CN106745551A - The apparatus and method of chlorion in removal industrial circulating water - Google Patents

The apparatus and method of chlorion in removal industrial circulating water Download PDF

Info

Publication number
CN106745551A
CN106745551A CN201710005355.3A CN201710005355A CN106745551A CN 106745551 A CN106745551 A CN 106745551A CN 201710005355 A CN201710005355 A CN 201710005355A CN 106745551 A CN106745551 A CN 106745551A
Authority
CN
China
Prior art keywords
water
electrode
reative cell
plate
battery lead
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
Application number
CN201710005355.3A
Other languages
Chinese (zh)
Inventor
高冬
朱骏峰
马力
鲍平利
周伟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
China National Chemical Engineering No14 Construction Co Ltd
Jiangsu Poly Environmental Technology Co Ltd
Original Assignee
China National Chemical Engineering No14 Construction Co Ltd
Jiangsu Poly Environmental Technology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by China National Chemical Engineering No14 Construction Co Ltd, Jiangsu Poly Environmental Technology Co Ltd filed Critical China National Chemical Engineering No14 Construction Co Ltd
Priority to CN201710005355.3A priority Critical patent/CN106745551A/en
Publication of CN106745551A publication Critical patent/CN106745551A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46133Electrodes characterised by the material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46152Electrodes characterised by the shape or form
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/12Halogens or halogen-containing compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices

Abstract

The device of chlorion in a kind of removal industrial circulating water, including reative cell, control device and power module;It is characterized in that being provided with water inlet, delivery port and sewage draining exit on the reative cell;Discharge duct is housed at the top of reative cell, the exhaust outlet of discharge duct is connected to chlorine collection and treatment device, air exhauster is housed on discharge duct;Reative cell is built with electrode group and level sensor;Electrode group includes at least 1 pair battery lead plate;Electric control valve is equipped with water inlet, delivery port and sewage draining exit;Water inlet is located at the left side of reative cell, and delivery port is located at the top on the right of reative cell, and sewage draining exit is located at the bottom on the right of reative cell;Each group electrode group is sequentially placed along water (flow) direction.The application method of the present apparatus is to open electrode set power supplies switch and exits and entrances valve, and the water to flowing through electrode group is processed;The reacting gas produced in reative cell is exhausted and gas treatment simultaneously;Step 2:Operation carries out flushing pollution discharge after 10~30 days.

Description

The apparatus and method of chlorion in removal industrial circulating water
Technical field
The technical program is related to water technology, is gone more particularly, to chlorion in the recirculated water in industrial circulating water field Except technology.
Background technology
During 13, China will be attached most importance to improving environmental quality as core with solving ecological environment field outstanding problem Point, increases ecological environmental protection dynamics.National policy proposes requirement very high, the circulation of industrial water to enterprise's industrial production Using extremely urgent with improvement.
Industrial water consumption accounts for more than the 70% of city total water consumption, and strengthens running on for industrial circulating cooling water system Management, is one of important measures of Industrial Water Saving.Raising recirculated water cycles of concentration is relatively more feasible at present and effectively one kind is saved Water approach, but while cycles of concentration is improved, various ion concentrations constantly rise in recirculated water, the particularly increasing of chlorion Plus.
Chlorion is a kind of severe corrosive ion, and ionic radius is small, and penetrability is strong, easily propagates through film layer, replaces oxygen atom The carrying out of chloride accelerating anode process is formed, accelerates corrosion, be the main cause for causing spot corrosion.In addition it can also be destroyed not The passivating film on the metal or alloy surfaces such as rust steel and aluminium, the crevice corrosion and stress corrosion for causing metal is destroyed.Currently, to chlorine from The removal of son does not have particularly effectively method, such as:Chemical precipitation technology, ion exchange technique, traditional electrolyte technology etc..Chemistry Sedimentation typically uses silver nitrate, stannous chloride method not only high cost, and there is secondary pollution.Ion exchange technique needs Periodic replacement resin, increased cost.Effect is bad because side reaction is too many for traditional electrolyte technology.
The content of the invention
In order to solve the above-mentioned problems in the prior art, the invention proposes a kind of new chlorion electrochemistry Minimizing technology and device.
The device of chlorion in a kind of removal industrial circulating water, including reative cell, control device and power module;It is described anti- Answer and be provided with room water inlet, delivery port and sewage draining exit;
Discharge duct is housed at the top of reative cell, the exhaust outlet of discharge duct is connected to chlorine collection and treatment device, arranges Air exhauster is housed in feed channel;Reative cell is built with electrode group and level sensor;Electrode group includes at least 1 pair battery lead plate;Enter Electric control valve (such as magnetic valve, electrical ball valve etc.) is equipped with the mouth of a river, delivery port and sewage draining exit;Water inlet is located at reative cell The left side, delivery port is located at the top on the right of reative cell, and sewage draining exit is located at the bottom on the right of reative cell;
The electrode group has at least 2 groups;Each group electrode group is sequentially placed along water (flow) direction;
Any electrode group has the multipair battery lead plate being parallel to each other to constitute;The battery lead plate is plate electrode;The material of battery lead plate Matter is titanium compound (such as titanyl compound can be titanium dioxide etc.), and NACF is covered with electrode plate surface;Electrode Using the enhanced Ti electrode of carbon fiber surface, titanium has good electric conductivity, and carbon fiber relative area is big, and both increase after combining Add the relative contact between electrode and raw water to accumulate, lift electrolytic efficiency.
Plate electrode is parallel with water (flow) direction;
The thickness L1 of battery lead plate is 3mm≤L1≤3.6mm;
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm;
The area S of battery lead plate is 0.6 square metre≤S≤1.4 square metre;
The scope of any spacing d to battery lead plate is:6mm < d≤10mm;
The battery lead plate quantity n of any one electrode group is:12 couples≤n < 50 couples, or 50 pairs of < n≤72 pair;
It is any to being provided with insulating materials packed layer between battery lead plate;The scope of the thickness D of insulating materials packed layer is: 1.8mm≤D < 2mm;
The power module is powered for control device, level sensor, electrode group, air exhauster and each electric control valve;
The control device includes microcontroller, interface signal change-over circuit, polarity of electrode change-over circuit, analog-to-digital conversion Device, digital analog converter;
The data-signal and control signal input/output terminal of the microcontroller are outer by the connection of interface signal change-over circuit The binding post of portion's control device (such as upper industrial computer);
Each electric control valve control signal output of the microcontroller connects corresponding respectively after digital analog converter The control signal input of electric control valve;
The air exhauster control signal output of the microcontroller is by connecting corresponding air exhauster after digital analog converter Control signal input;
The Enable Pin of the polarity of electrode changeover control signal output end connection electrode polarity switching of the microcontroller; The input of polarity of electrode change-over circuit connects the electrode group feeder ear of power module, and the output end of polarity of electrode change-over circuit connects Receiving electrode group;
The output end of the level sensor connects the external signal input terminals of microcontroller by analog-digital converter.
Power module becomes industrial-frequency alternating current and is pressed into required voltage, using adapter or inverter etc. according to power device Can realize.Control device is used for being controlled the signal acquisition and external electrical device of whole machine, in the prior art, adopts It is to be capable of achieving with programmable logic devices such as single-chip microcomputer (microcontroller) or PLC.
The scope of any spacing d to battery lead plate is:
6mm < d≤7mm:In small distance, the migration rate and fouling ability of ion can all strengthen, go dechlorination from Sub- effect can reach 90% or so during 7mm < d≤9mm, now may there is larger electrical body due in small distance Into causing short circuit;
7mm < d≤9mm:This interval Inner electrolysis efficiency is best.Specific removal effect will also regard chloride ion content in water body And electrode logarithm, the group number being equipped with etc.;
9mm < d≤10mm:Because decomposition voltage is less, only 3.0V, its electrolytic efficiency when pole plate spacing is further increased Can be lower, the influence of turbidity etc. in plus water, effect only up to reach 65% during 7mm < d≤9mm;
The battery lead plate quantity n scopes of any one electrode group are:12 couples≤n < 35 couples, or 35 couples≤n < 50 couples, or 50 pairs of < n≤60 pair, or 60 pairs of < n≤72 pair;
For same water quality, same treatment amount, electrode pair is The more the better in principle;But it is also necessary to take into account that treatment is effective Property, it is to avoid cause unnecessary waste.Different quality situation, the electrode pair quantity of use is different, for example:It is to chloride ion content For the water quality of 500mg/L, the electrode pair quantity of 35≤n < 50 can substantially meet demand, and clearance is up to 70% or so;It is right For the water quality of 1000mg/L, electrode pair quantity could on an equal basis reach effect for 60 < n≤72.
Electrode pair quantity can not infinitely increase, it is contemplated that fluctuation when power supply, device size and work, maximum is chosen 72 groups of electrodes.
Electrode group has at least 2 groups.
The increase of electrode group quantity is that the chlorine for being electrolysed out in order to further process the chlorion in water, and in water has A part is redissolved in water, and multi-group electrode need to be used to strengthen efficiency.2 groups are chosen in principle, for chloride ion content The water quality of 500mg/L, using the battery lead plate of 35 pairs, if at only one group, dechlorination effect is 52% or so, and has 2 groups of timeliness Fruit is changed into 81% or so at once, and effect is fairly obvious.If increasing to 5 groups, effect now only increases to 86% or so, this be because Very high by 2 groups for the treatment of removal effects for chloride ion content is not high in water, not only effect is failed to understand to continue increase group number It is aobvious, and increase cost.
If chloride ion content reaches more than 5000mg/L in water quality, increase group is also needed while electrode logarithm is increased Number.
The thickness D scopes of insulating materials packed layer are:1.8mm≤D < 1.9mm, or 1.9mm≤D < 2mm.
Fill insulant is used for spaced-apart electrodes to avoiding causing short circuit, and size and the actual production difficulty of its thickness have Close.
The area S of battery lead plate is:1.0 square metres of 0.6 square metre≤S <, or 1.0 square metres≤S≤1.4 square metre.
In theory, the bigger effects of area S are better, because area is bigger, the water quality for the treatment of can be more in the unit interval.Actual measurement In, typically under equal conditions 1.0 square metres or so effects preferably, at 0.6 square metre effect be only its 75%;1.4 square metres Shi Xiaoguo for its 80% because the more big stability for being difficult to ensure that all parts of area, there is a possibility that fluctuation Bigger, the possibility that electrolysis removes other ions is higher, such as:OH-
The thickness L1 of battery lead plate is:3mm≤L1≤3.6mm.
Electrode plate thickness and the convenience being fixedly connected, and operation when stability it is relevant, it is bigger that electrode area does, Electrode plate thickness is corresponding thick.It has to be noted here that thickness is not increased always, the thicker energy loss for causing of thickness is more Seriously, such as:The electrode efficiency that 5.0mm is only has 70% during 3.6mm.
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm.
Battery lead plate is titanium-based material, and on plated surface is NACF, and thickness is more thick better, but in view of attachment difficulty And cost of manufacture, have chosen above-mentioned value.
The wall of the reative cell is the thick PP plastics of 15mm, and reative cell inner chamber is cubic shaped.
Also include numerical-control direct-current voltage regulator;The input of numerical-control direct-current voltage regulator connects the output of power module End, the output end of numerical-control direct-current voltage regulator is used as electrode group feeder ear;The control signal of numerical-control direct-current voltage regulator is defeated Enter the polar plate voltage value control signal output of the end connection microcontroller.
The polarity of electrode change-over circuit includes two groups of on-off circuits;The polarity of electrode changeover control signal of microcontroller is defeated Go out end and connect two groups of Enable Pins of on-off circuit respectively;
One group of on-off circuit includes two on-off circuits, wherein:The input and output end of one on-off circuit connect respectively First pole plate of the direct current "+" of receiving electrode group feeder ear extremely and in paired electrode plate;The input of another on-off circuit Second pole plate in and paired electrode plate extreme with the direct current "-" of output end difference connection electrode group feeder ear;
Another group of on-off circuit includes two on-off circuits, wherein:Input and the output end difference of one on-off circuit Second pole plate of the direct current "+" of connection electrode group feeder ear extremely and in paired electrode plate;The input of another on-off circuit First pole plate of the direct current "-" of end and output end difference connection electrode group feeder ear extremely and in paired electrode plate.
On-off circuit can select power tube according to demanded power output, or the switching device such as relay is core Circuit.The enable of two on-off circuits is controlled using microcontroller, you can realize dipole inversion.
Also include filter and descaler;The delivery port of filter connects the water inlet of descaler, the delivery port of descaler Connect the water inlet of the closed container;
The filter is quartz filter, cellulose filter or self-cleaning filter;The descaler is electricity Chemical cleaning equipment or ion-exchange unit.
The method for removing chlorion in industrial circulating water of the device of chlorion, step bag in above-mentioned removal industrial circulating water Include:
Step 1:Electrode set power supplies switch and exits and entrances valve are opened, the water to flowing through electrode group is processed;It is simultaneously right The reacting gas produced in reative cell is exhausted and gas treatment;
Because the standard electrolytic current potential of chlorion is Φ0=+1.3595V, the actual electrolytic potential of water is 1.6V, based on reality With property, the current potential between coordination electrode plate is 3.0V;
Because water body has dissolved carbon dioxide, bicarbonate ion is generated, water shows faintly acid, and the reaction on battery lead plate is such as Under:
1) reaction on positive plate
Anion includes chlorion and sulfate ion in circulating water body;During logical direct current, anion is to anode movement, electricity Solution chlorion and water:
Generation side reaction generates a small amount of ozone, hydrogen peroxide, hydrogen ion, hypochlorite ion and chlorition;Cause For the residence time is short, they can quickly react and disappear:
2) reaction on minus plate
Because recirculated water shows faintly acid, when leading to direct current, the hydrogen ion contained in water is sent out to movable cathode in cathode surface Raw cell reaction generation hydrogen effusion:
Hydroxide ion in water has the carbonate for promoting fouling ability by the reaction generation with bicarbonate ion Ion, generates magnesium hydroxide and precipitation of calcium carbonate:
3) in running, every 1~3 hour polarity of reverse battery lead plate;After former minus plate polarity, battery lead plate table The dirty layer in face is dissolved into water, is reacted as follows:
Step 2:Operation carries out flushing pollution discharge after 10~30 days, and import, sewage draining exit valve are opened during blowdown, closes delivery port Valve, washing time is 10~30min;After the completion of flushing, return to step 1.
Above in chemical formula, ClO2 -It is an electronegative ClO2Molecule.
Often run 1~2 year, change battery lead plate.
Step 1 and step 2 also include step:Water inlet to reative cell is pre-processed;
Preprocess method is, first using filter method reduction turbidity, to reach the turbidity≤5NTU of water to the water inlet of reative cell, Again using calcium, the concentration of magnesium ion in descaler reduction water, the total hardness≤300mg/L of water is reached;
Water feeding reative cell after the completion of pretreatment removes removing chloride.
The technical program using a set of equipment can realize removal industrial circulating water in chlorion, it is simple and easy to do, dechlorinate effect It is good.
Brief description of the drawings
Fig. 1 is the principle schematic diagram. of the present apparatus;
In figure:1-shell;2-the first group electrode;3-outlet pipe;4-air exhauster;5-the second group electrode;6-go out The mouth of a river;7-water inlet;The arrow of 8-expression water (flow) direction;9-reative cell;10-sewage draining exit.
Specific embodiment
It is further described below with specific embodiment correlation technique scheme below in conjunction with the accompanying drawings:
Such as Fig. 1, the device of chlorion in a kind of removal industrial circulating water, including reative cell, control device and power module; Water inlet, delivery port and sewage draining exit are provided with the reative cell;
Discharge duct is housed at the top of reative cell, the exhaust outlet of discharge duct is connected to chlorine collection and treatment device, arranges Air exhauster is housed in feed channel;Reative cell is built with electrode group and level sensor;Electrode group includes at least 1 pair battery lead plate;Enter Electric control valve is equipped with the mouth of a river, delivery port and sewage draining exit;Water inlet is located at the left side of reative cell, and it is right that delivery port is located at reative cell The top on side, sewage draining exit is located at the bottom on the right of reative cell;
The electrode group has at least 2 groups;Each group electrode group is sequentially placed along water (flow) direction;
Any electrode group has the multipair battery lead plate being parallel to each other to constitute;The battery lead plate is plate electrode;The material of battery lead plate Matter is titanium compound, and NACF is covered with electrode plate surface;
Plate electrode is parallel with water (flow) direction;
The thickness L1 of battery lead plate is 3mm≤L1≤3.6mm;
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm;
The area S of battery lead plate is 0.6 square metre≤S≤1.4 square metre;
The scope of any spacing d to battery lead plate is:6mm < d≤10mm;
The battery lead plate quantity n of any one electrode group is:12 couples≤n < 50 couples, or 50 pairs of < n≤72 pair;
It is any to being provided with insulating materials packed layer between battery lead plate;The scope of the thickness D of insulating materials packed layer is: 1.8mm≤D < 2mm;
The power module is powered for control device, level sensor, electrode group, air exhauster and each electric control valve;
The control device includes microcontroller, interface signal change-over circuit, polarity of electrode change-over circuit, analog-to-digital conversion Device, digital analog converter;
The data-signal and control signal input/output terminal of the microcontroller are outer by the connection of interface signal change-over circuit The binding post of portion's control device;
Each electric control valve control signal output of the microcontroller connects corresponding respectively after digital analog converter The control signal input of electric control valve;
The air exhauster control signal output of the microcontroller is by connecting corresponding air exhauster after digital analog converter Control signal input;
The Enable Pin of the polarity of electrode changeover control signal output end connection electrode polarity switching of the microcontroller; The input of polarity of electrode change-over circuit connects the electrode group feeder ear of power module, and the output end of polarity of electrode change-over circuit connects Receiving electrode group;
The output end of the level sensor connects the external signal input terminals of microcontroller by analog-digital converter.
The scope of any spacing d to battery lead plate is:6mm < d≤7mm, or 7mm < d≤9mm, or 9mm < d≤ 10mm;
The battery lead plate quantity n scopes of any one electrode group are:12 couples≤n < 35 couples, or 35 couples≤n < 50 couples, or 50 pairs of < n≤60 pair, or 60 pairs of < n≤72 pair;
Electrode group has at least 2 groups;
The thickness D scopes of insulating materials packed layer are:1.8mm≤D < 1.9mm, or 1.9mm≤D < 2mm;
The area S of battery lead plate is:1.0 square metres of 0.6 square metre≤S <, or 1.0 square metres≤S≤1.4 square metre;
The thickness L1 of battery lead plate is:3mm≤L1≤3.6mm;
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm.
The wall of the reative cell is the thick PP plastics of 15mm, and reative cell inner chamber is cubic shaped.
Also include numerical-control direct-current voltage regulator;The input of numerical-control direct-current voltage regulator connects the output of power module End, the output end of numerical-control direct-current voltage regulator is used as electrode group feeder ear;The control signal of numerical-control direct-current voltage regulator is defeated Enter the polar plate voltage value control signal output of the end connection microcontroller.
The polarity of electrode change-over circuit includes two groups of on-off circuits;The polarity of electrode changeover control signal of microcontroller is defeated Go out end and connect two groups of Enable Pins of on-off circuit respectively;
One group of on-off circuit includes two on-off circuits, wherein:The input and output end of one on-off circuit connect respectively First pole plate of the direct current "+" of receiving electrode group feeder ear extremely and in paired electrode plate;The input of another on-off circuit Second pole plate in and paired electrode plate extreme with the direct current "-" of output end difference connection electrode group feeder ear;
Another group of on-off circuit includes two on-off circuits, wherein:Input and the output end difference of one on-off circuit Second pole plate of the direct current "+" of connection electrode group feeder ear extremely and in paired electrode plate;The input of another on-off circuit First pole plate of the direct current "-" of end and output end difference connection electrode group feeder ear extremely and in paired electrode plate.
Also include filter and descaler;The delivery port of filter connects the water inlet of descaler, the delivery port of descaler Connect the water inlet of the closed container;
The filter is quartz filter, cellulose filter or self-cleaning filter;The descaler is electricity Chemical cleaning equipment or ion-exchange unit.
The method for removing chlorion in industrial circulating water of the device of chlorion, step in a kind of removal industrial circulating water Suddenly include:
Step 1:Electrode set power supplies switch and exits and entrances valve are opened, the water to flowing through electrode group is processed;It is simultaneously right The reacting gas produced in reative cell is exhausted and gas treatment;
Because the standard electrolytic current potential of chlorion is Φ0=+1.3595V, the actual electrolytic potential of water is 1.6V, based on reality With property, the current potential between coordination electrode plate is 3.0V;
Because water body has dissolved carbon dioxide, bicarbonate ion is generated, water shows faintly acid, and the reaction on battery lead plate is such as Under:
1) reaction on positive plate
Anion includes chlorion and sulfate ion in circulating water body;During logical direct current, anion is to anode movement, electricity Solution chlorion and water:
Generation side reaction generates a small amount of ozone, hydrogen peroxide, hydrogen ion, hypochlorite ion and chlorition;Cause For the residence time is short, they can quickly react and disappear:
2) reaction on minus plate
Because recirculated water shows faintly acid, when leading to direct current, the hydrogen ion contained in water is sent out to movable cathode in cathode surface Raw cell reaction generation hydrogen effusion:
Hydroxide ion in water has the carbonate for promoting fouling ability by the reaction generation with bicarbonate ion Ion, generates magnesium hydroxide and precipitation of calcium carbonate:
3) in running, every 1~3 hour polarity of reverse battery lead plate;After former minus plate polarity, battery lead plate table The dirty layer in face is dissolved into water, is reacted as follows:
Step 2:Operation carries out flushing pollution discharge after 10~30 days, and import, sewage draining exit valve are opened during blowdown, closes delivery port Valve, washing time is 10~30min;After the completion of flushing, return to step 1.
Often run 1~2 year, change battery lead plate.
Also include step between step 1 and step 2:Water inlet to reative cell is pre-processed;
Preprocess method is, first using filter method reduction turbidity, to reach the turbidity≤5NTU of water to the water inlet of reative cell, Again using calcium, the concentration of magnesium ion in descaler reduction water, the total hardness≤300mg/L of water is reached;
Water feeding reative cell after the completion of pretreatment removes removing chloride.
The technical program can automatic conversion anode and cathode to remove removing chloride, it is specific as follows:
The technical program uses titanium-based carbon fiber surface enhanced electrode, and electrode spacing is controlled in 6~10mm.To protect Card operating efficiency should ensure that and for 12~72 pairs of battery lead plates be arranged into one group, and set two groups along the direction of current, every group anti-with insulation Oxidation material polypropylene plastics PP is fixed together and avoids the generation of short circuit, and battery lead plate connects same power supply, when running one section Between after, change anode and cathode automatically, strengthen efficiency.Because the standard electrolytic current potential of chlorion is Φ0=+1.3595V, the reality of water Border electrolytic potential is generally 1.6V, it is contemplated that extraneous factor during real work, and the current potential between coordination electrode plate is 3.0V.Due to following Contain CO in ring water3 2—、HCO3 , can be in alkalescent plus constantly circulation, the reaction on electrode is as follows:
1) reaction on anode
During logical direct current, to anode movement, anion is mainly chlorion, sulfate ion to anion in circulating water body, Wherein sulfate ion will not be electrolysed, and mainly be electrolysed chlorion, while can also be electrolysed a small amount of water.
Due to operating voltage very little, it may occur that minimal amount of side reaction, a small amount of ozone, hydrogen peroxide, hypochlorous acid is produced Root plasma, these ions because the residence time it is very short, and will soon react with certain sterilization algae removal ability and Disappear.
2) reaction on negative electrode
Recirculated water shows alkalescent mostly, and in the presence of additional power source, negative electrode Direct Electrolysis water produces hydrogen
Anode can a small amount of hydroxide ion OH of electrolysis water production during electrolysis-, by with bicarbonate ion Reaction generation have promote fouling ability carbanion, generate a small amount of magnesium hydroxide, precipitation of calcium carbonate, have following Side reaction:
The incrustation scale of generation can be attached to electrode surface, by prolonged operation after can form one layer in cathode surface Dirt, reduces and even eliminates electrolytic efficiency.Therefore, by the way of 1-3 hours reverse electrode, carry out guard electrode, preferably protection Electrode extends its service life.Negative electrode originally is inverted to a small amount of dirty layer in surface after anode can be dissolved into water, and electrode is anti- Should be as follows:
The present apparatus such as Fig. 1, water inlet, delivery port, sewage draining exit are connected with flange, and valve can use electrical ball valve, if Operation is controlled using switch board during standby work, it is specific as follows:
1) prepare, water inlet valve opens water inlet and device interior is once cleaned, sewage draining exit is opened after full of water Valve, water is all put clean;
2) bring into operation, close sewage draining exit valve, open water inlet valve and outlet valve, wait current normally steady It is fixed from delivery port out when open electrode set power supplies switch, while starting air exhauster;
3) in running, after automatic conversion both positive and negative polarity after work 1-3 hours, (it is true that specific time setting regards original water hardness Fixed, hardness is higher, and the conversion both positive and negative polarity time is shorter);
4) blowdown process, (setting value, to prevent dirt from accumulating) closes outlet valve after running 10-30 days, the row of opening Dirty mouth valve, 10-30min of constant flushing of intaking;
5) after the completion of rinsing, sewage draining exit valve is closed, opens outlet valve, normal work is started again.
Battery lead plate can be because of the extension of working time, and fixed insulation material PP can be deposited between electrode surface carbon fiber layer, electrode In destruction, therefore, work 1-2 years ensures equipment with maximum, it is necessary to electrode is taken out again into coated carbon fibers with PP plastics are changed Operating efficiency operation.
The technical program has certain requirement for influent quality, especially turbidity and calcium, the concentration of magnesium ion, it is proposed that turbid Degree≤5NTU, carbonate hardness (in terms of CaCO3)≤300mg/L, in order to avoid because the too high fouling of calcium ions and magnesium ions is serious damage electrode, Reduce service efficiency, if water quality is not up to standard, it is proposed that use pre-processing device, can be used quartz filter, cellulose filter, Self-cleaning filter reduces turbidity, and electrochemical descaling equipment, ion-exchange unit reduction calcium, magnesium ion concentration can be used.
Voltage during work between every group of battery lead plate is only 3.0V, can greatly guard electrode material.
Using the enhanced Ti electrode of carbon fiber surface, titanium has good electric conductivity to electrode, and carbon fiber relative area is big, Both increased the relative contact product between electrode and raw water after combining, lift electrolytic efficiency.To ensure enough efficiency, stop Time should be as long as possible, and flow velocity is up to 0.3m/s, generally 0.1m/s.
This technology due to frequent reverse electrode, theoretically from the point of view of can't cause secondary pollution, but in running Still a small amount of pollutant can be produced, therefore, every 10~30 days automatic pollution discharges once, each 10-30min of blowdown.Electrolysis is anti- Answer room using 15mm thick PP plastics, reative cell is rendered as cubic.
Electrolysis chlorion generation chlorine, electrolysis water generation hydrogen, oxygen are raising electrolytic efficiency above electrode reaction room One air exhauster (rotating speed 2400r/min, power 18w) is installed, the chlorine of generation, hydrogen and a small amount of oxygen are discharged in time, plus Fast electrolytic process;Meanwhile, the mechanism of air exhauster can mix rapidly the chlorine, hydrogen, the oxygen that generate with air, reduce There is dangerous possibility.
Present apparatus processing cycle water is 20~200t/h, typically takes bypass and is arranged in circulation.
Using the test data of this electrochemical dechlorination technology:
Recirculated water using this electrochemical dechlorination equipment respectively at different chloride ion contents is tested, chloride ion content every Every detection in 10 days once, data such as following table:
Machine monitoring data unit:mg/L
Sequence number 0d 10d 20d 30d 40d
1 280.5 196.9 141.7 86.2 81.7
2 415.3 298.0 205.2 132 148.4
3 1350 692.5 447.6 319 320.5
4 2910 1811.8 920 616 603
5 5012 2876 1753 890.6 698.2
In upper table, the data of 0d are the original amount of chlorion.
Equipment dechlorination effect is obvious as seen from the above table.With 30d as standard, every group of clearance difference of recirculated water chlorion For:69.27%th, 68.19%, 76.37%, 78.83%, 82.23%, data display, raw water chloride ion content removal effect higher Fruit can be better.

Claims (9)

1. a kind of device for removing chlorion in industrial circulating water, including reative cell, control device and power module;It is characterized in that Water inlet, delivery port and sewage draining exit are provided with the reative cell;
Discharge duct is housed at the top of reative cell, the exhaust outlet of discharge duct is connected to chlorine collection and treatment device, blast pipe Air exhauster is housed on road;Reative cell is built with electrode group and level sensor;Electrode group includes at least 1 pair battery lead plate;Water inlet, Electric control valve is equipped with delivery port and sewage draining exit;Water inlet is located at the left side of reative cell, and delivery port is located on the right of reative cell Top, sewage draining exit is located at the bottom on the right of reative cell;
The electrode group has at least 2 groups;Each group electrode group is sequentially placed along water (flow) direction;
Any electrode group has the multipair battery lead plate being parallel to each other to constitute;The battery lead plate is plate electrode;The material of battery lead plate is Titanium compound, NACF is covered with electrode plate surface;
Plate electrode is parallel with water (flow) direction;
The thickness L1 of battery lead plate is 3mm≤L1≤3.6mm;
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm;
The area S of battery lead plate is 0.6 square metre≤S≤1.4 square metre;
The scope of any spacing d to battery lead plate is:6mm < d≤10mm;
The battery lead plate quantity n of any one electrode group is:12 couples≤n < 50 couples, or 50 pairs of < n≤72 pair;
It is any to being provided with insulating materials packed layer between battery lead plate;The scope of the thickness D of insulating materials packed layer is:1.8mm≤D < 2mm;
The power module is powered for control device, level sensor, electrode group, air exhauster and each electric control valve;
The control device includes microcontroller, interface signal change-over circuit, polarity of electrode change-over circuit, analog-digital converter, number Weighted-voltage D/A converter;
The data-signal and control signal input/output terminal of the microcontroller are by the outside control of interface signal change-over circuit connection The binding post of control equipment;
Each electric control valve control signal output of the microcontroller connects corresponding automatically controlled respectively after digital analog converter The control signal input of valve;
The air exhauster control signal output of the microcontroller is by connecting the control of corresponding air exhauster after digital analog converter Signal input part;
The Enable Pin of the polarity of electrode changeover control signal output end connection electrode polarity switching of the microcontroller;Electrode The input of polarity switching connects the electrode group feeder ear of power module, the output end connection electricity of polarity of electrode change-over circuit Pole group;
The output end of the level sensor connects the external signal input terminals of microcontroller by analog-digital converter.
2. in removal industrial circulating water according to claim 1 chlorion device, it is characterized in that any to battery lead plate The scope of spacing d is:6mm < d≤7mm, or 7mm < d≤9mm, or 9mm < d≤10mm;
The battery lead plate quantity n scopes of any one electrode group are:12 couples≤n < 35 couples, or 35 couples≤n < 50 couples, or 50 pairs < n≤60 pair, or 60 pairs of < n≤72 pair;
Electrode group has at least 2 groups;
The thickness D scopes of insulating materials packed layer are:1.8mm≤D < 1.9mm, or 1.9mm≤D < 2mm;
The area S of battery lead plate is:1.0 square metres of 0.6 square metre≤S <, or 1.0 square metres≤S≤1.4 square metre;
The thickness L1 of battery lead plate is:3mm≤L1≤3.6mm;
The thickness L2 of activated carbon fiber layers is 0.053mm≤L2≤0.058mm.
3. it is according to claim 1 removal industrial circulating water in chlorion device, it is characterized in that the wall of the reative cell It is the thick PP plastics of 15mm, reative cell inner chamber is cubic shaped.
4. it is according to claim 1 to remove the device of chlorion in industrial circulating water, it is characterized in that also including numerical-control direct-current Voltage regulator;The input of numerical-control direct-current voltage regulator connects the output end of power module, numerical-control direct-current voltage regulator Output end as electrode group feeder ear;The control signal input of numerical-control direct-current voltage regulator connects the microcontroller Polar plate voltage value control signal output.
5. it is according to claim 1 removal industrial circulating water in chlorion device, it is characterized in that the polarity of electrode turn Changing circuit includes two groups of on-off circuits;The polarity of electrode changeover control signal output end of microcontroller connects two groups of switch electricity respectively The Enable Pin on road;
One group of on-off circuit includes two on-off circuits, wherein:The input and output end of one on-off circuit connect electricity respectively First pole plate of the direct current "+" of pole group feeder ear extremely and in paired electrode plate;The input of another on-off circuit and defeated Go out second pole plate of the direct current "-" of end difference connection electrode group feeder ear extremely and in paired electrode plate;
Another group of on-off circuit includes two on-off circuits, wherein:The input and output end of one on-off circuit are connected respectively Second pole plate of the direct current "+" of electrode group feeder ear extremely and in paired electrode plate;The input of another on-off circuit and First pole plate of the direct current "-" of output end difference connection electrode group feeder ear extremely and in paired electrode plate.
6. it is according to claim 1 removal industrial circulating water in chlorion device, it is characterized in that also include filter and Descaler;The delivery port of filter connects the water inlet of descaler, and the delivery port of descaler connects the water inlet of the closed container Mouthful;
The filter is quartz filter, cellulose filter or self-cleaning filter;The descaler is electrochemistry Descaling equipment or ion-exchange unit.
7. in a kind of any removal industrial circulating water of claim 1~6 in the removal industrial circulating water of the device of chlorion The method of chlorion, its feature is comprised the following steps:
Step 1:Electrode set power supplies switch and exits and entrances valve are opened, the water to flowing through electrode group is processed;Simultaneously to reaction The reacting gas of indoor generation is exhausted and gas treatment;
Because the standard electrolytic current potential of chlorion is Φ0=+1.3595V, the actual electrolytic potential of water is 1.6V, based on practicality, Current potential between coordination electrode plate is 3.0V;
Because water body has dissolved carbon dioxide, bicarbonate ion is generated, water shows faintly acid, and the reaction on battery lead plate is as follows:
1) reaction on positive plate
Anion includes chlorion and sulfate ion in circulating water body;During logical direct current, anion is to anode movement, electrolytic chlorine Ion and water:
Generation side reaction generates a small amount of ozone, hydrogen peroxide, hydrogen ion, hypochlorite ion and chlorition;Because stopping Stay the time short, they can quickly react and disappear:
2) reaction on minus plate
Because recirculated water shows faintly acid, when leading to direct current, the hydrogen ion contained in water occurs to movable cathode in cathode surface Cell reaction generation hydrogen effusion:
Hydroxide ion in water have by the reaction generation with bicarbonate ion promote the carbonate of fouling ability from Son, generates magnesium hydroxide and precipitation of calcium carbonate:
3) in running, every 1~3 hour polarity of reverse battery lead plate;After former minus plate polarity, electrode plate surface Dirty layer be dissolved into water, react it is as follows:
Step 2:Operation carries out flushing pollution discharge after 10~30 days, and import, sewage draining exit valve are opened during blowdown, closes water outlet valve Door, washing time is 10~30min;After the completion of flushing, return to step 1.
8. method according to claim 7, it is characterized in that often running 1~2 year, changes battery lead plate.
9. method according to claim 7, it is characterized in that the water inlet to reative cell is pre-processed;
Preprocess method is, first using filter method reduction turbidity, to reach the turbidity≤5NTU of water, then adopt to the water inlet of reative cell With the concentration of calcium, magnesium ion in descaler reduction water, the purpose of the total hardness≤300mg/L of water is reached;
Water feeding reative cell after the completion of pretreatment removes removing chloride.
CN201710005355.3A 2017-01-04 2017-01-04 The apparatus and method of chlorion in removal industrial circulating water Pending CN106745551A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710005355.3A CN106745551A (en) 2017-01-04 2017-01-04 The apparatus and method of chlorion in removal industrial circulating water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710005355.3A CN106745551A (en) 2017-01-04 2017-01-04 The apparatus and method of chlorion in removal industrial circulating water

Publications (1)

Publication Number Publication Date
CN106745551A true CN106745551A (en) 2017-05-31

Family

ID=58950156

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710005355.3A Pending CN106745551A (en) 2017-01-04 2017-01-04 The apparatus and method of chlorion in removal industrial circulating water

Country Status (1)

Country Link
CN (1) CN106745551A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108439553A (en) * 2018-04-20 2018-08-24 武汉大学 A kind of Electrochemical oxidation device for removing chlorion in water removal
CN108502985A (en) * 2018-06-01 2018-09-07 山东深信节能环保科技有限公司 A kind of the combined electrical chemical system and processing method of scale removal dechlorination
CN110143774A (en) * 2019-05-29 2019-08-20 中实泰广(北京)环保科技有限公司 Sea sand purification system
CN111072112A (en) * 2020-01-09 2020-04-28 河北超绿节能环保科技有限公司 Wastewater treatment method and system for zero discharge of desulfurization wastewater
CN112393966A (en) * 2021-01-18 2021-02-23 湖南久钰电子有限公司 Ion enrichment device in water and ion concentration monitoring system in water

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1128980A (en) * 1994-05-31 1996-08-14 东陶机器株式会社 Electrolysis apparatus and method for chloride ion-containing flowing water
JPH08290168A (en) * 1995-04-21 1996-11-05 Toto Ltd Device for electrolyzing running water containing chloride ion and electrolytic method
KR20070115568A (en) * 2006-05-30 2007-12-06 전치중 Electro-chemical water processing apparatus and method of the same
WO2013065797A1 (en) * 2011-11-04 2013-05-10 クロリンエンジニアズ株式会社 Method for producing hypochlorite
CN104341029A (en) * 2014-11-28 2015-02-11 陕西科技大学 EDI (Electro-deionization) and electro-catalytic integrated reactor and method for removing nitrate
CN104528957A (en) * 2014-12-18 2015-04-22 江苏润聚新材料科技有限公司 Circulating water treatment method and equipment
CN105668710A (en) * 2016-01-08 2016-06-15 北京中睿水研环保科技有限公司 Device for removing chlorine roots and calcium and magnesium ions from industrial circulating water
CN105905999A (en) * 2016-06-06 2016-08-31 中南大学 Method for removing sulfate solution chloride ions through electric absorption of three dimensional electrodes
CN206538237U (en) * 2017-01-04 2017-10-03 江苏润聚环保科技有限公司 Remove the device of chlorion in industrial circulating water

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1128980A (en) * 1994-05-31 1996-08-14 东陶机器株式会社 Electrolysis apparatus and method for chloride ion-containing flowing water
JPH08290168A (en) * 1995-04-21 1996-11-05 Toto Ltd Device for electrolyzing running water containing chloride ion and electrolytic method
KR20070115568A (en) * 2006-05-30 2007-12-06 전치중 Electro-chemical water processing apparatus and method of the same
WO2013065797A1 (en) * 2011-11-04 2013-05-10 クロリンエンジニアズ株式会社 Method for producing hypochlorite
CN104341029A (en) * 2014-11-28 2015-02-11 陕西科技大学 EDI (Electro-deionization) and electro-catalytic integrated reactor and method for removing nitrate
CN104528957A (en) * 2014-12-18 2015-04-22 江苏润聚新材料科技有限公司 Circulating water treatment method and equipment
CN105668710A (en) * 2016-01-08 2016-06-15 北京中睿水研环保科技有限公司 Device for removing chlorine roots and calcium and magnesium ions from industrial circulating water
CN105905999A (en) * 2016-06-06 2016-08-31 中南大学 Method for removing sulfate solution chloride ions through electric absorption of three dimensional electrodes
CN206538237U (en) * 2017-01-04 2017-10-03 江苏润聚环保科技有限公司 Remove the device of chlorion in industrial circulating water

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108439553A (en) * 2018-04-20 2018-08-24 武汉大学 A kind of Electrochemical oxidation device for removing chlorion in water removal
CN108502985A (en) * 2018-06-01 2018-09-07 山东深信节能环保科技有限公司 A kind of the combined electrical chemical system and processing method of scale removal dechlorination
CN110143774A (en) * 2019-05-29 2019-08-20 中实泰广(北京)环保科技有限公司 Sea sand purification system
CN111072112A (en) * 2020-01-09 2020-04-28 河北超绿节能环保科技有限公司 Wastewater treatment method and system for zero discharge of desulfurization wastewater
CN112393966A (en) * 2021-01-18 2021-02-23 湖南久钰电子有限公司 Ion enrichment device in water and ion concentration monitoring system in water
CN112393966B (en) * 2021-01-18 2021-04-06 湖南久钰电子有限公司 Ion enrichment device in water and ion concentration monitoring system in water

Similar Documents

Publication Publication Date Title
CN106745551A (en) The apparatus and method of chlorion in removal industrial circulating water
CN101573299B (en) Electro-chemical water processing apparatus and method thereof
CN104261573A (en) Electrochemical water scale removal device
CN210122508U (en) Power plant circulating water treatment system comprising electrochemical sterilization and descaling device and electrodialysis device
CN102718349B (en) Device and method for electrolytic treatment of acid organic wastewater with high salinity
CN209835849U (en) Desulfurization waste water utilization system
CN103086550A (en) Method for treating desulfurization wastewater by electrolysis
CN206538237U (en) Remove the device of chlorion in industrial circulating water
CN104291450A (en) Electrochemical water scale removal device
CN104291451A (en) Electrochemical water scale removal device
CN106045139A (en) Device and process for composite electrochemical reaction pretreatment and recycling of board surface cleaning water in circuit board industry
CN209685921U (en) Hypochlorite generator
CN208964696U (en) It is a kind of except silicon electrochemical reaction appts and to remove the electrochemical reaction system of silicon
CN204198499U (en) A kind of electrochemistry incrustation scale removal device
CN204198535U (en) A kind of electrochemistry incrustation scale removal device
CN207738494U (en) A kind of electrolysis unit removing ammonia nitrogen in ammonia alkali waste water
CN207596522U (en) A kind of galvanized liquid waste handles retracting device
CN105036423A (en) Electrolytic treatment system of ship domestic sewage
CN205442736U (en) Industrial cycle water removes chlorine root, removes calcium magnesium ion device
CN209383462U (en) A kind of processing equipment of industrial circulating water
CN106757132A (en) Electrolysis installation
CN110204016A (en) A kind of system and method for ammonia-containing water electrolysis unit pickling
CN112661359A (en) System and method for breaking and oxidizing chemical nickel plating residual liquid of vehicle parts
CN214141926U (en) Heavy metal sewage treatment device
CN213895302U (en) Electrochemistry circulating cooling water purification installation

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