CN203877954U - MAP-synthesis-based turbulence-state dephosphorization device - Google Patents

MAP-synthesis-based turbulence-state dephosphorization device Download PDF

Info

Publication number
CN203877954U
CN203877954U CN201420308195.1U CN201420308195U CN203877954U CN 203877954 U CN203877954 U CN 203877954U CN 201420308195 U CN201420308195 U CN 201420308195U CN 203877954 U CN203877954 U CN 203877954U
Authority
CN
China
Prior art keywords
map
inner core
empty chamber
endless tube
synthetic
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.)
Active
Application number
CN201420308195.1U
Other languages
Chinese (zh)
Inventor
安明哲
钟和平
苏建
刘阳
张富勇
彭智辅
乔宗伟
赵东
练顺才
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Wuliangye Yibin Co Ltd
Original Assignee
Wuliangye Yibin Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Wuliangye Yibin Co Ltd filed Critical Wuliangye Yibin Co Ltd
Priority to CN201420308195.1U priority Critical patent/CN203877954U/en
Application granted granted Critical
Publication of CN203877954U publication Critical patent/CN203877954U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The utility model discloses an MAP-synthesis-based turbulence-state dephosphorization device with simple structure and lower cost, which comprises a vertical tank body and an inner cylinder, wherein the inside of the vertical tank body is sequentially divided into an upper empty chamber, a middle fluidization region and a lower settling region; the top of the upper empty chamber is provided with a feed pipe and a sewage inlet pipe; the side wall of the upper empty chamber is provided with a water outlet; the inner cylinder is suspended on the top of the upper empty chamber and positioned in the middle fluidization region; the inner wall of the inner cylinder is provided with an obliquely downward screen baffle; the screen baffle is provided with at least one through hole; the lower side of the inner cylinder is provided with an aeration ring pipe; the upper part of the aeration ring pipe is provided with at least one aeration hole; the aeration ring pipe is also provided with a gas inlet pipe; and the bottom of the lower settling region is provided with a drainage port. The screen baffle enables the phosphorus-containing wastewater to form turbulence and sufficiently react with the fed material, and thus, the dephosphorization rate is high. The device has the advantages of simple structure, small occupied area and low construction cost, and is easy for popularization and application.

Description

A kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP
Technical field
The utility model relates to a kind of dephosphorization apparatus, especially a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP.
Background technology
Phosphoric is the important element that causes body eutrophication, and in the time that in environment water, total phosphorus concentration reaches 0.02mg/L, the eubiosis of water surrounding is destroyed.Struvite MAP is a kind of white crystal that is insoluble in water, and its main component is six hypophosphite monohydrate ammonium magnesium (MgNH 4pO 46H 2o), positive rhomboidan structure.The synthetic physical chemistry of struvite MAP precipitation dephosphorization method is the magnesium chloride that adopts price lower, magnesium oxide, ammonium chloride etc., ammonia nitrogen, phosphate radical in waste water are precipitated with the form of struvite, realize the purifying treatment of phosphorus and can be used for fertilizer or phosphoric acid salt manufacture, be regarded as having the dephosphorization technique of prospect.
In the past, sewage work's dephosphorization mainly contain biological process, absorption method and chemical method.Biological process dephosphorization is to utilize certain micro-organisms (as polyP bacteria PAOs) in the time of anaerobism, to discharge phosphorus, and absorbs the organism of the easy degradeds such as lower fatty acid; At aerobic section, excess absorbs phosphorus, and by the discharge of excess sludge, phosphorus is removed.Absorption method is mainly by material adsorption and dephosphorizations such as crystal, filler or filter membranes.Chemical method is obvious to the phosphorus removal effect of lower concentration.The dephosphorization apparatus that sewage work uses based on above method is generally made up of two tank bodies of anaerobic and aerobic or other multiple tank bodies, and its complex structure, floor space is large, input cost is very high, is unfavorable for widespread use.
Utility model content
Problem to be solved in the utility model has been to provide a kind of simple in structure, lower-cost based on the synthetic Turbulent Flow dephosphorization apparatus of MAP.
In order to address the above problem, the utility model provides a kind of and has comprised vertical tank body based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, also comprises inner core; The inside of described vertical tank body is divided into empty chamber, top, fluidization regions, middle part and settling region, bottom from top to bottom successively; Kong Shi top, described top is provided with commissioning pipe and enters waste pipe, and the sidewall of empty chamber, top is provided with water outlet; Described inner core is suspended on Kong Shi top, top and is positioned at fluidization regions, middle part; Sieve formula baffle plate under the inwall of described inner core is provided with and is tilted to, described sieve formula baffle plate is divided into two relative row along the short transverse of inner core, and two row sieve formula baffle plates are crisscross arranged, and described sieve formula baffle plate is provided with at least one through hole; The downside of described inner core is provided with aeration endless tube, and the top of described aeration endless tube is provided with at least one solarization air cap, on described aeration endless tube, is also provided with inlet pipe; The bottom of settling region, described bottom is provided with sewage draining exit.
Further, the angle of described sieve formula baffle plate and vertical direction is 60 °~75 °.
Further, be also provided with interior aeration endless tube in the ring of described aeration endless tube, described interior aeration endless tube is communicated with aeration endless tube, and the top of interior aeration endless tube is provided with at least one production well.
Further, the sidewall of empty chamber, described top tilts and is provided with flow deflector, and described flow deflector is positioned at the below of water outlet.
Further, the top of described inner core is provided with reduction of speed baffle ring.
Further, the sidewall of empty chamber, described top is provided with pH meter.
Further, the bottom of settling region, described bottom is funnel-form, and described sewage outfalls setting is in the central authorities of bottom, settling region, bottom, and described sewage draining exit is provided with graduating valve.
Further, described in, enter waste pipe and be provided with intake pump.
The beneficial effects of the utility model are: feed intake and enter in inner core and mix with phosphorus-containing wastewater, concurrent biochemical reaction precipitates phosphoric generation struvite; Sieve formula baffle plate has greatly been promoted the transmission of phosphorus-containing wastewater, and waste water flows and forms Turbulent Flow with zigzag in inner core, makes to feed intake and fully mixes with phosphorus-containing wastewater, promotes precipitin reaction, has improved the clearance of Phosphorus From Wastewater; Inner core downside aeration not only makes to feed intake and further mixes, reacts more complete with phosphorus-containing wastewater, and adopts stripping CO 2method continues aeration can improve pH value, reduces struvite crystals and forms required time; Meanwhile, aeration also makes to react postprecipitation and water overflows from inner tube wall upside, between inner core and tank body, precipitates, and has realized mixing, precipitin reaction and discrete group and has been combined in same tank body and carries out; Compared with prior art this dephosphorization apparatus is simple in structure, and only a tank body of need can be to waste water dephosphorization, greatly reduces floor space and fabrication cost, is easy to apply.Interior aeration endless tube makes inner core bottom aeration more evenly fully; Flow deflector can prevent that precipitating mixing water enters water outlet; Reduction of speed baffle ring can slowly overflow by the interior mixing water of inner core, and the precipitin reaction time is longer; PH meter can detect the potential of hydrogen of tank interior water body, so that staff regulates potential of hydrogen in time, is beneficial to the generation of struvite precipitation; Funnel shaped bottom can facilitate sedimentary discharge and recycling; Intake pump can make the better convenience of water inlet.
Brief description of the drawings
Fig. 1 is enforcement structural representation of the present utility model;
Fig. 2 be in Fig. 1 A to view;
Mark in figure: the empty chamber 11 of vertical tank body 1, top, fluidization regions, middle part 12, settling region, bottom 13, inner core 2, aeration gas distribution pipe 21, solarization air cap 211, sieve formula baffle plate 22, through hole 221, reduction of speed baffle ring 23, commissioning pipe 3, enter waste pipe 4, intake pump 41, water outlet 5, sewage draining exit 6, graduating valve 61, flow deflector 7 and pH meter 8.
Embodiment
Below in conjunction with accompanying drawing, the utility model is described in further detail.
As shown in Figure 1, 2, a kind ofly comprise vertical tank body 1 based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, also comprise inner core 2; The inside of described vertical tank body 1 is divided into empty chamber 11, top, fluidization regions, middle part 12 and settling region, bottom 13 from top to bottom successively; The top of empty chamber 11, described top is provided with commissioning pipe 3 and enters waste pipe 4, and the sidewall of empty chamber 11, top is provided with water outlet 5; Commissioning pipe 3 and enter the inside that when waste pipe 4 arranges will guarantee feed intake (magnesium source or alkali lye) and sewage to send into inner core 2; Inner core 2 is suspended on the top of empty chamber 11, top and is positioned at fluidization regions 12, middle part, and inner core 2 can be by suspentions such as antiseptic chain or corrosion resistant ropes; Sieve formula baffle plate 22 under the inwall of described inner core 2 is provided with and is tilted to, described sieve formula baffle plate 22 is divided into two relative row along the short transverse of inner core 2, two row sieve formula baffle plates 22 are crisscross arranged, described sieve formula baffle plate 22 is provided with at least one through hole 221, when being installed, sieve formula baffle plate 22 to ensure that neighbouring sieve formula baffle plate 22 is tilted relatively at inner core 2, staggered but non-interference downwards; The downside of described inner core 2 is provided with aeration endless tube 21, and the top of described aeration endless tube 21 is provided with at least one solarization air cap 211, on described aeration endless tube 21, is also provided with inlet pipe 212; Aeration endless tube 21 is annular, and ring footpath is less than inner core external diameter, and aeration endless tube 21 is generally fixed on the downside of inner core 2 by being arranged on the anchor of vertical tank body 1 bottom, and solarization air cap 211 is general more than three and at an upper portion thereof uniform along the annulus of aeration endless tube 21; The bottom of settling region, described bottom 13 is provided with sewage draining exit 6.
When use, by entering waste pipe 4, phosphorus-containing wastewater is added to the inside of inner core 2, by commissioning pipe 3, magnesium source is dropped into the inside of inner core 2 simultaneously, phosphorus-containing wastewater and magnesium source enter inner core 2 and mix; Pressurized gas is entered aeration endless tube 21 and is passed through solarization air cap 211 to the inner aeration of inner core 2 by inlet pipe 212, and phosphorus-containing wastewater is mixed with magnesium source; Phosphorus-containing wastewater flows and forms Turbulent Flow with zigzag on sieve formula baffle plate 22, and phosphorus-containing wastewater further mixes with magnesium source; Ammonia nitrogen in phosphorus-containing wastewater, phosphate radical react raw struvite and precipitate with magnesium source, aeration makes to react postprecipitation mixing water and overflows from inner core 2 wall upsides the fluidization regions, middle part 12 entering between vertical tank body 1 and inner core 2 and precipitate, part struvite is at the inner Direct precipitation of inner core 2, and struvite sinks to settling region, bottom 13 and discharges and reclaim from sewage draining exit 6; The water outlet 5 of water after dephosphorization from 11 sidewalls of empty chamber, top flows out.Generally we adopt seawater, magnesium chloride, magnesium hydroxide or magnesium oxide etc. as magnesium source.The input ratio of magnesium source and sewage is generally by (Mg 2+): (PO 4 3-)=1.3:1 adds, and it is 8.0~10.7 that alkali lye adds the water pH value scope in tank of controlling, optimal ph because of sewage quality different; Adopt if desired stripping CO 2method continues aeration to improve pH value, reduces struvite crystals and forms required time; The cycle that sewage draining exit 6 is got rid of struvite precipitation is generally 3 days/time.
Concrete, in order to make current form good Turbulent Flow to improve dephosphorizing rate, described sieve formula baffle plate 22 is 60 °~75 ° with the angle of vertical direction.
As shown in Figure 2, in order to make the aeration under inner core 2 more even, abundant, be also provided with interior aeration endless tube 213 in the ring of described aeration endless tube 21, described interior aeration endless tube 213 is communicated with aeration endless tube 21, and the top of interior aeration endless tube 213 is provided with at least one production well 2131.
As shown in Figure 1, the sidewall of empty chamber 11, described top tilts and is provided with flow deflector 7, and described flow deflector 7 is positioned at the below of water outlet 5, and flow deflector 7 is for preventing because the precipitation mixing water that aeration overflows from inner core 2 upper walls enters water outlet 5.
From Fig. 1, it can also be seen that, the top of described inner core 2 is provided with reduction of speed baffle ring 23, and reduction of speed baffle ring 23 is for cushioning the precipitation mixing water overflowing because of aeration, and waste water is elongated in the residence time of inner core, makes precipitin reaction more abundant, and phosphor-removing effect is better.
Concrete, the sidewall of empty chamber 11, described top is provided with pH meter 8, and pH meter 8 can detect the potential of hydrogen of tank interior water body, so that staff regulates potential of hydrogen in time, is beneficial to the generation of struvite precipitation.
In order to make throw out better discharge collection, the bottom design funnel-form of settling region, bottom 13, described sewage draining exit 6 is arranged on the central authorities of 13 bottoms, settling region, bottom, as shown in Figure 1; On sewage draining exit 6, be also provided with the graduating valve 61 for controlling sediment discharge.
Concrete, in order to facilitate entering of sewage, enter to be provided with intake pump 41 on waste pipe 4 described.

Claims (8)

1. based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, comprise vertical tank body (1), it is characterized in that: also comprise inner core (2); The inside of described vertical tank body (1) is divided into empty chamber, top (11), fluidization regions, middle part (12) and settling region, bottom (13) from top to bottom successively; The top of empty chamber, described top (11) is provided with commissioning pipe (3) and enters waste pipe (4), and the sidewall of empty chamber, top (11) is provided with water outlet (5); Described inner core (2) is suspended on the top of empty chamber, top (11) and is positioned at fluidization regions, middle part (12); The inwall of described inner core (2) is provided with the sieve formula baffle plate (22) under being tilted to, described sieve formula baffle plate (22) is divided into two relative row along the short transverse of inner core (2), two row sieve formula baffle plates (22) are crisscross arranged, and described sieve formula baffle plate (22) is provided with at least one through hole (221); The downside of described inner core (2) is provided with aeration endless tube (21), the top of described aeration endless tube (21) is provided with at least one solarization air cap (211), is also provided with inlet pipe (212) on described aeration endless tube (21); The bottom of settling region, described bottom (13) is provided with sewage draining exit (6).
2. as claimed in claim 1 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: described sieve formula baffle plate (22) is 60 °~75 ° with the angle of vertical direction.
3. as claimed in claim 1 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: in the ring of described aeration endless tube (21), be also provided with at least one interior aeration endless tube (213), described interior aeration endless tube (213) is communicated with aeration endless tube (21), and the top of interior aeration endless tube (213) is provided with at least one production well (2131).
4. as claimed in claim 1 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: the sidewall of empty chamber, described top (11) tilts and is provided with flow deflector (7), and described flow deflector (7) is positioned at the below of water outlet (5).
5. as claimed in claim 1 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: the top of described inner core (2) is provided with reduction of speed baffle ring (23).
6. as claimed in claim 1 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: the sidewall of empty chamber, described top (11) is provided with pH meter (8).
7. a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP as described in claim 1 to 6 any one, it is characterized in that: the bottom of settling region, described bottom (13) is funnel-form, described sewage draining exit (6) is arranged on the central authorities of bottom, settling region, bottom (13), and described sewage draining exit (6) is provided with graduating valve (61).
8. as claimed in claim 7 a kind of based on the synthetic Turbulent Flow dephosphorization apparatus of MAP, it is characterized in that: described in enter waste pipe (4) and be provided with intake pump (41).
CN201420308195.1U 2014-06-11 2014-06-11 MAP-synthesis-based turbulence-state dephosphorization device Active CN203877954U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201420308195.1U CN203877954U (en) 2014-06-11 2014-06-11 MAP-synthesis-based turbulence-state dephosphorization device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201420308195.1U CN203877954U (en) 2014-06-11 2014-06-11 MAP-synthesis-based turbulence-state dephosphorization device

Publications (1)

Publication Number Publication Date
CN203877954U true CN203877954U (en) 2014-10-15

Family

ID=51678478

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201420308195.1U Active CN203877954U (en) 2014-06-11 2014-06-11 MAP-synthesis-based turbulence-state dephosphorization device

Country Status (1)

Country Link
CN (1) CN203877954U (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106517132A (en) * 2016-12-30 2017-03-22 贵州开磷集团股份有限公司 Device and method for recycling phosphorus and magnesium from phosphorus ore magnesium removal liquid
CN106689019A (en) * 2016-12-19 2017-05-24 苏州格池小绵羊水族用品有限公司 Fish tank circulation filtration separation system
CN108358294A (en) * 2018-05-04 2018-08-03 谢晓进 Livestock and poultry cultivation sewage extracts the equipment and its application method of phosphate fertilizer

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106689019A (en) * 2016-12-19 2017-05-24 苏州格池小绵羊水族用品有限公司 Fish tank circulation filtration separation system
CN106517132A (en) * 2016-12-30 2017-03-22 贵州开磷集团股份有限公司 Device and method for recycling phosphorus and magnesium from phosphorus ore magnesium removal liquid
CN106517132B (en) * 2016-12-30 2019-03-05 贵州开磷集团矿肥有限责任公司 A kind of phosphorus ore de-magging liquid carries out the device and method of phosphorus magnesium recycling
CN108358294A (en) * 2018-05-04 2018-08-03 谢晓进 Livestock and poultry cultivation sewage extracts the equipment and its application method of phosphate fertilizer

Similar Documents

Publication Publication Date Title
EP2540676B1 (en) Continuous flow reactor and method for treating wastewater having high-concentration nitrogen and phosphorus
CN101602535B (en) Phosphor recovery crystallization reactor and phosphor recovery method
KR20120116951A (en) Waste water treatment equipment
CN103880225A (en) Multistage ferric-carbon microelectrolysis coupled Fenton oxidation bed reactor
CN102180560B (en) Device and method for continuously and biologically treating urban sewage
CN201082874Y (en) MAP three-phase fluidizing nitrogen phosphorus reclaiming reactor
CN203877954U (en) MAP-synthesis-based turbulence-state dephosphorization device
CN103626295B (en) Sewage disposal device and processing method
CN105060613A (en) High-nitrogen and high-phosphorus pharmaceutical wastewater treatment system
KR20020005521A (en) Process and system for wastewater treatment using struvite(MAP)
CN110482801A (en) Integrated wastewater biological simultaneous denitrification calcium-removing device and its method
CN203877952U (en) Reflux type dephosphorization device based on MAP synthesis
CN103193370A (en) Phosphorus recovery device for excess sludge
CN102381817B (en) System for processing waste water generated in acrylamide production and processing method thereof
CN203877951U (en) MAP-synthesis-based packed phosphorus removal device
CN204022616U (en) Integral type denitrification of autotrophic organism works in coordination with chemical dephosphorizing reactor
CN103214146B (en) Biological-physicochemical combined process for controlling N2O discharge in sewage treatment process
KR20120100083A (en) Phosphorus recovery apparatus and method thereof
CN106277314B (en) A kind of biochemistry denitrogenation dephosphorizing sewage disposal system and method
CN107540148B (en) Wastewater treatment system and wastewater treatment method for preparing ethanol from cellulose
CN109052833A (en) A kind of recycled water process units
CN108751572A (en) A kind of wastewater treatment equipment and method of intensified denitrification and dephosphorization
CN204550198U (en) A kind of SBR equipment realizing mud rapid subsidence
CN204058056U (en) A kind of Continuous Flow permanent water level SBR waste disposal plant
CN103588355A (en) Device for removing high-concentration ammonia nitrogen in waste water

Legal Events

Date Code Title Description
C14 Grant of patent or utility model
GR01 Patent grant