CN103304022B - Sewage treatment device containing magnetic carrier and sewage treatment method - Google Patents

Sewage treatment device containing magnetic carrier and sewage treatment method Download PDF

Info

Publication number
CN103304022B
CN103304022B CN201310287921.6A CN201310287921A CN103304022B CN 103304022 B CN103304022 B CN 103304022B CN 201310287921 A CN201310287921 A CN 201310287921A CN 103304022 B CN103304022 B CN 103304022B
Authority
CN
China
Prior art keywords
reactor
magnetic carrier
magnetic
water
sewage treatment
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
CN201310287921.6A
Other languages
Chinese (zh)
Other versions
CN103304022A (en
Inventor
袁振宏
孙永明
李连华
孔晓英
甄峰
李颖
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.)
Guangzhou Institute of Energy Conversion of CAS
Original Assignee
Guangzhou Institute of Energy Conversion of CAS
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 Guangzhou Institute of Energy Conversion of CAS filed Critical Guangzhou Institute of Energy Conversion of CAS
Priority to CN201310287921.6A priority Critical patent/CN103304022B/en
Publication of CN103304022A publication Critical patent/CN103304022A/en
Application granted granted Critical
Publication of CN103304022B publication Critical patent/CN103304022B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The invention discloses a sewage treatment device containing a magnetic carrier and a sewage treatment method. The sewage treatment device comprises a reactor which is internally provided with a magnetic carrier, wherein the reactor is provided with a water inlet and a water outlet; the reactor is internally provided with at least one hollow separation plate; a reaction region is formed between the separation plates, and a reaction region is formed between the separation plates and the side wall of the reactor; each separation plate is internally provided with a magnetic coil which is electrified with the outside; the separation plates are arrayed in a staggered manner; the adjacent separation plates are respectively staggered with the bottom and the top of the reactor to form a water flow channel; the electrification sequence of the magnetic coil is changed so that the magnetic carrier has the states that the magnetic carrier in the water flow channel is consistent to the flow direction of sewage and is opposite to the flow direction of the sewage. The sewage treatment device is different from a conventional sewage treatment reactor containing the magnetic carrier; the magnetic carrier in the reactor is at a circulating flowing state so that subsequent magnetic seed separation is not needed, the fixed cost investment is reduced, and a technical process is simplified.

Description

A kind of waste disposal plant and method containing magnetic carrier
Technical field
The present invention relates to a kind of sewage disposal device and method, especially relate to the sewage that the solids content such as natural pond liquid is lower after sanitary sewage, organic sewage and solid-liquid separation.
Background technology
Pollutant component in sewage is complicated, is main greatly mainly with organic pollutant.Process for treating industrial waste water domestic at present mainly contains chemical method and biological treatment.Chemical method carries out the effect such as electrostatic neutralization, adsorption bridging by coagulating agent, inhibiter, Scale inhibitors, sterilant etc. to colloidal particle makes colloidal particle de-steady, in order to remove suspended substance in sewage and solubility organic pollutant.Depart from from water because organic pollutant is just condensed into bulk, organism itself is not effectively degraded, and causes a large amount of mud flco, make running cost high and produce secondary pollution; Biological treatment utilizes the biochemical action of microorganism, by the organic matter degradation of complexity, conversion, decontamination effect improving is higher than chemical method, avoid secondary pollution simultaneously, it is the most economical effective means of sewage disposal, and biological process is divided into the large class of activated sludge process and biomembrance process two, Activated Sludge Process is ripe, operational management is convenient, application is comparatively extensive, China have an appointment 40% municipal sewage plant adopt Activated Sludge Process.But greatly, easily there is sludge bulking, not high to sewage denitrification and dephosphorization processing efficiency in activated sludge process structures floor space.The immobilized microorganism technique being devoted to improve saprobia method processing efficiency in recent years obtains rapid progress, thus biomembrane process becomes the main flow direction of following biological sewage treatment development, representational bio membrane process has BAF, contact oxidation technology, blodisc and biological fluidized bed, wherein organism fluidization bed process is to solve BAF and contact oxidation technology pond body blockage problem and the New biological membrane method technique developed, it is by sand, gac, polymer carriers etc. are filled in reactor, at filling surface apposition growth microbial film, along with drainage flow or aeration make filler in reactor fluidisation, microbial film on filler contacts with dirty water pollutant and makes contaminant degradation.
Biochemical reactor at present for sewage disposal has anaerobic filter (AF), up-flow anaerobic sludge blanket (UASB), anaerobism floats film expanded bed reactor (AAFEB), anaerobic fluidized bed (AFB), anaerobe rotating disk (ARBCP), expanded granular sludge bed (EGSB), anaerobic internal circulation reactor (IC), anaerobic sequencing batch batch reactor (ASBR), anaerobic baffled reactor (ABR), upflowing segmentation sludge bed reactor (USSB), upflow sludge blanket-strainer reactor (UBF), anaerobic migrating blanket reactor (AMBR), anaerobic membrane bioreactor (AnMBR) etc.These reactors all also exist active sludge skewness in reactor, and need complicated triphase separator or the membrane module of costliness.Magnetic separation technique is a kind of technology of material being carried out magnetic field treatment, utilizes the difference of element or component magnetic susceptibility, by foreign field, material is carried out magnetic field treatment, thus reaches a kind of emerging technology of idetified separation process, belongs to physical partition method.Mainly utilizing magnetic----stress effect, applies magnetic field to waste water, makes the magnetic-particle in waste water magnetize, condense, and forms the flocs unit being easy to be separated, directly separates; For non-magnetic particle, carrying out chemical flocculation by adding magnetic kind, generating magnetic flocs unit thus being separated.Magneto separate water technology have investment little, treatment effect good, take up an area the advantages such as little.
Publication number be 102249404A patent discloses a kind of sewage disposal device containing magnetic carrier and sewage water treatment method, wherein said sewage disposal device comprises biochemical reaction tank, magnetic separator for separating of mud and magneticsubstance, device for dehydrating sladge waste and demoulding equipment.Independent magnetic separating apparatus is needed in this patent.
Publication number be 102070231A patent discloses a kind of combined type wastewater treatment method and device, wherein saidly in sewage, add magnetic kind, coagulating agent, coagulant aids carry out coagulating, now form magnetic flco group in water, by magnetic separation technique, magnetic flco group is separated from water again, now water body has purified up to standard, and isolated magnetic flco group is by the organic pollutant in electrochemical oxidation reactions brute force degraded flco group, its burning conversion is made to be water and carbonic acid gas, kill bacteria.Magnetic kind and nontoxic silt sediment are only contained after electrochemical treatment in magnetic flco group, then reclaim magnetic kind through calutron, continue recycle, and remaining nontoxic mud Direct Dehydration.Physico-chemical process is mainly adopted to carry out sewage disposal in this patent.
Publication number is 1204625 patent discloses a kind of microorganisms-immobilized magnetic carriers and produce the method for this magnetic carrier, and wherein relate in embodiment 9 and arrange dividing plate in reactor, magnetic carrier is adsorbed on permanent magnet, and they is maintained.Carrier in this embodiment is in be fixed but not flowable state.
Summary of the invention
The object of this patent there is active sludge skewness in current sewage-treating reactor, and need the problems such as the membrane module of complicated triphase separator or costliness, a kind of waste disposal plant based on magnetic carrier and method are provided, by making magnetic carrier at reactor internal circulation flow, magnetic carrier can be made fully to contact with sewage on the one hand, avoid follow-up magnetic kind to be in addition separated, be of value to the whole efficiency improving reactor.
For realizing above object, this invention takes following technical scheme: a kind of waste disposal plant containing magnetic carrier, the reactor of magnetic carrier is established in including, reactor is provided with water-in and water outlet, the dividing plate of at least one hollow is established in reactor, forming reactions district between dividing plate and between dividing plate and sidewall of reactor, the built-in magnetic coil that can be energized with the external world of dividing plate, described dividing plate is staggered, the formation water stream channel staggered between the bottom of described adjacent separator respectively and in reactor and top, by changing the order of magnetic coil energising, described magnetic carrier have in this water stream channel with effluent stream to consistent and with effluent stream to contrary state.
Described magnetic carrier is tool one or more materials magnetic.The adsorbable microorganism of described magnetic carrier.
A sewage water treatment method containing magnetic carrier, comprises the steps:
Step one: sewage enters in reactor from water-in, mix with magnetic carrier in reactor, first successively magnetic coil is energized along from water-in to the direction of water outlet, make magnetic carrier consistent with the direction of drainage flow, by making magnetic coil be energized successively, magnetic carrier is made to be fluidization;
Step 2: when magnetic carrier to move to the water outlet of reactor with drainage flow, change the power-up sequence of magnetic coil, make its direction that is energized be changed to water-in by water outlet, make the travel direction of magnetic carrier and effluent stream to for reverse, reciprocal with this.
The present invention compared with prior art, tool has the following advantages: the present invention is different from the conventional sewage-treating reactor containing magnetic carrier, because magnetic carrier in this patent is that cycling stream is dynamic at reactor, is separated without the need to follow-up magnetic kind, reduce fixed cost investment, and simplify technological process.
Accompanying drawing explanation
Fig. 1 is apparatus of the present invention structural representation.
Embodiment
Below in conjunction with the drawings and specific embodiments, content of the present invention is described in further details.
Embodiment:
Refer to described in Fig. 1, a kind of waste disposal plant containing magnetic carrier, the reactor 6 of magnetic carrier 7 is established in including, reactor 6 is provided with water-in 61, water outlet 62, air outlet 63 and inlet mouth 64, the dividing plate of at least one hollow is established in reactor 6, forming reactions district between dividing plate and between dividing plate and reactor 6 sidewall, the built-in magnetic coil that can be energized with the external world of dividing plate, described dividing plate is staggered, the formation water stream channel staggered between the bottom of described adjacent separator respectively and in reactor 6 and top, by changing the order of magnetic coil energising, magnetic carrier 7 have in this water stream channel with effluent stream to consistent and with effluent stream to contrary state.
The present embodiment illustrates to be provided with four pieces of dividing plates, refers to shown in Fig. 1.Natural pond liquid after solid-liquid separation enters in reactor 6 after feed system, mix in reactor 6 with magnetic carrier 7, meanwhile, magnetic coil 8 in reactor 6 in the first dividing plate 11 of water-in 61 is energized, produce magnetic field, magnetic carrier is made to be gathered in the first reaction zone 1, after natural pond liquid flows through magneticsubstance, magnetic coil 8 in second partition 21 is energized, magnetic coil 8 is wherein made to produce magnetic field, and stop being energized to the magnetic coil 8 in the first dividing plate 11, on this basis, magnetic carrier in first reaction zone 1 is moved to second reaction zone 2 under the influence of a magnetic field, make magnetic carrier consistent with the direction of the flowing of sewage along reactor 6 when magnetic field changes with this, when magnetic carrier flow to water outlet 62, magnetic coil 8 in 3rd dividing plate 31 is energized, coil is wherein made to produce magnetic field, and stop being energized to the magnetic coil 8 in the 4th dividing plate 41, on this basis, magnetic carrier in 5th reactor zone 5 is moved to the 4th reaction zone 4 under the influence of a magnetic field, with this, the side of magnetic carrier 7 when magnetic field changes along the flowing with sewage is moved in the opposite direction, magnetic carrier 7 is made to be back to water-in 61, thus magnetic carrier 7 is moved at reactor 6 internal recycle.
Above-listed detailed description is illustrating for possible embodiments of the present invention, and this embodiment is also not used to limit the scope of the claims of the present invention, and the equivalence that all the present invention of disengaging do is implemented or changed, and all should be contained in the scope of the claims of this case.

Claims (2)

1. the waste disposal plant containing magnetic carrier, the reactor (6) of magnetic carrier (7) is established in including, reactor (6) is provided with water-in (61) and water outlet (62), it is characterized in that: the dividing plate establishing at least one hollow in reactor (6), forming reactions district between dividing plate and between dividing plate and reactor (6) sidewall, the built-in magnetic coil that can be energized with the external world of dividing plate, described dividing plate is staggered, the formation water stream channel staggered between the bottom of adjacent separator respectively and in reactor (6) and top, by changing the order of magnetic coil energising, described magnetic carrier (7) have in this water stream channel with effluent stream to consistent and with effluent stream to contrary state.
2. utilize a sewage water treatment method for the waste disposal plant containing magnetic carrier as claimed in claim 1, be characterised in that, comprise the steps:
Step one: sewage enters in reactor from water-in, mix with magnetic carrier in reactor, first successively magnetic coil is energized along from water-in to the direction of water outlet, make magnetic carrier consistent with the direction of drainage flow, by making magnetic coil be energized successively, magnetic carrier is made to be fluidization;
Step 2: when magnetic carrier to move to the water outlet of reactor with drainage flow, change the power-up sequence of magnetic coil, make its direction that is energized be changed to water-in by water outlet, make the travel direction of magnetic carrier and effluent stream to for reverse, reciprocal with this.
CN201310287921.6A 2013-07-09 2013-07-09 Sewage treatment device containing magnetic carrier and sewage treatment method Active CN103304022B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310287921.6A CN103304022B (en) 2013-07-09 2013-07-09 Sewage treatment device containing magnetic carrier and sewage treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310287921.6A CN103304022B (en) 2013-07-09 2013-07-09 Sewage treatment device containing magnetic carrier and sewage treatment method

Publications (2)

Publication Number Publication Date
CN103304022A CN103304022A (en) 2013-09-18
CN103304022B true CN103304022B (en) 2015-03-04

Family

ID=49129787

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310287921.6A Active CN103304022B (en) 2013-07-09 2013-07-09 Sewage treatment device containing magnetic carrier and sewage treatment method

Country Status (1)

Country Link
CN (1) CN103304022B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105948262A (en) * 2016-07-18 2016-09-21 江超 Water treatment technology and operation method thereof
CN105967322A (en) * 2016-07-18 2016-09-28 胡勇飞 Immobilized microbial ball used in sewage treatment plant and operating method thereof
CN111981895B (en) * 2020-08-07 2021-11-23 常州工学院 Heat exchange equipment and pipeline scale prevention and removal device and method for heat exchange equipment

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003010880A (en) * 2001-06-29 2003-01-14 Yoshihiro Kodama Reduction of generation amount of sludge and commercialization method of the same
CN2612665Y (en) * 2003-04-18 2004-04-21 宜兴市东方水设备有限公司 Water treatment equipment by electrochemical flocculating coal
JP2007125504A (en) * 2005-11-04 2007-05-24 Takao Ejiri Filtering method and filtration apparatus
CN201873559U (en) * 2010-10-12 2011-06-22 李泽 Chain-type sewage treatment unit
CN102249404A (en) * 2010-05-17 2011-11-23 宜兴中北科大环境科技有限公司 Magnetic carrier containing sewage treatment device and sewage treatment method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003010880A (en) * 2001-06-29 2003-01-14 Yoshihiro Kodama Reduction of generation amount of sludge and commercialization method of the same
CN2612665Y (en) * 2003-04-18 2004-04-21 宜兴市东方水设备有限公司 Water treatment equipment by electrochemical flocculating coal
JP2007125504A (en) * 2005-11-04 2007-05-24 Takao Ejiri Filtering method and filtration apparatus
CN102249404A (en) * 2010-05-17 2011-11-23 宜兴中北科大环境科技有限公司 Magnetic carrier containing sewage treatment device and sewage treatment method
CN201873559U (en) * 2010-10-12 2011-06-22 李泽 Chain-type sewage treatment unit

Also Published As

Publication number Publication date
CN103304022A (en) 2013-09-18

Similar Documents

Publication Publication Date Title
Hahn et al. Pilot scale application of anaerobic baffled reactor for biologically enhanced primary treatment of raw municipal wastewater
CN203461878U (en) Aerobic granular sludge internal circulation reactor
CN102616930B (en) Methane air floating anaerobic reactor
CN101698555A (en) Integrated up-flow reactor and advanced treatment method of fermentation industrial effluent
CN205773937U (en) A kind of ozone occurs and processing means
CN105565581B (en) Coal ethylene wastewater integrated conduct method
JP2008029993A (en) Methane fermenter
CN104529092A (en) Acrylic fiber waste water treatment system
CN108409024A (en) A kind of biological adsorption strengthens Magneto separate sewage carbon source concentration recycling system and method
CN102923916A (en) Chemical pharmaceutical wastewater treatment system
CN103304022B (en) Sewage treatment device containing magnetic carrier and sewage treatment method
Shen et al. Progress of anaerobic membrane bioreactor in municipal wastewater treatment
CN203256030U (en) Anaerobic bioreactor for enhancing wastewater treatment
KR101167488B1 (en) Simultaneous eliminating system of phosphorous and nitrogen in wastewater
CN107032493A (en) Pharmacy wastewater treatment method and processing system
CN204162505U (en) A kind of built-in zero-valent iron anaerobic reactor
CN103332833A (en) Anaerobic granular sludge expanded bed-gravity flow membrane filter sewage treatment system and method utilizing same to treat sewage
Biniaz et al. Wastewater treatment: employing biomass
CN207210064U (en) Internal-circulation type biofilter anaerobic reactor
CN107473514A (en) A kind of domestic landfill leachate treatment system and technique
CN108946939A (en) A kind of distributed domestic sewage treatment equipment and its technique
McCarty et al. Anaerobic fluidized bed membrane bioreactors for the treatment of domestic wastewater
CN101618907A (en) Self-cleaning biological filter and self-cleaning technology of filter
CN203382611U (en) Treatment device for wastewater from production of purified terephthalic acid
CN201495154U (en) Biological wastewater treatment system combining biological fluidized bed with biological filter bed

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant