CN106430567A - Technology for treating organic wastewater by means of efficient anaerobic reactor - Google Patents
Technology for treating organic wastewater by means of efficient anaerobic reactor Download PDFInfo
- Publication number
- CN106430567A CN106430567A CN201610945501.6A CN201610945501A CN106430567A CN 106430567 A CN106430567 A CN 106430567A CN 201610945501 A CN201610945501 A CN 201610945501A CN 106430567 A CN106430567 A CN 106430567A
- Authority
- CN
- China
- Prior art keywords
- reactor
- organic wastewater
- anaerobic
- water
- preposition pre
- 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
Links
Classifications
-
- 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
- C02F3/286—Anaerobic digestion processes including two or more steps
-
- 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
- C02F3/2866—Particular arrangements for anaerobic reactors
- C02F3/2873—Particular arrangements for anaerobic reactors with internal draft tube circulation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/06—Nutrients for stimulating the growth of microorganisms
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Microbiology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
The invention provides a technology for treating organic wastewater by means of an efficient anaerobic reactor. The technology comprises the following steps of 1 water charging, 2 treating conducted in a front pre-reactor, 3 material feeding, 4 treating conducted in a main reactor, 5 water discharging, 6 biogas collecting and 7 sludge collecting. According to the technology, efficient anaerobic treatment is conducted on the high-concentration organic wastewater by adopting the technology of combining the front pre-reactor with the anaerobic main reactor, therefore, the removal rate of COD in effluent is higher than 92%, and the working efficiency of the technology is greatly improved.
Description
Technical field
Patent of the present invention is related to technical field for the treatment of of organic waste, and particularly a kind of high efficiency anaerobic reactor processes organic waste
The technique of water.
Background technology
With the reach of science, the deepening continuously of scientific research, many new technologies, new material, new concept is widely used in ring
Industry is protected in border, makes the significant progress that China environmental protection technology obtains.Food, brewage, pharmacy, the discharge of the industry such as chemical industry big
Effluent part broadly falls into high concentrated organic wastewater, reaches processing intent using conventional materialization, biochemical treatment difficulty, there is behaviour simultaneously
Manage, investment is big, operating cost is high to wait a system problem.
High concentrated organic wastewater is processed using anaerobic process, its superiority progressively obtains recognizing and paying attention to, in recent years of people
Anaerobic technology is developed quickly, and in UASB anaerobic treatment process equipment, upward flow anaerobic sludge comes with its simple structure, process
Efficiency high, effect are good, applied widely, floor space is little, processing cost is low, reduced investment and adopted in a large number.
First generation anaerobic reactor with anaerobic digester as representative, due to cannot be to hydraulic detention time and sludge retention
Temporal separation, causes to process the time of staying at least 20-30d of waste water, therefore treatment effeciency is extremely low.
In the 60-70 age in 20th century, occur in that second generation anaerobic reactor with UASB as representative it is achieved that during hydraulic retention
Between and sludge retention time separation.Thus improve the concentration of mud in reactor.The top setting gas of UASB reactor,
Solid, liquid three phase separator, bottom is sludge suspension floor area and Sludge Bed area, and waste water uniformly pumps into Sludge Bed by reactor bottom
Area, is fully contacted reaction with anaerobic sludge, and organic matter is resolved into biogas by anaerobe.Liquid, gas and solid form mixed
Close liquor stream and rise to three phase separator, so that three is separated well, make more than 80 organic matter be converted into biogas, complete to give up
Water treatment procedure.The formation that its advantage is mainly reflected in granule sludge makes the sludge concentration in reactor increase substantially, waterpower
The time of staying therefore greatly shortens, thus improving operational efficiency.
Efficient anaerobic reactor, in addition to ensureing hydraulic detention time and sludge retention time, also will ensure that both are abundant
Mixing, but simple mixing occurs the present of sludge loss.Therefore, the nineties in 20th century, have developed with EGSB as representative
Third generation anaerobic reactor.Its construction with UASB reactor have similarity, can be divided into into water water distribution system, reaction zone,
Three-phase separation area and outlet canal system.It is a difference in that with UASB reactor, EGSB reactor is provided with special effluent recycling system
System.EGSB reactor is generally cylindric turriform, and feature is that have very big ratio of height to diameter, and typically up to 3~5, process units is anti-
The height answering device is up to 15~20 meters.The expanded bed of granule sludge improves the contact between useless Organic substance in water and microorganism,
Enhance mass transfer effect, improve the biochemical reaction speed of reactor, thus substantially increasing the treatment efficiency of reactor.But
It is that the water at anaerobic reactor top flows to bottom, is uniformly flowed back by water distributor, flow velocity is too high, mud is easy to run off, operational effect is not
Stable.
Content of the invention
The purpose of the present invention is exactly to high concentration by the group technology using preposition pre-reactor and anaerobism main reactor
Organic wastewater carries out efficient anaerobic process so that the COD clearance in water outlet is more than 92%, and organic loading is up to 15~30Kg/
m3.d, substantially increase its operating efficiency.
For solving above-mentioned technical problem, the invention provides a kind of high efficiency anaerobic reactor processes the work of organic wastewater
Skill, its step is as follows
S1:Water inlet:Organic wastewater is delivered in preposition pre-reactor;
S2:Preposition pretreatment:Convey organic wastewater while to preposition pre-reactor in add nutritional agents, defoamer
And alkali, improve activity and the COD clearance of microorganism, organic wastewater can be useless with main reactor backflow in preposition pre-reactor
Water, biogas are fully mixed in the presence of circulating pump, carry out initial hydrolysis acidifying degradation water in the presence of amphimicrobe
In COD, using backflow biogas can effectively deviate from waste water overflow pernicious gas;
S3:Feeding:Start feed pump to convey the mixed liquor being formed in step S2 in main reactor;
S4:Main reactor is processed:Mixed liquor enters in the first anaerobic reaction area from the bottom of main reactor, with the first anaerobism
Granule sludge in reaction zone is fully contacted and carries out anaerobic reaction, then carries out separating by the first three phase separator, after separating
Waste water go successively to the second anaerobic reaction area, using 3 D elastic filler make the abundant blending of activated sludge, water, biogas contact hand over
Change, then carry out separation, the effluent part after 3 D elastic filler physical absorption and warp using the second three phase separator
Cross the first three phase separator and biogas that the second three phase separator collects conveys into preposition by return duct and gas distribution pipe respectively
In pre-reactor, the pernicious gas (hydrogen sulfide) in removing water, the equal Heshui matter of stirring;
S5:Water outlet:Current after three phase separator twice separates are by the top being connected with outlet pipe in step s 4
Portion's collecting system delivers into discharge bay after collecting;
S6:Collecting methane:Biogas produced in step S2 and step S4 and pernicious gas are passed through preposition pre- anti-
The gas outlet answering device and anaerobic reactor top conveys and is stored in tank for sewage gas;
S7:Mud is collected:By starting sludge pump, the mud of the first anaerobic reaction area inner bottom part is conveyed into mud storage tank
Inside carry out concentrating, stabilize.
Further:Described nutritional agents composition is to be made up of N, P and trace heavy metal element, makes the C in waste water:N:P=
300~500:5:1, described trace heavy metal element has potassium, Calcium Magnesium Sulphur, iron, nickel, cobalt, molybdenum, zinc, manganese, copper.
Further:Described defoamer is polyethers defoamer, and dosage is less than 5mg/L.
Further:Described alkali is sodium carbonate, adjusts waste water PH between 6.5~7.5 by adding sodium carbonate.
Further:Described 3 D elastic filler is polyamide-based 3 D elastic filler.
Further:Described nutritional agents, defoamer, alkali and waste water mix in preposition pre-reactor during temperature
Degree controls at 30~40 degree, and Stress control is in below 10KPa.
Further:A kind of structure bag of the described device of technique processing organic wastewater using high efficiency anaerobic reactor
Include
Preposition pre-reactor, the described side wall of preposition pre-reactor is connected with waste water feed tube, and described is preposition pre-
Discharging opening is offered on the side wall of reactor lower end, the top of described preposition pre-reactor offers the first gas outlet,
Circulation pipe, described one end of circulation pipe is connected with the discharging opening of preposition pre-reactor, described circulation pipe another
One end is connected on the side wall of preposition pre-reactor upper end, and described circulation pipe is also equipped with circulating pump,
Main reactor, the bottom of described main reactor offers charging aperture, described charging aperture pass through feed pipe with front
The discharging opening putting pre-reactor is connected, and described feed pipe is provided with feed pump, in described main reactor from the bottom up
It is disposed with the first anaerobic reaction area, the first three phase separator, the second anaerobic reaction area and the second three phase separator, described
It is additionally provided with packing layer in second anaerobic reaction area, in described packing layer, be filled with polyamide-based 3 D elastic filler, described
The side wall of main reactor upper end on be connected with outlet pipe, described outlet pipe is connected with the effluent trough in preposition pre-reactor
Logical, described effluent trough is connected with discharge bay, and the top of described anaerobic reactor offers the second gas outlet,
Gas distribution pipe, described gas distribution pipe is provided with two, one end of described two gas distribution pipes respectively with main reactor in
Two three phase separators be connected, the other end of two described gas distribution pipes is connected on the side wall of preposition pre-reactor,
Tank for sewage gas, described tank for sewage gas is connected with the first methane outlet and the second methane outlet by pipeline respectively,
Mud storage tank, described mud storage tank passes through the first anaerobic reaction area phase of sludge out pipe and bottom in main reactor
Connection, described sludge out pipe is provided with granule sludge pump.
Using above-mentioned design the device have the advantages that as follows:
A, whole system outer circulation design system are stable, anti impulsion load;
B, occupation of land are few, and gas collection is convenient;
C, structure are simple, and maintenance is few;
The hermetically sealed malleation of D, package unit designs, and can save gas-liquid separator, tank for sewage gas;
The unique design of E, anaerobic reactor and operation control, and organic loading is up to 15~30Kg/m3.d, sulfur-bearing is given up
Water, high-ammonia wastewater have stronger adaptability and treatment effect;
F, efficient clearance, the actual clearance of COD reaches more than 92%, improves granule sludge and biogas output.
Brief description
The present invention is further detailed explanation with reference to the accompanying drawings and detailed description.
Fig. 1 is the structural representation of the present invention.
Specific embodiment
The invention provides a kind of high efficiency anaerobic reactor processes the technique of organic wastewater, its step is as follows
S1:Water inlet:Organic wastewater is delivered in preposition pre-reactor;
S2:Preposition pretreatment:Convey organic wastewater while to preposition pre-reactor in add nutritional agents, defoamer
And alkali, improve activity and the COD clearance of microorganism, organic wastewater can be useless with main reactor backflow in preposition pre-reactor
Water, biogas are fully mixed in the presence of circulating pump, carry out initial hydrolysis acidifying degradation water in the presence of amphimicrobe
In COD, using backflow biogas can effectively deviate from waste water overflow pernicious gas;
S3:Feeding:Start feed pump to convey the mixed liquor being formed in step S2 in main reactor;
S4:Main reactor is processed:Mixed liquor enters in the first anaerobic reaction area from the bottom of main reactor, with the first anaerobism
Granule sludge in reaction zone is fully contacted and carries out anaerobic reaction, then carries out separating by the first three phase separator, after separating
Waste water go successively to the second anaerobic reaction area, using 3 D elastic filler make the abundant blending of activated sludge, water, biogas contact hand over
Change, then carry out separation, the effluent part after 3 D elastic filler physical absorption and warp using the second three phase separator
Cross the first three phase separator and biogas that the second three phase separator collects conveys into preposition by return duct and gas distribution pipe respectively
In pre-reactor, the pernicious gas (hydrogen sulfide) in removing water, the equal Heshui matter of stirring;
S5:Water outlet:Current after three phase separator twice separates are by the top being connected with outlet pipe in step s 4
Portion's collecting system delivers into discharge bay after collecting;
S6:Collecting methane:Biogas produced in step S2 and step S4 and pernicious gas are passed through preposition pre- anti-
The gas outlet answering device and anaerobic reactor top conveys and is stored in tank for sewage gas;
S7:Mud is collected:By starting sludge pump, the mud of the first anaerobic reaction area inner bottom part is conveyed into mud storage tank
Inside carry out concentrating, stabilize.
Above-mentioned nutritional agents composition is to be made up of N, P and trace heavy metal element, makes the C in waste water:N:P=300~
500:5:1, described trace heavy metal element has potassium, Calcium Magnesium Sulphur, iron, nickel, cobalt, molybdenum, zinc, manganese, copper.
Above-mentioned defoamer is polyethers defoamer, and dosage is less than 5mg/L.
Above-mentioned alkali is sodium carbonate, adjusts waste water PH between 6.5~7.5 by adding sodium carbonate.
Above-mentioned 3 D elastic filler is polyamide-based 3 D elastic filler.
During above-mentioned nutritional agents, defoamer, alkali and waste water mix in preposition pre-reactor 2, temperature control exists
30~40 degree, Stress control is in below 10KPa.
A kind of structure of the above-mentioned device of technique being processed organic wastewater using high efficiency anaerobic reactor is included
Preposition pre-reactor 2, the described side wall of preposition pre-reactor 2 is connected with waste water feed tube, described is preposition
Discharging opening is offered on the side wall of pre-reactor 2 lower end, the top of described preposition pre-reactor 2 offers the first gas outlet,
Circulation pipe, described one end of circulation pipe is connected with the discharging opening of preposition pre-reactor 2, described circulation pipe another
One end is connected on the side wall of preposition pre-reactor 2 upper end, and described circulation pipe is also equipped with circulating pump 4,
Main reactor 5, the bottom of described main reactor 5 offers charging aperture, described charging aperture pass through feed pipe with
The discharging opening of preposition pre-reactor 2 is connected, and described feed pipe is provided with feed pump 3, in described main reactor 5 under
Up it is disposed with the first anaerobic reaction area, the first three phase separator, the second anaerobic reaction area and the second three phase separator, institute
It is additionally provided with packing layer in the second anaerobic reaction area stated, in described packing layer, be filled with polyamide-based 3 D elastic filler,
Outlet pipe, the effluent trough in described outlet pipe and preposition pre-reactor are connected with the described side wall of main reactor 5 upper end
It is connected, described effluent trough is connected with discharge bay 8, the top of described anaerobic reactor 5 offers the second gas outlet,
Gas distribution pipe 10, described gas distribution pipe 10 is provided with two, and one end of two described gas distribution pipes 10 is anti-with main respectively
In device 5 two three phase separators are answered to be connected, the other end of two described gas distribution pipes 10 is connected to preposition pre-reactor 2
On the wall of side,
Tank for sewage gas 9, described tank for sewage gas 9 is connected with the first methane outlet and the second methane outlet by pipeline respectively,
Mud storage tank 7, described mud storage tank 7 passes through the first anaerobic reaction of sludge out pipe and bottom in main reactor 5
Area is connected, and described sludge out pipe is provided with granule sludge pump 6.
Raw water initially enters preposition pre-reactor, the waste water (capacity of returns is 2~6 times of inflow) with main reactor backflow
Fully mixed in the presence of circulating pump, carried out the COD in initial hydrolysis acidifying degradation water in the presence of amphimicrobe,
The pernicious gas (as hydrogen sulfide) overflowing in waste water can effectively be deviate from using the biogas of backflow hence it is evident that main anti-device microorganism can be improved
Activity.According to water water quality property, can be optionally, it is determined whether add some nutritional agents (nutrition in preposition pre-reactor
Agent composition is constituted mainly has N, P and trace heavy metal element to constitute, and makes the C in waste water:N:P=300~500:5:1, required
Trace element mainly have potassium, Calcium Magnesium Sulphur, iron, nickel, cobalt, molybdenum, zinc, manganese, copper etc.), defoamer (be typically not added with, if waste water produce
Raw foam is excessive, can suitably add a small amount of polyethers defoamer, dosage<5mg/L), alkali (if the basicity in waste water is too low, makes
When PH in water is less than 6, can suitably add some sodium carbonate, adjustment waste water PH is between 6.5~7.5), to improve microorganism
Activity and COD clearance.
Preposition pre-reactor water outlet is promoted to main reactor through feed pump, after the water-locator uniform water distribution of bottom, and anti-
Answer the granule sludge in device to be fully contacted and carry out anaerobic reaction, the biogas of generation causes inner loop, is conducive to granule sludge
Formed.Sewage continues to rise to first order three phase separator under the effect of the pressure, carries out gas, liquid, solid three phase separation, is separated
Gas enter after collecting preposition pre-reactor (for remove the pernicious gas in waste water and stirring all and water quality);Separated
Granule sludge be back to granule sludge bed, proceed anaerobic biochemical reaction;A small amount of suspension is carried by the liquid after separation
Mud rises to the second anaerobic reaction area, is provided with polyamide-based 3 D elastic filler in this reaction zone, and this filler can make activity dirt
Mud, water, biogas abundant blending contact exchanges, and biofilm effect is good, and treatment effeciency is high.Sewage by with filler on microorganism and outstanding
The activated sludge floating in water is fully contacted, using the COD in the further degradation water of the metabolism of microorganism and
The pollutants such as removing nitrogen, phosphorus.Then current enter second level three phase separator, carry out gas, liquid, solid three phase separation again, are divided
From gas enter after collecting preposition pre-reactor (for remove the pernicious gas in waste water and stirring all and water quality);Divided
From suspended sludge be back to filler contact zone, proceed anaerobic biochemical reaction;By the liquid after separation through top collection water system
System enters discharge bay after collecting.
Preposition pre-reactor, the biogas of main reactor collected overhead, are fed directly to biogas storage tank and are stored, Wu Xuzai
Plus knockout drum, air-introduced machine because the biogas producing carry out being dehydrated in anaerobic reactor uphill process, removal of impurities;Reaction
Device running environment is pressure-fired.In main reactor, unnecessary mud is delivered to mud storage tank, carries out subsequent concentration, stabilisation, takes off
Water process.
The present invention passes through using this design, its have the beneficial effect that:(1) pass through to arrange preposition pre-reactor, can effectively increase
The buffer capacity of strong system, can remove the pernicious gas in waste water, provide a system to nutrient source, improve activity and the fall of microorganism
Solution efficiency, the objectionable impurities in removing biogas, increase the biodegradability of waste water;(2) setting sewage, biogas backflow in main reaction region
Device, improves resource utilization;(3) system running pressure is pressure-fired, decreases marsh gas treating system equipment;(4) system
Volumetric loading is very high, and COD volumetric loading is in 15~30KgCOD/m3.d and more than, be the 3 of traditional UASB anaerobic reactor load
More than times;(5) the resistance to sulfate concentration of system is high, up to more than 5000mg/L;(6) there is storage biogas function;(7) process is simple,
Treatment effect is stable and operation maintenance is relatively easily it is easy to promote in practical engineering application;(8) efficient clearance, COD is real
Border clearance reaches more than 92%, improves granule sludge and biogas output.
Claims (7)
1. a kind of high efficiency anaerobic reactor process organic wastewater technique it is characterised in that:Its step is as follows
S1:Water inlet:Organic wastewater is delivered in preposition pre-reactor;
S2:Preposition pretreatment:Convey organic wastewater while to preposition pre-reactor in add nutritional agents, defoamer and
Alkali, improves activity and the COD clearance of microorganism, and organic wastewater can be useless with main reactor backflow in preposition pre-reactor
Water, biogas are fully mixed in the presence of circulating pump, carry out initial hydrolysis acidifying degradation water in the presence of amphimicrobe
In COD, using backflow biogas can effectively deviate from waste water overflow pernicious gas;
S3:Feeding:Start feed pump to convey the mixed liquor being formed in step S2 in main reactor;
S4:Main reactor is processed:Mixed liquor enters in the first anaerobic reaction area from the bottom of main reactor, with the first anaerobic reaction
Granule sludge in area is fully contacted and carries out anaerobic reaction, then carries out separating by the first three phase separator, useless after separating
Water goes successively to the second anaerobic reaction area, so that the abundant blending of activated sludge, water, biogas is contacted using 3 D elastic filler and exchanges,
Then carry out separating using the second three phase separator, the effluent part after 3 D elastic filler physical absorption and through the
The biogas that one three phase separator and the second three phase separator collect conveys into preposition pre- anti-by return duct and gas distribution pipe respectively
Answer in device, the pernicious gas (hydrogen sulfide) in removing water, the equal Heshui matter of stirring;
S5:Water outlet:Current after three phase separator twice separates are by the top collection being connected with outlet pipe in step s 4
Water system delivers into discharge bay after collecting;
S6:Collecting methane:Biogas produced in step S2 and step S4 and pernicious gas are passed through preposition pre-reactor
And the gas outlet at anaerobic reactor top conveys and is stored in tank for sewage gas;
S7:Mud is collected:By starting sludge pump, the mud of the first anaerobic reaction area inner bottom part is conveyed to enter in mud storage tank
Row concentrates, stabilisation.
2. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
Nutritional agents composition be to be made up of N, P and trace heavy metal element, make the C in waste water:N:P=300~500:5:1, described
Trace heavy metal element has potassium, Calcium Magnesium Sulphur, iron, nickel, cobalt, molybdenum, zinc, manganese, copper.
3. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
Defoamer be polyethers defoamer, dosage be less than 5mg/L.
4. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
Alkali be sodium carbonate, by add sodium carbonate adjust waste water PH between 6.5~7.5.
5. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
3 D elastic filler be polyamide-based 3 D elastic filler.
6. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
Nutritional agents, defoamer, alkali and waste water mix in preposition pre-reactor 2 during temperature control at 30~40 degree, pressure
Power controls in below 10KPa.
7. a kind of high efficiency anaerobic reactor according to claim 1 process organic wastewater technique it is characterised in that:Described
A kind of structure of device of the technique that organic wastewater is processed using high efficiency anaerobic reactor include
Preposition pre-reactor (2), the described side wall of preposition pre-reactor (2) is connected with waste water feed tube, described is preposition
Discharging opening is offered on the side wall of pre-reactor (2) lower end, the top of described preposition pre-reactor (2) offers first and gives vent to anger
Mouthful,
Circulation pipe, described one end of circulation pipe is connected with the discharging opening of preposition pre-reactor (2), described circulation pipe another
End is connected on the side wall of preposition pre-reactor (2) upper end, and described circulation pipe is also equipped with circulating pump (4),
Main reactor (5), the bottom of described main reactor (5) offers charging aperture, described charging aperture pass through feed pipe with
The discharging opening of preposition pre-reactor (2) is connected, and described feed pipe is provided with feed pump (3), described main reactor (5)
Inside it is disposed with the first anaerobic reaction area, the first three phase separator, the second anaerobic reaction area and the second three-phase separate from the bottom up
It is additionally provided with packing layer in device, the second described anaerobic reaction area, in described packing layer, be filled with polyamide-based solid bullet
Property filler, the described side wall of main reactor (5) upper end is connected with outlet pipe, in described outlet pipe and preposition pre-reactor
Effluent trough be connected, described effluent trough is connected with discharge bay (8), and the top of described anaerobic reactor (5) offers
Two gas outlets,
Gas distribution pipe (10), described gas distribution pipe (10) is provided with two, one end of described two gas distribution pipes (10) respectively with master
Two three phase separators in reactor (5) are connected, and the other end of two described gas distribution pipes (10) is connected to preposition pre- anti-
Answer on the side wall of device (2),
Tank for sewage gas (9), described tank for sewage gas (9) is connected with the first methane outlet and the second methane outlet by pipeline respectively,
Mud storage tank (7), it is anti-with the first anaerobism of the interior bottom of main reactor (5) that described mud storage tank (7) passes through sludge out pipe
Answer area to be connected, described sludge out pipe is provided with sludge pump (6).
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610945501.6A CN106430567B (en) | 2016-10-26 | 2016-10-26 | A kind of technique of high efficiency anaerobic reactor processing organic wastewater |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610945501.6A CN106430567B (en) | 2016-10-26 | 2016-10-26 | A kind of technique of high efficiency anaerobic reactor processing organic wastewater |
Publications (2)
Publication Number | Publication Date |
---|---|
CN106430567A true CN106430567A (en) | 2017-02-22 |
CN106430567B CN106430567B (en) | 2019-10-08 |
Family
ID=58179132
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201610945501.6A Active CN106430567B (en) | 2016-10-26 | 2016-10-26 | A kind of technique of high efficiency anaerobic reactor processing organic wastewater |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106430567B (en) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106882996A (en) * | 2017-03-29 | 2017-06-23 | 上海净豚环保科技有限公司 | It is applied to micronutrient liquid of micro-organism treatment process and preparation method thereof |
CN107720957A (en) * | 2017-11-16 | 2018-02-23 | 广州市普淳环保科技有限公司 | Constant-temperatureanaerobic anaerobic processing high concentrated organic wastewater and the reaction unit and processing method of solid waste in batch-type |
CN107986439A (en) * | 2017-12-04 | 2018-05-04 | 长沙埃比林环保科技有限公司 | A kind of sewage-treatment plant |
CN108101208A (en) * | 2017-12-13 | 2018-06-01 | 同济大学 | The anaerobic in low temperature processing unit and its treatment process of a kind of high concentrated organic wastewater |
CN109319928A (en) * | 2018-12-13 | 2019-02-12 | 北京舞鹤环境工程设计有限公司 | High Fat wastewater treatment device and technique |
CN109534498A (en) * | 2018-12-29 | 2019-03-29 | 江苏索普(集团)有限公司 | A kind of biochemical treatment is organic to contain SO4 containing acid2-The processing method of waste water |
CN111573989A (en) * | 2020-05-28 | 2020-08-25 | 广西大学 | High-calcium wastewater calcification blocking treatment method and device used by same |
CN113697949A (en) * | 2021-08-20 | 2021-11-26 | 中钢集团鞍山热能研究院有限公司 | Short-flow anaerobic reactor device and high-concentration organic wastewater pretreatment method |
CN114436397A (en) * | 2022-01-14 | 2022-05-06 | 南京大学 | A processing apparatus for high concentration organic, difficult biochemical waste water |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101423292A (en) * | 2008-11-20 | 2009-05-06 | 浙江大学 | Anaerobic bioreactor for treating high concentration printing and dyeing wastewater and method thereof |
CN104291438A (en) * | 2014-08-25 | 2015-01-21 | 杭州清城能源环保工程有限公司 | Method and system for producing biogas through two-stage anaerobic processing of high-concentration waste |
CN204162506U (en) * | 2014-09-28 | 2015-02-18 | 江苏元捷环境科技有限公司 | A kind of anaerobic reactor of high salt organic waste water |
CN104671597A (en) * | 2015-01-29 | 2015-06-03 | 浦城正大生化有限公司 | Treatment process of antibiotic wastewater |
CN105776528A (en) * | 2016-03-31 | 2016-07-20 | 山东中新环境工程有限公司 | Dual-reflux efficient anaerobic reaction device and wastewater treatment method |
-
2016
- 2016-10-26 CN CN201610945501.6A patent/CN106430567B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101423292A (en) * | 2008-11-20 | 2009-05-06 | 浙江大学 | Anaerobic bioreactor for treating high concentration printing and dyeing wastewater and method thereof |
CN104291438A (en) * | 2014-08-25 | 2015-01-21 | 杭州清城能源环保工程有限公司 | Method and system for producing biogas through two-stage anaerobic processing of high-concentration waste |
CN204162506U (en) * | 2014-09-28 | 2015-02-18 | 江苏元捷环境科技有限公司 | A kind of anaerobic reactor of high salt organic waste water |
CN104671597A (en) * | 2015-01-29 | 2015-06-03 | 浦城正大生化有限公司 | Treatment process of antibiotic wastewater |
CN105776528A (en) * | 2016-03-31 | 2016-07-20 | 山东中新环境工程有限公司 | Dual-reflux efficient anaerobic reaction device and wastewater treatment method |
Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106882996A (en) * | 2017-03-29 | 2017-06-23 | 上海净豚环保科技有限公司 | It is applied to micronutrient liquid of micro-organism treatment process and preparation method thereof |
CN107720957A (en) * | 2017-11-16 | 2018-02-23 | 广州市普淳环保科技有限公司 | Constant-temperatureanaerobic anaerobic processing high concentrated organic wastewater and the reaction unit and processing method of solid waste in batch-type |
CN107720957B (en) * | 2017-11-16 | 2023-09-08 | 广州市普淳环保科技有限公司 | Reaction device and method for anaerobic treatment of high-concentration organic wastewater and solid waste at constant temperature in sequencing batch |
CN107986439A (en) * | 2017-12-04 | 2018-05-04 | 长沙埃比林环保科技有限公司 | A kind of sewage-treatment plant |
CN108101208A (en) * | 2017-12-13 | 2018-06-01 | 同济大学 | The anaerobic in low temperature processing unit and its treatment process of a kind of high concentrated organic wastewater |
CN109319928B (en) * | 2018-12-13 | 2021-09-17 | 北京舞鹤环境工程设计有限公司 | High-grease wastewater treatment device and process |
CN109319928A (en) * | 2018-12-13 | 2019-02-12 | 北京舞鹤环境工程设计有限公司 | High Fat wastewater treatment device and technique |
CN109534498B (en) * | 2018-12-29 | 2021-12-03 | 江苏索普化工股份有限公司 | Organic acid-containing SO4 for biochemical treatment2-Method for treating waste water |
CN109534498A (en) * | 2018-12-29 | 2019-03-29 | 江苏索普(集团)有限公司 | A kind of biochemical treatment is organic to contain SO4 containing acid2-The processing method of waste water |
CN111573989A (en) * | 2020-05-28 | 2020-08-25 | 广西大学 | High-calcium wastewater calcification blocking treatment method and device used by same |
CN113697949A (en) * | 2021-08-20 | 2021-11-26 | 中钢集团鞍山热能研究院有限公司 | Short-flow anaerobic reactor device and high-concentration organic wastewater pretreatment method |
CN113697949B (en) * | 2021-08-20 | 2023-03-10 | 中钢集团鞍山热能研究院有限公司 | Short-process anaerobic reactor device and high-concentration organic wastewater pretreatment method |
CN114436397A (en) * | 2022-01-14 | 2022-05-06 | 南京大学 | A processing apparatus for high concentration organic, difficult biochemical waste water |
Also Published As
Publication number | Publication date |
---|---|
CN106430567B (en) | 2019-10-08 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106430567B (en) | A kind of technique of high efficiency anaerobic reactor processing organic wastewater | |
CN203256029U (en) | Two-stage and two-circle anaerobic reactor | |
CN206014509U (en) | A kind of two-phase laminated flow inner-outer circulation anaerobic reactor | |
CN202089869U (en) | High-efficient composite reaction device for anaerobic organism | |
CN203715375U (en) | Automatic circulation rotary mixing type internal circulation anaerobic reactor | |
CN203307190U (en) | Anaerobic reactor | |
CN207537218U (en) | Air lift full-mixing type anaerobic reactor | |
CN105776528A (en) | Dual-reflux efficient anaerobic reaction device and wastewater treatment method | |
CN204999694U (en) | High concentration organic waste water's anaerobic treatment device | |
CN101602546B (en) | Anaerobic reactor and wastewater treatment method with same | |
CN204824339U (en) | Gu - liquid - gas three -phase separator | |
CN106315983A (en) | Starch alcohol wastewater treatment system and method | |
CN201433135Y (en) | Anaerobic reactor | |
CN205953809U (en) | Mud takes off device that filtrating produced methane | |
CN112142196A (en) | Method for treating high-concentration degradation-resistant wastewater by using anaerobic self-circulation system | |
CN105502648A (en) | Anaerobic reactor | |
CN105776525A (en) | Integrated two-phase anaerobic desulfurization reactor and wastewater treatment method thereof | |
CN102897909A (en) | Self-circulation anaerobic reactor | |
CN204111410U (en) | Two sections of internal recycle integral type rectangle anaeroic digestors | |
CN205527993U (en) | Good oxygen integrated reactor of anaerobism | |
CN107720956A (en) | A kind of efficient double-cycling anaerobic reactor | |
CN104370366B (en) | Integral type rectangle anaeroic digestor is circulated in a kind of two sections | |
CN209522654U (en) | Sulfur-bearing/nitrogenous organic wastewater and electroplating wastewater combined apparatus | |
CN103288207A (en) | Integrated secondary-fermentation anaerobic digestion tank | |
CN113502208A (en) | Three-phase separation complete mixing type anaerobic reactor |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |