CN106045208A - Domestic sewage treatment method - Google Patents

Domestic sewage treatment method Download PDF

Info

Publication number
CN106045208A
CN106045208A CN201610552228.0A CN201610552228A CN106045208A CN 106045208 A CN106045208 A CN 106045208A CN 201610552228 A CN201610552228 A CN 201610552228A CN 106045208 A CN106045208 A CN 106045208A
Authority
CN
China
Prior art keywords
domestic sewage
processing method
time
sewage processing
adsorption
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.)
Pending
Application number
CN201610552228.0A
Other languages
Chinese (zh)
Inventor
不公告发明人
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.)
Foshan Jiezhi Information Technology Co Ltd
Original Assignee
Foshan Jiezhi Information Technology 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 Foshan Jiezhi Information Technology Co Ltd filed Critical Foshan Jiezhi Information Technology Co Ltd
Priority to CN201610552228.0A priority Critical patent/CN106045208A/en
Publication of CN106045208A publication Critical patent/CN106045208A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

The invention provides a domestic sewage treatment method, and belongs to the field of sewage treatment. The method comprises the steps of mesh filtration; precipitating adjustment, wherein a phosphorus removing agent is adopted; biochemical treatment, wherein sewage treatment is conducted through active sludge, an intermittent electrostatic field is set, and after the active sludge is pretreated by ultrasonic waves, tourmaline powder is added into the active sludge; precipitating adsorption, wherein porous adsorption filler is adopted as an adsorption material; wet land treatment. According to the method, the activity of microorganisms can be greatly activated, the adaptive capacity of the microorganisms to the electric field is improved, the sewage treatment time is shortened, reproduction of the microorganisms can be accelerated, the utilization rate of the active sludge is increased, and water body purification is promoted.

Description

One way of life sewage water treatment method
Technical field
The present invention relates to sewage treatment area, be specifically related to one way of life sewage water treatment method.
Background technology
China's water resource lacks, and occupancy volume per person is little.In domestic water, content of material is complicated, if do not carried out processing directly row Put to environment, it will polluted underground water, have a strong impact on human health and ecological environment.
Also wideling popularize and develop sewage disposal both at home and abroad at present, sanitary sewage comparison of ingredients is fixed, the Organic substance contained More, biodegradability is strong, is relatively suitable for the growth of antibacterial, and therefore the processing method major part of sanitary sewage is biochemical treatment.Quiet Electric treatment technology is the important technology during water processes, and utilizes electric field to act on the microorganism in water so that it is biology effect occurs Should, improve the activity of microorganism, but mainly with in the process of biomembranous water.
It is strong that Publication No. CN102249409B Chinese invention patent discloses a kind of anaerobism sewage disposal utilizing solar energy Gasifying device and method, the method utilizes solar energy to be converted into electric energy, act on anaerobism occur wherein, make sewage generation microorganism- Micro-electrolysis reaction, remove hard-degraded substance.Publication number CN103482773 B discloses the dephosphorization medicine of a kind of domestic sewage in rural areas Agent and method thereof, containing polyP bacteria in this Dephosphorization reagent, and be provided with positive-negative electrode plate in preliminary sedimentation tank, utilize solar powered. After both reaction principles are for adding extra electric field by battery lead plate, being affected by external electric field, the zwitterion produced in reaction can accelerate Move to specific pole plate direction, fundamentally add substrate mass-transfer efficiency.In microorganism-micro-electrolysis reaction, ion can be Under the influence of external electric field, motion formation local concentration is poor, and reaction can generate more polyion by degradation of organic substances, reaches dynamic equilibrium, accelerates W-response process.But activated sludge has certain applicable time to electric field, extends the process time, adds energy consumption, Fertility in microorganism is reduced simultaneously, reduces the recycling rate of waterused to activated sludge.
Summary of the invention
The present invention is to solve drawbacks described above, it is provided that a kind of shortening sewage disposal time, improve activated sludge utilization rate Domestic sewage processing method with wastewater purification efficiency.
To achieve these goals, the present invention is achieved through the following technical solutions:
One way of life sewage water treatment method, including sanitary sewage being carried out grid filtration, precipitation regulation, biochemical treatment, heavy Form sediment absorption and wetland variation, uses dephosphorization agent in the regulation of described precipitation, and described biochemical treatment includes intermittent static electric field process, Pretreated activated sludge is utilized to carry out sewage disposal;Described precipitation adsorption uses adsorption stuffing;In described biochemical treatment Activated sludge carries out pretreatment.
Further, described dephosphorization agent includes dephosphorization bacterial in being;
Further, described dephosphorization bacterial is amphimicrobian type Denitrifying Phosphate Accumulating Organisms;
Further, being provided with biochemical reactor in described biochemical treatment, the water inlet of biochemical reactor is provided with negative plate, goes out The mouth of a river is provided with negative plate;
Further, the voltage in described biochemical reactor is set to 50-60kV, described electric field E=4.5x103- 5.0x103V/m, the described intermittent static electric field process time is 48-72h, and wherein the static electric field process time is 1-2h every time, intermittently Time is 30-60min.
Further, the pretreatment of described activated sludge is: after activated sludge is utilized ultrasonic Treatment 30-60min, then Add the tourmaline powder of the 10-20% of activated sludge weight.
Further, described biochemical treatment uses after static electric field process intermittent aeration, at described intermittent aeration The reason time is 2-5 days, and wherein aeration time is 4-6h every time, and interval time is 2-3h.
Further, described adsorption stuffing is the weight portion of following components:
Activated carbon 30-50 part, Maifanitum 50-60 part, montmorillonite 30-40 part, acrylic acid 20-30 part, acrylamide 20-30 Part.
Further, described activated carbon, the particle diameter of Maifanitum and montmorillonite is 8-10 centimetre, described activated carbon, Maifanitum Being porous with the inside of montmorillonite, percent opening is 45%-60%.
Further, the preparation method of described adsorption stuffing is: weighs each raw material of weight portion, is placed in reactor, if Put temperature and be 60-80 DEG C, stirring reaction 1-2h.
The principle of the invention is: after utilizing grid to remove the solid refuse in sanitary sewage, uses and hold concurrently in precipitation regulation Property anaerobic type Denitrifying Phosphate Accumulating Organisms carries out dephosphorization to sewage.Owing to activated sludge has certain adaptability to electric field, therefore exist Early stage electric field is inconspicuous to the effect of microorganism, causes viability to reduce.Activated sludge carries out pretreatment, uses ultrasound wave to enter Row section time-triggered protocol, it is possible to significantly activate the activity of microorganism, improve the microorganism adaptation ability to electric field simultaneously, shorten sewage The process time.Activated sludge after the pre-treatment adds tourmaline powder, it is possible to stimulate the enzymatic activity in microbial body, accelerate micro- Biological metabolism, while raising microorganism is to organic decomposition, moreover it is possible to accelerate the breeding of microorganism, improves activity The utilization rate of mud;The adsorption stuffing used in precipitation adsorption is modified activated carbon and mineral, activated carbon, Maifanitum and Meng Tuo Stone is loose structure, has adsorption, and employing acrylic acid and acrylamide are as monomer, with activated carbon, Maifanitum and illiteracy De-stone mixing, carries out graft polymerization modification, makes the surface of activated carbon, Maifanitum and montmorillonite can form cationic on surface Positive charge, can form again anionic negative charge, accelerates the precipitation of colloidal particle in sewage, promotes the purification of water body.
Domestic sewage processing method of the present invention, it has the beneficial effects that:
1, activated sludge carries out pretreatment, uses the ultrasound wave section of carrying out time-triggered protocol, it is possible to significantly activate the work of microorganism Property, improve the microorganism adaptation ability to electric field simultaneously, shorten the sewage disposal time.
2, pretreated activated sludge adds tourmaline powder, it is possible to stimulate the enzymatic activity in microbial body, accelerate micro- Biological metabolism, while raising microorganism is to organic decomposition, moreover it is possible to accelerate the breeding of microorganism, improves activity The utilization rate of mud.
3, adsorption stuffing is modified activated carbon and Maifanitum and montmorillonite, for loose structure, has adsorption, it is possible to carry High water body purification, carries out graft polymerization modification on surface, accelerates the precipitation of colloidal particle in sewage, promotes the purification of water body.
Detailed description of the invention
Below in conjunction with embodiment and detailed description of the invention, the present invention is described in further detail.But this should not understood Scope for the above-mentioned theme of the present invention is only limitted to below example, and all technology realized based on present invention belong to this The scope of invention.
Embodiment 1
One way of life sewage water treatment method, its method step includes:
(1) being collected by sanitary sewage, use multi grid to filter solid matter, the sewage after filtration enters precipitation Pond;
(2) in sedimentation tank, being adjusted the pH value of sewage by acid-base modifier, regulation pH value is 6, adds and removes After phosphorus agent is sufficiently mixed, keep reaction 10h;
(3) activated sludge carries out pretreatment, after activated sludge is utilized ultrasonic Treatment 60min, adds activated sludge After the tourmaline powder of the 20% of weight is sufficiently mixed, it is seeded in biochemical reactor;Sewage reacted in sedimentation tank is passed through Advection enters in biochemical reactor, and the water inlet of biochemical reactor is provided with negative plate, and outlet is provided with negative plate, uses solar energy Or commercial power provides power supply, concurrently setting voltage is that voltage is set to 60kV, electric field E=4.5x103V/m, circular treatment 72h, wherein the static electric field process time is 2h every time, and the intermittent time is 60min, takes at intermittent aeration after static electric field process Managing 5 days, wherein aeration time is 6h every time, and interval time is 2h;
(4), after after processing in step (3), upper water settles in entering one-level Sedimentation tank, upper water advection enters sedimentation In adsorption tank, containing adsorption stuffing in sedimentation adsorption tank, after upper water stops 10h in adsorption stuffing, it is directly discharged into Manual moist In ground, can be directly discharged in environment after processing.
Wherein adsorption stuffing is the weight portion of following components: activated carbon 50 parts, Maifanitum 60 parts, montmorillonite 30 parts, propylene Acid 30 parts, acrylamide 30 parts, preparation method is: weighs each raw material of weight portion, is placed in reactor, and arranging temperature is 80 DEG C, stirring reaction 1h.
Embodiment 2
One way of life sewage water treatment method, its method step includes:
(1) being collected by sanitary sewage, use multi grid to filter solid matter, the sewage after filtration enters precipitation Pond;
(2) in sedimentation tank, being adjusted the pH value of sewage by acid-base modifier, regulation pH value is 7, adds and removes After phosphorus agent is sufficiently mixed, keep reaction 8h;
(3) activated sludge carries out pretreatment, after activated sludge is utilized ultrasonic Treatment 40min, adds activated sludge After the tourmaline powder of the 15% of weight is sufficiently mixed, it is seeded in biochemical reactor;Sewage reacted in sedimentation tank is passed through Advection enters in biochemical reactor, and the water inlet of biochemical reactor is provided with negative plate, and outlet is provided with negative plate, uses solar energy Or commercial power provides power supply, concurrently setting voltage is that voltage is set to 60kV, electric field E=5.0x103V/m, circular treatment 48h, wherein the static electric field process time is 1h every time, and the intermittent time is 30min;Intermittent aeration 3 is taked after static electric field process My god, each aeration time is 4h, and interval time is 3h;
(4), after after processing in step (3), upper water settles in entering one-level Sedimentation tank, upper water advection enters sedimentation In adsorption tank, containing adsorption stuffing in sedimentation adsorption tank, after upper water stops 6h in adsorption stuffing, it is directly discharged into artificial swamp In, can be directly discharged in environment after processing.
Wherein adsorption stuffing is the weight portion of following components: activated carbon 30 parts, Maifanitum 50 parts, montmorillonite 40 parts, propylene Acid 25 parts, acrylamide 25 parts, preparation method is: weighs each raw material of weight portion, is placed in reactor, and arranging temperature is 60 DEG C, stirring reaction 2h.
Embodiment 3
One way of life sewage water treatment method, its method step includes:
(1) being collected by sanitary sewage, use multi grid to filter solid matter, the sewage after filtration enters precipitation Pond;
(2) in sedimentation tank, being adjusted the pH value of sewage by acid-base modifier, regulation pH value is 7.5, adds After dephosphorization agent is sufficiently mixed, keep reaction 6h;
(3) activated sludge carries out pretreatment, after activated sludge is utilized ultrasonic Treatment 30min, adds activated sludge After the tourmaline powder of the 10% of weight is sufficiently mixed, it is seeded in biochemical reactor;Sewage reacted in sedimentation tank is passed through Advection enters in biochemical reactor, and the water inlet of biochemical reactor is provided with negative plate, and outlet is provided with negative plate, uses solar energy Or commercial power provides power supply, concurrently setting voltage is that voltage is set to 50kV, electric field E=5.0x103V/m, circular treatment 60h, wherein the static electric field process time is 1h every time, and the intermittent time is 30min;Intermittent aeration 2 is taked after static electric field process My god, each aeration time is 6h, and interval time is 3h;
(4), after after processing in step (3), upper water settles in entering one-level Sedimentation tank, upper water advection enters sedimentation In adsorption tank, containing adsorption stuffing in sedimentation adsorption tank, after upper water stops 8h in adsorption stuffing, it is directly discharged into artificial swamp In, can be directly discharged in environment after processing.
Wherein adsorption stuffing is the weight portion of following components: activated carbon 40 parts, Maifanitum 55 parts, montmorillonite 35 parts, propylene Acid 20 parts, acrylamide 20 parts, preparation method is: weighs each raw material of weight portion, is placed in reactor, and arranging temperature is 70 DEG C, stirring reaction 1.5h.
Following table is the assay of domestic sewage processing method of the present invention, and indices is as follows: (condition: 10m3Life dirt Water, 25 DEG C, 2 time-of-weeks)
Project Index
CODCr(mg/L) 25
BOD5(mg/L) 7.3
SS(mg/L) 5
PH 6-9
Colourity (is spent) 50
Time LVFS 30%
Mud utilization rate >= 95%
As can be seen from the above embodiments, the effluent quality in the inventive method significantly improves, and the contracting of sewage disposal time Short by 30%, and mud utilization rate is also greatly improved, and reduces energy consumption, promotes and recycle.

Claims (10)

1. one way of life sewage water treatment method, it is characterised in that: sanitary sewage is included that grid filters, precipitation regulation, raw Change processes, precipitation adsorption and wetland variation, uses dephosphorization agent in the regulation of described precipitation, and described biochemical treatment includes intermittent electrostatic Field processes, and utilizes the activated sludge of pretreatment to carry out sewage disposal;Described precipitation adsorption uses adsorption stuffing.
Domestic sewage processing method the most according to claim 1, it is characterised in that: described dephosphorization agent includes dephosphorization in being Bacterium.
Domestic sewage processing method the most according to claim 2, it is characterised in that: described dephosphorization bacterial is that amphimicrobian type is anti- Nitrification polyP bacteria.
Domestic sewage processing method the most according to claim 1, it is characterised in that: described biochemical treatment is provided with biochemical anti- Answering device, the water inlet of biochemical reactor is provided with negative plate, and outlet is provided with negative plate.
Domestic sewage processing method the most according to claim 1, it is characterised in that: the intermittence in described biochemical reactor In electrostatic field, voltage is set to 50-60kV, described electric field E=4.5x103-5.0x103V/m, during described intermittent static electric field process Between be 48-72h, wherein every time the static electric field process time is 1-2h, and the intermittent time is 30-60min.
Domestic sewage processing method the most according to claim 1, it is characterised in that: the pretreatment of described activated sludge is: After activated sludge is utilized ultrasonic Treatment 30-60min, add the tourmaline powder of the 10-20% of activated sludge weight.
Domestic sewage processing method the most according to claim 1, it is characterised in that: in described biochemical treatment at electrostatic field Using intermittent aeration after reason, the described intermittent aeration process time is 2-5 days, and wherein aeration time is 4-6h every time, interval Time is 2-3h.
Domestic sewage processing method the most according to claim 1, it is characterised in that: described adsorption stuffing is following components Weight portion:
Activated carbon 30-50 part, Maifanitum 50-60 part, montmorillonite 30-40 part, acrylic acid 20-30 part, acrylamide 20-30 part.
Domestic sewage processing method the most according to claim 8, it is characterised in that: described activated carbon, Maifanitum and Meng Tuo The particle diameter of stone is 8-10 centimetre, described activated carbon, and the inside of Maifanitum and montmorillonite is porous.
Domestic sewage processing method the most according to claim 8, it is characterised in that: the preparation method of described adsorption stuffing For: weighing the activated carbon of weight portion, Maifanitum, montmorillonite, acrylic acid and acrylamide, be placed in reactor, arranging temperature is 60-80 DEG C, stirring reaction 1-2h.
CN201610552228.0A 2016-07-12 2016-07-12 Domestic sewage treatment method Pending CN106045208A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610552228.0A CN106045208A (en) 2016-07-12 2016-07-12 Domestic sewage treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610552228.0A CN106045208A (en) 2016-07-12 2016-07-12 Domestic sewage treatment method

Publications (1)

Publication Number Publication Date
CN106045208A true CN106045208A (en) 2016-10-26

Family

ID=57186379

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610552228.0A Pending CN106045208A (en) 2016-07-12 2016-07-12 Domestic sewage treatment method

Country Status (1)

Country Link
CN (1) CN106045208A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106746354A (en) * 2017-01-22 2017-05-31 浙江阿凡柯达环保科技有限公司 A kind of sewage in-situ processes integrated equipment
CN108996848A (en) * 2018-09-06 2018-12-14 杨镒玮 A kind of sewage-treatment plant and method
CN111603838A (en) * 2019-02-25 2020-09-01 冀勃睿 Domestic sewage physical method processing apparatus with deodorant function
CN112079532A (en) * 2020-09-17 2020-12-15 苏州科技大学 Urban sewage treatment process for recovering organic matters and phosphorus
CN113060830A (en) * 2021-04-11 2021-07-02 郑州大学 Method for accelerating aerobic sludge granulation by using tourmaline as crystal nucleus

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20040091463A (en) * 2003-04-22 2004-10-28 백순기 sewage and waste water treating system by ceramics and method for purifying sewage and waste water using the same
CN1669956A (en) * 2004-03-18 2005-09-21 昆明柯利欣环保科技有限公司 High efficiency sewage treatment method
CN1966424A (en) * 2006-11-24 2007-05-23 北京国环清华环境工程设计研究院 Biological adsorption and artificial wetland combined town sewage treatment system and method
CN101108757A (en) * 2006-07-21 2008-01-23 厦门中联环环保工程有限公司 Activated sludge method processing technique at sewage continuous drainage interval
CN101264974A (en) * 2008-04-18 2008-09-17 北京工业大学 Device for increasing active sludge oxygen-consuming rate by using electrostatic field
CN101792234A (en) * 2010-03-22 2010-08-04 浙江鎏源环保科技有限公司 System for disposing artificial wetland sewage and disposal method thereof
CN102115293A (en) * 2010-04-27 2011-07-06 北京新源国能科技有限公司 Waste water biochemical treatment method
CN102603116A (en) * 2012-03-07 2012-07-25 光大环保科技发展(北京)有限公司 Distribution treatment combination technological method for domestic sewage of small-sized towns
CN103159385A (en) * 2013-04-15 2013-06-19 合肥中达环境科技有限公司 Treatment method for carton packaging and printing production wastewater
CN105693042A (en) * 2015-05-20 2016-06-22 余素萍 Method for treating phosphorus-containing sewage
CN105712592A (en) * 2016-05-04 2016-06-29 四川格瑞斯环境科技有限公司 Novel domestic sewage treatment main station

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20040091463A (en) * 2003-04-22 2004-10-28 백순기 sewage and waste water treating system by ceramics and method for purifying sewage and waste water using the same
CN1669956A (en) * 2004-03-18 2005-09-21 昆明柯利欣环保科技有限公司 High efficiency sewage treatment method
CN101108757A (en) * 2006-07-21 2008-01-23 厦门中联环环保工程有限公司 Activated sludge method processing technique at sewage continuous drainage interval
CN1966424A (en) * 2006-11-24 2007-05-23 北京国环清华环境工程设计研究院 Biological adsorption and artificial wetland combined town sewage treatment system and method
CN101264974A (en) * 2008-04-18 2008-09-17 北京工业大学 Device for increasing active sludge oxygen-consuming rate by using electrostatic field
CN101792234A (en) * 2010-03-22 2010-08-04 浙江鎏源环保科技有限公司 System for disposing artificial wetland sewage and disposal method thereof
CN102115293A (en) * 2010-04-27 2011-07-06 北京新源国能科技有限公司 Waste water biochemical treatment method
CN102603116A (en) * 2012-03-07 2012-07-25 光大环保科技发展(北京)有限公司 Distribution treatment combination technological method for domestic sewage of small-sized towns
CN103159385A (en) * 2013-04-15 2013-06-19 合肥中达环境科技有限公司 Treatment method for carton packaging and printing production wastewater
CN105693042A (en) * 2015-05-20 2016-06-22 余素萍 Method for treating phosphorus-containing sewage
CN105712592A (en) * 2016-05-04 2016-06-29 四川格瑞斯环境科技有限公司 Novel domestic sewage treatment main station

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
张玉龙,董晖主编: "《水处理剂配方设计与实例》", 31 May 2011, 中国纺织出版社 *
毛玉红编著: "《水生物处理新技术》", 30 April 2015, 中国铁道出版社 *
辛寅昌,王彦玲编著: "《胶体与界面化学在石油工业中的应用》", 31 July 2014, 石油工业出版社 *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106746354A (en) * 2017-01-22 2017-05-31 浙江阿凡柯达环保科技有限公司 A kind of sewage in-situ processes integrated equipment
CN108996848A (en) * 2018-09-06 2018-12-14 杨镒玮 A kind of sewage-treatment plant and method
CN111603838A (en) * 2019-02-25 2020-09-01 冀勃睿 Domestic sewage physical method processing apparatus with deodorant function
CN112079532A (en) * 2020-09-17 2020-12-15 苏州科技大学 Urban sewage treatment process for recovering organic matters and phosphorus
CN112079532B (en) * 2020-09-17 2021-09-17 苏州科技大学 Urban sewage treatment process for recovering organic matters and phosphorus
CN113060830A (en) * 2021-04-11 2021-07-02 郑州大学 Method for accelerating aerobic sludge granulation by using tourmaline as crystal nucleus

Similar Documents

Publication Publication Date Title
CN102206019B (en) Refuse incineration plant percolate treatment system
CN106045208A (en) Domestic sewage treatment method
CN106242190A (en) A kind of modularity sewage disposal system
CN1872745A (en) Infiltration method for treating garbage
CN102153232B (en) Side-flow circulation BAF (Biological Aerated Filter) intensified dephosphorization system and method for treating urban sewage with the dephosphorization system
CN105384302A (en) Aquaculture wastewater processing system and method thereof
CN101041537A (en) Method for treating percolation liquid of water deficiency area garbage embedding field
CN106830542A (en) UASB two-stage A/O coagulating treatments pig farm biogas slurry system
CN110092464A (en) A kind of waste water reinforcing nitration processes based on Zeolite modifying polymer suspension bio-carrier
CN103183447A (en) Treatment method of piggery wastewater
CN104591473A (en) Advanced nitrogen and phosphorus removal technology
CN105174621A (en) System and method for treating wastewater by applying activated sludge
CN106186317B (en) A kind of artificial rapid infiltration system of strengthened denitrification
CN105130096A (en) Chemical engineering sewage deep treatment system
CN102718360A (en) Integrated livestock breeding waste water treatment method
CN201458895U (en) Integrated type sewage treatment device for hotels and residential quarters
CN103043869B (en) Recycling sewage treatment equipment by utilizing automatic backflow reactor and sewage treatment method thereof
CN204824516U (en) Breed advanced waste treatment system
CN103112948A (en) Method for rapidly culturing autotrophic nitrogen removal granule sludge under conditions of low substrate concentration and high ascending velocity
CN106946403A (en) UASB two-stage A/O coagulating treatments pig farm biogas slurry technique
CN101665308A (en) Method for advanced treatment of landfill leachate
CN102557324B (en) Method for treating garbage leachate
CN108751581A (en) A kind for the treatment of process of landfill leachate bio-chemical effluent
CN106966492A (en) A kind of method of porous hydroxyapatite bio-carrier Fiber differentiation aerobic particle mud
CN209113683U (en) A kind of energy-efficient biofilm integrated sewage disposal system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20161026

RJ01 Rejection of invention patent application after publication