CN109111081A - A kind of dehydration of sludge high-drying and dehydration filtrate pretreating process and its processing system - Google Patents

A kind of dehydration of sludge high-drying and dehydration filtrate pretreating process and its processing system Download PDF

Info

Publication number
CN109111081A
CN109111081A CN201811037531.2A CN201811037531A CN109111081A CN 109111081 A CN109111081 A CN 109111081A CN 201811037531 A CN201811037531 A CN 201811037531A CN 109111081 A CN109111081 A CN 109111081A
Authority
CN
China
Prior art keywords
sludge
dehydration
filtrate
drying
acid
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.)
Granted
Application number
CN201811037531.2A
Other languages
Chinese (zh)
Other versions
CN109111081B (en
Inventor
司恩良
王传江
刘明中
何光亚
熊霞
张焜
江沛
王金森
陈斌
郝友苗
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 Tongyuan Environment Energy Saving Co Ltd
Original Assignee
Anhui Tongyuan Environment Energy Saving 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 Tongyuan Environment Energy Saving Co Ltd filed Critical Anhui Tongyuan Environment Energy Saving Co Ltd
Priority to CN201811037531.2A priority Critical patent/CN109111081B/en
Publication of CN109111081A publication Critical patent/CN109111081A/en
Application granted granted Critical
Publication of CN109111081B publication Critical patent/CN109111081B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/14Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • 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
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Treatment Of Sludge (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention discloses a kind of dehydration of sludge high-drying and dehydration filtrate pretreating process, are related to technical field of sludge treatment.The present invention includes the following steps: S01, by sludge conditioning system enhancement excess sludge dewatering;Sludge after S02, conditioning obtains mud cake and dehydration filtrate by sludge high-drying dewatering system;S03, dehydration filtrate make the metal ion in filtrate form wadding body through filtrate alkali tune flocculation system;S04, wadding body is removed by filtrate filtration system, cleaner liquid is obtained;S05, cleaner liquid is crossed by acid-base neutralization system adjusting pH to neutrality, be emitted into water treatment system.The present invention improves dewatering performance of sludge by addition inorganic coagulant and organic flocculant, in conjunction with dehydration equipments such as plate compressions, it can be achieved that sludge high-drying is dehydrated.

Description

A kind of dehydration of sludge high-drying and dehydration filtrate pretreating process and its processing system
Technical field
The invention belongs to technical field of sludge treatment, pre-process more particularly to a kind of dehydration of sludge high-drying and dehydration filtrate Technique and a kind of dehydration of sludge high-drying and dehydration filtrate pretreatment system.
Background technique
Sewage treatment can generate a large amount of excess sludges, and excess sludge shale is complicated, contain a large amount of hydroaropic substances, sludge dewatering It needs to improve sludge before, chemical method conditioning is the most common means, cooperates organic flocculant frequently with inorganic coagulant Mode.
The addition of inorganic coagulant will increase the concentration of metal ions such as dehydration filtrate hardness and iron, aluminium, and filtrate needs list Reason of staying alone is back to Raw water treatment system mixed processing with qualified discharge.With the continuous operation of dehydration equipment, if not right Metal ion is removed, and metal ion can be constantly enriched in water treatment system, final to influence system throughput and effluent quality. Especially to the sewage treatment process using the film process unit such as ultrafiltration, MBR, since film makees the interception of bulky grain metal ion With, lead to metal ion fast enriching in systems, it is dirty to block up film unit.
Summary of the invention
It is inorganic by adding the purpose of the present invention is to provide a kind of dehydration of sludge high-drying and dehydration filtrate pretreating process Coagulant and organic flocculant improve dewatering performance of sludge, in conjunction with dehydration equipments such as plate compressions, it can be achieved that sludge high-drying is dehydrated.
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 dehydration of sludge high-drying and dehydration filtrate pretreating process, is included the following steps:
S01, pass through sludge conditioning system enhancement excess sludge dewatering;
Sludge after S02, conditioning obtains mud cake and dehydration filtrate by sludge high-drying dewatering system;
S03, dehydration filtrate make the metal ion in filtrate form wadding body through filtrate alkali tune flocculation system;
S04, wadding body is removed by filtrate filtration system, cleaner liquid is obtained;
S05, cleaner liquid is crossed by acid-base neutralization system adjusting pH to neutrality, be emitted into water treatment system.
Further, the improvement dewatering performance of sludge in the S01 is specially that inorganic coagulation is added in sludge conditioning pond Agent and organic flocculant.
Further, the inorganic coagulant dosage is the 20%-80% of over dry sludge quality;The inorganic coagulant For at least one of ferric trichloride, bodied ferric sulfate, ferric sulfate of polymerized silica, aluminium polychloride, bisgallic acid iron.
Further, the organic flocculant dilution ratio is 0.1%-0.4%, is added after dilution to sludge conditioning pond Amount is the 100%-150% of over dry sludge quality in conditioner.
Further, it is specifically included in the S03 and first adjusts dehydration filtrate pH to 8-13 using basic agent, then added Organic flocculant obtains alkaline filtrate;The organic flocculant ratio is 0.1%-0.4% and adds to filtrate alkali tune to flocculate The amount of system is the 1%-2% of filtrate volume;
Wherein, the basic agent includes sodium hydroxide, sodium carbonate, sodium bicarbonate, potassium hydroxide.
Further, the organic flocculant is polyacrylamide, in polyetheramine, polydimethyl diallyl ammonium chloride It is at least one.
Further, addition acid medicine is specifically included in the S05 and adjusts pH to 6-9, is flowed back into water treatment system; The acid medicine includes concentrated hydrochloric acid or the concentrated sulfuric acid.
The present invention also provides a kind of dehydration of sludge high-drying and dehydration filtrate pretreatment systems, including sludge conditioning system, dirt Mud high level cadre dewatering system, alkali tune flocculation system, filtration system, acid-base neutralization system and water treatment system;
The sludge conditioning system front end is connected with water treatment system, for extracting excess sludge, rear end and sludge high-drying Dewatering system is connected, for providing conditioned sludge;
Sludge high-drying dewatering system rear end is connected with alkali tune flocculation system;By sludge in conditioner is conveyed into dredge pump To by the dehydration equipment in sludge high-drying dewatering system, mud-water separation, mud cake outward transport disposition are realized, filtrate is transported to alkali tune flocculation Filtrate reaction unit in system;
The rear end of the alkali tune flocculation system is connected with filtration system;The rear end of the filtration system and acid-base neutralization system It is connected;The rear end of the acid-base neutralization system is connected with water treatment system.
Further, the sludge conditioning system includes a sludge conditioning pond, and the sludge conditioning pond is equipped with inorganic coagulation Agent and organic flocculant dosing mouth, for adding conditioning medicament;Sludge conditioning pond hiccup also sets agitating device, will improve medicine Agent is uniformly mixed with sludge.
Further, the alkali tune flocculation system includes filtrate reaction unit, and stirring is equipped in the filtrate reaction unit Device is precipitated the precipitation by metallic ion such as iron in filtrate, aluminium, calcium by adding basic agent in filtrate reaction unit, and leads to Crossing addition organic flocculant makes sediment flocculation at bulky grain floc sedimentation.
Further, the filtration system includes filter plant, and the filter plant is above-mentioned by metal ion for retaining The bulky grain floc sedimentation to flocculate is precipitated, metal ion in filtrate is removed, cleaner liquid is obtained.
Further, the sludge high-drying dewatering system includes dehydration equipment and auxiliary device composition, the dehydration equipment For one of plate and frame type filter-press, membrane filter press, vacuum drying formula filter press.
The invention has the following advantages:
1, the present invention improves dewatering performance of sludge by addition inorganic coagulant and organic flocculant, in conjunction with plate compression etc. Dehydration equipment is, it can be achieved that sludge high-drying is dehydrated;
2, for the present invention by pre-processing to dehydration filtrate, concentration of metal ions in removal filtrate reduces filtrate hardness, The load with film unit water treatment system is advantageously reduced, membrane flux is improved.
3, present invention process is reasonable, by dehydration equipment and adjust dehydration filtrate pH filtrate is pre-processed, investment and Operating cost is low and easily controllable.
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 sludge high-drying dehydration and dehydration filtrate pretreating process flow chart of the invention;
Fig. 2 is sludge high-drying dehydration and dehydration filtrate pretreatment system block diagram of the invention.
Specific embodiment
To keep purpose, process program and the advantage of embodiment of the present invention clearer, below with reference to the embodiment of the present invention The technical solution in embodiment of the present invention is clearly and completely described with attached drawing, it is clear that described embodiment is this Invent a part of embodiment, rather than whole embodiments.
Fig. 2, a kind of dehydration of shown sludge high-drying and dehydration filtrate pretreatment system, including sludge conditioning system, sludge are high Dry dewatering system, alkali tune flocculation system, filtration system, acid-base neutralization system and water treatment system;
Sludge conditioning system front end is connected with water treatment system, and for extracting excess sludge, rear end and sludge high-drying are dehydrated System is connected, for providing conditioned sludge;
Sludge high-drying dewatering system rear end is connected with alkali tune flocculation system;It is logical by being delivered to sludge in conditioner into dredge pump The dehydration equipment in sludge high-drying dewatering system is crossed, realizes mud-water separation, mud cake outward transport disposition, filtrate is transported to alkali tune flocculation system In filtrate reaction unit;
The rear end of alkali tune flocculation system is connected with filtration system;The rear end of filtration system is connected with acid-base neutralization system;Acid The rear end of alkali neutralization system is connected with water treatment system.
Preferably, sludge conditioning system includes a sludge conditioning pond, and sludge conditioning pond is equipped with inorganic coagulant and organic wadding Solidifying agent dosing mouth, for adding conditioning medicament;The hiccup of sludge conditioning pond also sets agitating device, and conditioning medicament is mixed with sludge It is even.
Preferably, alkali tune flocculation system includes filtrate reaction unit, agitating device is equipped in filtrate reaction unit, in filtrate The precipitation by metallic ion such as iron in filtrate, aluminium, calcium are precipitated by adding basic agent in reaction unit, and by adding organic wadding Solidifying agent makes sediment flocculation at bulky grain floc sedimentation.
Preferably, filtration system includes filter plant, and filter plant above-mentioned is flocculated for retaining by precipitation by metallic ion At bulky grain floc sedimentation, remove filtrate in metal ion, cleaner liquid is obtained.
Preferably, sludge high-drying dewatering system includes that dehydration equipment and auxiliary device form,.
Preferably, dehydration equipment and filter plant are a diaphragm type plate and frame filter press, plate and frame filter press model XMZGS300/1500-UF, filter press maximum are frequency control into dredge pump into mud pressure 1.2MPa, maximum squeeze pressure 2.0MPa Screw pump.
Shown in Fig. 1, a kind of sludge high-drying is dehydrated and dehydration filtrate pretreating process, includes the following steps:
Excess sludge is delivered to sludge conditioning pond by Pulp pump in S1, water treatment system, improves pool volume 50m3, sludge Moisture content 97%, first adds 0.62m after mixing evenly3Bisgallic acid iron stirs 20min, then adds 1.5m3Diluted concentration is 0.2% Cationic polyacrylamide stirs 5min.
S2, filter-press dehydration is carried out by the way that sludge in conditioner is delivered to diaphragm type plate and frame filter press into mud screw pump;Pressure Filter low pressure is into mud pressure 0.6Mpa, and into mud time 60min, high pressure is into mud pressure 1.2MPa, into mud time 90min, squeezing pressure Power 2.0Mpa squeezes time 90min;Pressing filtering liquid is delivered to filtrate reactor tank by submersible sewage pump through reservoir.
S3, filtrate hardness described in S2 is measured as 1958mg/L, total concentration of iron is 13.67ppm.Filtrate reacts tank volume 50m3 adds the liquid alkaline that 240L concentration is 30% into reactor tank and adjusts pH to 12, is stirring evenly and then adding into 600L diluted concentration It is stirred evenly for 0.2% polyacrylamide.
S4, above-mentioned pressing filtering liquid is filtered by being delivered to plate and frame filter press into mud screw pump, twice pressing after filtering, squeezing pressure Power 2.0Mpa squeezes time 30min;Moisture content of the cake 58% after filters pressing, secondary filtrate are conveyed through clean solution tank by submersible sewage pump To water treatment system, adds concentrated hydrochloric acid online on pipeline and adjust back pH value to 7-8.
S5, measure secondary filtrate hardness described in S4 be 13mg/L, removal rate 99.3%;Total concentration of iron is 0.02ppm, is gone Except rate is 88.85%.
Wherein, bisgallic acid iron density is 1.45g/ml.
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 (9)

1. a kind of sludge high-drying dehydration and dehydration filtrate pretreating process, which comprises the steps of:
S01, pass through sludge conditioning system enhancement excess sludge dewatering;
Sludge after S02, conditioning obtains mud cake and dehydration filtrate by sludge high-drying dewatering system;
S03, dehydration filtrate make the metal ion in filtrate form wadding body through filtrate alkali tune flocculation system;
S04, wadding body is removed by filtrate filtration system, cleaner liquid is obtained;
S05, cleaner liquid is crossed by acid-base neutralization system adjusting pH to neutrality, be emitted into water treatment system.
2. a kind of sludge high-drying dehydration according to claim 1 and dehydration filtrate pretreating process, which is characterized in that described Improvement dewatering performance of sludge in S01 is specially that inorganic coagulant and organic flocculant are added in sludge conditioning pond.
3. a kind of sludge high-drying dehydration according to claim 2 and dehydration filtrate pretreating process, which is characterized in that described Inorganic coagulant dosage is the 20%-80% of over dry sludge quality;The inorganic coagulant is ferric trichloride, polyaluminum sulfate At least one of iron, ferric sulfate of polymerized silica, aluminium polychloride, bisgallic acid iron.
4. a kind of sludge high-drying dehydration according to claim 2 and dehydration filtrate pretreating process, which is characterized in that described Organic flocculant dilution ratio is 0.1%-0.4%, and the amount added after dilution to sludge conditioning pond is over dry sludge in conditioner The 100%-150% of quality.
5. a kind of sludge high-drying dehydration according to claim 1 and dehydration filtrate pretreating process, which is characterized in that described It is specifically included in S03 and first adjusts dehydration filtrate pH to 8-13 using basic agent, then added organic flocculant and obtain alkaline filter Liquid;The organic flocculant ratio is 0.1%-0.4% and the amount that adds to filtrate alkali tune flocculation system is filtrate volume 1%-2%;
Wherein, the basic agent includes sodium hydroxide, sodium carbonate, sodium bicarbonate, potassium hydroxide.
6. a kind of sludge high-drying dehydration according to claim 4 or 5 and dehydration filtrate pretreating process, which is characterized in that The organic flocculant is at least one of polyacrylamide, polyetheramine, polydimethyl diallyl ammonium chloride.
7. a kind of sludge high-drying dehydration according to claim 1 and dehydration filtrate pretreating process, which is characterized in that described Addition acid medicine is specifically included in S05 and adjusts pH to 6-9, is flowed back into water treatment system;The acid medicine includes dense salt Acid or the concentrated sulfuric acid.
8. a kind of sludge high-drying dehydration and dehydration filtrate pretreatment system, which is characterized in that high including sludge conditioning system, sludge Dry dewatering system, alkali tune flocculation system, filtration system, acid-base neutralization system and water treatment system;
The sludge conditioning system front end is connected with water treatment system, and for extracting excess sludge, rear end and sludge high-drying are dehydrated System is connected, for providing conditioned sludge;
Sludge high-drying dewatering system rear end is connected with alkali tune flocculation system;It is logical by being delivered to sludge in conditioner into dredge pump The dehydration equipment in sludge high-drying dewatering system is crossed, realizes mud-water separation, mud cake outward transport disposition, filtrate is transported to alkali tune flocculation system In filtrate reaction unit;
The rear end of the alkali tune flocculation system is connected with filtration system;The rear end of the filtration system and acid-base neutralization system phase Even;The rear end of the acid-base neutralization system is connected with water treatment system.
9. a kind of sludge high-drying dehydration according to claim 8 and dehydration filtrate pretreatment system, which is characterized in that described Sludge high-drying dewatering system includes dehydration equipment and auxiliary device composition, and the dehydration equipment is plate and frame type filter-press, diaphragm type One of filter press, vacuum drying formula filter press.
CN201811037531.2A 2018-09-06 2018-09-06 Sludge high-dry dehydration and dehydration filtrate pretreatment process and treatment system thereof Active CN109111081B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811037531.2A CN109111081B (en) 2018-09-06 2018-09-06 Sludge high-dry dehydration and dehydration filtrate pretreatment process and treatment system thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811037531.2A CN109111081B (en) 2018-09-06 2018-09-06 Sludge high-dry dehydration and dehydration filtrate pretreatment process and treatment system thereof

Publications (2)

Publication Number Publication Date
CN109111081A true CN109111081A (en) 2019-01-01
CN109111081B CN109111081B (en) 2021-12-14

Family

ID=64858833

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811037531.2A Active CN109111081B (en) 2018-09-06 2018-09-06 Sludge high-dry dehydration and dehydration filtrate pretreatment process and treatment system thereof

Country Status (1)

Country Link
CN (1) CN109111081B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1535321A (en) * 2001-06-29 2004-10-06 ���п�ķ�����Ϲɷݹ�˾ Method for removal of metal from aqueous solution using lime precipitation
CN104310747A (en) * 2014-10-30 2015-01-28 湖南大学 Waste drilling mud treatment process
CN104445734A (en) * 2014-11-25 2015-03-25 中国矿业大学(北京) Method and device for removing residual aluminum in mine water
JP2016221458A (en) * 2015-05-29 2016-12-28 株式会社ピーシーエス Fertilization volume reduction system of agricultural-forestry resources
CN108358431A (en) * 2018-04-28 2018-08-03 上海同臣环保有限公司 A kind of Sludge Chemical Conditioning deep dehydration method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1535321A (en) * 2001-06-29 2004-10-06 ���п�ķ�����Ϲɷݹ�˾ Method for removal of metal from aqueous solution using lime precipitation
CN104310747A (en) * 2014-10-30 2015-01-28 湖南大学 Waste drilling mud treatment process
CN104445734A (en) * 2014-11-25 2015-03-25 中国矿业大学(北京) Method and device for removing residual aluminum in mine water
JP2016221458A (en) * 2015-05-29 2016-12-28 株式会社ピーシーエス Fertilization volume reduction system of agricultural-forestry resources
CN108358431A (en) * 2018-04-28 2018-08-03 上海同臣环保有限公司 A kind of Sludge Chemical Conditioning deep dehydration method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
郭宇杰等主编: "《工业废水处理工程》", 31 October 2016, 华东理工大学出版社 *

Also Published As

Publication number Publication date
CN109111081B (en) 2021-12-14

Similar Documents

Publication Publication Date Title
CN204824453U (en) Desulfurization pretreatment of water device that gives up
CN103964609A (en) Membrane treatment method of landfill leachate concentrate
CN104803504A (en) Novel desulfurization waste water treatment method
CN108892276A (en) A kind of waste water treatment system and its method of lead refinery
JP3248188B2 (en) Organic sludge dewatering method
CN109111081A (en) A kind of dehydration of sludge high-drying and dehydration filtrate pretreating process and its processing system
JPS58146499A (en) Improved treating method and apparatus of physical-chemical waste material
CN207986882U (en) A kind of rubbish percolation liquid membrane filtering and concentrating liquid processing device
CN215756976U (en) Sludge deep dehydration processing system
CN109626638A (en) A kind for the treatment of process of high P content waste water Zero-discharge reuse
CN205933496U (en) Desulfurization waste water zero release processing apparatus based on electrodialysis
CN211896410U (en) Desulfurization waste water resource recovery system
JPS6054797A (en) Treatment of sludge
CN209456210U (en) One kind is for the personal reasonable reclaiming system of water of Boiler water Feeding System
JPH04190891A (en) Treating method for rice cleansing waste water
CN210683418U (en) Landfill leachate and landfill leachate membrane concentrated solution zero discharge and water recovery device
CN219670293U (en) Waste water treatment device
CN220412999U (en) Metallurgical wastewater recycling device utilizing cation exchanger
JP5723916B2 (en) Method and apparatus for dewatering organic sludge
CN110054317A (en) A kind of processing method of the highly concentrated waste liquid generated in wiring board manufacture
CN210855783U (en) Sludge on-line conditioning and concentrating system
JP2001321795A (en) Liquid cleaning apparatus
CN217127133U (en) Calcium fluoride effluent disposal system
JPH05317896A (en) Dehydration treatment of sewage
JP2005007246A (en) Treatment method for organic waste water

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CP02 Change in the address of a patent holder
CP02 Change in the address of a patent holder

Address after: No. 3966, Qimen Road, Baohe District, Hefei, Anhui Province, 230009

Patentee after: ANHUI TONGYUAN ENVIRONMENT ENERGY SAVING Co.,Ltd.

Address before: 230022 no.856, Jinzhai South Road, Baohe District, Hefei City, Anhui Province

Patentee before: ANHUI TONGYUAN ENVIRONMENT ENERGY SAVING Co.,Ltd.