CN112321067A - Sewage treatment method - Google Patents

Sewage treatment method Download PDF

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Publication number
CN112321067A
CN112321067A CN202011096072.2A CN202011096072A CN112321067A CN 112321067 A CN112321067 A CN 112321067A CN 202011096072 A CN202011096072 A CN 202011096072A CN 112321067 A CN112321067 A CN 112321067A
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China
Prior art keywords
sewage
treatment
heavy metal
tank
inputting
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CN202011096072.2A
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Chinese (zh)
Inventor
陈朝粦
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Kaiping Hui Shun Technology Co ltd
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Kaiping Hui Shun Technology Co ltd
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Priority to CN202011096072.2A priority Critical patent/CN112321067A/en
Publication of CN112321067A publication Critical patent/CN112321067A/en
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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
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • 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
    • 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
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5281Installations for water purification using chemical agents
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • 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
    • C02F2001/007Processes including a sedimentation step
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/10Temperature conditions for biological treatment
    • 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
    • C02F3/30Aerobic and anaerobic 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
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F5/00Softening water; Preventing scale; Adding scale preventatives or scale removers to water, e.g. adding sequestering agents
    • C02F5/02Softening water by precipitation of the hardness

Abstract

The invention relates to the technical field of sewage treatment, and discloses a sewage treatment method, which comprises the following steps: 1) sewage pretreatment, 2) softening treatment, 3) flocculation treatment, 4) heavy metal removal treatment, 5) heavy metal content detection, 6) biochemical treatment, 7) organic matter content detection, 8) secondary precipitation treatment and 9) disinfection treatment. According to the sewage treatment method, insoluble substances in sewage are sequentially removed through the steps of 1) sewage pretreatment, 2) softening treatment and 3) flocculation treatment, then heavy metal ions in the sewage are removed through the step 4) heavy metal removal treatment, BOD and COD contents in the sewage are reduced through the step 3) flocculation treatment, and organic matters in the sewage are degraded through the step 6) biochemical treatment, so that the problems that the existing industrial sewage mainly adopts a biological matched physical and chemical treatment method, but the treatment method is complex and the cost is high are solved.

Description

Sewage treatment method
Technical Field
The invention relates to the technical field of sewage treatment, in particular to a sewage treatment method.
Background
Sewage treatment: the biochemical treatment method is a sewage treatment method which mixes and contacts waste water or solid waste with microorganisms, decomposes organic matters and certain inorganic poisons (such as cyanides, sulfides and the like) in the waste water by utilizing biochemical action in the microorganisms and converts unstable organic matters and inorganic poisons into nontoxic substances.
The industrial sewage is characterized by complex water quality components, high suspended matters and turbidity, high salt content, high chemical oxygen demand and various heavy metals, and the existing industrial sewage mainly adopts a biological treatment method matched with a physical treatment method and a chemical treatment method, but has the problems of complex treatment method, high cost and the like, so the sewage treatment method is provided to solve the problems.
Disclosure of Invention
Technical problem to be solved
Aiming at the defects of the prior art, the invention provides a sewage treatment method, which has the advantages of good organic pollutant degradation effect and high heavy metal recovery rate, and solves the problems that the existing industrial sewage mainly adopts a biological treatment method matched with a physical and chemical treatment method, but still has a complex treatment method and higher cost.
(II) technical scheme
In order to achieve the purposes of good degradation effect of the organic pollutants and high recovery rate of heavy metals, the invention provides the following technical scheme:
a sewage treatment method comprises the following steps:
1) pretreatment of sewage: firstly, sewage is input into a coarse grid filtering device to remove large-particle impurities in the sewage, then the filtered sewage is conveyed to a fine grid device from the coarse grid filtering device through a water pump, the fine grid device is used for filtering small-particle impurities in the sewage, the filtered sewage enters an oil-water separator, impurities, floating oil and suspended matters are removed, and pretreated sewage is obtained;
2) softening treatment: conveying the pretreated sewage in the step 1) into an adjusting tank, adding a proper amount of acid and alkali, stirring and mixing, removing calcium, magnesium and other hardness ions to soften a water body, simultaneously reacting to generate suspended floc particles, testing the pH value of the sewage in real time by using a pH monitor, and stopping adding the acid and alkali when the result measured by the pH monitor is within a set range to obtain softened sewage;
3) flocculation treatment: inputting the softened sewage in the step 2) into a flocculation tank, adding a cationic flocculant into the flocculation tank according to 0.2-0.4 kg per ton of water, and removing grease, colloid and suspended solids in the sewage and suspended floc particles generated in the step 2) through an air flotation machine to obtain primary filtered sewage;
4) heavy metal removal treatment: inputting the primary filtered sewage in the step 3) into a heavy metal adsorption device, adsorbing particle residues and heavy metal ion residues in the sewage by using an adsorbent, and then inputting the adsorbed sewage into a removal device to remove metal ions with high heavy metal content;
5) and (3) heavy metal content detection: carrying out heavy metal content detection on the sewage treated in the step 4), and if the detection does not reach the standard, pumping the sewage back into the heavy metal adsorption device in the step 4) through a water pump for secondary treatment;
6) biochemical treatment: inputting the sewage with the detected heavy metal content reaching the standard in the step 5) into a biochemical reaction tank, and degrading organic matters in the sewage by using microbial bacteria cultured in the biochemical reaction tank to reduce the concentration of pollutants in the sewage;
7) and (3) detecting the content of organic matters: sampling the sewage treated in the step 6) and detecting the sewage by a COD detector;
8) secondary precipitation treatment: inputting the sewage reaching the COD detection standard in the step 7) into a radial flow type secondary sedimentation tank for secondary sedimentation, and filtering to obtain clear water;
9) and (3) disinfection treatment: inputting the clarified water obtained in the step 8) into a disinfection tank, and carrying out disinfection and sterilization treatment on the clarified water through ultraviolet ozone to obtain purified water.
Preferably, the setting range of the PH monitor in step 2) is 8-11, and the adsorbent in step 4) includes macroporous cation exchange resin, titanium chloride, manganese carbonate, sodium permanganate, trivalent cerium ions, divalent manganese ions, trivalent titanium ions, chitosan, acrylic acid solution, AMPS solution, acrylamide, acrylic acid, MBA, and potassium persulfate.
Preferably, biochemical treatment pond comprises anaerobism pond, oxygen deficiency pond and aerobic tank in step 6), the oxygen deficiency pond communicates anaerobism pond and aerobic tank respectively, heavy metal content detects up to standard sewage input anaerobism pond in step 5), the top fixed mounting in aerobic tank has the air-blower, the output of air-blower stretches into to the bottom of the pool in aerobic tank, fixed mounting has the micropore aerator in the aerobic tank, the top fixed mounting in biochemical treatment pond has the cover that keeps warm.
Preferably, the filtering device in the step 8) is a belt dehydrator, the radial flow type secondary sedimentation tank is communicated with a sludge concentration tank through a sludge pump, and the sludge concentration tank is communicated with the belt dehydrator through the sludge pump.
(III) advantageous effects
Compared with the prior art, the invention provides a sewage treatment method, which has the following beneficial effects:
1. according to the sewage treatment method, insoluble substances in the sewage are sequentially removed through the step 1) sewage pretreatment, the step 2) softening treatment and the step 3) flocculation treatment, then heavy metal ions in the sewage are removed through the step 4) heavy metal removal treatment, the loss of directly removing the heavy metals from the sewage is reduced, the service lives of a heavy metal adsorption device and a heavy metal removal device are prolonged, the maintenance cost of equipment is reduced, and the purpose of high heavy metal recovery rate is achieved.
2. This sewage treatment method can reduce BOD and COD content in the sewage through step 3) flocculation treatment, can degrade the organic matter in the sewage through step 6) biochemical treatment, reduces the concentration of pollutant in the sewage, can keep warm to the biochemical reaction pond through setting up the cover that keeps warm, prevents that the temperature is low excessively and influence the efficiency of reaction to reached the effectual purpose of organic pollutant degradation.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
A sewage treatment method comprises the following steps:
1) pretreatment of sewage: firstly, sewage is input into a coarse grid filtering device to remove large-particle impurities in the sewage, then the filtered sewage is conveyed to a fine grid device from the coarse grid filtering device through a water pump, the fine grid device is used for filtering small-particle impurities in the sewage, the filtered sewage enters an oil-water separator, impurities, floating oil and suspended matters are removed, and pretreated sewage is obtained;
2) softening treatment: conveying the pretreated sewage in the step 1) into an adjusting tank, adding a proper amount of acid and alkali, stirring and mixing, removing calcium, magnesium and other hardness ions to soften a water body, simultaneously reacting to generate suspended floc particles, testing the pH value of the sewage in real time by using a pH monitor, and stopping adding the acid and alkali when the measured result of the pH monitor is within 8-11 to obtain softened sewage;
3) flocculation treatment: inputting the softened sewage in the step 2) into a flocculation tank, adding a cationic flocculant into the flocculation tank according to 0.2-0.4 kg per ton of water, and removing grease, colloid and suspended solids in the sewage and suspended floc particles generated in the step 2) through an air flotation machine to obtain primary filtered sewage;
4) heavy metal removal treatment: inputting the primary filtered sewage in the step 3) into a heavy metal adsorption device, adsorbing particle residues and heavy metal ion residues in the sewage by using an adsorbent, then inputting the adsorbed sewage into a removal device, and removing metal ions with high heavy metal content, wherein the adsorbent comprises macroporous cation exchange resin, titanium chloride, manganese carbonate, sodium permanganate, trivalent cerium ions, divalent manganese ions, trivalent titanium ions, chitosan, an acrylic acid solution, an AMPS solution, acrylamide, acrylic acid, MBA and potassium persulfate;
5) and (3) heavy metal content detection: carrying out heavy metal content detection on the sewage treated in the step 4), and if the detection does not reach the standard, pumping the sewage back into the heavy metal adsorption device in the step 4) through a water pump for secondary treatment;
6) biochemical treatment: inputting the sewage with the heavy metal content reaching the standard in the step 5) into a biochemical reaction tank, wherein the biochemical treatment tank consists of an anaerobic tank, an anoxic tank and an aerobic tank, the anoxic tank is respectively communicated with the anaerobic tank and the aerobic tank, the sewage with the heavy metal content reaching the standard in the step 5) is input into the anaerobic tank, the top of the aerobic tank is fixedly provided with an air blower, the output end of the air blower extends into the bottom of the aerobic tank, a microporous aerator is fixedly arranged in the aerobic tank, the top of the biochemical treatment tank is fixedly provided with a heat-insulating cover, and the organic matters in the sewage are degraded by microbial bacteria cultured in the biochemical reaction tank, so that the concentration of pollutants in the sewage is reduced;
7) and (3) detecting the content of organic matters: sampling the sewage treated in the step 6) and detecting the sewage by a COD detector;
8) secondary precipitation treatment: inputting the sewage reaching the COD detection standard in the step 7) into a radial flow type secondary sedimentation tank for secondary sedimentation, and filtering to obtain clear water, wherein a filtering device is a belt type dehydrator, the radial flow type secondary sedimentation tank is communicated with a sludge concentration tank through a sludge pump, and the sludge concentration tank is communicated with the belt type dehydrator through the sludge pump;
9) and (3) disinfection treatment: inputting the clarified water obtained in the step 8) into a disinfection tank, and carrying out disinfection and sterilization treatment on the clarified water through ultraviolet ozone to obtain purified water.
The invention has the beneficial effects that: the method comprises the steps of 1) sewage pretreatment, 2) softening treatment and 3) flocculation treatment, wherein insoluble substances in the sewage are sequentially removed, then heavy metal ions in the sewage are removed through 4) heavy metal removal treatment, the loss of directly removing the heavy metals from the sewage is reduced, the service lives of a heavy metal adsorption device and a heavy metal removal device are prolonged, the maintenance cost of equipment is reduced, the aim of high recovery rate of the heavy metals is fulfilled, BOD and COD content in the sewage can be reduced through 3) flocculation treatment, organic matters in the sewage can be degraded through 6) biochemical treatment, the concentration of pollutants in the sewage is reduced, the biochemical reaction tank can be insulated through arranging an insulation cover, the effect of reaction caused by too low temperature is prevented, and the aim of good degradation effect of the organic pollutants is fulfilled, thereby solving the problems that the prior industrial sewage mainly adopts biological treatment method combined with physical and chemical treatment method, but the treatment method is complex and the cost is higher.
Although embodiments of the present invention have been shown and described, it will be appreciated by those skilled in the art that changes, modifications, substitutions and alterations can be made in these embodiments without departing from the principles and spirit of the invention, the scope of which is defined in the appended claims and their equivalents.

Claims (4)

1. A sewage treatment method is characterized by comprising the following steps:
1) pretreatment of sewage: firstly, sewage is input into a coarse grid filtering device to remove large-particle impurities in the sewage, then the filtered sewage is conveyed to a fine grid device from the coarse grid filtering device through a water pump, the fine grid device is used for filtering small-particle impurities in the sewage, the filtered sewage enters an oil-water separator, impurities, floating oil and suspended matters are removed, and pretreated sewage is obtained;
2) softening treatment: conveying the pretreated sewage in the step 1) into an adjusting tank, adding a proper amount of acid and alkali, stirring and mixing, removing calcium, magnesium and other hardness ions to soften a water body, simultaneously reacting to generate suspended floc particles, testing the pH value of the sewage in real time by using a pH monitor, and stopping adding the acid and alkali when the result measured by the pH monitor is within a set range to obtain softened sewage;
3) flocculation treatment: inputting the softened sewage in the step 2) into a flocculation tank, adding a cationic flocculant into the flocculation tank according to 0.2-0.4 kg per ton of water, and removing grease, colloid and suspended solids in the sewage and suspended floc particles generated in the step 2) through an air flotation machine to obtain primary filtered sewage;
4) heavy metal removal treatment: inputting the primary filtered sewage in the step 3) into a heavy metal adsorption device, adsorbing particle residues and heavy metal ion residues in the sewage by using an adsorbent, and then inputting the adsorbed sewage into a removal device to remove metal ions with high heavy metal content;
5) and (3) heavy metal content detection: carrying out heavy metal content detection on the sewage treated in the step 4), and if the detection does not reach the standard, pumping the sewage back into the heavy metal adsorption device in the step 4) through a water pump for secondary treatment;
6) biochemical treatment: inputting the sewage with the detected heavy metal content reaching the standard in the step 5) into a biochemical reaction tank, and degrading organic matters in the sewage by using microbial bacteria cultured in the biochemical reaction tank to reduce the concentration of pollutants in the sewage;
7) and (3) detecting the content of organic matters: sampling the sewage treated in the step 6) and detecting the sewage by a COD detector;
8) secondary precipitation treatment: inputting the sewage reaching the COD detection standard in the step 7) into a radial flow type secondary sedimentation tank for secondary sedimentation, and filtering to obtain clear water;
9) and (3) disinfection treatment: inputting the clarified water obtained in the step 8) into a disinfection tank, and carrying out disinfection and sterilization treatment on the clarified water through ultraviolet ozone to obtain purified water.
2. The method of sewage treatment according to claim 1, wherein: the setting range of the pH monitor in the step 2) is 8-11, and the adsorbent in the step 4) comprises macroporous cation exchange resin, titanium chloride, manganese carbonate, sodium permanganate, trivalent cerium ions, divalent manganese ions, trivalent titanium ions, chitosan, an acrylic acid solution, an AMPS solution, acrylamide, acrylic acid, MBA and potassium persulfate.
3. The method of sewage treatment according to claim 1, wherein: the biochemical treatment pond comprises anaerobism pond, oxygen deficiency pond and aerobic tank in step 6), the oxygen deficiency pond communicates anaerobism pond and aerobic tank respectively, the sewage input anaerobism pond up to standard of heavy metal content detection in step 5), the top fixed mounting of aerobic tank has the air-blower, the output of air-blower stretches into to the bottom of the pool in aerobic tank, fixed mounting has micropore aerator in the aerobic tank, the top fixed mounting in biochemical treatment pond has the cover that keeps warm.
4. The method of sewage treatment according to claim 1, wherein: the filtering device in the step 8) is a belt type dehydrator, the radial flow type secondary sedimentation tank is communicated with a sludge concentration tank through a sludge pump, and the sludge concentration tank is communicated with the belt type dehydrator through the sludge pump.
CN202011096072.2A 2020-10-14 2020-10-14 Sewage treatment method Pending CN112321067A (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113354050A (en) * 2021-07-16 2021-09-07 浙江浙能技术研究院有限公司 Heavy metal wastewater treating agent and wastewater treatment method
CN114249498A (en) * 2021-12-22 2022-03-29 陈辉 Village and town sewage treatment equipment and treatment method thereof
CN115432863A (en) * 2022-11-08 2022-12-06 菲立化学工程(遂昌)有限公司 Urban sewage purification device

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Publication number Priority date Publication date Assignee Title
JP2003236584A (en) * 2002-02-18 2003-08-26 Ataka Construction & Engineering Co Ltd Sewage treatment apparatus
CN104591489A (en) * 2015-01-07 2015-05-06 光大水务(济南)有限公司 Sewage treatment system and sewage treatment method
CN105585220A (en) * 2016-01-27 2016-05-18 程冠华 Urban sewage treatment system and purification method
CN105884145A (en) * 2016-06-22 2016-08-24 四川格瑞斯环境科技有限公司 System and method for treating sewage
CN107840545A (en) * 2017-11-30 2018-03-27 重庆精创联合环保工程有限公司 Process for treating industrial waste water
CN108358375A (en) * 2018-04-28 2018-08-03 许欠欠 A kind of industrial sewage process method
CN108947015A (en) * 2018-08-10 2018-12-07 李海霞 A kind of heavy metal-polluted method for treating water and its processing system
CN111762970A (en) * 2020-07-06 2020-10-13 武汉环联环境工程有限公司 Method for treating leachate of garbage transfer station

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003236584A (en) * 2002-02-18 2003-08-26 Ataka Construction & Engineering Co Ltd Sewage treatment apparatus
CN104591489A (en) * 2015-01-07 2015-05-06 光大水务(济南)有限公司 Sewage treatment system and sewage treatment method
CN105585220A (en) * 2016-01-27 2016-05-18 程冠华 Urban sewage treatment system and purification method
CN105884145A (en) * 2016-06-22 2016-08-24 四川格瑞斯环境科技有限公司 System and method for treating sewage
CN107840545A (en) * 2017-11-30 2018-03-27 重庆精创联合环保工程有限公司 Process for treating industrial waste water
CN108358375A (en) * 2018-04-28 2018-08-03 许欠欠 A kind of industrial sewage process method
CN108947015A (en) * 2018-08-10 2018-12-07 李海霞 A kind of heavy metal-polluted method for treating water and its processing system
CN111762970A (en) * 2020-07-06 2020-10-13 武汉环联环境工程有限公司 Method for treating leachate of garbage transfer station

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113354050A (en) * 2021-07-16 2021-09-07 浙江浙能技术研究院有限公司 Heavy metal wastewater treating agent and wastewater treatment method
CN114249498A (en) * 2021-12-22 2022-03-29 陈辉 Village and town sewage treatment equipment and treatment method thereof
CN114249498B (en) * 2021-12-22 2024-01-12 厦门裕清水环保工程有限公司 Village and town sewage treatment equipment and treatment method thereof
CN115432863A (en) * 2022-11-08 2022-12-06 菲立化学工程(遂昌)有限公司 Urban sewage purification device

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Application publication date: 20210205