CN202576143U - High-efficient and stable coking wastewater deep treatment system - Google Patents
High-efficient and stable coking wastewater deep treatment system Download PDFInfo
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- CN202576143U CN202576143U CN2012201675034U CN201220167503U CN202576143U CN 202576143 U CN202576143 U CN 202576143U CN 2012201675034 U CN2012201675034 U CN 2012201675034U CN 201220167503 U CN201220167503 U CN 201220167503U CN 202576143 U CN202576143 U CN 202576143U
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/131—Reverse-osmosis
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
The utility model relates to a high-efficient and stable coking wastewater deep treatment system, which comprises a micro-electrolysis pool, a microwave auxiliary catalysis oxidation device, a mixing reaction pool, a sedimentation pool, a filter, a frequently changing pole electrodialysis apparatus and a reverse osmosis device, wherein the microwave auxiliary catalysis oxidation device is connected with the micro-electrolysis pool; the mixing reaction pool is connected with the microwave catalysis oxidation device, and the sedimentation pool is connected with the mixing reaction pool; the filter is connected with the sedimentation pool; the frequently changing pole electrodialysis apparatus is connected with the filter; and the reverse osmosis device is connected with a fresh water outlet of the frequently changing pole electrodialysis apparatus. According to the micro-electrolysis pool treatment of the treatment system, contents of chemical oxygen demand (COD) and salt in outflow water obtained after subsequent treatments of microwave catalysis oxidation, coagulation sedimentation, filtration and electrodialysis are lower, so as to enable that a front device can be matched with a rear electrodialysis and reverse osmosis desalination device, and the system can stably operate while realizing high-effective desalination. Additionally, by the adoption of the treatment system, a concentrated water recovery method of the desalination system is optimized, and the outflow water quality is greatly improved under the circumstance of not reducing the rate of water utilization.
Description
Technical field
The utility model relates to the Treatment of Coking Effluent field, is specifically related to a kind of coking advanced waste treatment system of efficient stable.
Background technology
Coking chemical waste water is the waste water that contains a large amount of aromatics and heterogeneous ring compound that in coal system coke, gas purification and coke chemicals removal process, produces; Have that quantity discharged is big, organism and characteristics such as ammonia nitrogen concentration is high, biodegradability is poor, organic components complicacy, belong to the organic waste water of difficult for biological degradation.Be containment coking industry low-level duplicate construction and blind expansion trend; Promote industrial structure upgrading; Promote energy-saving and emission-reduction and technical progress; The Ministry of Industry and Information Technology of country revised former " coking industry entry criteria " in 2008, spelt out Treatment of Coking Effluent and will recycle after qualified, must not efflux.
The mode of two stages of treatment is generally adopted in the processing of early stage coking chemical waste water; The first step be with high density contain phenol and cyanide wastewater carries out pre-treatment such as dephenolize decyanation and ammonia still process air supporting; The second stage is that the pretreated coking chemical waste water of process is carried out biochemical treatment, adopts the A/O technology in the activated sludge process usually.But through after the above-mentioned two stages of treatment, water outlet can't direct reuse in recirculating cooling water system.This is because according to relevant national standard, and reuse water wants reuse to do the recirculated cooling water moisturizing, except to COD
Cr, BOD
5Have beyond the strict more regulation Deng the organic pollutant index; Inorganic salt indexs such as total dissolved solid, total hardness, total alkalinity, muriate are also had certain requirement, and the water outlet that after above-mentioned two stages of treatment, obtains can not reach the requirement of relevant national standard fully.
In order to reach the requirement of relevant national standard, need carry out advanced treatment once more to the water outlet after above-mentioned two stages of treatment.Coking chemical waste water is carried out the technology of advanced treatment as disclosing a kind of method that adopts catalytic oxidation to combine among the Chinese patent document CN101781039A with membrane separation technique; In this technology; Coking chemical waste water after pre-treatment, A/O biochemical treatment through catalytic oxidation treatment, and then is handled through coagulating sedimentation; After after uf processing and reverse osmosis system handle, promptly can be used as the make up water of circulating water system.
But, the water outlet of adopting the pretreatment technology of above-mentioned catalyzed oxidation+coagulating sedimentation+ultrafiltration to obtain, wherein COD
CrThough content can be reduced to below the 80mg/L, but still can not satisfy the water inlet COD of reverse osmosis desalination system
CrShould be less than the requirement of 30mg/L, long-time running still can be polluted said reverse osmosis membrane or caused it to stop up, and makes the fluctuation of service of technology, and the work-ing life of having reduced reverse osmosis membrane, has increased the running cost of technology.In order to address this problem; Chinese patent document CN102120663A discloses a kind of coking advanced waste treatment system and technology thereof; This technology will be sent into the micro ware auxiliary catalysis oxidizer unit through the coking chemical waste water after the A/O biochemical treatment, under the effect of microwave field, coking chemical waste water carried out catalytic oxidation treatment; Mixed reaction pond is sent in the water outlet of micro ware auxiliary catalysis oxidizer unit again, and interpolation pH value regulator transfers to 6.0-9.0 with the pH value of said coking chemical waste water in the coking chemical waste water in mixed reaction pond, adds coagulant aids again and carries out flocculation reaction; Coking chemical waste water after the completion flocculation reaction is sent into settling tank to be precipitated; Again the supernatant in the said settling tank is successively sent into the filtration with manganese sand device and accurate filter filters; Waste water through after the accurate filter filtration is sent into the frequently pole-reversing electroosmosis device, and the fresh water that behind said frequently pole-reversing electroosmosis device desalination, obtains promptly can be used as the recirculated cooling water moisturizing.Electrodialysis unit in the above-mentioned technology is compared with reverse osmosis unit for the requirement of influent quality and is wanted wide in range many, is usually less than 80mg/L and gets final product.Coking chemical waste water after above-mentioned micro ware auxiliary catalysis oxidizer unit is handled, the COD in the water
CrContent can reach below the 80mg/L, and the water outlet that after follow-up coagulating sedimentation+filtration with manganese sand device+accurate filter is handled, obtains again can be satisfied the water inlet requirement of electrodialysis unit fully.Therefore in this technology, preceding pre-treatment with after electrodialysis desalination plant between can reach coupling highly, make that said system can steady running, COD in the fresh water that after above-mentioned art breading, obtains
CrContent less than 80mg/L, the 1000mg/L that saltiness (total dissolve solid) requires less than GB.
But after above-mentioned advanced treatment process is handled; Saltiness in the fresh water can meet the requirement of GB; But in application of practical project, for some use occasion, the requirement that only can reach GB also can not be satisfied its production needs; Some industrial enterprise can propose than country or the more strict water quality requirement of industry standard according to self needs.In this case, above-mentioned technology then can't satisfy this requirement, how when further reducing the water outlet saltiness, can also guarantee system stable operation, is the still unsolved difficult problem of prior art.
The utility model content
In order to solve in the microwave catalysis oxidation style of using in the prior art and the coking advanced waste treatment system that electrodialytic technique combines; Though through after this art breading; Saltiness in the fresh water can meet the requirement of GB; But still can not satisfy the production needs of some industrial enterprise, even and the problem of system that can also steady running when further reducing the water outlet saltiness in the prior art.The utility model provides a kind of water outlet saltiness low and stable coking advanced waste treatment system.
The technical scheme of the coking advanced waste treatment system of the described efficient stable of the utility model is:
A kind of coking advanced waste treatment system of efficient stable comprises:
Micro cell;
The micro ware auxiliary catalysis oxidizer unit that is connected with said micro cell;
Be connected mixed reaction pond that is provided with and the settling tank that is connected with said mixed reaction pond with said micro ware auxiliary catalysis oxidizer unit;
The strainer that is connected with said settling tank;
The frequently pole-reversing electroosmosis device that is connected with said strainer;
Said coking advanced waste treatment system also comprises the reverse osmosis unit that is connected with the water outlet of said frequently pole-reversing electroosmosis device.
Described coking advanced waste treatment system also comprises:
The mixing equalizing tank that is connected with said micro cell, said mixing equalizing tank is arranged on before the said micro cell;
First intermediate pool, said first intermediate pool are arranged between said micro cell and the said micro ware auxiliary catalysis oxidizer unit;
Between said first intermediate pool and said micro ware auxiliary catalysis oxidizer unit, connect the dosing agitated pool that is provided with;
Between said settling tank and said strainer, connect second intermediate pool that is provided with, said second intermediate pool is provided with aerator.
Said strainer comprises prime filter, and first accurate filter that is connected with said prime filter, and said prime filter is arranged on before said first accurate filter.
Said prime filter is a kind of in filtration with manganese sand device and the more medium filter or both uses of connecting.
Also be provided with dense water circulation tank, said dense water circulation tank is connected with the water-in of said frequently pole-reversing electroosmosis device, dense water out and utmost point water out;
Between the water outlet of said frequently pole-reversing electroosmosis device and said reverse osmosis unit, also be provided with Buffer Pool;
The dense water out of said reverse osmosis unit is connected with said second intermediate pool.
Between said Buffer Pool and said reverse osmosis unit, also be provided with second accurate filter.
Treatment process based on the coking advanced waste treatment system of above-mentioned efficient stable comprises:
(1) coking chemical waste water after biochemical treatment is added acid and be adjusted to the pH value for 2.0-4.0; In the presence of the iron carbon filler coking chemical waste water that adds after acid is regulated is being carried out aeration; GWR is 3:1-8:1, and be 0.5-1h the duration of contact of said coking chemical waste water and said iron carbon filler;
(2) in the water outlet after step (1) is handled, add ferrous salt and ydrogen peroxide 50 and stir, under the effect of microwave field, carry out catalytic oxidation treatment;
(3) in the water outlet after step (2) is handled, add pH value regulator the pH value of said coking chemical waste water is transferred to 6.0-9.0, add coagulant aids again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is precipitated;
(4) supernatant that post precipitation is formed filters, and the waste water after filtering is sent into the frequently pole-reversing electroosmosis device;
The fresh water that (5) will behind said frequently pole-reversing electroosmosis device desalination, obtain is sent into reverse osmosis unit, and the fresh water that behind the reverse osmosis unit desalination, obtains again promptly can be used as the recirculated cooling water moisturizing.
In the said step (2), the interpolation concentration of said ferrous salt is with Fe
2+The 0.3-0.36 that counts COD concentration in the water outlet after step (1) is handled doubly, the interpolation concentration of said ydrogen peroxide 50 is with H
2O
2The 2.12-2.54 that counts COD concentration in the water outlet after step (1) is handled doubly, the residence time of said coking chemical waste water in said microwave field is 30-60s;
In the said step (3), said coagulant aids is a cationic-type polyacrylamide, and the addition of said coagulant aids is 1-7mg/L.
Coking chemical waste water after biochemical treatment imports earlier and mixes equalizing tank, again micro cell is sent in the water outlet of said mixing equalizing tank and is carried out the processing in the said step (1);
In the said step (2); Water outlet after micro cell is handled is introduced into first intermediate pool; Again the dosing agitated pool is sent in the water outlet of said first intermediate pool, added ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said dosing agitated pool and stir, send into the micro ware auxiliary catalysis oxidizer unit again; Under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment, the microwave output power of said micro ware auxiliary catalysis oxidizer unit is 20-120kW;
In the said step (3); Coking chemical waste water after the completion flocculation reaction is sent into settling tank to be precipitated; Supernatant in the said settling tank is introduced into second intermediate pool, and the aerator in said second intermediate pool is sent it into strainer again and filtered after said supernatant is carried out aeration.
70-75% from the dense water that said frequently pole-reversing electroosmosis device comes out and the utmost point water that comes out from said frequently pole-reversing electroosmosis device get into dense water circulation tank, are back to the water-in of said frequently pole-reversing electroosmosis device after the two mixes again from said dense water circulation tank;
The fresh water that comes out from said frequently pole-reversing electroosmosis device gets into Buffer Pool, sends into said reverse osmosis unit from said Buffer Pool again, concentrate recirculation to said second intermediate pool of coming out from said reverse osmosis unit.
The described advanced treatment process of coking waste water of the utility model; Step (1) adds acid to the coking chemical waste water after the A/O biochemical treatment and is adjusted to the pH value for 2.0-4.0; In the presence of the iron carbon filler coking chemical waste water that adds after acid is regulated is being carried out aeration then; GWR is 3:1-8:1, and be 0.5-1h the duration of contact of said coking chemical waste water and said iron carbon filler; Step (1) is that coking chemical waste water is carried out little electrolysis treatment, and little electrolysis is under cold situation, utilizes the micro-electrolysis stuffing of filling in the equipment to produce " galvanic cell " effect waste water is handled.After water flowing, in equipment, can form " galvanic cell " that countless potential differences reaches 1.2V, " galvanic cell " done ionogen with waste water; Form electric current through discharge waste water is carried out electrolytic oxidation and reduction processing; To reach the purpose of degradable organic pollutant, micro-electrolysis reaction need carry out under acidic conditions, in order to guarantee the effect of electrolysis treatment; The pH value that the utility model is provided with coking chemical waste water is 2.0-4.0; Be 0.5-1h the duration of contact of coking chemical waste water and iron carbon filler, the coking chemical waste water in the utility model after little electrolysis treatment, its COD
CrContent reduced 30-50% than former water.
Water outlet in the step (2) after said micro cell electrolysis treatment gets into said micro ware auxiliary catalysis oxidizer unit; Add ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said micro ware auxiliary catalysis oxidizer unit and stir, under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment; Said ferrous ion and peroxo-Hydrogen Energy generate the hydroxyl radical free radical of strong oxidizing property, and the organism generation organic free radical with difficult degradation in the aqueous solution makes it structure deteriorate, final oxygenolysis.
It is 30-60s that the utility model also is provided with the residence time of said coking chemical waste water in said microwave field; Reason is, if the said residence time be provided with too short, also just lower to removal effect of organic matter; Thereby cause water outlet COD higher, easy blocking is perhaps polluted the film in the desalination plant; If it is long that the said residence time is provided with; Can increase the construction cost of said technology again, the utility model is according to the characteristic of said coking chemical waste water, and it is 30-60s that the said residence time is set; Removing significantly the organic while in the water, also reducing the construction cost of said technology as far as possible.
The microwave output power that the utility model also is provided with said micro ware auxiliary catalysis oxidizer unit is 20-120kW; Said microwave output power is that the flooding quantity size according to said advanced treatment system is provided with; Power setting is too small if flooding quantity is big; Then do not reach the water outlet effect of expection; And if that the flooding quantity smaller power is provided with is very big, then can improve the working cost of said micro ware auxiliary catalysis oxidizer unit, cause unnecessary waste; The utility model is through with reference to the water inlet scope that possibly occur in the reality, and the microwave output power that limits said micro ware auxiliary catalysis oxidizer unit is 20-120kW; As preferred embodiment, the microwave output power that the utility model further limits said micro ware auxiliary catalysis oxidizer unit is 40-60kW;
The utility model also is provided with the interpolation concentration of said ferrous salt with Fe
2+The 0.3-0.36 that counts water COD concentration into doubly, the interpolation concentration of said ydrogen peroxide 50 is with H
2O
2The 2.12-2.54 that counts water COD concentration into doubly.Why be provided with like this,, can cause said micro ware auxiliary catalysis oxidation not reach due catalyzed oxidation effect if be because the addition of ferrous salt and ydrogen peroxide 50 is too small.But as Fe as catalyzer
2+When consumption increases, too much Fe
2+Can consume ydrogen peroxide 50 and form ferric iron, reduce treatment effect.And for ydrogen peroxide 50, excessive H
2O
2Hydroxyl radical free radical in meeting and the water reacts, and said ferrous ion is oxidized to ferric iron, and then reduces the catalytic effect of said medicament, and the excessive running cost that also can improve said technology of pharmaceutical quantities.Therefore only when the addition of molysite and ydrogen peroxide 50 suits, could when minimizing cost, reach best treatment effect.Step (3) is sent the water outlet of said micro ware auxiliary catalysis oxidizer unit into said mixed reaction pond, and interpolation pH value regulator transfers to 6.0-9.0 with the pH value of said coking chemical waste water in the coking chemical waste water in said mixed reaction pond; Add coagulant aids again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is sent into settling tank precipitate; The pH value of regulating said coking chemical waste water transfers to 6.0-9.0; Reason is; The water inlet of mixed reaction pond all keeps acid in step (1) before and step (2); And the tart reuse water is not suitable for as the recirculated cooling water moisturizing, and adding pH value regulator at this can be suitable for said reuse water furnishing to be used as the neutral of recirculated cooling water moisturizing or omit meta-alkalescence water; In addition, through adding pH value regulator, in said waste water, introduced an amount of OH
-Ion, said OH
-Ion combines with iron ion in the waste water, forms bigger flco, has accelerated sedimentary speed.Handle through said coagulating sedimentation, can effectively remove colloidal particle and fine suspension in the waste water, thereby reduce the turbidity and the colourity of said coking chemical waste water.
Step (4) is sent the supernatant in the said settling tank into strainer and is filtered, and purpose is for follow-up electrodialysis desalination good water inlet condition to be provided; To pass through filtering waste water and send into the frequently pole-reversing electroosmosis device; The fresh water that step (5) will obtain behind said frequently pole-reversing electroosmosis device desalination is sent into reverse osmosis unit again; The desalting efficiency of reverse osmosis unit is very high; Fresh water saltiness after said reverse osmosis unit is handled is lower, and it always dissolves solid content and is approximately 20-90mg/L.
The advantage of the described coking advanced waste treatment system of the utility model is:
(1) the described coking advanced waste treatment system of the utility model comprises micro cell, micro ware auxiliary catalysis oxidizer unit, coagulating sedimentation treatment unit, strainer, electrodialysis unit and reverse osmosis unit.Micro cell in the utility model, it has mainly acted on following 2 points:
The first, remove the portion C OD in the coking chemical waste water in advance
CrCoking chemical waste water after said micro cell is handled, COD
CrContent reduced 30-50%, COD in the water outlet that after follow-up microwave catalysis oxidation, coagulating sedimentation, filtration, electrodialyzer are handled, obtains again
CrContent lower, between 15-25mg/L, can satisfy reverse osmosis unit water inlet COD
CrContent is lower than the requirement of 30mg/L, has avoided reverse osmosis membrane that the phenomenon of stopping up or polluting takes place.
The second, reduced saltiness in the coking chemical waste water that gets into electrodialysis unit and reverse osmosis unit.Because COD in the coking chemical waste water after micro cell is handled
CrContent reduce greatly, therefore in follow-up microwave catalysis oxidation step, the dosage of ferrous salt also reduces greatly, after ferrous salt is added in the coking chemical waste water, though Fe wherein
2+Ion can be removed through follow-up coagulating sedimentation, but the negatively charged ion of its introducing still is present in the system, so adding of ferrous salt can increase the saltiness of coking chemical waste water, thereby has increased the load of electrodialysis unit and reverse osmosis unit, makes its reduction in work-ing life.The utility model falls a part of COD through the micro cell pre-treatment is set
Cr, reduced the dosage of molysite, thereby reduced the microwave catalysis oxidizer unit saltiness in the coking chemical waste water of coming out.
Therefore; Handle through said micro cell; COD content and saltiness in the coking chemical waste water that after follow-up microwave catalysis oxidation, coagulating sedimentation, filtration, electrodialysis process, obtains again are all lower; Thereby make formerly device with after electrodialysis and reverse osmosis desalination plant can be complementary, system can realize steady running.
In addition; Also has synergy between little electrolysis described in the utility model and the microwave catalysis oxidation; In the utility model in the micro cell pH value of coking chemical waste water be 2-4; Carry out micro ware auxiliary catalysis oxidation requirement pH and be lower than 6.0, the waste water that therefore comes out from said micro cell does not need re-adjustment pH when getting into the micro ware auxiliary catalysis oxidizer unit; And said micro cell can produce a part of Fe when operation
2+, this part Fe
2+Ion can be used as catalyzer and is used effectively after getting into the microwave catalysis oxidizer unit, thereby has reduced the dosage of ferrous salt in the microwave catalysis oxidation step.
(2) the described coking advanced waste treatment system of the utility model, it is a kind of or two kinds of series connection uses in filtration with manganese sand device and the more medium filter that said strainer also further is set.Said filtration with manganese sand device and/or more medium filter, the pigment in the water is removed in the small suspended substance and the absorption that can effectively filter out in the waste water, and then reduces the turbidity and the colourity of waste water.
(3) the described coking advanced waste treatment system of the utility model; Also be provided with dense water circulation tank; Said dense water circulation tank is connected with the water-in of said frequently pole-reversing electroosmosis device, dense water out and utmost point water out; When actual motion, the dense water and the utmost point water that come out from said frequently pole-reversing electroosmosis device are introduced into dense water circulation tank, are back to the water-in of said frequently pole-reversing electroosmosis device again from said dense water circulation tank; The utility model can be so that quantity of circulating water keeps balance through utmost point water being replenished into dense water circulation tank; Because electrodialysis has 70 ~ 75% concentrate recirculation to advance dense water circulation tank; Remaining dense water of 25 ~ 30% effluxes; If utmost point water is not replenished into dense water circulation tank, can cause the water level of dense water circulation tank to descend gradually; The salinity that removes owing to electrodialysis in addition all is concentrated in the dense water; If do not replenish utmost point water, the saltiness of dense water circulation tank can build up, and is increasingly high; And the saltiness of utmost point water is far below dense water; Add in the dense water circulation tank, just can guarantee that the saltiness of dense water circulation tank is in a basic balance, be unlikely to accumulate De Taigao.
(4) the described coking advanced waste treatment system of the utility model; Between the water outlet of said frequently pole-reversing electroosmosis device and said second accurate filter, also be provided with Buffer Pool, the dense water out of said reverse osmosis unit is connected with said second intermediate pool.The fresh water that comes out from said frequently pole-reversing electroosmosis device during actual motion is successively through getting into said reverse osmosis unit behind the Buffer Pool and second accurate filter, concentrate recirculation to said second intermediate pool of coming out from said reverse osmosis unit.The utility model is in frequently pole-reversing electroosmosis and reverse osmosis desalination system; Through improving dense water cycle mode; Under the situation that does not reduce water use efficiency; Improved effluent quality greatly, made that 70-75% and the whole dense water of reverse osmosis unit in the dense water of said electrodialysis unit can both obtain reuse, the water use efficiency of whole desalination plant can reach 75%.
Description of drawings
For the content that makes the utility model is expressly understood more easily, below in conjunction with specific embodiment and accompanying drawing the content of the utility model is done further detailed explanation, wherein
Fig. 1 is the structure iron of the described coking advanced waste treatment system of the utility model;
Fig. 2 is provided with the structure iron of the coking advanced waste treatment system that mixes equalizing tank and intermediate pool for the utility model is described;
Fig. 3 is the described structure iron that is provided with the coking advanced waste treatment system of dense water circulation tank and Buffer Pool of the utility model;
Wherein, Reference numeral is:
The 1-micro cell; 2-micro ware auxiliary catalysis oxidizer unit; The 3-mixed reaction pond; The 4-settling tank; 5-filtration with manganese sand device; 6-frequently pole-reversing electroosmosis device; The 7-reverse osmosis unit; 8-mixing equalizing tank; 9-first intermediate pool; 10-dosing agitated pool; 11-second intermediate pool; The 12-more medium filter; 13-first accurate filter; The 14-Buffer Pool; 15-second accurate filter; The dense water circulation tank of 16-.
Embodiment
Embodiment 1
Coking advanced waste treatment system described in the present embodiment is as shown in Figure 1, comprising:
Micro cell 1;
The micro ware auxiliary catalysis oxidizer unit 2 that is connected with said micro cell 1;
Be connected mixed reaction pond 3 that is provided with and the settling tank 4 that is connected with said mixed reaction pond 3 with said micro ware auxiliary catalysis oxidizer unit 2;
With the strainer that said settling tank 4 is connected, the strainer that uses in the present embodiment is filtration with manganese sand device 5;
The frequently pole-reversing electroosmosis device 6 that is connected with said filtration with manganese sand device 5;
Said coking advanced waste treatment system also comprises the reverse osmosis unit 7 that is connected with the water outlet of said frequently pole-reversing electroosmosis device 6.
The treatment process of the coking advanced waste treatment system described in the present embodiment is:
(1) coking chemical waste water after biochemical treatment is with 1200m
3The flooding quantity of/d gets into micro cell 1; The pH value that adds the said coking chemical waste water of acid adjusting in the coking chemical waste water in said micro cell 1 is 2.0; And said coking chemical waste water carried out aeration, and GWR is 3:1, be 0.5h the duration of contact of the iron carbon filler in said coking chemical waste water and the said micro cell 1;
(2) water outlet after said micro cell 1 electrolysis treatment gets into said micro ware auxiliary catalysis oxidizer unit 2; Add ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said micro ware auxiliary catalysis oxidizer unit 2 and stir, under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment;
The interpolation concentration of ferrous salt described in the present embodiment is with Fe
2+Counting 48 mg/L, is 0.3 times of COD concentration in the water outlet after step (1) is handled; The interpolation concentration of said ydrogen peroxide 50 is with H
2O
2Counting 339.2 mg/L, is 2.12 times of COD concentration in the water outlet after step (1) is handled, and the residence time of said coking chemical waste water in said microwave field is 30s; The microwave output power of the oxidizer unit of micro ware auxiliary catalysis described in the present embodiment 2 is 20kW.
(3) water outlet of said micro ware auxiliary catalysis oxidizer unit 2 gets into said mixed reaction pond 3, and interpolation lime transfers to 6.0 with the pH value of said coking chemical waste water in the coking chemical waste water in said mixed reaction pond 3; Add cationic-type polyacrylamide again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is sent into settling tank 4 precipitate, the addition of said cationic-type polyacrylamide is 10mg/L;
(4) supernatant in the said settling tank 4 is sent into filtration with manganese sand device 5 and filter, the waste water after strainer filters is sent into frequently pole-reversing electroosmosis device 6;
The fresh water that (5) will behind said frequently pole-reversing electroosmosis device 6 desalinations, obtain is sent into reverse osmosis unit 7, and the fresh water that behind reverse osmosis unit 7 desalinations, obtains again promptly can be used as the recirculated cooling water moisturizing.
Embodiment 2
Coking advanced waste treatment system described in the present embodiment is identical with embodiment 1.
The treatment process of the coking advanced waste treatment system described in the present embodiment is:
(1) coking chemical waste water after the A/O biochemical treatment is with 1200m
3The flooding quantity of/d gets into micro cell 1; The pH value that adds the said coking chemical waste water of acid adjusting in the coking chemical waste water in said micro cell 1 is 4.0; And said coking chemical waste water carried out aeration, and GWR is 8:1, be 1h the duration of contact of the iron carbon filler in said coking chemical waste water and the said micro cell 1;
(2) water outlet after said micro cell 1 electrolysis treatment gets into said micro ware auxiliary catalysis oxidizer unit 2; Add ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said micro ware auxiliary catalysis oxidizer unit 2 and stir, under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment;
The interpolation concentration of ferrous salt described in the present embodiment is with Fe
2+Counting 49.5 mg/L, is 0.3 times of COD concentration in the water outlet after step (1) is handled; The interpolation concentration of said ydrogen peroxide 50 is with H
2O
2Counting 349.8 mg/L, is 2.12 times of COD concentration in the water outlet after step (1) is handled, and the residence time of said coking chemical waste water in said microwave field is 30s; The microwave output power of the oxidizer unit of micro ware auxiliary catalysis described in the present embodiment 2 is 40kW.
(3) said mixed reaction pond 3 is sent in the water outlet of said micro ware auxiliary catalysis oxidizer unit 2, interpolation sodium hydroxide regulator transfers to 6.0 with the pH value of said coking chemical waste water in the coking chemical waste water in said mixed reaction pond 3; Add cationic-type polyacrylamide again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is sent into settling tank 4 precipitate; The addition of said cationic-type polyacrylamide is 7mg/L;
(4) supernatant in the said settling tank 4 is sent into filtration with manganese sand device 5 and filter, the waste water that will pass through after filtration with manganese sand device 5 filters is sent into frequently pole-reversing electroosmosis device 6;
The fresh water that (5) will behind said frequently pole-reversing electroosmosis device 6 desalinations, obtain is sent into reverse osmosis unit 7, and the fresh water that behind reverse osmosis unit 7 desalinations, obtains again promptly can be used as the recirculated cooling water moisturizing.
Embodiment 3
Coking advanced waste treatment system described in the present embodiment is as shown in Figure 2, comprising:
Mix equalizing tank 8; Be connected with micro cell 1 with the said equalizing tank 8 that mixes; Be connected with first intermediate pool 9 with said micro cell 1; After said first intermediate pool 9, also be connected with dosing agitated pool 10, be connected with micro ware auxiliary catalysis oxidizer unit 2 with said dosing agitated pool 10;
Be connected the mixed reaction pond 3 that is provided with said micro ware auxiliary catalysis oxidizer unit 2, and the settling tank 4 that is connected with said mixed reaction pond 3, being connected with second intermediate pool 11 with said settling tank 4, said second intermediate pool 11 is provided with aerator;
The more medium filter 12 that is connected with said second intermediate pool 11 is connected with first accurate filter 13 with said more medium filter 12;
The frequently pole-reversing electroosmosis device 6 that is connected with said first accurate filter 13;
Said coking advanced waste treatment system also comprises the reverse osmosis unit 7 that is connected with the water outlet of said frequently pole-reversing electroosmosis device 6, between said frequently pole-reversing electroosmosis device 6 and said reverse osmosis unit 7, is provided with second accurate filter 15.
The treatment process of the coking advanced waste treatment system described in the present embodiment is:
(1) coking chemical waste water after the A/O biochemical treatment is with 8000m
3The flooding quantity of/d imports and mixes equalizing tank 8; Again the coking chemical waste water in the said mixing equalizing tank 8 is sent into said micro cell 1; The pH value that adds the said coking chemical waste water of acid adjusting in the coking chemical waste water in said micro cell 1 is 2.0; And said coking chemical waste water carried out aeration, and GWR is 5:1, be 0.5h the duration of contact of the iron carbon filler in said coking chemical waste water and the said micro cell 1;
(2) water outlet after said micro cell 1 electrolysis treatment is introduced into first intermediate pool 9; Get into said dosing agitated pool 10 from said first intermediate pool 9 again; Add ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said dosing agitated pool 10 and stir; Send into said micro ware auxiliary catalysis oxidizer unit 2 again, under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment
The interpolation concentration of ferrous salt described in the present embodiment is with Fe
2+Counting 53.64mg/L, is 0.36 times of COD concentration in the water outlet after step (1) is handled; The interpolation concentration of said ydrogen peroxide 50 is with H
2O
2Counting 378.46mg/L, is 2.54 times of COD concentration in the water outlet after step (1) is handled, and the residence time of said coking chemical waste water in said microwave field is 60s; The microwave output power of the oxidizer unit of micro ware auxiliary catalysis described in the present embodiment 2 is 60kW.
(3) said mixed reaction pond 3 is sent in the water outlet of said micro ware auxiliary catalysis oxidizer unit 2, interpolation sodium hydrogencarbonate regulator transfers to 9.0 with the pH value of said coking chemical waste water in the coking chemical waste water in said mixed reaction pond 3; Add cationic-type polyacrylamide again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is sent into settling tank 4 precipitate, the addition of said cationic-type polyacrylamide is 5mg/L;
(4) supernatant in the said settling tank 4 successively being sent into said more medium filter 12 filters with said first accurate filter 13; Waste water after will filtering through first accurate filter 13 is sent into frequently pole-reversing electroosmosis device 6;
(5) will after the fresh water that obtains behind said frequently pole-reversing electroosmosis device 6 desalinations sent into 15 filtrations of second accurate filter, send into said reverse osmosis unit 7 again, and behind reverse osmosis unit 7 desalinations, obtain fresh water and promptly can be used as the recirculated cooling water moisturizing.
Embodiment 4
Coking advanced waste treatment system described in the present embodiment is as shown in Figure 3, comprising:
Mix equalizing tank 8; Be connected with micro cell 1 with the said equalizing tank 8 that mixes; Be connected with first intermediate pool 9 with said micro cell 1; After said first intermediate pool 9, also be connected with dosing agitated pool 10, be connected with micro ware auxiliary catalysis oxidizer unit 2 with said dosing agitated pool 10;
Be connected the mixed reaction pond 3 that is provided with said micro ware auxiliary catalysis oxidizer unit 2, and the settling tank 4 that is connected with said mixed reaction pond 3, being connected with second intermediate pool 11 with said settling tank 4, said second intermediate pool 11 is provided with aerator;
Be connected with filtration with manganese sand device 5 and more medium filter 12 with said second intermediate pool 11, also be connected with first accurate filter 13 with said more medium filter 12;
Be connected with frequently pole-reversing electroosmosis device 6 with said first accurate filter 13; Be connected with Buffer Pool 14 with the water outlet of said frequently pole-reversing electroosmosis device 6; Be connected with second accurate filter 15 with said Buffer Pool 14, be connected with reverse osmosis unit 7 with said second accurate filter 15.
In addition, the coking advanced waste treatment system in the present embodiment also is provided with dense water circulation tank 16, and said dense water circulation tank 16 is connected with the water-in of said frequently pole-reversing electroosmosis device 6, dense water out and utmost point water out; The dense water out of said reverse osmosis unit 7 is connected with said second intermediate pool 11.
The treatment process of the coking advanced waste treatment system described in the present embodiment is:
(1) coking chemical waste water after biochemical treatment is with 13000m
3The flooding quantity of/d imports and mixes equalizing tank 8; Again the coking chemical waste water in the said mixing equalizing tank 8 is sent into said micro cell 1; The pH value that adds the said coking chemical waste water of acid adjusting in the coking chemical waste water in said micro cell 1 is 3.0; And said coking chemical waste water carried out aeration, and GWR is 6:1, be 0.5h the duration of contact of the iron carbon filler in said coking chemical waste water and the said micro cell 1;
(2) water outlet after said micro cell 1 electrolysis treatment is introduced into said first intermediate pool 9; Get into said dosing agitated pool 10 from said first intermediate pool 9 again; Add ferrous salt and ydrogen peroxide 50 in the coking chemical waste water in said dosing agitated pool 10 and stir; Send into said micro ware auxiliary catalysis oxidizer unit 2 again, under the effect of microwave field, coking chemical waste water is carried out catalytic oxidation treatment;
The interpolation concentration of ferrous salt described in the present embodiment is with Fe
2+Counting 50.4mg/L, is 0.36 times of COD concentration in the water outlet after step (1) is handled; The interpolation concentration of said ydrogen peroxide 50 is with H
2O
2Counting 355.6 mg/L, is 2.54 times of COD concentration in the water outlet after step (1) is handled, and the residence time of said coking chemical waste water in said microwave field is 60s; The microwave output power of the oxidizer unit of micro ware auxiliary catalysis described in the present embodiment 2 is 120kW.
(3) said mixed reaction pond 3 is sent in the water outlet of said micro ware auxiliary catalysis oxidizer unit 2, interpolation sodium hydrogencarbonate regulator transfers to 9.0 with the pH value of said coking chemical waste water in the coking chemical waste water in said mixed reaction pond 3; Add cationic-type polyacrylamide again and carry out flocculation reaction, the coking chemical waste water after the completion flocculation reaction is sent into settling tank 4 precipitate;
The addition of said cationic-type polyacrylamide is 3mg/L;
(4) supernatant in the said settling tank 4 successively being sent into said filtration with manganese sand device 5, more medium filter 12 and said first accurate filter 13 filters; Waste water after will filtering through first accurate filter 13 is sent into frequently pole-reversing electroosmosis device 6;
(5) from the dense water that said frequently pole-reversing electroosmosis device 6 comes out 75%; And be introduced into dense water circulation tank 16 from the utmost point water that said frequently pole-reversing electroosmosis device 6 comes out, after mixing, the two is back to the water-in of said frequently pole-reversing electroosmosis device 6 again from said dense water circulation tank 16; The fresh water that comes out from said frequently pole-reversing electroosmosis device 6 gets into Buffer Pool 14, after second accurate filter 15 filters, sends into said reverse osmosis unit 7 again, and the concentrate recirculation that comes out from said reverse osmosis unit 7 is said second intermediate pool 11 extremely.
In embodiment 1-4, the specific configuration of said micro cell 1 is:
The filler that adopts in the said micro cell 1 is commercially available iron-carbon micro-electrolysis filler, and filler proportion is 1 ton/cubic metre, and specific surface area is 1.2 meters squared per gram, and voidage is 65%.
The operation volts DS of said frequently pole-reversing electroosmosis is 80 ~ 130V, and the interval of falling the interpolar is 40 ~ 90 minutes;
The operating pressure of said r-o-is 0.5 ~ 1.5MPa.
In the above-described embodiments, in " adding the pH value that said coking chemical waste water is regulated in acid in the coking chemical waste water in said dosing agitated pool ", said acid can be such as in the acid such as sulfuric acid, hydrochloric acid, nitric acid any one or multiple.The selection of this acid is to well known to a person skilled in the art technology, there is no need to give exhaustive at this again.Equally as selectable embodiment, the pH value regulator described in the foregoing description can be in milk of lime or other commercially available arbitrarily pH value regulator one or more, like lime, yellow soda ash etc.; Coagulant aids in the foregoing description can also be selected other arbitrarily commercially available coagulant aids except " cationic-type polyacrylamide ", such as anion-polyacrylamide etc.
Water quality situation before and after handling
In order to further specify the technique effect of the described coking advanced waste treatment system of the utility model, down in the face of describing through the effluent quality situation of the described coking chemical waste water of the utility model after each technique unit is handled:
Can find out the COD in the coking chemical waste water after the micro cell in the utility model, microwave catalysis oxidizer unit, electrodialysis unit are handled from The above results
CrContent less than 30mg/L, can satisfy the water inlet requirement of reverse osmosis unit, can guarantee the long-term stability operation of process system.
Other index to the water outlet of each technique unit detects as follows:
Can find out that from The above results the fresh water saltiness after the reverse osmosis unit described in the utility model is handled is lower, it always dissolves solid content and is approximately 20-90mg/L.
Obviously, the foregoing description only be for explanation clearly done for example, and be not qualification to embodiment.For the those of ordinary skill in affiliated field, on the basis of above-mentioned explanation, can also make other multi-form variation or change.Here need not also can't give all embodiments exhaustive, and conspicuous variation of being extended out thus or change still are among the protection domain that the utility model creates.
Claims (6)
1. the coking advanced waste treatment system of an efficient stable comprises:
Micro cell;
The micro ware auxiliary catalysis oxidizer unit that is connected with said micro cell;
Be connected mixed reaction pond that is provided with and the settling tank that is connected with said mixed reaction pond with said micro ware auxiliary catalysis oxidizer unit;
The strainer that is connected with said settling tank;
The frequently pole-reversing electroosmosis device that is connected with said strainer;
Said coking advanced waste treatment system also comprises the reverse osmosis unit that is connected with the water outlet of said frequently pole-reversing electroosmosis device.
2. treatment system according to claim 1 is characterized in that, also comprises:
The mixing equalizing tank that is connected with said micro cell, said mixing equalizing tank is arranged on before the said micro cell;
First intermediate pool, said first intermediate pool are arranged between said micro cell and the said micro ware auxiliary catalysis oxidizer unit;
Between said first intermediate pool and said micro ware auxiliary catalysis oxidizer unit, connect the dosing agitated pool that is provided with;
Between said settling tank and said strainer, connect second intermediate pool that is provided with, said second intermediate pool is provided with aerator.
3. treatment system according to claim 1 and 2 is characterized in that said strainer comprises prime filter, and first accurate filter that is connected with said prime filter, and said prime filter is arranged on before said first accurate filter.
4. treatment system according to claim 3 is characterized in that, said prime filter is a kind of in filtration with manganese sand device and the more medium filter or both uses of connecting.
5. according to claim 1 or 2 or 4 described treatment systems, it is characterized in that, also be provided with dense water circulation tank, said dense water circulation tank is connected with the water-in of said frequently pole-reversing electroosmosis device, dense water out and utmost point water out;
Between the water outlet of said frequently pole-reversing electroosmosis device and said reverse osmosis unit, also be provided with Buffer Pool;
The dense water out of said reverse osmosis unit is connected with said second intermediate pool.
6. treatment system according to claim 5 is characterized in that, between said Buffer Pool and said reverse osmosis unit, also is provided with second accurate filter.
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| Application Number | Priority Date | Filing Date | Title |
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| CN2012201675034U CN202576143U (en) | 2012-04-19 | 2012-04-19 | High-efficient and stable coking wastewater deep treatment system |
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104291505A (en) * | 2014-09-18 | 2015-01-21 | 中国海洋石油总公司 | Method for treating oily wastewater by combining microwave enhanced iron carbon treatment with microwave oxidation |
| CN105036434A (en) * | 2015-08-26 | 2015-11-11 | 广东省工程技术研究所 | Method for treating landfill leachate nanofiltration concentrated solution through iron-carbon micro-electrolysis synergistic with microwave |
-
2012
- 2012-04-19 CN CN2012201675034U patent/CN202576143U/en not_active Expired - Lifetime
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104291505A (en) * | 2014-09-18 | 2015-01-21 | 中国海洋石油总公司 | Method for treating oily wastewater by combining microwave enhanced iron carbon treatment with microwave oxidation |
| CN104291505B (en) * | 2014-09-18 | 2016-01-20 | 中国海洋石油总公司 | A kind of method of microwave reinforced iron charcoal United microwave oxide treatment oily(waste)water |
| CN105036434A (en) * | 2015-08-26 | 2015-11-11 | 广东省工程技术研究所 | Method for treating landfill leachate nanofiltration concentrated solution through iron-carbon micro-electrolysis synergistic with microwave |
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