The stack anaerobic treatment equipment for wastewater of built-in biological catalytic electrolysis system and use its
The method for handling waste water
Technical field
The regulation and control method of used water difficult to degradate is handled the present invention relates to a kind of refractory wastewater device and with it, is specifically related to
And a kind of stack anaerobic treatment equipment for wastewater (the stackable anaerobic of built-in biological catalytic electrolysis system
digestion bioreactor with built-inbiocatalyzed electrolysis system:SADB-BES)
And the method using its processing waste water.
Background technology
Industrial wastewater occupies sizable proportion in China's discharge of wastewater, is shown according to Chinese Ministry of Environmental Protection's data, 2013 I
The discharged volume of industrial waste water of state is more than 200 hundred million tons, and such a large amount of discharge of wastewater causes heavy burden to environment;Meanwhile it also answering
It recognizes that industrial wastewater is a kind of potential water resource, is used industrial wastewater as lasting water resource, be to alleviate water
The important channel of shortage of resources, and to mitigate receiving water body environmental pollution, the effective ways improved the ecological environment.State affairs in 2013
Institute issues《Circular Economy Development Strategy and Immediate action plan》, it is desirable that during " 12th Five-Year Plan ", industrial water reclamation rate at least carries
High by 4.3%, at the same time, various industrial wastewater discharge standards are also revised, updated and are issued in succession, the raising of standard both body
The new demand for having showed discharge of wastewater control, also implies that industrial wastewater deep treatment is faced with bigger challenge.
The organic wastewater with difficult degradation thereby of 50% or more discharged volume of industrial waste water is accounted for all the time, such as:Papermaking, chemical industry, weaving, system
Medicine etc. is the problem of water treatment field, and a large amount of toxic organic compounds difficult to degrade, such as halogenated aromatic are remained in this kind of waste water secondary effluent
Hydrocarbon, artificial dye-stuff, antibiotic etc., content account for 80% or more of the total COD of water outlet, are difficult using traditional anaerobic technique
It realizes the removal to toxic pollutant difficult to degrade in industrial wastewater secondary effluent, is discharged into natural water, not only cause serious
Environmental Health and problems of ecological security, also become industrial wastewater regeneration important limiting factor.
Therefore, it develops effective water treatment technology to improve for industrial wastewater secondary effluent water quality, targetedly to difficulty
Degradation of contaminant efficiently removes, and realizes deep purifying and the regeneration of industrial wastewater, is the extremely urgent weight of environmentalist
Appoint.
Living things catalysis electrolysis system has attracted the sight of more and more people as a kind of emerging water technology.
Potter elaborated that microorganism can convert the viewpoint for generating electric current by substance in 1991, but by microorganism and fuel cell
In conjunction with and use it for wastewater treatment and just gradually spread out in 21 century, in this system, microorganism, will be chemical as catalyst
It can be converted into electric energy, which has the characteristics that:(1) low-carbon-source electron donor demand;In bioelectrochemical system, anode is micro-
Biology can efficiently using the small organic molecule in water as carbon source, especially volatile acid (VFAs), meanwhile, orientation tame
Cathode microbial using electrode as direct electron donor, using inorganic carbon realize autotrophy, be based on this characteristic, biology
Cathode can convert object under conditions of not depending on organic carbon, therefore, need of the bioelectrochemical system to carbon source electron donor
The amount of asking is much smaller than traditional anaerobic technique;(2) Recalcitrant chemicals orientation removal efficiency is high;Hardly degraded organic substance in water, including:
Nitryl aromatic hydro carbons, azo, high chlorocarbon, arene, usually contain it is double build, hale electron group, azo bond etc., these objects
The resistance group of matter has chemical reducibility mostly, and the product bio-toxicity after reduction substantially reduces.Studies have shown that these
In biological-cathode by smaller energy input and control of Electric potentials nitrate reduction, nitro reduction, antibiosis can occur for substance
Plain dechlorination, halogenated aromatic dehalogenation, chromophoric group decoloration etc., and then be efficiently removed.
In recent years, living things catalysis electrolysis system is coupled with anaerobic technique, is received significant attention, the technique is by bioelectrochemical
System is built in anaerobic technique, improves the space availability ratio of anaerobic device, and electrode increases life as a kind of bio-carrier
Object amount is reacted remaining Recalcitrant chemicals and is realized and efficiently determine under the conditions of adding controllable small voltage outside to anaerobic organism
To conversion, wherein electrode holder is larger by specific surface area and configuration can flexible and changeable conductive material be made, adhere to above
Electroactive biomembrane has the function of electrochemical reaction feature and microorganism catalysis characteristic and traditional biological filler.
Therefore, living things catalysis electrolysis system is combined with anaerobic organism technique, handles indegradable industrial effluent, it not only can be with
Overcome in industrial wastewater that carbon source is few, C/N can effectively promote the efficiency of anaerobic organism technique, fortified water than low drawback
Conversion, the removal of middle Recalcitrant chemicals.
Invention content
In consideration of it, at the purpose of the present invention is to provide a kind of stack anaerobic waste water of built-in biological catalytic electrolysis system
The method managed device and waste water is handled using it, for refractory wastewater.
To achieve the goals above, as one aspect of the present invention, the present invention provides a kind of built-in biological catalysis electricity
The stack anaerobic treatment equipment for wastewater of solution system, the stack anaerobic treatment equipment for wastewater include sequentially following sections:Detest
Oxygen area, living things catalysis electrolysis zone and water phase area, which is characterized in that the stack anaerobic treatment equipment for wastewater using stack and
Modularized design, each section can carry out assembling combination as needed, can according to target waste water feature, adjust anaerobic zone with
The number of sections of living things catalysis electrolysis zone.
Wherein, the stack anaerobic treatment equipment for wastewater is designed using up-flow, and it is useless that water inlet pipe is located at the stack
Downflow weir and overflow area, stream is arranged at the top of the stack anaerobic treatment equipment for wastewater in the bottom of water anaerobic processing device
The treated waste water for entering the water phase area flows into overflow area by downflow weir, then imports outlet pipe.
As another aspect of the present invention, the present invention also provides a kind of using built-in biological as described above catalysis electricity
The method of the stack anaerobic treatment equipment for wastewater processing waste water of solution system.
Based on the above-mentioned technical proposal it is found that the stack anaerobic treatment equipment for wastewater of the present invention has the characteristics that and beneficial
Effect:(1) design of present apparatus modular, can be by the volume ratio flexible modulation in four areas, and can be according to change of water quality and place
Reason needs, and increases or decreases the quantity of electrode module;Using the form of stacking, device can be made to pass through adjusting blade diameter length ratio, in space
Upper amplification;(2) use anaerobic zone under, living things catalysis electrolysis zone utilizes living things catalysis electrolysis system pair in upper arrangement mode
The advantage of low concentration pollutant removal, further strengthens removal to the remaining pollutant in anaerobic sludge zone;(3) by living things catalysis electricity
Solution system is placed in the water phase area of anaerobic device, and effectively improve anaerobic device utilizes space, increases biomass;It (4) will be cloudy
It is separated using amberplex between anode, and anode module is placed among cathode module, anode module can be greatly reduced
Volume, reduce cost, and in preventing anode electrode microorganism from being intake by cathode noxious material toxicity inhibition, can be abundant
Play the function of anode and cathode;By the arrangement of upper and lower and circulating type and the use of amberplex, adequately protect each area
The microbial activity in domain makes each region play one's part to the full;(5) anode module area can divide with anaerobism-cathode module unicom area
Manage the waste water of two kinds of different qualities in other places;By the regulation and control of applied voltage, hydraulic detention time and pollutant concentration of intaking, can make
The device keeps optimum performance.
Description of the drawings
Fig. 1 is the stack anaerobic treatment equipment for wastewater (SADB-BES) of the built-in biological catalytic electrolysis system of the present invention
Structural schematic diagram;
SADB-BES is compared with the decoloration efficiency of AD devices and AYR concentration under the respectively intermittent flow condition of Fig. 2A, 2B
Curve graph;
Fig. 3 A, 3B be respectively it is different water inlet dye strengths under the conditions of SADB-BES and AD devices decoloration efficiency and COD go
Except efficiency compares block diagram;
Fig. 4 is contribution rate block diagram of the living things catalysis electrolysis zone in dyestuff removal in SADB-BES.
【Reference sign】
1. water inlet, 2. blow-down pipes, 3. sludge buckets, 4-9. dismountable type sleeves, 10. outlet pipes, 11. downflow weirs, 12. collection
Gas port, 13. anode assemblies, 14. anode water inlet pipes, 15. anode outlet pipes, 16. three phase separators, 17. thief hatch follow in 18.
Collar extension, 19. guidewire ports.
Specific implementation mode
To make the objectives, technical solutions, and advantages of the present invention clearer, below in conjunction with specific embodiment, and reference
Attached drawing, the present invention is described in further detail.
In order to solve the problems, such as that existing anaerobic technique is low to Recalcitrant chemicals removal efficiency, degradation speed is slow, it is simultaneously
Realize the amplification application of living things catalysis electrolysis system, the invention discloses a kind of stacking of built-in biological catalytic electrolysis system
Formula anaerobic treatment equipment for wastewater and use its wastewater treatment method, be related to used water difficult to degradate anaerobic processing device and utilize the dress
The method for setting processing used water difficult to degradate.The present invention solves efficiency during traditional anaerobic organism process used water difficult to degradate
Problem low, speed is slow, electron donor demand is big.
More specifically, the invention discloses a kind of stack Anaerobic wastewater treatment of built-in biological catalytic electrolysis system dresses
It sets, stack anaerobic treatment equipment for wastewater includes sequentially following sections:Anaerobic zone, living things catalysis electrolysis zone and water phase area stack
Formula anaerobic treatment equipment for wastewater uses stack and modularized design, each section that can carry out assembling combination, energy as needed
Enough according to target waste water feature, the number of sections of anaerobic zone and living things catalysis electrolysis zone are adjusted.
Preferably, stack anaerobic treatment equipment for wastewater is designed using up-flow, water inlet pipe, which is located at stack waste water, to be detested
The bottom of oxygen processing unit is arranged downflow weir and overflow area at the top of stack anaerobic treatment equipment for wastewater, flows into water phase area
Treated waste water overflow area is flowed by downflow weir, then import outlet pipe.
Preferably, anaerobic zone is made of anaerobic mud bed, anaerobic zone individually controls cycle in muddy water, can either ensure dirt
The effective flowing of mud prevents short stream, and can prevent electrode module surface from adhering to blocked up anaerobic sludge.
Preferably, setting anode module and cathode module, anode module are placed in cathode mould in living things catalysis electrolysis zone
Among block, and it is separated from each other using amberplex.
Preferably, cathode module is connected to up and down with anaerobic zone, anode module and cathode module-anaerobic zone independently intake
Control, can handle the waste water of two kinds of different qualities simultaneously.
Preferably, anode module and cathode module include carbon fiber brush, wherein cathode module passes through titanium silk series connection carbon
Fiber brush.
Preferably, when using stack anaerobic treatment equipment for wastewater processing target waste water, according to target contaminant feature,
Anode module and cathode module applied voltage are 0.5~0.9V.
The invention also discloses a kind of stacks using the built-in biological catalytic electrolysis system described in any one as above
The method that anaerobic treatment equipment for wastewater handles waste water.
Preferably, living things catalysis electrolysis zone includes anode module and cathode module, wherein cathode module and anaerobic zone
Connection up and down, the water inlet of anode module and cathode module-anaerobic zone individually controls, anaerobic zone water outlet, cathode module water outlet and
Anode module water outlet comes together in water phase area, passes through downflow weir, is discharged from outlet pipe.
As a preferred embodiment of the invention, apparatus of the present invention are by 7 section diameter 15cm, the different cylindrical drum of length
Splicing stack, be divided into 11 components, by anaerobic zone, living things catalysis electrolysis zone and water phase district's groups at, component can be disassembled flexibly,
And the ratio of different zones is adjusted as needed.Wherein, living things catalysis electrolysis zone is by independent anode module and cathode module structure
At anode module includes anode electrode (carbon fiber brush), anodic porous sleeve and amberplex three parts;Cathode module is by carbon
Fiber brush is connected in series by titanium silk, and cathode module is looped around around anode module, by amberplex by cathode and anode mold
Block separates.Using at the device when target waste water, anode and cathode both ends according to target contaminant feature, additional small voltage (0.5~
0.9V), negative and positive electrode potential is made to reach potential needed for contaminant degradation;Anode module is individually intake;Cathode module connects with anaerobic zone
It is logical, individually control water inlet;Two kinds of water inlets are different characteristic water quality waste water;Anaerobic zone individually controls cycle in muddy water.The design fills
Method is set and regulated and controled, the device can be used to handle the waste water of two kinds of water quality simultaneously, and according to pollutant characteristic and concentration, spirit
The ratio living for adjusting different zones in assembling device, and by the arrangement of upper and lower and circulating type and the use of amberplex, fill
Code insurance protects the microbial activity in each region, and each region is made to play one's part to the full;And pass through applied voltage, hydraulic detention time
And the regulation and control of water inlet pollutant concentration, so that the device technique device is kept optimum performance.
As a preferred embodiment of the invention, as shown in Figure 1, the invention discloses a built-in biological catalysis electricity
The stack anaerobic processing device and regulation and control method, the device of solution system are designed using up-flow, are made of 19 parts, component
1 is water inlet, and component 2 is blow-down pipe, and apparatus main body is spliced by 7 pitch circle cylinders, and stack screws up, and barrel bore is 15cm, outside
Diameter 17cm, bottom are sludge bucket area (component 3), high 38cm, the high 38cm of 4 cylinder of component, component 5-9 cylindrical shapes and size phase
Together, highly it is 20cm, and flanged joint per partial cylinder outer wall, is twisted by screw and flange between each two cylinder part
Close connection;Component 10 is the outlet pipe of device anaerobic zone and cathode module connected region, caliber 2cm;Component 11 is downflow weir, weir area
Internal diameter is 15cm, and overflow area is outer diameter 38cm, and internal diameter is the ring region of 27cm;Component 12 is collection gas port;Component 13 is to be placed in anaerobism
The anode assemblies of bioelectrochemical system in device, including anode canister and head cover, the stack shell of anode are uniformly covered with aperture above
The circular hole of 2mm, cylinder outer wall closely paste cation-exchange membrane, and cylinder lower part is equipped with water inlet pipe, caliber 1cm, and top cap central is equipped with
Outlet pipe, caliber 1cm;Component 14 is anode water inlet pipe;Component 15 is anode outlet pipe;Component 16 is the three-phase separate of apparatus main body
From device;Component 17 is thief hatch, is equipped with valve;Component 18 is interior circulation port, and internal circulation pump is connected between blow-down pipe;Component
19 be the conducting wire outlet of electrode module.
Component 3#-6# is anaerobic zone, is inoculated with anaerobic sludge;7#-8# is biological catalytic electrolysis area, during anode module is placed in
Between, surrounding is evenly distributed with cathode, and anode module is made of electrode, porous insulation cylinder and amberplex, and anode electrode is a diameter
The carbon fiber brush of 4cm, long 8cm, by titanium silk as current collector, titanium silk is drawn among porous insulation cylinder head cover, and connection is outer
Circuit, cathode module are connected in series by the carbon fiber brush of 10 diameters 4cm, long 10cm, by titanium silk as current collector, are surround
It around anode canister, is fixed on anode module insulation cover plate, and is filled in 7# and 8# cylinders, the moon in 7# and 8# cylinder parts
Pole module is identical with anode module arrangement mode, and two arrays of electrodes distinguishes ejector, individually controls;9# cylinders are water phase area.
The present apparatus is up-flow, is followed successively by from top to bottom:Anaerobic zone, living things catalysis electrolysis zone, water phase area, overflow area,
In, individually control, the water inlet of anaerobic zone and cathode module individually control for the anode module water inlet of living things catalysis electrolysis system.Anaerobism
Area's water outlet, cathode water outlet and anode water outlet come together in 9# components, pass through the downflow weir of 11#, are discharged from drainpipe, reach dirty
Contaminate the purpose of object step enhancing degradation.
Specific implementation mode one:
Embodiment is described with reference to Fig. 1, and the stack waste water of the built-in biological catalytic electrolysis system of present embodiment is detested
Oxygen treatment process device includes 1. water inlets, and 2. blow-down pipes, 3. sludge buckets, 4-9. dismountable type sleeves, 10. outlet pipes, 11. overflow
Flow weir, 12. collection gas ports, 13. anode assemblies, 14. anode water inlet pipes, 15. anode outlet pipes, 16. three phase separators, 17. samplings
Mouthful, circulation port in 18., 19. guidewire ports.Anode and the conducting wire of cathode module are drawn by the guidewire port of No. 6 and No. 9 sleeves;Often
Group cathode and anode module constitute one group of electrode, difference group electrode modules between, on circuit use independent control mode, no
Different voltages can be loaded with electrode module;Between different anode modules, adopts and be connected serially on water intake mode.
The device of present embodiment is divided into three areas, and in conjunction with attached drawing 1, lower part is anaerobic hydrolysis-acidification area, and centre is biology
Catalytic electrolysis area, top are water phase area, and sewage is flowed into from bottom of device, is advanced in upper up-flow pulling flow type, is first passed through anaerobic hydrolysis
Acidification region passes through cathode module, achievees the purpose that pollutant step strengthens removal.
Specific implementation mode two:
Embodiment is described with reference to Fig. 1, the refractory wastewater device Anodic module of present embodiment use from
Proton exchange surrounds form, is placed among cathode module, itself and cathode is made to separate, this design both can avoid anode biology by
The influence of noxious material in waste water makes it keep stable excellent performance, and can make anode module area water inlet individually control, makes
The device can handle the waste water of two kinds of different qualities simultaneously.Other compositions and connection relation are same as the specific embodiment one.
Specific implementation mode three:
Embodiment is described with reference to Fig. 1, and the material of the anode and cathode of present embodiment is carbon fiber.So set
It sets, electrode surface area can be increased, and reduce installation cost.Other compositions and connection relation and specific implementation mode one or two-phase
Together.
Specific implementation mode four:
Illustrate present embodiment, the stack waste water of the built-in biological catalytic electrolysis system of present embodiment in conjunction with Fig. 2-4
Anaerobic treatment process device and regulation and control method, can by water intake mode, water inlet pollutant concentration, hydraulic detention time (HRT) and
Electrode module applied voltage regulates and controls to realize optimization process efficiency of the process unit to target waste water.
Beneficial effects of the present invention are further proved by following instance:
1. decolorizing azo dye waste water efficiency
The present apparatus is investigated to the treatment efficiency containing azo dye wastewater using intermittent water intake mode first, is given up according to target
Water water quality characteristic is mainly removed conversion using anaerobism and cathode module area azo dyes.It is individually continuous in anode module
It intakes, dyestuff is not contained in water, anaerobic zone and cathode module area individually intake, and dye strength is 80mg/L, electrode mould in water inlet
Block both ends applied voltage 0.7V, as shown in Fig. 2A, 2B, apparatus of the present invention SADB-BES is significantly faster than that list to the removal efficiency of dyestuff
Pure bio anaerobic device AD, after 5h, the dye strength of electrode district reduces to obtain 15mg/L, dyestuff in SADB-BES devices
Percent of decolourization reaches 72%, and sludge area also reaches 60% to the removal efficiency of dyestuff, is higher than the 55% of AD devices.
On this basis, water intake mode is changed to continuous stream mode, further investigates the stability and antithesis of apparatus of the present invention
The treatment efficiency of nitrogen waste water from dyestuff.Water inlet dye strength is divided into three gradients:50,70 and 90mg/L, applied voltage 0.7V, waterpower
Residence time HRT is 12h, as shown in Fig. 3 A, 3B, under the conditions of different water inlet dye strengths (50,70,90mg/L), and this hair
The electrode district water outlet of bright device SADB-BES is always maintained at highest percent of decolourization, respectively 92.9%, 93.2% and 87.7%, table
The removal of the bright coupled system azo dyes has apparent invigoration effect, this is because living things catalysis electrolysis zone utilizes electrode
The bioelectrochemistry on surface is reacted, and remaining dyestuff further orient quickly converts in so that anaerobic zone is discharged.Compare SADB-
BES from AD to the removal effect of waste water COD it can also be seen that under the conditions of different water inlet dye strengths, COD during the former is discharged
Removal rate is apparently higher than the latter, this is because on electrode module biomembrane enrichment, on the one hand increase the biomass of device, separately
One side electrode microorganism easily biodegradable organics using in water carry out reducing dye as electron donor, and the collective effect of the two promotes
The further removal of COD in water.This also demonstrates the validity of the present apparatus and method in terms of strengthening dye wastewater treatment.
2. electron recovery efficiency
Living things catalysis electrolysis zone in SADB-BES is calculated by the electric current of electrode, and the amount of the azo dyes of removal
Electron recovery efficiency, to characterize the contribution of living things catalysis electrolysis zone azo dyes removal.As shown in figure 4, electrode contribution rate into
Water dye strength reaches maximum when being 70mg/L, be 10.5%, when dye strength of intaking is relatively low (50mg/L), the contribution of electrode
Relatively low rate is 5.8%, when intake dye strength be increased to 90mg/L when, electrode contribution rate be 7.5%, this result shows that, when
When dye strength is relatively low, the dyestuff in waste water is largely removed by anaerobic zone, at this point, anaerobic organism reaction is to dyestuff in system
Removal play main function, when dye strength improves, the contribution rate of electrode district gradually increases, and shows electrode district to anaerobic zone
Dyestuff in water outlet plays the role of further strengthening removal, but when dye strength higher, coupled system SADB-BES is to dyestuff
Percent of decolourization also decline, dye load has been more than the processing load of system at this time, and the efficiency of electrode district is made to decrease, electrode tribute
It is also restrained to offer rate.
Particular embodiments described above has carried out further in detail the purpose of the present invention, technical solution and advantageous effect
Describe in detail bright, it should be understood that the above is only a specific embodiment of the present invention, is not intended to restrict the invention, it is all
Within the spirit and principles in the present invention, any modification, equivalent substitution, improvement and etc. done should be included in the protection of the present invention
Within the scope of.