CN108488802A - House refuse and waste water combined treatment process - Google Patents

House refuse and waste water combined treatment process Download PDF

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Publication number
CN108488802A
CN108488802A CN201810214857.1A CN201810214857A CN108488802A CN 108488802 A CN108488802 A CN 108488802A CN 201810214857 A CN201810214857 A CN 201810214857A CN 108488802 A CN108488802 A CN 108488802A
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CN
China
Prior art keywords
waste water
house refuse
treatment process
steps
combined treatment
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.)
Withdrawn
Application number
CN201810214857.1A
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Chinese (zh)
Inventor
高秋红
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 Wanshan Environmental Protection & Technology Co Ltd
Original Assignee
Foshan Wanshan 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 Foshan Wanshan Environmental Protection & Technology Co Ltd filed Critical Foshan Wanshan Environmental Protection & Technology Co Ltd
Priority to CN201810214857.1A priority Critical patent/CN108488802A/en
Publication of CN108488802A publication Critical patent/CN108488802A/en
Withdrawn legal-status Critical Current

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/033Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment comminuting or crushing
    • 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
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/04Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment drying
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic 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
    • 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste

Abstract

The invention discloses a kind of house refuse and waste water combined treatment process, which includes the following steps:S1. house refuse is collected, and is classified;S2. it is crushed house refuse;S3. broken house refuse is mixed with waste water, collects floating material and sediment is collected and burned as fuel;S4. the waste water after S3 steps is by shunting and saving;S5. the pH of waste water is adjusted, and the wastewater disposal basin after adjusting pH is filtered by filter device, flocculant is then added, suspended matter is made to precipitate, collect sediment according to S3 step burning disposals;S6. to treated in S5 steps, waste water carries out purified treatment.House refuse and waste water treatment process are combined together by above-mentioned technical proposal, simplify treatment process, reduce processing cost.

Description

House refuse and waste water combined treatment process
Technical field
The present invention relates to house refuses and technical field of waste water processing, combine more particularly to a kind of house refuse and waste water Treatment process.
Background technology
With the quickening of Process of Urbanization Construction, house refuse and waste water cause Groundwater Environmental Quality deterioration, pollution problem day It is beneficial serious.In order to solve house refuse and waste water, people have done many research work.Currently, the processing of house refuse is basic It is divided into burial, burning, biogas fermentation.Wherein, it buries and burning be easy to cause secondary pollution;And the technique and equipment of biogas fermentation Complexity is difficult universal in city.Moreover, the processing of house refuse and waste water is typically separated in the prior art, make in this way It is high to obtain processing cost, is unfavorable for promoting the use of.
Invention content
Based on this, it is necessary to for the high technical problem of above-mentioned processing processing cost, provide a kind of house refuse and waste water Combined treatment process.
The technical solution that the present invention solves above-mentioned technical problem is as follows:
A kind of house refuse and waste water combined treatment process, the treatment process include the following steps:
S1. house refuse is collected, and house refuse is divided into recyclable class and not recyclable class;
S2. expendable house refuse is crushed;
S3. broken house refuse is mixed with waste water, by waste water floating material and sediment collect conduct Fuel burns, and the heat generated in burning process is for generating electricity;
S4. the waste water after S3 steps shunts acid waste water, alkaline waste water and neutral waste water by part flow arrangement, And it saves in corresponding spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin;
S5. it adjusts the pH in spent acidic pond and alkaline waste water pond to neutrality, and the wastewater disposal basin after pH and neutrality will be adjusted Wastewater disposal basin is filtered by filter device, then adds flocculant, suspended matter is made to precipitate, collect the suspended matter of precipitation according to S3 Step carries out burning disposal;
S6. to treated in S5 steps, waste water carries out purified treatment.
The Domestic garbage crushing in the S2 steps to grain size is 10mm~20mm in one of the embodiments,.
The S3 steps further include at dehydration and the drying to floating material and sediment in one of the embodiments, Reason.
The dehydration absorbs the moisture in floating material and sediment by activated carbon in one of the embodiments,.
The drying and processing uses hot wind air-dry machine or tunnel type mesh belt dryer in one of the embodiments,.
The temperature of the drying and processing is 60 DEG C in one of the embodiments, and the time is 2h~3h.
The filter device in the S5 steps uses nuclepore membrane filter in one of the embodiments,.
Flocculant is aluminum sulfate, aluminium chloride, ferric sulfate, iron chloride in the S5 steps in one of the embodiments, It is a kind of.
Flocculant addition is 200mg/L~250mg/L in the S5 steps in one of the embodiments, and flocculation is heavy The drop time is 1h~2h.
In one of the embodiments, by CO in the S5 steps2It is passed through in alkaline waste water pond and adjusts pH to neutrality, by stone Ash, which is added in spent acidic pond, adjusts pH to neutrality.
House refuse and waste water treatment process are combined together by above-mentioned technical proposal, simplify treatment process, are reduced Refuse treatment plant reduces processing cost;And floating material in waste water and sediment can be used for power generation by waste combustion, to generate Economic benefit.
Description of the drawings
Fig. 1 is the flow diagram of the house refuse and waste water combined treatment process of the present invention.
Specific implementation mode
To facilitate the understanding of the present invention, below with reference to relevant drawings to invention is more fully described.In attached drawing Give presently preferred embodiments of the present invention.But the present invention can realize in many different forms, however it is not limited to this paper institutes The embodiment of description.Keep the understanding to the disclosure more thorough on the contrary, purpose of providing these embodiments is Comprehensively.
Unless otherwise defined, all of technologies and scientific terms used here by the article and belong to the technical field of the present invention The normally understood meaning of technical staff is identical.Used term is intended merely to description tool in the description of the invention herein The purpose of the embodiment of body, it is not intended that in the limitation present invention.Term as used herein "and/or" includes one or more phases Any and all combinations of the Listed Items of pass.
A kind of house refuse and waste water combined treatment process, the treatment process include the following steps:
S1. house refuse is collected, and house refuse is divided into recyclable class and not recyclable class.
Recyclable rubbish includes stationery, metal, plastics, glass etc., by integrated treatment, is recycled, it is possible to reduce dirty Dye saves resource.
Recyclable rubbish does not include rubbish from cooking, leaf, dirt, brick and tile.
S2. expendable house refuse is crushed.
S3. broken house refuse is mixed with waste water, by waste water floating material and sediment collect conduct Fuel burns, and the heat generated in burning process is for generating electricity.
Wherein, S3 steps further include dehydration and the drying and processing to floating material and sediment.And dehydration can adopt With pressure dehydration, centrifugal dehydration or chemical substance dehydration.
The essence of burning is to be oxidized to gaseous inert gas object and nothing by house refuse at 1500 DEG C and under conditions of oxygen supply is sufficient Machine noncombustibles, to form stable solid precipitation object.
S4. the waste water after S3 steps shunts acid waste water, alkaline waste water and neutral waste water by part flow arrangement, And it saves in corresponding spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin.
S5. it adjusts the pH in spent acidic pond and alkaline waste water pond to neutrality, and the wastewater disposal basin after pH and neutrality will be adjusted Wastewater disposal basin is filtered by filter device, then adds flocculant, suspended matter is made to precipitate, collect the suspended matter of precipitation according to S3 Step carries out burning disposal.
Wherein, filter device can be bag filter, intermittent pressure filter, membrane filter or turntable vacuum filter One kind of device;Flocculant is one kind of aluminum sulfate, aluminium chloride, ferric sulfate or iron chloride.
S6. to treated in S5 steps, waste water carries out purified treatment.
House refuse and waste water treatment process are combined together by above-mentioned technical proposal, simplify treatment process, are reduced Refuse treatment plant reduces processing cost;And floating material in waste water and sediment can be used for power generation by waste combustion, to generate Economic benefit.
Embodiment 1
1) house refuse is collected, and house refuse is divided into recyclable class and not recyclable class, recyclable class house refuse By integrated treatment, recycle.
2) expendable house refuse is poured into domestic garbage crusher, and it is 10mm to be crushed grain size.
3) house refuse that grain size is 10mm is poured into wastewater disposal basin and is mixed with waste water, by the floating material and precipitation in waste water Object collects, and absorbs the moisture of floating material and sediment by activated carbon to be carried out dehydrating, drying and processing uses hot wind Air-dry machine, by after dehydration floating material and sediment be added in hot wind air-dry machine, heating temperature is adjusted to 60 DEG C, heating Time is 2h;Then the floating material of drying and sediment are burned as fuel, the heat generated in burning process can be used for sending out Electricity, the residue after burning can also be used to manufacture clay or brick.
4) acid waste water, alkaline waste water and neutral waste water are shunted by part flow arrangement, and saved corresponding In spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin.
5) by CO2It is passed through in alkaline waste water pond and adjusts pH to neutrality, utilize cheap CO2To adjust alkaline waste water pond In pH value, CO2Neutralising capacity got well than inorganic acid.And safety coefficient is high, alleviates labor intensity, improved program-controlled The ability of system.Lime is added in spent acidic pond and adjusts pH to neutrality, lime derives from a wealth of sources, cheap, can further drop Reduction process cost.
Filter device uses nuclepore membrane filter, flocculant that aluminum sulfate, addition 200mg/L, flocculation is used to sink The time of drop is 1h.
6) to 5) treated, waste water carries out purified treatment.
Embodiment 2
1) house refuse is collected, and house refuse is divided into recyclable class and not recyclable class, recyclable class house refuse By integrated treatment, recycle.
2) expendable house refuse is poured into domestic garbage crusher, and it is 15mm to be crushed grain size.
3) house refuse that grain size is 15mm is poured into wastewater disposal basin and is mixed with waste water, by the floating material and precipitation in waste water Object collects, and absorbs the moisture of floating material and sediment by silica to be carried out dehydrating, drying and processing uses tunnel Road net belt dryer, by after dehydration floating material and sediment be added on tunnel type mesh belt dryer, heating temperature Degree is adjusted to 60 DEG C, heating time 2.5h;Then the floating material of drying and sediment are burned as fuel, is produced in burning process Raw heat can be used for generating electricity, and the residue after burning can also be used to manufacture clay or brick.
4) acid waste water, alkaline waste water and neutral waste water are shunted by part flow arrangement, and saved corresponding In spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin.
5) by CO2It is passed through in alkaline waste water pond and adjusts pH to neutrality, lime is added in spent acidic pond and adjusts pH to neutrality.
Filter device uses nuclepore membrane filter, flocculant that aluminium chloride, addition 225mg/L, flocculation is used to sink The time of drop is 1.5h.
6) to 5) treated, waste water carries out purified treatment.
Embodiment 3
1) house refuse is collected, and house refuse is divided into recyclable class and not recyclable class, recyclable class house refuse By integrated treatment, recycle.
2) expendable house refuse is poured into domestic garbage crusher, and it is 20mm to be crushed grain size.
3) house refuse that grain size is 20mm is poured into wastewater disposal basin and is mixed with waste water, by the floating material and precipitation in waste water Object collects, and absorbs the moisture of floating material and sediment by silica to be carried out dehydrating, drying and processing uses tunnel Road net belt dryer, by after dehydration floating material and sediment be added on tunnel type mesh belt dryer, heating temperature Degree is adjusted to 60 DEG C, heating time 3h;Then the floating material of drying and sediment are burned as fuel, is generated in burning process Heat can be used for generating electricity, the residue after burning can also be used to manufacture clay or brick.
4) acid waste water, alkaline waste water and neutral waste water are shunted by part flow arrangement, and saved corresponding In spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin.
5) by CO2It is passed through in alkaline waste water pond and adjusts pH to neutrality, lime is added in spent acidic pond and adjusts pH to neutrality.
Filter device uses nuclepore membrane filter, flocculant that ferric sulfate, addition 250mg/L, flocculation is used to sink The time of drop is 2h.
6) to 5) treated, waste water carries out purified treatment.
Embodiment 4
1) house refuse is collected, and house refuse is divided into recyclable class and not recyclable class, recyclable class house refuse By integrated treatment, recycle.
2) expendable house refuse is poured into domestic garbage crusher, and it is 20mm to be crushed grain size.
3) house refuse that grain size is 20mm is poured into wastewater disposal basin and is mixed with waste water, by the floating material and precipitation in waste water Object collects, and absorbs the moisture of floating material and sediment by silica to be carried out dehydrating, drying and processing uses tunnel Road net belt dryer, by after dehydration floating material and sediment be added on tunnel type mesh belt dryer, heating temperature Degree is adjusted to 60 DEG C, heating time 3h;Then the floating material of drying and sediment are burned as fuel, is generated in burning process Heat can be used for generating electricity, the residue after burning can also be used to manufacture clay or brick.
4) acid waste water, alkaline waste water and neutral waste water are shunted by part flow arrangement, and saved corresponding In spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin.
5) by CO2It is passed through in alkaline waste water pond and adjusts pH to neutrality, lime is added in spent acidic pond and adjusts pH to neutrality.
Filter device uses nuclepore membrane filter, flocculant that iron chloride, addition 250mg/L, flocculation is used to sink The time of drop is 2h.
6) to 5) treated, waste water carries out purified treatment.
Each technical characteristic of embodiment described above can be combined arbitrarily, to keep description succinct, not to above-mentioned reality It applies all possible combination of each technical characteristic in example to be all described, as long as however, the combination of these technical characteristics is not deposited In contradiction, it is all considered to be the range of this specification record.
Several embodiments of the invention above described embodiment only expresses, the description thereof is more specific and detailed, but simultaneously It cannot therefore be construed as limiting the scope of the patent.It should be pointed out that coming for those of ordinary skill in the art It says, without departing from the inventive concept of the premise, various modifications and improvements can be made, these belong to the protection of the present invention Range.Therefore, the protection domain of patent of the present invention should be determined by the appended claims.

Claims (10)

1. a kind of house refuse and waste water combined treatment process, which is characterized in that the treatment process includes the following steps:
S1. house refuse is collected, and house refuse is divided into recyclable class and not recyclable class;
S2. expendable house refuse is crushed;
S3. broken house refuse is mixed with waste water, by waste water floating material and sediment collect as fuel It burns, the heat generated in burning process is for generating electricity;
S4. the waste water after S3 steps shunts acid waste water, alkaline waste water and neutral waste water by part flow arrangement, and stores up It stores in corresponding spent acidic pond, alkaline waste water pond and neutral wastewater disposal basin;
S5. it adjusts the pH in spent acidic pond and alkaline waste water pond to neutrality, and the wastewater disposal basin after pH and neutral waste water will be adjusted Pond is filtered by filter device, then adds flocculant, suspended matter is made to precipitate, collect the suspended matter of precipitation according to S3 steps Carry out burning disposal;
S6. to treated in S5 steps, waste water carries out purified treatment.
2. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that in the S2 steps Domestic garbage crushing to grain size is 10mm~20mm.
3. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that the S3 steps are also wrapped Include dehydration and the drying and processing to floating material and sediment.
4. house refuse according to claim 3 and waste water combined treatment process, which is characterized in that the dehydration is logical Cross the moisture in activated carbon absorption floating material and sediment.
5. house refuse according to claim 3 and waste water combined treatment process, which is characterized in that the drying and processing is adopted With hot wind air-dry machine or tunnel type mesh belt dryer.
6. house refuse according to claim 3 and waste water combined treatment process, which is characterized in that the drying and processing Temperature is 60 DEG C, and the time is 2h~3h.
7. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that in the S5 steps Filter device uses nuclepore membrane filter.
8. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that wad a quilt with cotton in the S5 steps Solidifying agent is one kind of aluminum sulfate, aluminium chloride, ferric sulfate, iron chloride.
9. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that wad a quilt with cotton in the S5 steps Solidifying agent addition is 200mg/L~250mg/L, and the flocculating setting time is 1h~2h.
10. house refuse according to claim 1 and waste water combined treatment process, which is characterized in that in the S5 steps By CO2It is passed through in alkaline waste water pond and adjusts pH to neutrality, lime is added in spent acidic pond and adjusts pH to neutrality.
CN201810214857.1A 2018-03-15 2018-03-15 House refuse and waste water combined treatment process Withdrawn CN108488802A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810214857.1A CN108488802A (en) 2018-03-15 2018-03-15 House refuse and waste water combined treatment process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810214857.1A CN108488802A (en) 2018-03-15 2018-03-15 House refuse and waste water combined treatment process

Publications (1)

Publication Number Publication Date
CN108488802A true CN108488802A (en) 2018-09-04

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CN201810214857.1A Withdrawn CN108488802A (en) 2018-03-15 2018-03-15 House refuse and waste water combined treatment process

Country Status (1)

Country Link
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109809613A (en) * 2019-03-04 2019-05-28 长沙埃比林环保科技有限公司 A kind of processing method of sanitary sewage

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101786094A (en) * 2010-03-25 2010-07-28 河北省建筑材料工业设计研究院 Combined treatment process for household garbage and sewage
CN106430860A (en) * 2016-12-05 2017-02-22 海宁市丁桥镇芦湾股份经济合作社 Rural domestic sewage treatment technology

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101786094A (en) * 2010-03-25 2010-07-28 河北省建筑材料工业设计研究院 Combined treatment process for household garbage and sewage
CN106430860A (en) * 2016-12-05 2017-02-22 海宁市丁桥镇芦湾股份经济合作社 Rural domestic sewage treatment technology

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109809613A (en) * 2019-03-04 2019-05-28 长沙埃比林环保科技有限公司 A kind of processing method of sanitary sewage

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