CN2543951Y - Filling type baffle biological reactor - Google Patents

Filling type baffle biological reactor Download PDF

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Publication number
CN2543951Y
CN2543951Y CN 01222514 CN01222514U CN2543951Y CN 2543951 Y CN2543951 Y CN 2543951Y CN 01222514 CN01222514 CN 01222514 CN 01222514 U CN01222514 U CN 01222514U CN 2543951 Y CN2543951 Y CN 2543951Y
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China
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filler
treatment
chamber
pipe
reactor
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Expired - Fee Related
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CN 01222514
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Chinese (zh)
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王崇达
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Abstract

The utility model relates to a filling type baffling biological reactor. The utility model utilizes a baffle board and a filling to form a basic biological reactor treatment unit, and can maintain a higher concentration of different microorganisms and a stable existence of special bacteria floras, and can treat the substances which are difficult to be degraded. The utility model can according to different sewage treating requirements realize some necessary combinations of the basic biological reactor treatment units and add corresponding equipment to form different biological reactors, such as a hydrolyzing-acidification biological reactor, an anaerobic organism reactor, an aerobic organism reactor, a biological reacting filter and different combinations of the reactors above. Using the utility model to do an intensive treatment to sewages can dramatically enhance a sewage treating efficiency, and then the treated water can reach the relative national draining standard, and the dirt mud draining quantity can be reduced and even can be eliminated, and a structure and volume required by the treatment construction can be further simplified and reduced so as to save the construction space and reduce the investment, and the operation cost can be reduced and management conditions can be improved, etc. The utility model is suitable for the treatment of industrial organic sewages and city life sewages of various concentrations for nitrogen-removing and dephosphorization, and also can be used for sewage treatment projects of various scales. Once the simple treatment is further done, the recycle aim can be realized.

Description

The material filling type baffle bioreactor
Affiliated technical field
The utility model relates to the material filling type baffle bioreactor in a kind of water technology.
Background technology
In sewage disposal,,, be widely used in the processing of municipal effluent (more than 90%) and various industrial organic sewages always in occupation of crucial position because biological treatment has economy, effective and simple.The dominant mechanism of biological treatment is to utilize the metabolic function of microorganism, and organism is carried out biochemical degradation, removes organism and holophytic nutrition thing, and utilizes biofloculation to remove colloidal solid; Simultaneously can also obtain energy and product.But, traditional biological treatment exists some significantly deficiencies: as not keeping the higher concentration of microorganism, treatment scheme and time are long, efficient is not high, the effluent quality instability, a large amount of excess sludges of generation are handled bad meeting and are caused secondary pollution, can't handle the refractory organics material owing to can't keep the existence of specific flora, it is bigger than complexity and occupation of land to handle structures, initial cost and operational and administrative expenses are higher, and energy consumption is big, and the operational management condition is relatively poor etc.
Summary of the invention
The purpose of this utility model and task are exactly at the deficiencies in the prior art, and a kind of novel device that is called the material filling type baffle bioreactor is provided.This device can utilize traverse baffle and filler to form basic bioreactor for treatment unit according to different sewage disposal requirements, in conjunction with suitable aeration and mud reflow method, forms different processing modules, is applicable to the processing of multiple sewage.
The utility model is achieved through the following technical solutions: dose filler and constitute basic bioreactor for treatment unit in the stream chamber that is made of traverse baffle, the installation direction of traverse baffle constitutes upward flow chamber and following to the stream chamber respectively perpendicular to the direction of current; The width of upward flow chamber is down to the 1-8 of stream chamber doubly so that mud down to stream chamber short mix, and in the upward flow chamber, fully assemble, form granule sludge and be attracted on the biologic packing material; Be processed into the flow deflector of 30-60 degree down to the baffle plate its lower edge of stream chamber, be convenient to water is delivered to the center of upward flow chamber, make the muddy water thorough mixing; Filler in the stream chamber can help to obtain good precipitable active sludge down; The filler of various flows chamber not only can be kept the very content of microorganisms of high density, and helps the growth of specified microorganisms population, can handle the refractory organics material.
The beneficial effects of the utility model are, owing in the stream chamber, dosed filler, make the higher concentration that in this device, can keep different microorganisms and the stable existence of specified microorganisms population, be convenient to that different process object is carried out specific aim and handle, significantly improve effluent quality and processing efficiency, reduce and even the elimination sludge discharge, simplify and dwindle the structure and the volume of processing structures, save land used, reduce investment, reduce operational and administrative expenses, improve management condition etc.To basic bioreactor for treatment unit carry out some necessity adjustment and (or) combination, increase corresponding apparatus and can constitute different bio-reactors: as hydrolysis-acidifying bio-reactor; Anaerobic biological reactor; Aerobe reactor; The biological respinse strainer; And the multiple combination of different bio-reactors.
Description of drawings
Below in conjunction with drawings and Examples the utility model is further specified.
Fig. 1 is the basic bioreactor for treatment modular construction of a material filling type baffling synoptic diagram.
Fig. 2 is the structural representation of a kind of embodiment.
Among the figure 1, air entraining pipe, 2, collection chamber, 3, the scum silica frost outlet, 4, the scum silica frost vent pipe, 5, traverse baffle, 6, biologic packing material, 7, sewage water inlet pipe, 8, sludge-discharge pipe, 9, water pump, 10, mud return line, 11, inlet pipe, 12, aeration tube, 13, at the bottom of the reactor V-type pond, 14, the reactor outer wall, 15, filter packing, 16, rising pipe, 17, effluent weir, 18, air water separator, 19, biogas vent pipe etc., and form A, hydrolysis area respectively, B, anaerobic zone, C, aerobic zone and D, sedimentation and filtration district.
Embodiment
The embodiment of Fig. 2 is hydrolysis-anaerobic-aerobic-filtration combined treatment device.Mainly comprise at the bottom of air entraining pipe 1, collection chamber 2, scum silica frost outlet 3, scum silica frost vent pipe 4, traverse baffle 5, biologic packing material 6, sewage water inlet pipe 7, sludge-discharge pipe 8, water pump 9, mud return line 10, inlet pipe 11, aeration tube 12, the reactor V-type pond 13, reactor outer wall 14, filter packing 15, rising pipe 16, effluent weir 17, air water separator 18, biogas vent pipe 19 etc., and form hydrolysis area A, anaerobic zone B, aerobic zone C and sedimentation and filtration district D respectively.Sewage enters hydrolysis area A middle and lower part by sewage water inlet pipe 7, and gas and scum silica frost are discharged by scum silica frost outlet 3 and scum silica frost vent pipe 4; Sewage is by biologic packing material layer 6, particulate matter and colloidalmaterial during a large amount of microorganisms will be intake are held back rapidly, are adsorbed, metabolism at leisure is decomposed under the effect of hydrolytic bacteria, with insoluble hydrolysis of organic matter is dissolved matter, simultaneously under the synergy of acid-producing bacteria with macromolecular substance and be difficult to the degradation property material and be converted into and be easy to biodegradable small-molecule substance, again be discharged in the liquid, under higher hydraulic load, flow into anaerobic zone B with water; Flow through biologic packing material 6 downwards fast behind the sewage inflow anaerobic zone B after the hydrolysis and be folded to the upper reaches, by biologic packing material 6, organism is converted into gases such as methane and carbonic acid gas under the effect of anerobe, discharge through collection chamber 2, air entraining pipe 1, air water separator 18 and biogas vent pipe 19; Simultaneously, the storage phosphorus bacterium of anaerobic zone B is decomposed the poly-phosphate of storing, and is discharged in the water and enters aerobic zone C with current; Gas is by inlet pipe 11, aeration tube 12, carry out oxygenic aeration to aerobic zone C, the energy that microorganism then utilizes the oxidized decomposition of residual organic substances to be obtained, phosphorus in a large amount of d/d phosphorus of absorption and the raw waste water, finish the excessive accumulation of phosphorus and last luxurious amount absorption, synthetic poly-phosphate and storing in cell paste, make the phosphorus content in the sewage reach very low, thereby reach the purpose of removing organism and phosphorus, phosphorous high residual sludge reflux is handled after hydrolysis area A discharges to hydrolysis area A again again; Through nitration treatment, oxidation generates nitrous acid nitrogen and nitrate nitrogen to nitrogenous compound in the sewage at aerobic zone C, and the mud of nitrification liquid and sedimentation and filtration district D is back to hydrolysis area and carries out the denitration processing, thereby finishes the removal of nitrogen; The water outlet of aerobic zone C flows into sedimentation and filtration district D, through reaching the relevant emission standard of country behind the sedimentation and filtration substantially.
This device is applicable to the industrial organic sewage and the municipal effluent of various concentration, and can denitrogenation, dephosphorization, can be widely used in the sewage treatment project of various scales.If through further simple process, can reach the reuse purpose again.

Claims (5)

1, a kind of material filling type baffle bioreactor, at the bottom of comprising air entraining pipe, collection chamber, scum silica frost outlet, scum silica frost vent pipe, traverse baffle, biologic packing material, sewage water inlet pipe, sludge-discharge pipe, water pump, mud return line, inlet pipe, aeration tube, reactor V-type pond, reactor outer wall, filter packing, rising pipe, effluent weir, air water separator, biogas vent pipe, and form hydrolysis area A, anaerobic zone B, aerobic zone C and sedimentation and filtration district D respectively, it is characterized in that hydrolysis area A, anaerobic zone B, aerobic zone C are arranged in order with sedimentation and filtration district D to be connected; Sewage water inlet pipe 7 links to each other with hydrolysis area A middle and lower part, and scum silica frost purger 4 links to each other with hydrolysis area A middle and upper part, and sludge-discharge pipe 8 is installed in hydrolysis area A bottom; On the top of anaerobic zone B collection chamber 2 is arranged, air entraining pipe 1, air water separator 18 and biogas vent pipe 19 are installed on collection chamber 2 tops; Filter packing 15 is installed in D middle and upper part, sedimentation and filtration district, and top is equipped with rising pipe 16, effluent weir 17; In the upward flow chamber of upward flow chamber, anaerobic zone B and the aerobic zone C of hydrolysis area A with down to the indoor biologic packing material 6 of all can dosing of stream; Mud return line 10 is installed in bottom at hydrolysis area A, anaerobic zone B, aerobic zone C and sedimentation and filtration district D; Aeration tube 12 is installed in bottom at aerobic zone C and sedimentation and filtration district D.
2, according to the described material filling type baffle bioreactor of claim 1, it is characterized in that the direction of the installation direction of traverse baffle, and constitute upward flow chamber and following respectively to the stream chamber perpendicular to current; The width of upward flow chamber is down to the 1-8 that flows the chamber doubly, is processed into the flow deflector of 30-60 degree down to the baffle plate its lower edge of stream chamber.
3,, it is characterized in that basic bioreactor for treatment unit number of baffles is the 1-8 group according to the described material filling type baffle bioreactor of claim 1.
4, according to the described material filling type baffle bioreactor of claim 1, it is characterized in that down adopting light filler to the stream chamber, the proportion of filler is 0.5-1.5, when adopting proportion greater than 1 filler, should adopt the installation of support or frame mode.
5, according to the described material filling type baffle bioreactor of claim 1, it is characterized in that the upward flow chamber can adopt various fillers, as: hard filler, soft filler, medium-soft matter filler, elastic filler and combined stuffing etc., the proportion of filler is 0.9-5.0; When adopting proportion, should adopt the installation of support or frame mode greater than 1 filler.
CN 01222514 2001-05-08 2001-05-08 Filling type baffle biological reactor Expired - Fee Related CN2543951Y (en)

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Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100441521C (en) * 2006-12-08 2008-12-10 重庆大学 Peripherally-distributed water deflection composite reactor for hydrolysis and acidification
CN100465109C (en) * 2007-04-27 2009-03-04 浙江大学 sewage treatment device with denitrification function
CN1974752B (en) * 2006-12-13 2010-06-02 辽宁省农业科学院生命科学中心 Integrally designed, double cavity marsh gas fermenting system
CN102745858A (en) * 2011-04-17 2012-10-24 赵峰 Sewage processing method for mud-water separation and device thereof
CN102805956A (en) * 2011-06-05 2012-12-05 赵峰 Vertical pipe type sludge-water separation treating device
CN103523914A (en) * 2013-10-16 2014-01-22 哈尔滨工业大学 Anaerobic and micro-aerobic baffle plate reactor for treating sulfur-containing organic wastewater and method for treating sulfur-containing organic wastewater
CN104944675A (en) * 2014-03-31 2015-09-30 刘德周 Building block type modules of horizontal structure capable of continuous downstream filtration
CN105330021A (en) * 2015-11-24 2016-02-17 浙江大学宁波理工学院 Floatable sewage purification device
CN105731645A (en) * 2016-04-15 2016-07-06 王道光 Integrated sewage treatment device
CN106430584A (en) * 2016-10-20 2017-02-22 王海燕 Baffled bioreactor
CN107758863A (en) * 2017-11-27 2018-03-06 河北中科威德环境工程有限公司 Anaerobic baffled reactor
CN109647177A (en) * 2017-10-11 2019-04-19 中山大学 A kind of AO composite catalyzing Membrane Bioreactor for Wastewater Treatment method of nitrous oxides exhaust gas
CN111620446A (en) * 2020-06-05 2020-09-04 北京赛富威环境工程技术有限公司 Treatment method of high-concentration phenol-containing industrial wastewater

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100441521C (en) * 2006-12-08 2008-12-10 重庆大学 Peripherally-distributed water deflection composite reactor for hydrolysis and acidification
CN1974752B (en) * 2006-12-13 2010-06-02 辽宁省农业科学院生命科学中心 Integrally designed, double cavity marsh gas fermenting system
CN100465109C (en) * 2007-04-27 2009-03-04 浙江大学 sewage treatment device with denitrification function
CN102745858A (en) * 2011-04-17 2012-10-24 赵峰 Sewage processing method for mud-water separation and device thereof
CN102805956A (en) * 2011-06-05 2012-12-05 赵峰 Vertical pipe type sludge-water separation treating device
CN103523914B (en) * 2013-10-16 2015-05-20 哈尔滨工业大学 Anaerobic and micro-aerobic baffle plate reactor for treating sulfur-containing organic wastewater and method for treating sulfur-containing organic wastewater
CN103523914A (en) * 2013-10-16 2014-01-22 哈尔滨工业大学 Anaerobic and micro-aerobic baffle plate reactor for treating sulfur-containing organic wastewater and method for treating sulfur-containing organic wastewater
CN104944675A (en) * 2014-03-31 2015-09-30 刘德周 Building block type modules of horizontal structure capable of continuous downstream filtration
CN105330021A (en) * 2015-11-24 2016-02-17 浙江大学宁波理工学院 Floatable sewage purification device
CN105731645A (en) * 2016-04-15 2016-07-06 王道光 Integrated sewage treatment device
CN106430584A (en) * 2016-10-20 2017-02-22 王海燕 Baffled bioreactor
CN109647177A (en) * 2017-10-11 2019-04-19 中山大学 A kind of AO composite catalyzing Membrane Bioreactor for Wastewater Treatment method of nitrous oxides exhaust gas
CN107758863A (en) * 2017-11-27 2018-03-06 河北中科威德环境工程有限公司 Anaerobic baffled reactor
CN111620446A (en) * 2020-06-05 2020-09-04 北京赛富威环境工程技术有限公司 Treatment method of high-concentration phenol-containing industrial wastewater

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