CN108947130A - A kind of refuse leachate processing method based on anaerobic reaction - Google Patents

A kind of refuse leachate processing method based on anaerobic reaction Download PDF

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Publication number
CN108947130A
CN108947130A CN201810832963.6A CN201810832963A CN108947130A CN 108947130 A CN108947130 A CN 108947130A CN 201810832963 A CN201810832963 A CN 201810832963A CN 108947130 A CN108947130 A CN 108947130A
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CN
China
Prior art keywords
filtering
layer
refuse leachate
sawdust
anaerobic reaction
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
CN201810832963.6A
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Chinese (zh)
Inventor
张期凯
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.)
Anhui Anjiang Environmental Protection Technology Co Ltd
Original Assignee
Anhui Anjiang Environmental Protection 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 Anhui Anjiang Environmental Protection Technology Co Ltd filed Critical Anhui Anjiang Environmental Protection Technology Co Ltd
Priority to CN201810832963.6A priority Critical patent/CN108947130A/en
Publication of CN108947130A publication Critical patent/CN108947130A/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
    • 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • 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
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • 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
    • 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
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/06Contaminated groundwater or leachate
    • 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

Abstract

The refuse leachate processing method based on anaerobic reaction that the invention discloses a kind of, is related to environment protection field.Processing method of the present invention includes: pretreatment, carries out heating concentration to refuse leachate;Refuse leachate after concentration is transferred to progress anaerobic reaction processing in anaerobic reactor by Anaerobic Treatment;PH is adjusted, addition PH regulator adjusts PH to 6.5-9;It filters, by being filtered using the filter plant of sawdust materials filling as filter layer;Film filtering obtains filtering residual liquid by me.mbrane bioreactor jin filtrate progress film filtration treatment;System is fertile, filtered sawdust filter layer is recycled in stirring mixer and is added plant ash, clay and filtering residual liquid stir evenly, and extrusion, which is dried, is made cake fertilizer.For the present invention by being filtered absorption after carrying out anaerobic reaction processing to penetrating fluid and cake fertilizer being made, realization is recycled the Organic nutrient in refuse leachate, realizes the recycling of resource.

Description

A kind of refuse leachate processing method based on anaerobic reaction
Technical field
The invention belongs to environmental technology fields, more particularly to a kind of refuse leachate processing side based on anaerobic reaction Method.
Background technique
Sanitary landfills handles rubbish, and incident is the generation of landfill leachate: moisture, organic matter contained in rubbish The water that the moisture generated and Atmospheric precipitation, runoff etc. are penetrated into landfill area by earth's surface is decomposed, in addition to a part evaporation, remaining It will be stored in buring layer, and after buring layer water content reaches saturation, just form refuse leachate.
Currently, the processing for refuse leachate generally has the methods of biological treatment, materializing strategy, land treatment systems.With The development and popularization of technology, anaerobic-aerobic biological treatment method are gradually risen.Compared with aerobic method, anaerobic bio-treated takes up an area face It is the small, less energy consumption of product, easy to operate, therefore invest and operating cost is cheap.
Summary of the invention
The refuse leachate processing method based on anaerobic reaction that the purpose of the present invention is to provide a kind of, by penetrating fluid Absorption is filtered after carrying out anaerobic reaction processing and cake fertilizer is made, and realizes and the Organic nutrient in refuse leachate is carried out It recycles, realizes the recycling of resource.
In order to solve the above technical problems, the present invention is achieved by the following technical solutions:
The present invention is a kind of refuse leachate processing method based on anaerobic reaction, is included the following steps:
Step 1, pretreatment: heating concentration is carried out to refuse leachate;
Step 2, Anaerobic Treatment: the refuse leachate after concentration is transferred to progress anaerobic reaction processing in anaerobic reactor;
Step 3, PH are adjusted: addition PH regulator adjusts PH to 6.5-9;
Step 4, filtering: by being filtered using the filter plant of sawdust materials filling as filter layer;
Step 5, film filtering: film filtration treatment is carried out by me.mbrane bioreactor jin filtrate and obtains filtering residual liquid;
Step 6, system fertilizer: by filtered sawdust filter layer be recycled in stirring mixer and add plant ash, clay and Filtering residual liquid stirs evenly, and extrusion, which is dried, is made cake fertilizer.
Further, the PH regulator includes quick lime, hydrochloric acid and soda ash.
Further, the filter plant includes a cylinder;The bottom of the cylinder is equipped with filter opening;The interior bottom of the cylinder One layer of filtering layer of cloth is equipped on side, if being additionally provided with the dry filter screen of layer in the cylinder;Between filter screen described in adjacent two layers Or sawdust layer is formed filled with sawdust between filter screen and filtering layer of cloth.
Further, the number of plies of the filter screen is 3 layers;From top to bottom it is followed successively by the first filtering meshes, the second filter screen Layer and third filtering meshes.
Further, the sawdust fill factor between first filtering meshes and the second filtering meshes is 0.65-0.75, Filling thickness is 5-15cm;Sawdust fill factor between second filtering meshes and third filtering meshes is 0.70-0.85, Filling thickness is 5-15cm;Sawdust fill factor between the third filtering meshes and filtering layer of cloth is 0.80-0.95, filling With a thickness of 5-15cm.
Further, the filtering layer of cloth is a cotton layer or nonwoven layer.
The invention has the following advantages:
The present invention is realized by being filtered absorption after carrying out anaerobic reaction processing to penetrating fluid and cake fertilizer being made to rubbish Organic nutrient in penetrating fluid is recycled, and realizes the recycling of resource;The present invention passes through different fill factors in 3 Sawdust filled layer as filter layer, using sawdust in penetrating fluid organic components and impurity adsorb, reduce later period film mistake The operating pressure of filter membrane during filter, improves the service life of filter membrane;After the present invention handles refuse leachate It recycles, improves the utilization rate to resource, manufactured cake fertilizer is used for fertilising operation, improves the extra price of garbage disposal Value has good effects of energy conservation and environmental protection.
Certainly, it implements any of the products of the present invention and does not necessarily require achieving all the advantages described above at the same time.
Detailed description of the invention
In order to illustrate the technical solution of the embodiments of the present invention more clearly, will be described below to embodiment required Attached drawing is briefly described, it should be apparent that, drawings in the following description are only some embodiments of the invention, for ability For the those of ordinary skill of domain, without creative efforts, it can also be obtained according to these attached drawings other attached Figure.
Fig. 1 is filter plant structural schematic diagram of the present invention.
Specific embodiment
Following will be combined with the drawings in the embodiments of the present invention, and technical solution in the embodiment of the present invention carries out clear, complete Site preparation description, it is clear that described embodiments are only a part of the embodiments of the present invention, instead of all the embodiments.It is based on Embodiment in the present invention, it is obtained by those of ordinary skill in the art without making creative efforts all other Embodiment shall fall within the protection scope of the present invention.
Refering to Figure 1, the present invention is a kind of refuse leachate processing method based on anaerobic reaction, including walk as follows It is rapid:
Step 1, pretreatment: heating concentration is carried out to refuse leachate;
Step 2, Anaerobic Treatment: the refuse leachate after concentration is transferred to progress anaerobic reaction processing in anaerobic reactor;
Step 3, PH are adjusted: addition PH regulator adjusts PH to 6.5-9;
Step 4, filtering: by being filtered using the filter plant of sawdust materials filling as filter layer;
Step 5, film filtering: film filtration treatment is carried out by me.mbrane bioreactor jin filtrate and obtains filtering residual liquid;
Step 6, system fertilizer: by filtered sawdust filter layer be recycled in stirring mixer and add plant ash, clay and Filtering residual liquid stirs evenly, and extrusion, which is dried, is made cake fertilizer.
Preferably, PH regulator includes quick lime, hydrochloric acid and soda ash.
Preferably, filter plant includes a cylinder 1;The bottom of cylinder 1 is equipped with filter opening;It is laid on the interior bottom side of cylinder 1 There is one layer of filtering layer of cloth 11, if being additionally provided with 3 layers of filter screen 13 in cylinder 1;Between adjacent two layers filter screen 13 or filter screen 13 with It filters and forms sawdust layer 12 filled with sawdust between layer of cloth 11.
Preferably, filter screen 13 is from top to bottom followed successively by the first filtering meshes, the second filtering meshes and third filtering meshes.
Preferably, the sawdust fill factor between the first filtering meshes and the second filtering meshes is 0.70, and filling thickness is 10cm;Sawdust fill factor between second filtering meshes and third filtering meshes is 0.8, filling thickness 10cm;Third mistake Sawdust fill factor between filter mesh layer and filtering layer of cloth 11 is 0.90, filling thickness 10cm.
Preferably, filtering layer of cloth 11 is a cotton layer or nonwoven layer.
In the description of this specification, the description of reference term " one embodiment ", " example ", " specific example " etc. means Particular features, structures, materials, or characteristics described in conjunction with this embodiment or example are contained at least one implementation of the invention In example or example.In the present specification, schematic expression of the above terms may not refer to the same embodiment or example. Moreover, particular features, structures, materials, or characteristics described can be in any one or more of the embodiments or examples to close Suitable mode combines.
Present invention disclosed above preferred embodiment is only intended to help to illustrate the present invention.There is no detailed for preferred embodiment All details are described, are not limited the invention to the specific embodiments described.Obviously, according to the content of this specification, It can make many modifications and variations.These embodiments are chosen and specifically described to this specification, is in order to better explain the present invention Principle and practical application, so that skilled artisan be enable to better understand and utilize the present invention.The present invention is only It is limited by claims and its full scope and equivalent.

Claims (6)

1. a kind of refuse leachate processing method based on anaerobic reaction, which comprises the steps of:
Step 1, pretreatment: heating concentration is carried out to refuse leachate;
Step 2, Anaerobic Treatment: the refuse leachate after concentration is transferred to progress anaerobic reaction processing in anaerobic reactor;
Step 3, PH are adjusted: addition PH regulator adjusts PH to 6.5-9;
Step 4, filtering: by being filtered using the filter plant of sawdust materials filling as filter layer;
Step 5, film filtering: film filtration treatment is carried out by me.mbrane bioreactor jin filtrate and obtains filtering residual liquid;
Step 6, system fertilizer: filtered sawdust filter layer is recycled in stirring mixer and is added plant ash, clay and filtering Residual liquid stirs evenly, and extrusion, which is dried, is made cake fertilizer.
2. a kind of refuse leachate processing method based on anaerobic reaction according to claim 1, which is characterized in that described PH regulator includes quick lime, hydrochloric acid and soda ash.
3. a kind of refuse leachate processing method based on anaerobic reaction according to claim 1, which is characterized in that described Filter plant includes a cylinder (1);The bottom of the cylinder (1) is equipped with filter opening;It is equipped on the interior bottom side of the cylinder (1) One layer of filtering layer of cloth (11), the cylinder (1) is if interior be additionally provided with the dry filter screen of layer (13);Filter screen described in adjacent two layers (13) it Between or filter screen (13) and filtering layer of cloth (11) between filled with sawdust formed sawdust layer (12).
4. a kind of refuse leachate processing method based on anaerobic reaction according to claim 3, which is characterized in that described The number of plies of filter screen (13) is 3 layers;From top to bottom it is followed successively by the first filtering meshes, the second filtering meshes and third filtering meshes.
5. a kind of refuse leachate processing method based on anaerobic reaction according to claim 4, which is characterized in that described Sawdust fill factor between first filtering meshes and the second filtering meshes is 0.65-0.75, filling thickness 5-15cm;It is described Sawdust fill factor between second filtering meshes and third filtering meshes is 0.70-0.85, filling thickness 5-15cm;It is described Sawdust fill factor between third filtering meshes and filtering layer of cloth (11) is 0.80-0.95, filling thickness 5-15cm.
6. a kind of refuse leachate processing method based on anaerobic reaction according to claim 3, which is characterized in that described Filtering layer of cloth (11) is a cotton layer or nonwoven layer.
CN201810832963.6A 2018-07-26 2018-07-26 A kind of refuse leachate processing method based on anaerobic reaction Pending CN108947130A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810832963.6A CN108947130A (en) 2018-07-26 2018-07-26 A kind of refuse leachate processing method based on anaerobic reaction

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810832963.6A CN108947130A (en) 2018-07-26 2018-07-26 A kind of refuse leachate processing method based on anaerobic reaction

Publications (1)

Publication Number Publication Date
CN108947130A true CN108947130A (en) 2018-12-07

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Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20090127385A (en) * 2008-06-08 2009-12-11 에코랜드 주식회사 Eco panel(ep), eco box(eb), eco bioreactor(ebr), composite bioreactor(cbr) and clean up of water quality by them
CN102774975A (en) * 2012-07-27 2012-11-14 大连理工大学 Environment-friendly method for recovering and cyclically utilizing automobile washing wastewater
CN103373789A (en) * 2012-04-23 2013-10-30 西安皓海嘉环保工程有限责任公司 Treatment method of garbage leachate
CN207468425U (en) * 2017-10-18 2018-06-08 厦门东江环保科技有限公司 A kind of high-concentration emulsified liquid processing system

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20090127385A (en) * 2008-06-08 2009-12-11 에코랜드 주식회사 Eco panel(ep), eco box(eb), eco bioreactor(ebr), composite bioreactor(cbr) and clean up of water quality by them
CN103373789A (en) * 2012-04-23 2013-10-30 西安皓海嘉环保工程有限责任公司 Treatment method of garbage leachate
CN102774975A (en) * 2012-07-27 2012-11-14 大连理工大学 Environment-friendly method for recovering and cyclically utilizing automobile washing wastewater
CN207468425U (en) * 2017-10-18 2018-06-08 厦门东江环保科技有限公司 A kind of high-concentration emulsified liquid processing system

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Application publication date: 20181207

RJ01 Rejection of invention patent application after publication