board separates
Into degassing district and settling zone, the bottom of the degassing district is connected with the bottom of the settling zone so that waste water is from the anaerobic reaction
Room overflows in the degassing district and then is flowed in the settling zone from the bottom of the degassing district；
Precipitation inclined plate, the precipitation inclined plate are located in the settling zone；
Downflow weir, the downflow weir is located in the settling zone and the downflow weir forms overflowing with the separator water outlet
Chute.
32. pasture waste water treatment system according to claim 31, which is characterized in that limited with the partition board described de-
The upper edge of the box portion in gas area is less than the upper edge of the partition board and the chest portion of the settling zone is limited with the partition board
The upper edge divided.
33. pasture waste water treatment system according to claim 32, which is characterized in that the babinet is cuboid, described
The lower end of first longitudinal side wall of the lower part of babinet extends downward beyond the lower end of the second longitudinal side wall of the lower part of the babinet, and institute
Lower end and the lower end of second longitudinal side wall for stating the first longitudinal side wall are be overlapped in the up-down direction.
34. the pasture waste water treatment system according to any one of claim 24-29, which is characterized in that the anaerobism hair
Ferment reaction unit further includes：Precipitate separator, the precipitation separator is located at that the anaerobic fermentation tank is external and the water outlet
It is connected by the precipitation separator with the waste water dephosphorization reaction unit, the precipitation separator includes：
Babinet, the babinet is interior to form degassing precipitation chamber, and the degassing precipitates chamber, and there is import, separator water outlet and sludge to go out
Mouthful, the import is connected with the water outlet, and the separator water outlet is connected with the waste water dephosphorization reaction unit, described de-
The lower part of gas precipitation chamber is formed as at least one conical cavity that cross-sectional area is gradually reduced along direction from the top down, the sludge
Outlet is formed in the bottom of the conical cavity；
Precipitation inclined plate, the precipitation inclined plate are located at the degassing precipitation intracavitary；
Downflow weir, the downflow weir are located to be formed in the degassing precipitation intracavitary and the downflow weir and be discharged with the separator
The overflow launder of mouth connection.
35. pasture waste water treatment system according to claim 34, which is characterized in that the anaerobic fermentation reaction unit is also
Including：Sinker, the sinker are connected between the import of water outlet and the degassing precipitation chamber of the anaerobic reaction room.
36. pasture waste water treatment system according to claim 34, which is characterized in that the anaerobic fermentation reaction unit is also
Including：
Sludge for will be discharged from the sludge outlet returns to the indoor mud return line of the anaerobic reaction, the sludge
One end of return duct is connected with the anaerobic reaction room, and the sludge outlet passes through sludge discharge pipe and the mud return line phase
Even, the mud return line is equipped with sludge reflux pump.
37. the pasture waste water treatment system according to any one of claim 24-36, which is characterized in that the anaerobism hair
Ferment reaction unit further includes：Water sealed tank, the top of the anaerobic fermentation tank body are equipped with safe gas port, the safe gas port with it is described
Water sealed tank is connected.
38. the pasture waste water treatment system according to any one of claim 24-37, which is characterized in that the aeration dress
It puts with spaced multiple aeration heads or aeration tube.
39. the pasture waste water treatment system according to claim 38, which is characterized in that the waste water dephosphorization reaction unit is also
Including：
Multiple guide shells, the top and bottom of each guide shell are opened wide, multiple aeration heads or aeration tube respectively from
Multiple guide shells are stretched into the lower end of multiple guide shells.
40. the pasture waste water treatment system according to any one of claim 24-39, which is characterized in that waste water dephosphorization is anti-
Device is answered to further include：
It is located at the water distributor in the dephosphorization reative cell and below the aerator, the water distributor and the water inlet
It is connected.
41. pasture waste water treatment system according to claim 40, which is characterized in that the water distributor, which has, to be arranged at intervals
And multiple water distribution mouths that Open Side Down.
42. the pasture waste water treatment system according to any one of claim 24-41, which is characterized in that the dephosphorization is anti-
Answer room that there is the discharge gate positioned at the dephosphorization reacting tank body lower part.
43. pasture waste water treatment system according to claim 42, which is characterized in that waste water dephosphorization reaction unit also wraps
It includes：
Cyclone, the cyclone have cyclone inlets, mud mouth and cyclone outlet, the cyclone inlets and the row
Material mouth connects, and the cyclone outlet is connected by return pipe with the dephosphorization reative cell.
44. pasture waste water treatment system according to claim 42, which is characterized in that the waste water dephosphorization reaction unit is also
Including：Pump and with pumping the desliming device that is connected, clear liquid after the desliming device removing sludge is back to the dephosphorization reative cell.
45. pasture waste water treatment system according to claim 42, which is characterized in that the waste water dephosphorization reaction unit is also
Including：Pump and the settler being connected with the pump, the stillness of night after the settler precipitates return to the dephosphorization reative cell.
46. the pasture waste water treatment system according to any one of claim 24-45, which is characterized in that the degassing is heavy
Shallow lake separator includes：
Separator body, the separator body is interior to form degassing mud chamber, and the bottom of the degassing precipitation chamber is with sludge row
Mouthful, the cross-sectional area of the lower part of the degassing precipitation chamber is gradually reduced along direction from the top down；
Baffle, the baffle are located at the top of the degassing mud chamber, and the baffle separates the top of the degassing mud chamber
Into devolatilizing chamber and precipitation chamber, the bottom of the devolatilizing chamber is connected so as to waste water from described with the bottom of the precipitation chamber except phosphorus reaction
Room overflows in the devolatilizing chamber and then flows to the precipitation intracavitary from the bottom of the devolatilizing chamber；
Inclined settling plate tilts sediment tube, and the inclined settling plate or inclination sediment tube are located at the precipitation intracavitary；
Effluent overflow weir water, the effluent overflow weir water is located at the precipitation intracavitary and the effluent overflow weir water is formed with anti-with denitrogenation
Answer the water outlet overflow launder of separation outlet that device connects.
47. pasture waste water treatment system according to claim 46, which is characterized in that limited with the baffle described de-
The upper edge of the separator body part of air cavity limits the precipitation chamber less than the upper edge of the baffle and with the baffle
The upper edge of separator body part.
48. pasture waste water treatment system according to claim 46, which is characterized in that the cross section of the separator body
For rectangle.
49. pasture waste water treatment system according to claim 46, which is characterized in that the lower part of the separator body
The lower end of first longitudinal side wall extends downward beyond the lower end of the second longitudinal side wall of the lower part of the separator body, and described first
The lower end of longitudinal side wall and the lower end of second longitudinal side wall are be overlapped in the up-down direction.
50. the pasture waste water treatment system according to any one of claim 24-49, which is characterized in that the waste water removes
Phosphorus reaction device further includes：It is located at the aeration pump being connected outside the dephosphorization reacting tank body and with the aerator or aeration wind
Machine, the water inlet are connected with waste water control valve.
51. the pasture waste water treatment system according to any one of claim 24-50, which is characterized in that the dephosphorization is anti-
The top of tank body is answered to be equipped with head cover, the dephosphorization agent adding mouth is located on the head cover.
52. the pasture waste water treatment system according to claim requires any one of 24-51, which is characterized in that described de-
Analysis includes the anaerobic ammonia oxidation reactor being connected to each other and Anoxic/Aerobic reaction tank.
53. the pasture waste water treatment system according to claim requires any one of 24-52, which is characterized in that the COD
Coagulation reaction device is further included with denitrogenation processing system, the coagulation reaction device is connected to the denitrification reactor and the depth
It spends between processing system, the coagulation reaction device has the coagulating basin being sequentially communicated along the waste water treatment process direction, wadding
Solidifying pond and sedimentation basin.
54. the pasture waste water treatment system according to any one of claim 1-53, which is characterized in that the Fenton's reaction
Pond is equipped with the first stirring air intake connected with the Fenton's reaction chamber；And/or
The Fenton's reaction intracavitary is equipped with the first Fenton blender.
55. the pasture waste water treatment system according to any one of claim 1-53, which is characterized in that the Fenton's reaction
Pond is equipped with the second stirring air intake connected with PH readjustment chambers；And/or
The PH readjustments intracavitary is equipped with the second Fenton blender.
56. the pasture waste water treatment system according to any one of claim 1-53, which is characterized in that the Fenton's reaction
Pond is equipped with the third stirring air intake connected with the devolatilizing chamber；And/or
Third Fenton blender is equipped in the devolatilizing chamber.
57. pasture waste water treatment system according to claim 56, which is characterized in that the Fenton's reaction pond be equipped with
The third stirring air intake of the devolatilizing chamber connection, the advanced waste treatment system further include：
Air delivery pipe is stirred, the stirring air delivery pipe is stretched by third stirring air intake in the devolatilizing chamber.
58. the pasture waste water treatment system according to any one of claim 1-53, which is characterized in that the Fenton flocculation
Intracavitary is equipped with the 4th Fenton blender；And/or
The Fenton's reaction pond is equipped with the 4th stirring air intake connected with Fenton flocculation chamber.
59. the pasture waste water treatment system according to any one of claim 1-58, which is characterized in that the advanced treating
System further includes：
Acid adds pipe, and the acid, which adds pipe and adds mouth with the acid, to be connected；
Catalyst adds pipe, and the catalyst, which adds pipe and adds mouth with the catalyst, to be connected；
Oxidant adds pipe, and the oxidant, which adds pipe and adds mouth with the oxidant, to be connected；
Alkali adds pipe, and the alkali, which adds pipe and adds mouth with the alkali, to be connected；
Flocculant concentration pipe, the flocculant concentration pipe are connected with the flocculant concentration mouth.
60. the pasture waste water treatment system according to any one of claim 1-59, which is characterized in that the Fenton's reaction
It is equipped in pond and separates the first partition of the Fenton's reaction chamber and PH readjustment chambers, separates the PH readjustment chambers and the degassing
The second partition of chamber and the third partition board for separating the devolatilizing chamber and Fenton flocculation chamber, the first partition and the third
The lower end of partition board is connected with the bottom wall in the Fenton's reaction pond, the bottom wall of the lower end of the second partition and the Fenton's reaction pond
It is spaced apart and upper end is higher than the upper end of the first partition and the upper end of the third partition board.
61. the pasture waste water treatment system according to any one of claim 1-60, which is characterized in that the Fenton's reaction
Device further includes Fenton sedimentation basin, the Fenton's reaction pond and the Fenton sedimentation basin along the waste water treatment process direction successively
Connection.
62. pasture waste water treatment system according to claim 61, which is characterized in that the advanced treatment system also wraps
It includes：
Continuous sand filter, the continuous sand filter is connected between the Fenton sedimentation basin and the active carbon filter, described
Continuous filter sand utensil has compressed air inlet and water out is rinsed in sand filtration, and water out and the Fenton's reaction pond are rinsed in the sand filtration
Fenton's reaction chamber or the Fenton sedimentation basin connection.
63. pasture waste water treatment system according to claim 1, which is characterized in that further include with the pretreatment system,
The reuse pipe that at least one of the COD and denitrogenation processing system and advanced treatment system are connected.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201611240046.6A CN108249690A (en) | 2016-12-28 | 2016-12-28 | Pasture waste water treatment system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201611240046.6A CN108249690A (en) | 2016-12-28 | 2016-12-28 | Pasture waste water treatment system |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108249690A true CN108249690A (en) | 2018-07-06 |
Family
ID=62720652
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201611240046.6A Pending CN108249690A (en) | 2016-12-28 | 2016-12-28 | Pasture waste water treatment system |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108249690A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114149077A (en) * | 2021-11-27 | 2022-03-08 | 浙江沃乐环境科技有限公司 | Integrated wastewater synchronous denitrification and defluorination reactor device and use method thereof |
Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101023034A (en) * | 2004-09-10 | 2007-08-22 | 荷兰帕克有限公司 | Process for the simultaneous removal of BOD and phosphate from waste water |
| CN203307190U (en) * | 2013-06-19 | 2013-11-27 | 清勤水处理科技（上海）有限公司 | Anaerobic reactor |
| CN203461878U (en) * | 2013-08-30 | 2014-03-05 | 济南绿创环境技术有限公司 | Aerobic granular sludge internal circulation reactor |
| CN204022547U (en) * | 2014-06-07 | 2014-12-17 | 段国秀 | A kind of novel anaerobic reactor |
| CN204185333U (en) * | 2014-06-08 | 2015-03-04 | 段国秀 | Integration advanced treatment system |
| CN204474452U (en) * | 2015-02-05 | 2015-07-15 | 四川宇阳环境工程有限公司 | A kind of new and effective treating organic waste water by Fenton method deflector type integration apparatus |
| CN205346961U (en) * | 2015-12-29 | 2016-06-29 | 帕克环保技术(上海)有限公司 | Biological denitrification reactor |
| CN105936542A (en) * | 2016-06-20 | 2016-09-14 | 江西理工大学 | AB-process aerobic granular sludge reactor and treatment technology thereof |
| CN106242162A (en) * | 2016-08-18 | 2016-12-21 | 南方创业（天津）科技发展有限公司 | The dirt of livestock and poultry farms in scale excrement and the recycling treatment process of waste water |
| CN206843279U (en) * | 2016-12-28 | 2018-01-05 | 帕克环保技术(上海)有限公司 | Pasture Waste Water Treatment |
-
2016
- 2016-12-28 CN CN201611240046.6A patent/CN108249690A/en active Pending
Patent Citations (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101023034A (en) * | 2004-09-10 | 2007-08-22 | 荷兰帕克有限公司 | Process for the simultaneous removal of BOD and phosphate from waste water |
| CN203307190U (en) * | 2013-06-19 | 2013-11-27 | 清勤水处理科技（上海）有限公司 | Anaerobic reactor |
| CN203461878U (en) * | 2013-08-30 | 2014-03-05 | 济南绿创环境技术有限公司 | Aerobic granular sludge internal circulation reactor |
| CN204022547U (en) * | 2014-06-07 | 2014-12-17 | 段国秀 | A kind of novel anaerobic reactor |
| CN204185333U (en) * | 2014-06-08 | 2015-03-04 | 段国秀 | Integration advanced treatment system |
| CN204474452U (en) * | 2015-02-05 | 2015-07-15 | 四川宇阳环境工程有限公司 | A kind of new and effective treating organic waste water by Fenton method deflector type integration apparatus |
| CN205346961U (en) * | 2015-12-29 | 2016-06-29 | 帕克环保技术(上海)有限公司 | Biological denitrification reactor |
| CN105936542A (en) * | 2016-06-20 | 2016-09-14 | 江西理工大学 | AB-process aerobic granular sludge reactor and treatment technology thereof |
| CN106242162A (en) * | 2016-08-18 | 2016-12-21 | 南方创业（天津）科技发展有限公司 | The dirt of livestock and poultry farms in scale excrement and the recycling treatment process of waste water |
| CN206843279U (en) * | 2016-12-28 | 2018-01-05 | 帕克环保技术(上海)有限公司 | Pasture Waste Water Treatment |
Non-Patent Citations (2)
| Title |
|---|
| 彭党聪主编: "《排水工程 下 第4版》", vol. 2010, 30 April 2010, 北京：中国建筑工业出版社, pages: 195 * |
| 李永峰等: "《厌氧发酵生物制氢》", 30 November 2012, 东北林业大学出版社, pages: 40 - 41 * |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN114149077A (en) * | 2021-11-27 | 2022-03-08 | 浙江沃乐环境科技有限公司 | Integrated wastewater synchronous denitrification and defluorination reactor device and use method thereof |
| CN114149077B (en) * | 2021-11-27 | 2023-02-14 | 浙江沃乐环境科技有限公司 | Integrated wastewater synchronous denitrification and defluorination reactor device and use method thereof |
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