CN110577337A - Domestic sewage treatment method - Google Patents

Domestic sewage treatment method Download PDF

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Publication number
CN110577337A
CN110577337A CN201910963561.4A CN201910963561A CN110577337A CN 110577337 A CN110577337 A CN 110577337A CN 201910963561 A CN201910963561 A CN 201910963561A CN 110577337 A CN110577337 A CN 110577337A
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CN
China
Prior art keywords
tank
sewage
water
mbr
treating
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Pending
Application number
CN201910963561.4A
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Chinese (zh)
Inventor
沈江南
施金敏
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Zhejiang Blue Lake Environmental Protection Co Ltd
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Zhejiang Blue Lake Environmental Protection Co Ltd
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Priority to CN201910963561.4A priority Critical patent/CN110577337A/en
Publication of CN110577337A publication Critical patent/CN110577337A/en
Pending legal-status Critical Current

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    • 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
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • 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
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1268Membrane bioreactor systems
    • 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
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/302Nitrification and denitrification treatment

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Physical Water Treatments (AREA)

Abstract

The invention discloses a method for treating domestic sewage, which comprises the following steps: (1) treating domestic sewage in a grid, and treating the sewage treated by the grid in an oil separation tank to regulate water quantity and homogenize water quality; (2) the sewage lifted by the oil separation tank enters the sewage A2Treating in an O biochemical pool; (3) a. the2The effluent of the O biochemical tank enters an MBR tank for treatment; (4) performing advanced treatment on effluent of the MBR tank by using active coke; (5) and (3) the sewage treated by the active coke enters an ultraviolet sterilization and disinfection tank for sterilization and disinfection to obtain treated water, and the treated water meets the discharge standard of III-class water on the earth surface. The method for treating domestic sewage to the III-class water standard on the ground surface has strong operability and good treatment effect, and the effluent meets the III-class water discharge standard on the ground surface.

Description

Domestic sewage treatment method
Technical Field
the invention relates to a method for treating domestic sewage to the III-class water standard on the ground surface.
Background
Domestic sewage is mainly discharged water produced by various kitchen water, washing water and toilet water used in human life. If the waste water is directly discharged without being treated, pathogen pollution, aerobic organic matter pollution, water eutrophication pollution and the like can be caused. In this environment, the comprehensive treatment of domestic sewage is under great pressure. In the process adopted by urban sewage plants in China, various activated sludge methods are still used as the methodThe main stream. While the conventional domestic sewage treatment is mainly classified into a physical method, a chemical method, and a biological method. The physical method is mainly to remove insoluble suspended substances in water, and the chemical method is to add chemical agents into wastewater to achieve the water purification effect through chemical reaction. The biological method is a technology for degrading organic matters by utilizing the action of microorganisms, and is mainly used for removing organic matters, ammonia nitrogen and the like in water. Among them, the biological method is currently most advantageous in use. A. the2O is a common secondary sewage treatment process, has the function of synchronous nitrogen and phosphorus removal, can be used for secondary sewage treatment or tertiary sewage treatment, and has good nitrogen and phosphorus removal effect. MBR mainly replaces the water treatment technology of a secondary sedimentation tank in the traditional activated sludge process by combining the activated sludge process and the membrane separation technology. The activated coke is a porous carbonaceous substance, is similar to an adsorbent of activated carbon, has wide application space in the field of sewage treatment, and mainly serves to remove pollutants such as COD, chromaticity, colloid, heavy metals and the like.
In recent years, with the rapid development of sewage treatment technology, the pollutant discharge standard of sewage plants is continuously improved, and the treatment standard of domestic sewage is promoted from first grade A to surface III type water, wherein the surface III type water standard is BOD5≤4mg/L;CODcr≤20mg/L;SS≤10mg/L;NH4N is less than or equal to 1 mg/L; the total nitrogen is less than or equal to 1 mg/L; the total phosphorus is less than or equal to 0.2 mg/L. Therefore, the method for treating the domestic sewage by the integrated treatment system with reliable operation has important practical significance.
Disclosure of Invention
The invention aims to provide a method for treating domestic sewage to the III-class water standard on the ground surface, which has strong operability and good treatment effect, and the discharged water meets the III-class water discharge standard on the ground surface.
In order to meet the requirements, the technical scheme of the invention is as follows:
A method for treating domestic sewage comprises the following steps:
(1) Treating domestic sewage in a grid, and treating the sewage treated by the grid in an oil separation tank to regulate water quantity and homogenize water quality; the purpose of the step is to intercept large floating objects and large granular impurities in the sewage by using a grid, and meanwhile, because the sewage has uneven water quantity and water quality, an oil separation tank is arranged before the sewage enters a subsequent treatment device to adjust the water quantity and homogenize the water quality;
(2) The sewage lifted by the oil separation tank enters the sewage A2treating in an O biochemical pool; the purpose of this step is to utilize A2removing nitrogen and phosphorus; a is described2the O biochemical pool is composed of an anaerobic pool, an anoxic pool and an aerobic pool in sequence, an anaerobic environment is maintained in the anaerobic pool, phosphorus-accumulating bacteria are enabled to fully release phosphorus in the anaerobic pool, sewage in the anaerobic pool automatically flows into the anoxic pool, the sewage is hydrolyzed and acidified in the anaerobic pool, the load of subsequent treatment facilities can be effectively reduced, and the nitrification process is carried out in the rear-stage aerobic pool to achieve the purpose of denitrification;
(3)A2The effluent of the O biochemical tank enters an MBR tank for treatment;
(4) Performing advanced treatment on effluent of the MBR tank by using active coke; the step aims to remove macromolecular refractory organic matters, organic nitrogen and organic phosphorus by adsorption by utilizing the adsorption effect of the active coke;
(5) And (4) the sewage treated by the active coke enters an ultraviolet sterilization and disinfection tank for sterilization and disinfection to obtain treated water. The treated water meets the discharge standard of class III water on the earth surface.
Wherein the domestic sewage is CODcr=220-300mg/L;BOD5=50-150mg/L;NH4-15-30 mg/L domestic sewage.
Preferably, the grid gap in step (1) is 1-5 mm.
Preferably, in the step (1), the hydraulic retention time of the sewage in the oil separation tank is 6-20 h.
preferably, in the step (2), the hydraulic retention time of the sewage in the anaerobic tank is 1.5-3h, the hydraulic retention time in the anoxic tank is 2-6h, and the hydraulic retention time in the aerobic tank is 4-8 h.
Preferably, the bottom of the aerobic tank in the step (2) is provided with a microporous aeration disc.
Preferably, in the step (3), an MBR membrane and a sludge reflux pump are arranged in the MBR tank, and after membrane filtration is carried out on sewage, high-concentration activated sludge in raw water flows back to the anaerobic tank and the anoxic tank.
Preferably, in the step (3), the hydraulic retention time in the MBR tank is 1-3 h.
Preferably, in the step (4), the effluent of the MBR tank passes through an active coke adsorption column from bottom to top, and the adding amount of the active coke is 0.05-0.12t/m3And (4) waste water.
Preferably, in step (5), the intensity of the ultraviolet light is 5 to 20W/cm2the irradiation time is 0.5-2 h.
preferably, the treatment method consists of steps (1) to (5).
Preferably, each equipment is controlled by adopting a PLC full-automatic control operation program to realize automatic operation, and particularly, the automatic operation is realized by controlling mutual switching of a submersible sewage lifting pump and a fan of a grating and an oil separation tank, a sludge reflux pump of an MBR tank, an MBR self-priming pump, an MBR backwashing pump, an MBR dosing device and an ultraviolet sterilizer.
Compared with the prior art, the invention has the advantages that:
The integrated treatment method for upgrading domestic sewage from the first-grade A to the third-class water standard on the ground surface has the advantages of strong operability, small occupied area and low treatment cost, and the quality of effluent can completely reach the III-class water discharge standard on the ground surface.
Drawings
FIG. 1 is a process flow diagram
Detailed Description
the technical scheme of the invention is further explained by combining the specific example of the attached figure 1.
Examples
The water quality indexes of the domestic sewage treated by the experiment are as follows: CODcr=300mg/L;BOD5=150mg/L;NH4-N=20mg/L。
The domestic sewage enters the grating to intercept larger suspended matters or floaters, so that the blockage of a water pump, a drain pipe and a subsequent treatment structure is prevented, and the normal operation of treatment facilities and equipment is ensured. The grid gap is 5mm, and the grid is provided with one grid, and the grid slag is manually cleaned.
The sewage after the grid treatment enters an oil separation tank, 2 submersible lift pumps are arranged in the oil separation tank, the effective water depth of the tank is 3.5m, and the hydraulic retention time is 15 h. The oil separation tank removes most of floating oil in water by utilizing the characteristics of different oil-water specific gravity and complementary compatibility.
in A2In the O biochemical pool, the sewage lifted by the oil separation pool firstly enters an anaerobic pool, the effective water depth of the anaerobic pool is 2.7m, and the effective volume is 25m3The anaerobic environment is maintained in the anaerobic tank, phosphorus-accumulating bacteria can fully release phosphorus in the anaerobic tank, conditions are created for the phosphorus-accumulating bacteria to fully absorb phosphorus in the aerobic tank, and the hydraulic retention time is 2 hours. Sewage in the anaerobic tank automatically flows into an anoxic tank, the effective water depth of the anoxic tank is 2.7m, and the effective volume is 25m3The sewage is hydrolyzed and acidified in the pool, so that the load of subsequent treatment facilities can be effectively reduced, and the hydraulic retention time is 4 hours. Sewage in the anoxic tank automatically flows into the biological contact oxidation tank in the aerobic tank, the effective water depth of the aerobic tank is 2.7m, and the effective volume is 75m3The bottom of the tank is provided with a micropore aeration disc, the hydraulic retention time is 6 hours, and most COD is decomposed and removed in the tank. COD of effluent water qualitycr=54mg/L;BOD5=22.5mg/L;NH4-N=4mg/L。
A2The effluent O enters an MBR system and stays for 2 hours, the effective water depth of an MBR tank is 2.7m, a PVDF hollow fiber MBR membrane and a sludge reflux pump are placed in the tank, a certain maintenance space is reserved for membrane filtration, high-concentration active sludge in raw water flows back to an anaerobic tank and an anoxic tank, and supernatant fluid which flows back from the MBR tank has NO3the-N is denitrified in the anoxic tank and is subjected to the nitrification process in the later-stage aerobic tank, so that the aim of denitrification is fulfilled. Water quality COD of MBR systemcr=10.8mg/L;BOD5=2mg/L;NH4-N=1.2mg/L。
The effluent of the MBR system enters an active coke adsorption column, the active coke adsorption column is used for producing active coke with an iodine value of 500-700 mg/g by taking coal as a raw material in a mode of from bottom to top, and the adding amount of the active coke is 0.1t/m3The removal rate of each pollutant of the wastewater is up to more than 80 percent. COD of produced watercr=2.16mg/L;BOD5=0.37mg/L;NH4-N ═ 0.24 mg/L. WhereinThe active coke can be regenerated: cracking at 800 deg.c, opening active coke pore channel, recovering performance near 100%, and reusing with regeneration rate of about 70%.
the effluent of the MBR tank passes through a suction pump, then passes through active coke for adsorption, and then enters an ultraviolet sterilization disinfection tank, the length, the width and the height are 4 x 2 x 1m, and the intensity of ultraviolet light is 10W/cm2The irradiation time is 1h, and the treated water completely reaches the discharge standard of III-class water on the earth surface: BOD5≤4mg/L;CODcr≤20mg/L;NH4-N≤1mg/L。
It should be understood that the above-mentioned examples are only for the purpose of clearly illustrating the present invention, and are not intended to set the limitations on the implementation of the present invention. All equivalent changes and modifications made within the scope of the present invention are within the protection scope of the present invention.

Claims (10)

1. a method for treating domestic sewage comprises the following steps:
(1) Treating domestic sewage in a grid, and treating the sewage treated by the grid in an oil separation tank to regulate water quantity and homogenize water quality;
(2) The sewage lifted by the oil separation tank enters the sewage A2Treating in an O biochemical pool;
(3)A2The effluent of the O biochemical tank enters an MBR tank for treatment;
(4) Performing advanced treatment on effluent of the MBR tank by using active coke;
(5) And (3) the sewage treated by the active coke enters an ultraviolet sterilization and disinfection tank for sterilization and disinfection to obtain treated water, and the treated water meets the discharge standard of III-class water on the earth surface.
2. The process of claim 1, wherein: the domestic sewage is CODcr=220-300mg/L;BOD5=50-150mg/L;NH4-15-30 mg/L domestic sewage.
3. The processing method according to claim 1 or 2, characterized by: the grid gap in the step (1) is 1-5 mm.
4. The processing method according to claim 1 or 2, characterized by: in the step (1), the hydraulic retention time of the sewage in the oil separation tank is 6-20 h.
5. the processing method according to claim 1 or 2, characterized by: in the step (2), the hydraulic retention time of the sewage in the anaerobic tank is 1.5-3h, the hydraulic retention time in the anoxic tank is 2-6h, and the hydraulic retention time in the aerobic tank is 4-8 h.
6. The processing method according to claim 1 or 2, characterized by: in the step (3), an MBR membrane and a sludge reflux pump are arranged in the MBR tank, and high-concentration active sludge in raw water flows back to the anaerobic tank and the anoxic tank after membrane filtration of sewage; the hydraulic retention time in the MBR tank is 1-3 h.
7. The processing method according to claim 1 or 2, characterized by: in the step (4), the effluent of the MBR tank passes through an active coke adsorption column from bottom to top, and the adding amount of the active coke is 0.05-0.12t/m3And (4) waste water.
8. The processing method according to claim 1 or 2, characterized by: in the step (5), the intensity of the ultraviolet light is 5-20W/cm2The irradiation time is 0.5-2 h.
9. The process of any one of claims 1 to 8, wherein: the treatment method comprises the steps (1) to (5).
10. The processing method according to claim 1 or 2, characterized by: and a PLC full-automatic control operation program is adopted to control each device to realize automatic operation.
CN201910963561.4A 2019-10-11 2019-10-11 Domestic sewage treatment method Pending CN110577337A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111592110A (en) * 2020-06-29 2020-08-28 中材建设有限公司 Small-sized domestic sewage treatment system and sewage treatment process
CN111908608A (en) * 2020-07-07 2020-11-10 同济大学 Multi-section variable membrane bioreactor sewage treatment system and use method thereof
CN113233720A (en) * 2021-06-24 2021-08-10 浙江工业大学 Integrated treatment method for upgrading domestic sewage from first-level A to surface III-class water standard

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6517723B1 (en) * 2000-07-27 2003-02-11 Ch2M Hill, Inc. Method and apparatus for treating wastewater using membrane filters
CN101928096A (en) * 2009-12-28 2010-12-29 清华大学 Sewage treatment method and system in ecological sensitive areas
CN205821109U (en) * 2016-06-20 2016-12-21 浙江精功环境技术有限公司 Integrated domestic sewage treatment system
CN106430847A (en) * 2016-11-22 2017-02-22 河南鸿昇环保设备制造有限公司 Intensive swine wastewater treating equipment
CN206033470U (en) * 2016-08-24 2017-03-22 江苏华晖环保科技有限公司 High salt sewage treatment system
CN206289126U (en) * 2016-12-08 2017-06-30 福建省致青生态环保有限公司 A kind of sanitary sewage AAO processing systems
CN207193061U (en) * 2017-09-05 2018-04-06 宁夏百益科创新能源科技有限公司 A kind of domestic sewage processing system
CN109231734A (en) * 2018-11-26 2019-01-18 山东科技职业学院 Integrated sewage disposal domestic sewage in rural areas system
CN109293128A (en) * 2018-08-06 2019-02-01 浙江筑原生态科技有限公司 A kind of Sewage from Ships processing system
CN109970194A (en) * 2019-04-16 2019-07-05 凌志环保股份有限公司 It is a kind of integrate Ao Baoer, biological multiplication, MBBR, MBR diversification technique sewage treatment pot
CN110204150A (en) * 2019-07-04 2019-09-06 安吉起航环境工程有限公司 Municipal sewage mentions mark reforming technology

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6517723B1 (en) * 2000-07-27 2003-02-11 Ch2M Hill, Inc. Method and apparatus for treating wastewater using membrane filters
CN101928096A (en) * 2009-12-28 2010-12-29 清华大学 Sewage treatment method and system in ecological sensitive areas
CN205821109U (en) * 2016-06-20 2016-12-21 浙江精功环境技术有限公司 Integrated domestic sewage treatment system
CN206033470U (en) * 2016-08-24 2017-03-22 江苏华晖环保科技有限公司 High salt sewage treatment system
CN106430847A (en) * 2016-11-22 2017-02-22 河南鸿昇环保设备制造有限公司 Intensive swine wastewater treating equipment
CN206289126U (en) * 2016-12-08 2017-06-30 福建省致青生态环保有限公司 A kind of sanitary sewage AAO processing systems
CN207193061U (en) * 2017-09-05 2018-04-06 宁夏百益科创新能源科技有限公司 A kind of domestic sewage processing system
CN109293128A (en) * 2018-08-06 2019-02-01 浙江筑原生态科技有限公司 A kind of Sewage from Ships processing system
CN109231734A (en) * 2018-11-26 2019-01-18 山东科技职业学院 Integrated sewage disposal domestic sewage in rural areas system
CN109970194A (en) * 2019-04-16 2019-07-05 凌志环保股份有限公司 It is a kind of integrate Ao Baoer, biological multiplication, MBBR, MBR diversification technique sewage treatment pot
CN110204150A (en) * 2019-07-04 2019-09-06 安吉起航环境工程有限公司 Municipal sewage mentions mark reforming technology

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
MA DEHUA等: "Acute toxicity and chemical evaluation of coking wastewater under biological and advanced physicochemical treatment processes", 《ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH》 *
何伶俊等: "江苏太湖流域污水处理厂一级A提标改造技术总结", 《中国给水排水》 *
吴英等: "水解酸化-A~2/O-MBR-BAC组合工艺处理焦化废水试验研究", 《工业用水与废水》 *
朱宁伟等: "A~2O-MBR组合工艺处理城市污水的试验研究", 《中国给水排水》 *
马少华等: "800t/d小城镇生活污水处理站工程设计", 《石油和化工设备》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111592110A (en) * 2020-06-29 2020-08-28 中材建设有限公司 Small-sized domestic sewage treatment system and sewage treatment process
CN111908608A (en) * 2020-07-07 2020-11-10 同济大学 Multi-section variable membrane bioreactor sewage treatment system and use method thereof
CN113233720A (en) * 2021-06-24 2021-08-10 浙江工业大学 Integrated treatment method for upgrading domestic sewage from first-level A to surface III-class water standard

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