CN108503124A - A kind of zero discharge of industrial waste water processing method - Google Patents
A kind of zero discharge of industrial waste water processing method Download PDFInfo
- Publication number
- CN108503124A CN108503124A CN201710378111.XA CN201710378111A CN108503124A CN 108503124 A CN108503124 A CN 108503124A CN 201710378111 A CN201710378111 A CN 201710378111A CN 108503124 A CN108503124 A CN 108503124A
- Authority
- CN
- China
- Prior art keywords
- waste water
- processing method
- tank
- zero discharge
- water
- 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
Links
- 239000010842 industrial wastewater Substances 0.000 title claims abstract description 15
- 238000003672 processing method Methods 0.000 title claims abstract description 13
- 239000002351 wastewater Substances 0.000 claims abstract description 31
- 238000011282 treatment Methods 0.000 claims abstract description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 22
- 230000020477 pH reduction Effects 0.000 claims abstract description 17
- 230000007062 hydrolysis Effects 0.000 claims abstract description 14
- 238000006460 hydrolysis reaction Methods 0.000 claims abstract description 14
- 238000004659 sterilization and disinfection Methods 0.000 claims abstract description 10
- 230000015556 catabolic process Effects 0.000 claims abstract description 9
- 238000006731 degradation reaction Methods 0.000 claims abstract description 9
- 239000005416 organic matter Substances 0.000 claims abstract description 8
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 18
- 239000007788 liquid Substances 0.000 claims description 18
- 238000004062 sedimentation Methods 0.000 claims description 18
- 244000005700 microbiome Species 0.000 claims description 7
- 238000000926 separation method Methods 0.000 claims description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- 238000006386 neutralization reaction Methods 0.000 claims description 6
- 238000001556 precipitation Methods 0.000 claims description 6
- 230000001954 sterilising effect Effects 0.000 claims description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 5
- 239000001301 oxygen Substances 0.000 claims description 5
- 229910052760 oxygen Inorganic materials 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 4
- GNFTZDOKVXKIBK-UHFFFAOYSA-N 3-(2-methoxyethoxy)benzohydrazide Chemical compound COCCOC1=CC=CC(C(=O)NN)=C1 GNFTZDOKVXKIBK-UHFFFAOYSA-N 0.000 claims description 3
- 238000005273 aeration Methods 0.000 claims description 3
- 239000000919 ceramic Substances 0.000 claims description 3
- 150000001875 compounds Chemical class 0.000 claims description 3
- 230000000593 degrading effect Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 3
- 230000035764 nutrition Effects 0.000 claims description 3
- 235000016709 nutrition Nutrition 0.000 claims description 3
- FGUUSXIOTUKUDN-IBGZPJMESA-N C1(=CC=CC=C1)N1C2=C(NC([C@H](C1)NC=1OC(=NN=1)C1=CC=CC=C1)=O)C=CC=C2 Chemical compound C1(=CC=CC=C1)N1C2=C(NC([C@H](C1)NC=1OC(=NN=1)C1=CC=CC=C1)=O)C=CC=C2 FGUUSXIOTUKUDN-IBGZPJMESA-N 0.000 claims description 2
- 238000009395 breeding Methods 0.000 claims description 2
- 230000001488 breeding effect Effects 0.000 claims description 2
- 230000015572 biosynthetic process Effects 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 19
- 230000008569 process Effects 0.000 abstract description 13
- 230000008901 benefit Effects 0.000 abstract description 6
- 238000004140 cleaning Methods 0.000 abstract description 5
- 238000005189 flocculation Methods 0.000 abstract description 5
- 230000016615 flocculation Effects 0.000 abstract description 5
- 239000013049 sediment Substances 0.000 abstract description 5
- 238000009287 sand filtration Methods 0.000 abstract description 4
- 230000001351 cycling effect Effects 0.000 abstract description 3
- 238000011026 diafiltration Methods 0.000 abstract description 2
- 238000004065 wastewater treatment Methods 0.000 description 4
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 239000012528 membrane Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 230000003851 biochemical process Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000001311 chemical methods and process Methods 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000033116 oxidation-reduction process Effects 0.000 description 1
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000009279 wet oxidation reaction Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/04—Disinfection
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/1236—Particular type of activated sludge installations
- C02F3/1268—Membrane bioreactor systems
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
Abstract
The invention discloses a kind of zero discharge of industrial waste water processing methods, include the following steps:a:Waste water is just heavy;b:Hydrolysis acidification processing;c:Flocculation sediment;d:Organic matter degradation and nitrification processing;e:Biological film process;f:Diafiltration;g:Water outlet.The present invention to the processes such as first heavy, hydrolysis acidification, flocculation sediment, the organic matter degradation of waste water, disinfection, sand filtration by carrying out integrated treatment, and rear fully recovering up to standard is handled to cleaning process, realize zero-emission and the cycling and reutilization of waste water, economical environment-protective, the cost input of enterprise is greatly reduced, convenient for improving the economic benefit and social benefit of enterprise.
Description
Technical field
The present invention relates to Industrial Wastewater Treatment, resource recycling, technical field of energy saving and environmental protection, more particularly, to one kind
Zero discharge of industrial waste water processing method.
Background technology
Industry has the characteristics that scale is big, quantity of wastewater effluent is more, and the hydraulic loading of industrial wastewater and organic loading are all
It is higher, strongly to the pollution of environment, the eutrophication of water body can be especially caused, the self-purification capacity of water body is destroyed.If no
Waste water is timely handled, environment can be caused greatly to pollute.
Have at present for the processing method of bio-refractory organic wastewater generally used:Physico-chemical process, such as:Coagulating sedimentation
(Air supporting)Method, membrane separation process, air lift blow-off method, extraction etc.;Biochemical process, such as:Aerobic activated sludge process, PAM- activated sludge
Method, anaerobism-aerobic process and membrane bioreactor etc.;Chemical method, such as:Oxidation-reduction method, wet oxidation process, chemistry burn
Method etc..However it only with certain above-mentioned wastewater treatment method or unreasonable combining above-mentioned wastewater treatment method and is obtaining
In the case of waste water treatment process, ideal effect can not be obtained in practical applications.
Therefore in view of the above-mentioned problems, the present invention provides a kind of new technical solutions.
Invention content
The object of the present invention is to provide a kind of zero discharge of industrial waste water processing method, by industrial wastewater it is first it is heavy,
The processes such as hydrolysis acidification, flocculation sediment, organic matter degradation, disinfection, sand filtration carry out integrated treatment and fully recovering to cleaning process,
Realize the zero-emission of waste water, cost-effective input.
Used technical solution is the present invention in view of the above technical defects:
A kind of zero discharge of industrial waste water processing method, includes the following steps:
a:Waste water introducing primary sedimentation tank is pre-processed, pretreatment time 2-4h;
b:Waste water in step a after primary sedimentation tank is pretreated is introduced into anaerobic hydrolysis acidification tank, the anaerobic hydrolysis acidification tank
It is provided with microorganism porous ceramics reactor, adds and breeds into anaerobic hydrolysis acidification tank and be used to form the compound micro- of biomembrane
Acidification is hydrolyzed in biology;
c:Flocculant is added in the liquid after step b is processed to be precipitated, sedimentation time 2-5h, and is continuously added
NaOH or H2SO4To adjust acid-base value;
d:Liquid of the step c after processed is introduced into neutralization pond+biological nutrition liquid pool, hydrochloric acid is added into neutralization pond and adjusts waste water
PH adds and breeds aerobic and oxygen complex microorganism to 6-9, and is aided with aeration and carries out organic matter degradation and nitrification processing,
To the COD contents in degrading waste water, time 45-60min;
e:Liquid after step d degradation treatments is introduced into biomembrane processor, and the film of biomembrane processor is discharged and is introduced
Ultraviolet ray disinfector carries out sterilization treatment;
f:It will pass through by the middle water after sterilization treatment in step e and relay water tank introducing multimedium air bump rinse operation little Chi, use
More medium filter, chamber filter press and chemicals dosing plant centering water is filtered, is separated by solid-liquid separation and purified treatment;
g:Step g is discharged by the middle water after purified treatment by middle water tank, realizes the zero-emission of waste water.
Further, the pretreatment operation of the waste water in step a in preliminary sedimentation tank is:Into preliminary sedimentation tank be added PAC, PAM and
CaO so that the suspended matter removal in waste water, and it is continuously added NaOH or H2SO4To adjust acid-base value.
Further, the precipitation generated in step c is transported to the precipitation generated with primary sedimentation tank in chamber filter press and carries out
Solid-liquid separation treatment forms mud cake.
Further, the aerobic and oxygen complex microorganism for adding and breeding in step d is H type high efficiency composition floras.
Further, in step f the job content of more medium filter include just wash, gas backwash and water backwash.
The beneficial effects of the invention are as follows:The present invention is dropped by first heavy, hydrolysis acidification, flocculation sediment, the organic matter to waste water
The processes such as solution, disinfection, sand filtration carry out integrated treatment, and handle rear fully recovering up to standard to cleaning process, realize the zero of waste water
Discharge and cycling and reutilization, economical environment-protective, greatly reduce the cost input of enterprise, convenient for improving economic benefit and the society of enterprise
It can benefit.
Specific implementation mode
In order to deepen the understanding of the present invention, below in conjunction with embodiment, the invention will be further described, the embodiment
It is only used for explaining the present invention, not restrict the protection scope of the present invention.
A kind of zero discharge of industrial waste water processing method, includes the following steps:
a:Waste water introducing primary sedimentation tank is pre-processed, PAC, PAM and CaO are added into preliminary sedimentation tank so that the suspension in waste water
Object removes, and is continuously added NaOH or H2SO4To adjust acid-base value, pretreatment time 2-4h;
b:Waste water in step a after primary sedimentation tank is pretreated is introduced into anaerobic hydrolysis acidification tank, the anaerobic hydrolysis acidification tank
It is provided with microorganism porous ceramics reactor, adds and breeds into anaerobic hydrolysis acidification tank and be used to form the compound micro- of biomembrane
Acidification is hydrolyzed in biology;
c:Flocculant is added in the liquid after step b is processed to be precipitated, sedimentation time 2-5h, and is continuously added
NaOH or H2SO4To adjust acid-base value, at the same the precipitation generated be transported to the precipitation that is generated with primary sedimentation tank in chamber filter press into
Row solid-liquid separation treatment forms mud cake;
d:Liquid of the step c after processed is introduced into neutralization pond+biological nutrition liquid pool, hydrochloric acid is added into neutralization pond and adjusts waste water
PH adds and breeds aerobic and oxygen H type high efficiency composition floras to 6-9, and is aided with aeration and carries out organic matter degradation and nitre
Change is handled, to the COD contents in degrading waste water, time 45-60min;
e:Liquid after step d degradation treatments is introduced into biomembrane processor, and the film of biomembrane processor is discharged and is introduced
Ultraviolet ray disinfector carries out sterilization treatment;
f:It will pass through by the middle water after sterilization treatment in step e and relay water tank introducing multimedium air bump rinse operation little Chi, use
More medium filter, chamber filter press and chemicals dosing plant centering water is filtered, is separated by solid-liquid separation and purified treatment, wherein be situated between more
The job content of mass filter include just wash, gas backwash and water backwash can significantly improve middle water using a variety of cleaning ways
Diafiltration effect;
g:Step g is discharged by the middle water after purified treatment by middle water tank, realizes the zero-emission of waste water.
The beneficial effects of the invention are as follows:The present invention is dropped by first heavy, hydrolysis acidification, flocculation sediment, the organic matter to waste water
The processes such as solution, disinfection, sand filtration carry out integrated treatment, and handle rear fully recovering up to standard to cleaning process, realize the zero of waste water
Discharge and cycling and reutilization, economical environment-protective, greatly reduce the cost input of enterprise, convenient for improving economic benefit and the society of enterprise
It can benefit.
It these are only the preferred embodiment of the present invention, be not intended to restrict the invention, for those skilled in the art
For member, the invention may be variously modified and varied.Any modification made by all within the spirits and principles of the present invention,
Equivalent replacement, improvement etc., should all be included in the protection scope of the present invention.
Claims (5)
1. a kind of zero discharge of industrial waste water processing method, it is characterised in that:Include the following steps:
a:Waste water introducing primary sedimentation tank is pre-processed, pretreatment time 2-4h;
b:Waste water in step a after primary sedimentation tank is pretreated is introduced into anaerobic hydrolysis acidification tank, the anaerobic hydrolysis acidification tank
It is provided with microorganism porous ceramics reactor, adds and breeds into anaerobic hydrolysis acidification tank and be used to form the compound micro- of biomembrane
Acidification is hydrolyzed in biology;
c:Flocculant is added in the liquid after step b is processed to be precipitated, sedimentation time 2-5h, and is continuously added
NaOH or H2SO4To adjust acid-base value;
d:Liquid of the step c after processed is introduced into neutralization pond+biological nutrition liquid pool, hydrochloric acid is added into neutralization pond and adjusts waste water
PH adds and breeds aerobic and oxygen complex microorganism to 6-9, and is aided with aeration and carries out organic matter degradation and nitrification processing,
To the COD contents in degrading waste water, time 45-60min;
e:Liquid after step d degradation treatments is introduced into biomembrane processor, and the film of biomembrane processor is discharged and is introduced
Ultraviolet ray disinfector carries out sterilization treatment;
f:It will pass through by the middle water after sterilization treatment in step e and relay water tank introducing multimedium air bump rinse operation little Chi, use
More medium filter, chamber filter press and chemicals dosing plant centering water is filtered, is separated by solid-liquid separation and purified treatment;
g:Step g is discharged by the middle water after purified treatment by middle water tank, realizes the zero-emission of waste water.
2. a kind of zero discharge of industrial waste water processing method according to claim 1, it is characterised in that:Preliminary sedimentation tank in step a
The pretreatment operation of interior waste water is:PAC, PAM and CaO are added into preliminary sedimentation tank so that the suspended matter removal in waste water, not
It is disconnected that NaOH or H is added2SO4To adjust acid-base value.
3. a kind of zero discharge of industrial waste water processing method according to claim 1, it is characterised in that:It is generated in step c
Precipitation is transported to the precipitation generated with primary sedimentation tank in chamber filter press and carries out solid-liquid separation treatment formation mud cake.
4. a kind of zero discharge of industrial waste water processing method according to claim 1, it is characterised in that:It is added in step d
Aerobic and oxygen complex microorganism with breeding is H type high efficiency composition floras.
5. a kind of zero discharge of industrial waste water processing method according to claim 1, it is characterised in that:Multimedium in step f
The job content of filter include just wash, gas backwash and water backwash.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710378111.XA CN108503124A (en) | 2017-05-25 | 2017-05-25 | A kind of zero discharge of industrial waste water processing method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710378111.XA CN108503124A (en) | 2017-05-25 | 2017-05-25 | A kind of zero discharge of industrial waste water processing method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN108503124A true CN108503124A (en) | 2018-09-07 |
Family
ID=63374432
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710378111.XA Pending CN108503124A (en) | 2017-05-25 | 2017-05-25 | A kind of zero discharge of industrial waste water processing method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108503124A (en) |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101830601A (en) * | 2010-04-30 | 2010-09-15 | 浙江大学 | Biological treatment system and method thereof specific to industrial wastewater of fluorescent brightener |
CN104743737A (en) * | 2014-11-28 | 2015-07-01 | 广州新滔水质净化有限公司 | Industrial printing and dyeing wastewater treatment method |
CN205990325U (en) * | 2016-08-31 | 2017-03-01 | 济南市市政工程设计研究院(集团)有限责任公司 | A kind of Coal Chemical Industry, the processing system of mining industry waste water |
-
2017
- 2017-05-25 CN CN201710378111.XA patent/CN108503124A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101830601A (en) * | 2010-04-30 | 2010-09-15 | 浙江大学 | Biological treatment system and method thereof specific to industrial wastewater of fluorescent brightener |
CN104743737A (en) * | 2014-11-28 | 2015-07-01 | 广州新滔水质净化有限公司 | Industrial printing and dyeing wastewater treatment method |
CN205990325U (en) * | 2016-08-31 | 2017-03-01 | 济南市市政工程设计研究院(集团)有限责任公司 | A kind of Coal Chemical Industry, the processing system of mining industry waste water |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
TWI516454B (en) | Treatment for molasses spent wash and other wastewaters | |
CN100500594C (en) | Method for treating paper making sewage | |
CN111018187A (en) | Wastewater treatment process based on Fenton oxidation reaction | |
CN1792880A (en) | Tech. for treating waste water of fruit juice processing | |
CN102659281B (en) | Treatment method of liquor production wastewater | |
CN102174763A (en) | Treatment method for paper making waste water | |
KR20090064996A (en) | Method of water treatment | |
CN105776726A (en) | Treatment process of printing and dyeing wastewater in textile industry | |
CN102515435A (en) | Method for processing silicon carbide industrial wastewater | |
CN103739144A (en) | Detergent synthesis wastewater treatment technology | |
CN213623721U (en) | Hydrogen peroxide solution waste water processing system | |
CN111410334B (en) | Method for quickly recycling wastewater produced by crushing and cleaning line of dangerous waste plastic packaging container | |
KR20040002594A (en) | Liquid treatment method and apparatus | |
CN109422412A (en) | A kind of Integrated Processing Unit of coating waste-water and sanitary sewage | |
CN110395856A (en) | A kind of processing method of electrophoretic-coating wastewater | |
CN207031193U (en) | A kind of system for handling chlorine industry PVC polymeric mother liquid wastewater zero discharges | |
CN108503124A (en) | A kind of zero discharge of industrial waste water processing method | |
CN215559636U (en) | Wastewater treatment system | |
CN115367969A (en) | High-concentration water-based ink wastewater treatment method and treatment system | |
CN210457829U (en) | Landfill leachate's treatment facility | |
CN210945112U (en) | Leachate treatment system and pretreatment device for reducing inflow suspended matters and sulfides | |
CN103172224A (en) | Surface treatment wastewater reusing treatment technology | |
CN114105395A (en) | Garbage leachate wastewater treatment process | |
CN106745917A (en) | The process for purifying water of physics and chemistry water purifier at a kind of pickling waste waters | |
CN107265785A (en) | Paper-making industry advanced waste treatment system and its processing method |
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 | ||
WD01 | Invention patent application deemed withdrawn after publication | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20180907 |