CN205398337U - Fragrant integrative sewage treatment device of iron carbon - Google Patents
Fragrant integrative sewage treatment device of iron carbon Download PDFInfo
- Publication number
- CN205398337U CN205398337U CN201620151060.8U CN201620151060U CN205398337U CN 205398337 U CN205398337 U CN 205398337U CN 201620151060 U CN201620151060 U CN 201620151060U CN 205398337 U CN205398337 U CN 205398337U
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- fenton
- reative cell
- flabellum
- treating apparatus
- sewage treating
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Abstract
The utility model discloses a fragrant integrative sewage treatment device of iron carbon, including the feC reacting chamber, overflow cabin and fenton reacting chamber, be provided with the water inlet on the feC reacting chamber, the overflow under -deck overlaps in the feC reacting chamber, overflow tank top portion is equipped with the opening, fenton reacting chamber endotheca is in the overflow under -deck, fenton reacting chamber bottom is equipped with the trompil, the fenton reacting chamber is equipped with the delivery port, sewage passes through the water inlet and gets into the feC reacting chamber in proper order, overflow cabin and fenton reacting chamber, flow from the delivery port again after carrying out little electrolysis of feC and fenton reaction, reducing of the device space is realized to the integral structure, has saved area, has improved reaction efficiency, has practiced thrift the energy, reduce cost.
Description
Technical field
This utility model relates to technical field of sewage, is specifically related to a kind of ferrum carbon Fenton integrated sewage treating apparatus.
Background technology
High concentrated organic wastewater wide material sources, the waste water of the discharge such as printing and dyeing industry, pharmaceuticals industry mostly is high concentrated organic wastewater, organic concentration contained by this type of waste water is high, COD is typically in more than 2000mg/L, have even as high as several ten thousand so that hundreds of thousands mg/L, comparatively speaking, BOD is relatively low, and the ratio of a lot of waste water BOD and COD is less than 0.3；In addition such waste component is complicated, often also has aromatic compound and heterocyclic compound, more than containing sulfide, nitride, heavy metal and toxic organic compound, it is difficult to directly biochemical treatment.
Iron-carbon micro-electrolysis (Fe/C) and Fenton technique are the common methods processed for high concentrated organic wastewater.Fe/C micro-electrolysis method is to utilize Principles of Metal Erosion, utilizes Fe and C to form galvanic element and waste water is carried out light electrolysis；Fenton method is to utilize Fe2+And H2O2Reflection generates the Organic substance in hydroxyl radical free radical (OH) the oxidation Decomposition waste water that oxidisability is extremely strong.Two kinds of technological principle differences, have his own strong points.When sewage composition is excessively complicated, single Fe/C or Fenton is unable to reach effluent quality requirement, two kinds of techniques can carry out series connection and use.
Fe/C technique water inlet Optimal pH is 2～3, after micro-electrolysis reaction, pH can rise about 1 unit, and Fenton reaction water inlet optimal pH is 3～4, therefore from the requirement for influent quality, after high concentrated organic wastewater is adjusted pond adjustment entrance Fe/C technique, its water outlet pH is the suitable water inlet as Fenton technique just. in addition, in the process of Fe/C light electrolysis, ferrum can with Fe2+Form dissolution so that Fe in Fe/C Process for Effluent2+Content can increase, and just as the source of iron of Fenton reaction, therefore usually can be used by Fe/C+Fenton process integration.
But in existing Fe/C-Fenton combined treatment process, the process device of Fe/C and Fenton separates, and causes that floor space is big；And additional H in Fenton reaction2O2Price is high.Therefore, a kind of Fe/C-Fenton integrated sewage treating apparatus of design, to reduce occupation area of equipment, improves the efficiency of Fenton reaction to reduce H simultaneously2O2Make consumption thus the cost reducing waste water control is very necessary.
Summary of the invention
The technical problems to be solved in the utility model is, in view of the foregoing defects the prior art has, it is provided that a kind of ferrum carbon Fenton integrated sewage treating apparatus, integral structure realizes the reduction of the device space, saves floor space, improves reaction efficiency, save the energy, reduce cost.
This utility model be the technical scheme is that by the above-mentioned technical problem of solution
A kind of ferrum carbon Fenton integrated sewage treating apparatus, including Fe/C reative cell, overflow cabin and Fenton reative cell, Fe/C reative cell is provided with water inlet, it is placed in Fe/C reative cell in overflow cabin, top, overflow cabin is provided with opening, it is placed in overflow cabin in Fenton reative cell, it is provided with perforate bottom Fenton reative cell, Fenton reative cell is provided with outlet, sewage sequentially enters Fe/C reative cell, overflow cabin and Fenton reative cell by water inlet, flows out from outlet after carrying out Fe/C light electrolysis and Fenton reaction again.
Connecing technique scheme, be provided with Fe/C filler between described overflow cabin and Fe/C reative cell, the height of Fe/C filler is lower than overflow cabin entrance, and water inlet is arranged at the bottom of Fe/C reative cell, and outlet is arranged at Fenton reactor top.
Connect technique scheme, bottom described Fe/C reative cell, be provided with aerating system.
Connecing technique scheme, aerating system includes breather, aeration head and blower fan, and aeration head is evenly arranged on breather, and blower fan is connected with breather.
Connect technique scheme, be provided with one or more dividing plate in Fe/C reative cell, above each dividing plate, be equipped with charging aperture.
Connecing technique scheme, described dividing plate is netted.
Connect technique scheme, bottom Fe/C reative cell, be provided with mud valve.
Connect technique scheme, in described Fenton reative cell, be provided with impact flow reactor.
Connect technique scheme, described impact flow reactor includes rotating shaft, one or more first flabellum and one or more second flabellum, rotating shaft is arranged over motor, first flabellum and the second flabellum are arranged in rotating shaft, rotating shaft drives the first flabellum and the second flabellum to rotate, the flabellum of the first flabellum and the second flabellum is in opposite direction, forms contrary current direction during rotation.
Connecing technique scheme, be equipped with shading ring outside described first flabellum and the second flabellum, shading ring is all blow-by up and down, and shading ring is provided with stator, are connected fixing with Fenton reative cell tank body by stator.
This utility model has the advantages that
1, by the nesting type structure in Fe/C reative cell, overflow cabin and Fenton reative cell, carrying out Fe/C reative cell and Fenton reative cell in a tank body, integral structure reduces space, saves floor space, sewage and H in overflow cabin2O2Carried out premixing, improve reaction efficiency in subsequent step, in Fe/C reative cell sewage by overflow cabin can automatic overflow to Fenton reative cell, it is not necessary to unnecessary pump promotes, and has saved the energy, reduces cost.
2, form contrary current direction by impact flow reactor, make sewage occur impacting type to react in Fenton reative cell, with H2O2It is fully contacted, reacts, increase the reaction efficiency of Fenton reaction, reduce H2O2Make consumption, save the cost of sewage disposal.
Accompanying drawing explanation
Fig. 1 is the structural representation of ferrum carbon Fenton integrated sewage treating apparatus in this utility model embodiment；
Fig. 2 is the top view of Fig. 1；
Fig. 3 is that in this utility model embodiment, Fe/C fills schematic diagram；
Fig. 4 is Fenton reaction chamber structure figure in this utility model embodiment；
Fig. 5 be in this utility model embodiment sewage flow to schematic diagram；
In figure, 1-water inlet, 2-Fe/C reative cell, 2.1-dividing plate, 2.2-charging aperture, 2.3-aerating system, 2.3.1-aeration head, 2.3.2-breather, 2.3.3-blower fan, 2.4-mud valve, 3-overflow cabin, 3.1-H2O2Charge pipe, 4-Fenton reative cell, 4.1-rotating shaft, 4.2-the first flabellum, 4.3-the second flabellum, 4.4-shading ring, 4.5-stator, 5-outlet, 6-foot rest.
Detailed description of the invention
Below in conjunction with drawings and Examples, this utility model is described in detail.
With reference to shown in Fig. 1～Fig. 2, ferrum carbon Fenton integrated sewage treating apparatus in the embodiment that this utility model provides, including Fe/C reative cell 2, overflow cabin 3 and Fenton reative cell 4, Fe/C reative cell 2 is provided with water inlet 1, it is placed in Fe/C reative cell 2 in overflow cabin 3, top, overflow cabin 3 is provided with opening, it is placed in overflow cabin 3 in Fenton reative cell 4, it is provided with perforate bottom Fenton reative cell 4, Fenton reative cell 4 is provided with outlet 5, sewage sequentially enters Fe/C reative cell 2 by water inlet 1, overflow cabin 3 and Fenton reative cell 4, flow out from outlet 5 again after carrying out Fe/C light electrolysis and Fenton reaction；Sewage enters Fe/C reative cell 2 from water inlet 1, carries out Fe/C light electrolysis, then enters overflow cabin 3 from overflow cabin 3 open top, adds H from overflow cabin 3 open top simultaneously2O2, sewage is in overflow cabin 3 and H2O2Carry out initial contact and mix, then Fenton reative cell 4 is entered by the perforate bottom Fenton reative cell 4, after carrying out sufficient Fenton reaction, flow out from outlet 5, by the nesting type structure in Fe/C reative cell 2, overflow cabin 3 and Fenton reative cell 4, carrying out Fe/C reative cell 2 and Fenton reative cell 4 in a tank body, this integral structure realizes the reduction of the device space, save floor space, sewage and H in overflow cabin 32O2Carried out premixing, improve reaction efficiency in subsequent step, in Fe/C reative cell 2 sewage by overflow cabin 3 can automatic overflow to Fenton reative cell 4, it is not necessary to unnecessary pump promotes, and has saved the energy.
Further, it is provided with foot rest 6 bottom Fe/C reative cell 2.
Further, as it is shown on figure 3, be provided with Fe/C filler between described overflow cabin 3 and Fe/C reative cell 2, the height of Fe/C filler is lower than overflow cabin 3 entrance, and water inlet 1 is arranged at the bottom of Fe/C reative cell 2, and outlet 5 is arranged at Fenton reative cell 4 top.
Further, it is provided with aerating system 2.3 bottom described Fe/C reative cell 2；When sewage and Fe/C filler are reacted, aeration is uniform, it is provided that oxygen required in Fe/C microelectrolysis process.
Further, aerating system 2.3 includes breather 2.3.2, aeration head 2.3.1 and blower fan 2.3.3, and aeration head 2.3.1 is evenly arranged on breather 2.3.2, and blower fan 2.3.3 is connected with breather 2.3.2；Aeration head 2.3.1 is evenly arranged so that giving vent to anger uniformly, prevents trachea from blocking simultaneously.
Further, described breather 2.3.2 is ring-type.
Further, in Fe/C reative cell 2, it is provided with one or more dividing plate 2.1, is equipped with charging aperture 2.2, Fe/C filler above each dividing plate 2.1 and puts into from charging aperture 2.2；Dividing plate 2.1 is used for carrying Fe/C filler.
Further, Fe/C filler is arranged at above dividing plate 2.1, and Fe/C filler is filled full as much as possible, but the Fe/C filler of the superiors is not higher than top, overflow cabin 3, does not have Fe/C filler below basecoat dividing plate.
Further, described dividing plate 2.1 number is 2, is respectively intended to the Fe/C filler above carrying dividing plate 2.1.
Further, described dividing plate 2.1 is netted.
Further, it is provided with mud valve 2.4 bottom Fe/C reative cell 2；After Fe/C filler reacts for a long time, the Fe in filler can be consumed, and unnecessary carbon dust can form carbon mud, regularly will be arranged outside carbon mud by mud valve 2.4.
Further, as shown in Figure 4, it is provided with impact flow reactor in described Fenton reative cell 4；Form contrary current direction by impact flow reactor, make sewage occur impacting type to react in Fenton reative cell 4, with H2O2It is fully contacted, reacts, increase the reaction efficiency of Fenton reaction, reduce H2O2Make consumption, save the cost of sewage disposal.
Further, described impact flow reactor includes rotating shaft 4.1, one or more first flabellum 4.2 and one or more second flabellum 4.3, rotating shaft 4.1 is arranged over motor, first flabellum 4.2 and the second flabellum 4.3 are arranged in rotating shaft 4.1, rotating shaft 4.1 drives the first flabellum 4.2 and the second flabellum 4.3 to rotate, the flabellum of the first flabellum 4.2 and the second flabellum 4.3 is in opposite direction, forms contrary current direction during rotation；Rotated by the first flabellum 4.2 and the second flabellum 4.3 and form contrary current direction, make sewage occur impacting type to react in Fenton reative cell 4, with H2O2It is fully contacted, reacts, increase the reaction efficiency of Fenton reaction, reduce H2O2Make consumption, save the cost of sewage disposal.
Further, the first flabellum is arranged at above the second flabellum.
Further, being equipped with shading ring 4.4, the equal blow-by of shading ring about 4.4 outside described first flabellum 4.2 and the second flabellum 4.3, shading ring 4.4 is provided with stator 4.5, is connected fixing with Fenton reative cell 4 tank body by stator 4.5.
Further, described sewage-treatment plant is made of stainless steel.
Further, the open top of overflow cabin is arranged over H2O2Charge pipe 3.1.
In an embodiment of the present utility model, operation principle of the present utility model:
As shown in Figure 5, upon mediation pond is reconciled the waste water of extremely suitable pH and is entered bottom Fe/C reative cell 2 by water inlet 1, flow then up, it is fully contacted with Fe/C filler when by the gap of Fe/C filler, there is micro-electrolysis reaction, high-enriched organics is carried out initial breakdown, becomes Fe through the iron powder of micro-electrolysis reaction simultaneously2+It is dissolved in waste water；Overflow cabin 3 is entered from top, overflow cabin 3, at this and H through the reacted sewage of abundant Fe/C2O2The H flowed in charge pipe 3.12O2Carry out initial contact and mix, then entered Fenton reative cell 4 by the mouth of a river bottom Fenton reative cell 4；Containing Fe2+And H2O2Organic sewage under the effect of the first flabellum 4.2 and the second flabellum 4.3, in Fenton reative cell 4 occur impinging stream reaction, Fe2+And H2O2Fully reacting into the OH of strong oxidizing property, OH fully acts on the Organic substance in waste water simultaneously, is oxidized, is decomposed into small organic molecule, enters subsequent reactions unit.
Fenton reaction refers to H2O2At Fe2+Catalytic action under decompose produce OH, its oxidizing potential reaches 2.8V, and oxidation operation is resolved into little molecule by approach such as electron transfers by it, meanwhile, Fe2+It is oxidized to Fe3+Produce coagulating sedimentation, remove large amount of organic.There is oxidation and coagulation two kinds effect in water processes.
Above is only preferred embodiment of the present utility model, certainly with this interest field limiting this utility model, therefore can not change according to the equivalence that this utility model claim is made, still belong to protection domain of the present utility model.
Claims (10)
1. a ferrum carbon Fenton integrated sewage treating apparatus, it is characterized in that, including Fe/C reative cell, overflow cabin and Fenton reative cell, Fe/C reative cell is provided with water inlet, it is placed in Fe/C reative cell in overflow cabin, top, overflow cabin is provided with opening, it is placed in overflow cabin in Fenton reative cell, it is provided with perforate bottom Fenton reative cell, Fenton reative cell is provided with outlet, sewage sequentially enters Fe/C reative cell, overflow cabin and Fenton reative cell by water inlet, flows out from outlet after carrying out Fe/C light electrolysis and Fenton reaction again.
2. ferrum carbon Fenton integrated sewage treating apparatus according to claim 1, it is characterized in that, it is provided with Fe/C filler between described overflow cabin and Fe/C reative cell, the height of Fe/C filler is lower than overflow cabin entrance, water inlet is arranged at the bottom of Fe/C reative cell, and outlet is arranged at Fenton reactor top.
3. ferrum carbon Fenton integrated sewage treating apparatus according to claim 1, it is characterised in that be provided with aerating system bottom described Fe/C reative cell.
4. ferrum carbon Fenton integrated sewage treating apparatus according to claim 3, it is characterised in that aerating system includes breather, aeration head and blower fan, and aeration head is evenly arranged on breather, and blower fan is connected with breather.
5. ferrum carbon Fenton integrated sewage treating apparatus according to claim 1, it is characterised in that be provided with one or more dividing plate in Fe/C reative cell, be equipped with charging aperture above each dividing plate.
6. ferrum carbon Fenton integrated sewage treating apparatus according to claim 5, it is characterised in that described dividing plate is netted.
7. ferrum carbon Fenton integrated sewage treating apparatus according to claim 1, it is characterised in that be provided with mud valve bottom Fe/C reative cell.
8. ferrum carbon Fenton integrated sewage treating apparatus according to claim 1, it is characterised in that be provided with impact flow reactor in described Fenton reative cell.
9. ferrum carbon Fenton integrated sewage treating apparatus according to claim 8, it is characterized in that, described impact flow reactor includes rotating shaft, one or more first flabellum and one or more second flabellum, rotating shaft is arranged over motor, first flabellum and the second flabellum are arranged in rotating shaft, rotating shaft drives the first flabellum and the second flabellum to rotate, and the flabellum of the first flabellum and the second flabellum is in opposite direction, forms contrary current direction during rotation.
10. ferrum carbon Fenton integrated sewage treating apparatus according to claim 9, it is characterized in that, be equipped with shading ring outside described first flabellum and the second flabellum, shading ring is all blow-by up and down, shading ring is provided with stator, is connected fixing with Fenton reative cell tank body by stator.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201620151060.8U CN205398337U (en) | 2016-02-29 | 2016-02-29 | Fragrant integrative sewage treatment device of iron carbon |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201620151060.8U CN205398337U (en) | 2016-02-29 | 2016-02-29 | Fragrant integrative sewage treatment device of iron carbon |
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| Publication Number | Publication Date |
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| CN205398337U true CN205398337U (en) | 2016-07-27 |
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| Application Number | Title | Priority Date | Filing Date |
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| CN201620151060.8U Expired - Fee Related CN205398337U (en) | 2016-02-29 | 2016-02-29 | Fragrant integrative sewage treatment device of iron carbon |
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| CN (1) | CN205398337U (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105645647A (en) * | 2016-02-29 | 2016-06-08 | 武汉工程大学 | Fe/C-Fenton integrated sewage treatment device |
| CN109019837A (en) * | 2018-08-10 | 2018-12-18 | 杨明超 | A kind of aerobic aeration pond for sewage treatment |
-
2016
- 2016-02-29 CN CN201620151060.8U patent/CN205398337U/en not_active Expired - Fee Related
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105645647A (en) * | 2016-02-29 | 2016-06-08 | 武汉工程大学 | Fe/C-Fenton integrated sewage treatment device |
| CN105645647B (en) * | 2016-02-29 | 2019-03-08 | 武汉工程大学 | A kind of iron carbon Fenton integrated sewage treating apparatus |
| CN109019837A (en) * | 2018-08-10 | 2018-12-18 | 杨明超 | A kind of aerobic aeration pond for sewage treatment |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20160727 Termination date: 20190228 |
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| CF01 | Termination of patent right due to non-payment of annual fee |