CN107129010A - A kind of percolate secondary treatment method - Google Patents

A kind of percolate secondary treatment method Download PDF

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Publication number
CN107129010A
CN107129010A CN201710580510.4A CN201710580510A CN107129010A CN 107129010 A CN107129010 A CN 107129010A CN 201710580510 A CN201710580510 A CN 201710580510A CN 107129010 A CN107129010 A CN 107129010A
Authority
CN
China
Prior art keywords
dope
retention
percolate
delivered
supernatant
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
CN201710580510.4A
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Chinese (zh)
Inventor
鄞楠
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 Silver Enterprise Management Consulting Co Ltd
Original Assignee
Foshan Silver Enterprise Management Consulting 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 Silver Enterprise Management Consulting Co Ltd filed Critical Foshan Silver Enterprise Management Consulting Co Ltd
Priority to CN201710580510.4A priority Critical patent/CN107129010A/en
Publication of CN107129010A publication Critical patent/CN107129010A/en
Pending legal-status Critical Current

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Classifications

    • 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
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • 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
    • C02F2209/03Pressure
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/04Flow arrangements
    • C02F2301/043Treatment of partial or bypass streams
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/04Flow arrangements
    • C02F2301/046Recirculation with an external loop
    • 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

Abstract

The invention discloses a kind of percolate secondary treatment method, comprise the following steps:S1) percolate Jing Guo biochemical treatment passes sequentially through first flow valve, the first booster pump into dish tube type membrane system, obtain a supernatant and the retention dope containing organic matter, supernatant is delivered to the processing unit of next stage, and retention dope is delivered to dope water tank;S2) the retention dope of dope water tank passes sequentially through the second booster pump, second flow valve and is delivered to the entrance side of the first booster pump, is mixed with the percolate Jing Guo biochemical treatment, enters dish tube type membrane system via the first booster pump;S3 secondary supernatant and high concentration retention dope) are obtained, secondary supernatant is delivered to the processing unit of next stage, and high concentration retention dope is transmitted back to dope water tank.The present invention is filtered by secondary booster, and by the filtering of circulation, concentrated water is further concentrated, and reduces the yield of concentrated water, is improved the concentration of concentrated water after filter membrane, the yield of clear water is also improved.

Description

A kind of percolate secondary treatment method
Technical field
The present invention relates to advanced treatment of wastewater technical field, more specifically a kind of percolate after-treatment side Method.
Background technology
House refuse is during stacking, filling, due to anaerobic fermentation, organic matter decomposition, the immersion of rainwater shower, underground water Deng a variety of metabolites and moisture is produced, percolate is formed.Percolate processing is the important step of sewage disposal, if place Reason is not thorough, and immeasurable pollution and harm can be brought to surrounding environment, threat is brought to health.Sewage is carried out deep The equipment of processing is spent, the producing water ratio of advanced treating, the garbage filter of especially suitable house refuse power generation project can be effectively improved Liquid processing.At present, the sewage that house refuse power generation project is produced typically is entered using the technique of " physics+biochemistry+MBR+ film process " Row processing, using above-mentioned processing method, exist generation concentrated water amount it is larger, concentration is relatively low, the problem of producing water ratio is relatively low.
The content of the invention
The purpose of the present invention aim to provide it is a kind of can the high percolate after-treatment of output high concentration dope, producing water ratio Method, to overcome weak point of the prior art.
To achieve the above object, technical scheme provided by the present invention is:A kind of percolate secondary treatment method, its It is characterised by comprising the following steps:
S1) dish periosteum is filtered:Percolate by biochemical treatment passes sequentially through first flow valve, the first booster pump and enters dish Tube type membrane system, obtains a supernatant and the retention dope containing organic matter, and a supernatant is delivered to the processing of next stage Unit, retention dope is delivered to dope water tank;
S2) secondary back is filtered:The retention dope of dope water tank passes sequentially through the second booster pump, second flow valve and is delivered to The entrance side of one booster pump, is mixed with the percolate Jing Guo biochemical treatment, enters dish tube type membrane via the first booster pump System;
S3 secondary supernatant and high concentration retention dope) are obtained, secondary supernatant is delivered to the processing unit of next stage, highly concentrated Degree retention dope is transmitted back to dope water tank.
Pressure-detecting device is set in the dish tube type membrane system.
The dope water tank sets concentration detection apparatus.
The beneficial effects of the invention are as follows:
The present invention is filtered by secondary booster, and by the filtering of circulation, concentrated water is further concentrated, the yield of concentrated water is reduced, The concentration of concentrated water after filter membrane is improved, the yield of clear water is also improved.
Meanwhile, the present invention is simple in construction, as long as by circulating line, concentrated water is passed to before high-pressure pump, original is made in the duct Water is mixed with concentrated water, passes to film processing system.Supercharging equipment and mixing arrangement need not additionally be increased, with traditional one-level mistake Filter is compared, without extra increase power-equipment.
Brief description of the drawings
Fig. 1 is the flow chart of percolate secondary treatment method of the present invention.
Embodiment
Below in conjunction with accompanying drawing, embodiments of the present invention is described in detail.
Referring to Fig. 1, a kind of percolate secondary treatment method comprises the following steps:
S1) dish periosteum is filtered:Percolate by biochemical treatment passes sequentially through first flow valve 4, the first booster pump 5 and entered Dish tube type membrane system 1, obtains a supernatant and the retention dope containing organic matter, one time supernatant is delivered to the upper of next stage Clear liquid processing unit 2, retention dope is delivered to dope water tank 3;
S2) secondary back is filtered:The retention dope of dope water tank 3 passes sequentially through the second booster pump 7, second flow valve 6 and is delivered to The entrance side of first booster pump 5, is mixed with the percolate Jing Guo biochemical treatment, enters dish tubular type via the first booster pump 5 Filter membrane system 1;
S3 secondary supernatant and high concentration retention dope) are obtained, secondary supernatant is delivered to the processing unit of next stage, highly concentrated Degree retention dope is transmitted back to dope water tank.
The present invention to percolate take concentration dope secondary filter concentrate the step of, this method have it is easy to operate, Economical and efficient, saving power and preventing pollution dye, the advantages of practical, it is removed as a kind of further treatment technique, effectively has in percolate Machine thing dope, can be very good to make up the deficiency in existing consumer waste infiltration liquid treatment technology, reaches landfill leachate treatment To the target of " zero-emission ".
Pressure-detecting device is set in the dish tube type membrane system, by the valve opening for controlling first and second flow valve The pressure limit in system is set to be suitable to filtering.The dope water tank sets concentration detection apparatus, when the concentrated water in dope water tank and When concentration reaches processing requirement, then the dope of dope water tank is uniformly processed.
Although an embodiment of the present invention has been shown and described, it will be understood by those within the art that:Not In the case of departing from the principle and objective of the present invention a variety of change, modification, replacement and modification can be carried out to these embodiments, this The scope of invention is limited by claim and its equivalent substitution, without creative work improvements introduced etc., all should be included Within protection scope of the present invention.

Claims (3)

1. a kind of percolate secondary treatment method, it is characterised in that comprise the following steps:
S1) dish periosteum is filtered:Percolate by biochemical treatment passes sequentially through first flow valve, the first booster pump and enters dish Tube type membrane system, obtains a supernatant and the retention dope containing organic matter, and a supernatant is delivered to the processing of next stage Unit, retention dope is delivered to dope water tank;
S2) secondary back is filtered:The retention dope of dope water tank passes sequentially through the second booster pump, second flow valve and is delivered to The entrance side of one booster pump, is mixed with the percolate Jing Guo biochemical treatment, enters dish tube type membrane via the first booster pump System;
S3 secondary supernatant and high concentration retention dope) are obtained, secondary supernatant is delivered to the processing unit of next stage, highly concentrated Degree retention dope is transmitted back to dope water tank.
2. percolate secondary treatment method according to claim 1, it is characterised in that:The dish tube type membrane system Interior setting pressure-detecting device.
3. percolate secondary treatment method according to claim 1, it is characterised in that:The dope water tank sets dense Spend detection means.
CN201710580510.4A 2017-07-17 2017-07-17 A kind of percolate secondary treatment method Pending CN107129010A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710580510.4A CN107129010A (en) 2017-07-17 2017-07-17 A kind of percolate secondary treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710580510.4A CN107129010A (en) 2017-07-17 2017-07-17 A kind of percolate secondary treatment method

Publications (1)

Publication Number Publication Date
CN107129010A true CN107129010A (en) 2017-09-05

Family

ID=59737812

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710580510.4A Pending CN107129010A (en) 2017-07-17 2017-07-17 A kind of percolate secondary treatment method

Country Status (1)

Country Link
CN (1) CN107129010A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112473377A (en) * 2020-12-18 2021-03-12 青岛润扬环境科技有限公司 Tubular micro-filtration circulating water tank

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201834812U (en) * 2010-09-29 2011-05-18 湖北沙市水处理设备制造厂 Garbage leachate external pipe type ultrafiltration device
CN205061728U (en) * 2015-10-08 2016-03-02 武汉水怡环保科技工程有限公司 Dish tubular reverse osmosis membrane refuse disposal filtration liquid equipment

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201834812U (en) * 2010-09-29 2011-05-18 湖北沙市水处理设备制造厂 Garbage leachate external pipe type ultrafiltration device
CN205061728U (en) * 2015-10-08 2016-03-02 武汉水怡环保科技工程有限公司 Dish tubular reverse osmosis membrane refuse disposal filtration liquid equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112473377A (en) * 2020-12-18 2021-03-12 青岛润扬环境科技有限公司 Tubular micro-filtration circulating water tank

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Application publication date: 20170905