CN203229430U - Strong oxidation reaction and flocculation filter integrated machine - Google Patents
Strong oxidation reaction and flocculation filter integrated machine Download PDFInfo
- Publication number
- CN203229430U CN203229430U CN 201320191658 CN201320191658U CN203229430U CN 203229430 U CN203229430 U CN 203229430U CN 201320191658 CN201320191658 CN 201320191658 CN 201320191658 U CN201320191658 U CN 201320191658U CN 203229430 U CN203229430 U CN 203229430U
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- water
- sand
- flocculation
- strong oxidizing
- oxidizing reaction
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- Expired - Lifetime
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- 238000005189 flocculation Methods 0.000 title claims abstract description 20
- 230000016615 flocculation Effects 0.000 title claims abstract description 18
- 238000007254 oxidation reaction Methods 0.000 title abstract description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 112
- 239000004576 sand Substances 0.000 claims abstract description 52
- 238000001914 filtration Methods 0.000 claims abstract description 30
- 238000006243 chemical reaction Methods 0.000 claims abstract description 24
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 61
- 239000000706 filtrate Substances 0.000 claims description 20
- 238000000605 extraction Methods 0.000 claims description 17
- 230000001590 oxidative effect Effects 0.000 claims description 15
- 239000011148 porous material Substances 0.000 claims description 15
- 239000004744 fabric Substances 0.000 claims description 12
- 238000005406 washing Methods 0.000 claims description 12
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 claims description 11
- 239000006004 Quartz sand Substances 0.000 claims description 10
- 206010016256 fatigue Diseases 0.000 claims description 6
- 210000000988 bone and bone Anatomy 0.000 claims description 5
- 230000003647 oxidation Effects 0.000 abstract description 16
- 239000000126 substance Substances 0.000 abstract description 7
- 239000000463 material Substances 0.000 abstract description 5
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 238000005516 engineering process Methods 0.000 abstract description 4
- 230000015556 catabolic process Effects 0.000 abstract description 3
- 238000006731 degradation reaction Methods 0.000 abstract description 3
- 239000003814 drug Substances 0.000 abstract description 3
- 239000007787 solid Substances 0.000 abstract 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract 1
- 229940079593 drug Drugs 0.000 abstract 1
- 229910052760 oxygen Inorganic materials 0.000 abstract 1
- 239000001301 oxygen Substances 0.000 abstract 1
- 239000013049 sediment Substances 0.000 abstract 1
- 238000000034 method Methods 0.000 description 16
- 239000012530 fluid Substances 0.000 description 7
- 239000010865 sewage Substances 0.000 description 7
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 5
- -1 hydroxyl radical free radical Chemical class 0.000 description 5
- 239000000203 mixture Substances 0.000 description 5
- 230000009286 beneficial effect Effects 0.000 description 4
- 229910052742 iron Inorganic materials 0.000 description 4
- 230000002829 reductive effect Effects 0.000 description 4
- 239000002351 wastewater Substances 0.000 description 4
- 239000012028 Fenton's reagent Substances 0.000 description 3
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 239000013078 crystal Substances 0.000 description 3
- 238000005868 electrolysis reaction Methods 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 238000009303 advanced oxidation process reaction Methods 0.000 description 2
- 239000003054 catalyst Substances 0.000 description 2
- 238000002425 crystallisation Methods 0.000 description 2
- 230000008025 crystallization Effects 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000011010 flushing procedure Methods 0.000 description 2
- SURQXAFEQWPFPV-UHFFFAOYSA-L iron(2+) sulfate heptahydrate Chemical compound O.O.O.O.O.O.O.[Fe+2].[O-]S([O-])(=O)=O SURQXAFEQWPFPV-UHFFFAOYSA-L 0.000 description 2
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 239000003403 water pollutant Substances 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 239000003570 air Substances 0.000 description 1
- 239000007806 chemical reaction intermediate Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000011118 depth filtration Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 235000003891 ferrous sulphate Nutrition 0.000 description 1
- 239000011790 ferrous sulphate Substances 0.000 description 1
- 230000003311 flocculating effect Effects 0.000 description 1
- 238000005243 fluidization Methods 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- QOSATHPSBFQAML-UHFFFAOYSA-N hydrogen peroxide;hydrate Chemical compound O.OO QOSATHPSBFQAML-UHFFFAOYSA-N 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 150000002500 ions Chemical group 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 1
- 229910052753 mercury Inorganic materials 0.000 description 1
- QMQXDJATSGGYDR-UHFFFAOYSA-N methylidyneiron Chemical compound [C].[Fe] QMQXDJATSGGYDR-UHFFFAOYSA-N 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000012452 mother liquor Substances 0.000 description 1
- 125000000962 organic group Chemical group 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000010992 reflux Methods 0.000 description 1
- 230000002441 reversible effect Effects 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Images
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- Treatment Of Water By Oxidation Or Reduction (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The utility model relates to a strong oxidation reaction and flocculation filter integrated machine which comprises a reaction tank; the bottom in the reaction tank is provided with a conical bottom; the lower part of the reaction tank is provided with a water distributor; the upper part of the reaction tank is provided with an inclined tube; and the middle part of the reaction tank is provided with a filter bed provided with filter material, and an automatic circulating sand filtering device. The machine integrates the functions of strong oxidation, flocculation and filtering, and can remove suspended solids (SS) and sediment flocculation while removing chemical oxygen demand (COD) which is difficult in biochemical degradation; and compared with the oxidation-flocculation precipitation-filtration in the traditional technology, the strong oxidation reaction and flocculation filter integrated machine reduces the energy consumption and drug, lowers the running cost and saves the investment and the land use area.
Description
Technical field
The utility model belongs to the environmental protection equipment field, is that the useful strong oxidative function of a kind of sewage disposal apparatus flocculation filtration function of holding concurrently is the equipment of one specifically.
Background technology
In the sewage disposal, during particularly some industrial sewages are handled, usually run into the water quality of some difficult hardly-biodegradables, the common method of handling these water quality at present is:
1. advanced oxidation processes comprises ozone oxidation, Fenton reagent oxidation, hydrogen peroxide oxidation etc., with hardly degraded organic substance direct oxidation degraded in the waste water;
2. micro-electrolysis method, as iron-carbon micro-electrolysis etc., the electronics that utilizes little electrolysis to produce is opened more organic groups, resolves into small-molecule substance, is conducive to follow-up biochemical treatment;
3. distillation method is distilled the salt mother liquor etc. of containing of high density, and reducing has inhibiting inorganic salts etc. to biochemical bacterium in the waste water, is convenient to follow-up biochemical treatment.
The factor of integrated operation expense and cost of investment each side adopts advanced oxidation processes at present mostly, and maximum with Fenton reagent oxidation style employing wherein especially.
Present Fenton reagent oxidation style, mainly contain two types, a kind of is traditional Fenton oxidation style, another kind is to be the fluid bed Fenton oxidation style of representative with Taiwan Mercury, the great advantage that fluid bed Fenton oxidation style is compared the conventional oxidation method is to save medicament, sludge yield is few, is therefore also more and more used.
But also there is following weak point at present in fluid bed Fenton oxidation style: the one, and xln is in fluidized state in the sewage in order to make, waste water need keep than higher flow velocity, and in order to take into account the certain reaction time that guarantees, generally adopt the quantity of reflux way that increases waste water to improve flow velocity at present, so just increased the consumption of the energy; Simultaneously, because size, the density of crystal are inconsistent in the water, flow velocity is big, will flow away by the less xln of the less density of some particle, flow velocity is little, will some particle greater density bigger xln precipitation and fluidisation is not got up, therefore, whole fluid mapper process is difficult to control, can't reach best fluidized state, makes wastewater treatment efficiency not good.The 2nd, though fluid bed Fenton oxidation style is more many than traditional Fenton process mud decrement, but there are many valency iron mud to produce, the follow-up technology that flocculating settling and filtration also will be arranged has increased investment and working cost and floor space.The 3rd, in fluid bed, the solid phase content of crystal can be too high also unstable, influence fully contacting of sewage and crystal, feasiblely reacts insufficient.The 4th, because water distribution is inhomogeneous, influenced reaction effect, reduced effluent quality.
The utility model content
The utility model is wayward at energy consumption height, fluidized state that existing fluid bed Fenton oxidative treatment sewage exists, water distribution is inhomogeneous and deficiency such as subsequent treatment process complexity, a kind of strong oxidizing reaction and flocculation filtration all-in-one are provided, and energy consumption is little, water distribution is more even and have multiple function.
The utility model is by the following technical solutions:
A kind of strong oxidizing reaction and flocculation filtration all-in-one comprise reacting tank body, and the bottom in the reacting tank body is provided with tapered bottom, and water distributor is equipped with in the bottom, and top is provided with inclined tube, and the middle part is provided with filter bed and the self-circulation sand filtering device of band filtrate.
Described water distributor comprises at least one group of ring shape water distributor, every group of ring shape water distributor has at least two concentric(al) circles circumferences of cannon bone to become, wherein a concentric pipe connects oxygenant and former water water inlet pipe, and a concentric pipe connects catalyzer and former water water inlet pipe, and pipe is provided with water distributing pore with one heart.
Described self-circulation sand filtering device comprises the sand extraction tube that reaches in the tapered bottom, air-lift device is housed on the sand extraction tube, air-lift device links to each other with the pressurized air air-supply duct, the upper end of sand extraction tube communicates with the wash water bucket by sand-washing device, there is cloth sand cover the sand-washing device below, and the space of sand was arranged between sand-washing device and cloth sand cover, and there is filter bed the below of cloth sand cover, described wash water bucket upper end closed, the washed-out sand water out is arranged at the bottom.
Described inclined tube becomes 60 ° of angles with horizontal plane, water is by the mode water outlet of inclined tube to overflow, and can further remove suspended substance in the water outlet, dregs etc., makes water outlet limpider.
Top in the described reacting tank body is provided with effluent weir and water outlet.
Described water distributor is fixed in the reacting tank body by web plate.
Described every group of ring shape water distributor has two concentric(al) circles circumferences of cannon bone to become, the water distributing pore of opening on two concentric pipes passes through each tube hub line respectively, and it is angled with level, this angular range is 45 °--60 °, and respectively adjacent two centerline holes on two concentric pipes below intersect, be beneficial to the abundant hybrid reaction fast of oxygenant and catalyzer.
In general jar on the filter bed filtrate be quartz sand, particle diameter is between 0.5 millimeter to 3.0 millimeters, also hard, wear-resistant such as available haydite and density are greater than the filtrate of water.
During the utility model operation, after oxygenant and former water mix back, catalyzer and the mixing of former water, enter two water-ins of water distributor respectively, flow out from the water distributing pore of water distributor respectively then, two kinds of abundant hybrid reactions of water afterwards, organism in decomposition or the degradation water, current are in uphill process, on the one hand, sewage fully contacts with filtrate, and catalyst ion forms crystallization at filter material surface, prevent from running off with current, be beneficial to subsequent reactions, the input of save catalyst has reduced the generation of working cost and minimizing mud.Another reverse side, suspended substance and flocculate precipitate in the water are held back by filtrate, and effluent quality is greatly improved.Water through filtrate passes through tube settling again, discharges by water outlet.In the drainage flow process, filtrate also flows with certain speed, and velocity of flow can be stopped up the speed adjustment in filtrate space according to water pollutant; Obstruction speed is fast, just strengthens the amount of lift gas, otherwise reduces.In addition, the flowing of filtrate, i.e. continuous flow, but also discontinuous flow can be selected according to practical situation.The flow process of filtrate: the filtrate of the adhesion filth at jar end is carried to the wash water bucket from sand extraction tube with air-lift device, and in this process, the adhesion filth of filter material surface separates with filtrate, discharges from the washed-out sand water pipe; Filtrate falls, and during by sand-washing device, the water back flushing with after the filtration at upper reaches is further washed cleaning, flows back to filtering layer through cloth sand cover then, carries out circulating filtration again.
The strong oxidation of the utility model collection, flocculate, be filtered into one, when removing difficult hardly-biodegradable COD, removed SS and flocculate precipitate, compare with traditional technology oxidation-flocculation sediment-filtration, economization energy consumption, medicament, reduced working cost, saved investment and land use area simultaneously.
Description of drawings
Fig. 1 is the overall structure synoptic diagram of utility model.
Fig. 2 is the vertical view of water distributor.
Fig. 3 is the front view of water distributor.
Fig. 4 is the upward view of water distributor.
Fig. 5 is A among Fig. 4-A sectional view.
Wherein: 1, reacting tank body, 2, the washed-out sand water out, 3, inclined tube, 4, filter bed, 5, water distributor, 6, water inlet A, 7, tapered bottom, 8, air-lift device, 9, water inlet B, 10, sand extraction tube, 11, cloth sand cover, 12, sand-washing device, 13, the wash water bucket, 14, water outlet, 15, effluent weir, 16, the pressurized air air-supply duct, 17, the concentric pipe A of ring shape water distributor, 18, the concentric pipe B of ring shape water distributor, 19, oxygenant and former water water inlet pipe, 20, web plate, 21, catalyzer and former water water inlet pipe, 22, the concentric pipe C of ring shape water distributor, 23, the concentric pipe D of ring shape water distributor, 24, arm A, 25, arm B, 26, water distributing pore A, 27, water distributing pore B.
Embodiment
Further specify below in conjunction with specific embodiment.
As shown in Figure 1, a kind of strong oxidizing reaction and flocculation filtration all-in-one, comprise reacting tank body 1, bottom in the reacting tank body 1 is provided with tapered bottom 7, water distributor 5 is equipped with in the bottom, top is provided with inclined tube 3, the middle part is provided with filter bed 4 and the self-circulation sand filtering device of band filtrate, water distributor 5 comprises at least one group of ring shape water distributor such as ring shape water distributor A17, ring shape water distributor B18, every group of ring shape water distributor has at least two concentric(al) circles circumferences of cannon bone to become, wherein concentric pipe connects oxygenant and 19, concentric pipes of former water water inlet pipe connect catalyzer and former water water inlet pipe 21, and pipe is provided with water distributing pore such as water distributing pore A26 with one heart, water distributing pore B27.The self-circulation sand filtering device comprises the sand extraction tube 10 that reaches in the tapered bottom 7, air-lift device 8 is arranged on the sand extraction tube 10, air-lift device 8 links to each other with pressurized air air-supply duct 16, the upper end of sand extraction tube 10 communicates with wash water bucket 13 by sand-washing device 12, there is cloth sand cover 11 sand-washing device 12 belows, sand- washing device 12 and 11 spaces that sand was arranged of cloth sand cover, and there is filter bed 4 below of cloth sand cover 11, described wash water bucket 13 upper end closeds, washed-out sand water out 2 is arranged at the bottom.Inclined tube 3 is laid on reacting tank body 1 top, and water is by the mode water outlet of inclined tube to overflow, and can further remove suspended substance in the water outlet, dregs etc., makes water outlet limpider.Top in the reacting tank body is provided with effluent weir 15 and water outlet 14.Water distributing pore is by each concentric pipe tube hub line, and angled with level, and this angular range is 45 °--60 °, and two hole water distributing pore A26 and water distributing pore B27 medullary ray below intersect, be beneficial to the abundant hybrid reaction fast of oxygenant and catalyzer.
The utility model comprises reacting tank body 1, be installed in the tapered bottom 7 of reacting tank body inner bottom part, be installed in the water distributor 5 of bottom in the reacting tank body by web plate 20, the self-circulation sand filtering device that is installed in the inclined tube 3 of reacting tank body internal upper part and is positioned at the reacting tank body middle part, the inner quartz sand of loading of reacting tank body forms filter bed 4; Collect strong oxidation, flocculate, be filtered into one.
During operation, the former water that mixes up potential of hydrogen mixes with copperas solution and hydrogen peroxide solution respectively, pass through the water inlet A 6 of water distributor 5 then respectively, water inlet B 9, enter former water and ferrous sulfate water inlet pipe (catalyzer and former water water inlet pipe) 21 respectively, former water and hydrogen peroxide water inlet pipe (oxygenant and former water water inlet pipe) 19, again respectively through arm A24, arm B25, flow into the concentric pipe A of ring shape water distributor, B, C, D, last two kinds of water are by water distributing pore B27, water distributing pore A26 spurts in the tank body, and mix rapidly and carry out chemistry and send out and to generate the hydroxyl radical free radical OH with strong oxidizing property, the hydroxyl radical free radical oxidation, the difficult biochemical organism of difficult degradation in the water of decomposition reaches and removes organic purpose.Sewage fully contacts with the filtrate of filter bed 4 in the process of upper reaches, and reaction intermediate forms crystallization at filter material surface, prevents from running off with current, and iron ion is beneficial to the subsequent reactions recycling, has reduced the generation of working cost and minimizing mud.Simultaneously, the part iron ion impels the suspended substance of water pollutant flocculation in water to be held back by quartz sand, and water quality is greatly improved.By the water of filter bed 4, again through inclined tube 3 precipitations, discharge by effluent weir 15, water outlet 14.In this process, quartz sand still is the carrier of iron ion xln except playing filtrate simultaneously.
Quartz sand filter media automated cycle and automatic the cleaning by following process are realized:
The quartz sand of the adhesion filth in the tapered bottom 7 is carried to wash water bucket 13 by sand extraction tube with air-lift device 8, and the propulsion source of air-lift device 8 derives from the pressurized air that pressurized air air-supply duct 16 provides.In the quartz sand lifting process, the adhesion filth of filter material surface separates with filtrate by gas, water slug, discharges from washed-out sand water out 2; Quartz sand falls, and during by sand-washing device 12, the water back flushing with behind the process depth filtration, deep bed filtration at upper reaches is further washed cleaning, flows back to filter bed 4 surfaces through cloth sand cover 11 then, participates in filtering again; When the quartz sand in the tapered bottom 7 was mentioned, sand all around flowed to carrying the sand mouth, and the sand in the filter bed also slowly flows downward, thereby realized the automated cycle of filtrate and clear automatically.
Air-lift device is put forward the sand process: pressurized air enters air-lift device by inlet pipe, enter sand extraction tube again by the hole in the gas device then, part water in the sand extraction tube just replaces compressed air, thereby obtained the steam water interface that density is lower than the water of surrounding medium, therefore the static pressure of ambient water forces the mixture in the sand extraction tube to rise, sand extraction tube the suction side just produce very strong suction, be enough to make the sand water mixture to arrive the wash water bucket by sand extraction tube, and then drop to and wash husky device.Annotate: the density of sand, water, air mixture also is lower than the density of surrounding medium.
The utility model is not limited to the application of oxidizing reaction, and other class reactions and filtration are also within this protection domain.
Claims (7)
1. a strong oxidizing reaction and flocculation filtration all-in-one comprise reacting tank body, it is characterized in that, the bottom in the reacting tank body is provided with tapered bottom, and water distributor is equipped with in the bottom, and top is provided with inclined tube, and the middle part is provided with filter bed and the self-circulation sand filtering device of band filtrate.
2. a kind of strong oxidizing reaction according to claim 1 and flocculation filtration all-in-one, it is characterized in that, described water distributor comprises at least one group of ring shape water distributor, every group of ring shape water distributor has at least two concentric(al) circles circumferences of cannon bone to become, wherein a concentric pipe connects oxygenant and former water water inlet pipe, a concentric pipe connects catalyzer and former water water inlet pipe, and pipe is provided with water distributing pore with one heart.
3. a kind of strong oxidizing reaction according to claim 1 and flocculation filtration all-in-one, it is characterized in that, described self-circulation sand filtering device comprises the sand extraction tube that reaches in the tapered bottom, and air-lift device is housed on the sand extraction tube, and air-lift device links to each other with the pressurized air air-supply duct, the upper end of sand extraction tube communicates with the wash water bucket by sand-washing device, there is cloth sand cover the sand-washing device below, and the space of sand was arranged between sand-washing device and cloth sand cover, and there is filter bed the below of cloth sand cover, described wash water bucket upper end closed, the washed-out sand water out is arranged at the bottom.
4. a kind of strong oxidizing reaction according to claim 1 and flocculation filtration all-in-one is characterized in that, the top in the described reacting tank body is provided with effluent weir and water outlet.
5. a kind of strong oxidizing reaction according to claim 1 and flocculation filtration all-in-one is characterized in that described water distributor is fixed in the reacting tank body by web plate.
6. a kind of strong oxidizing reaction according to claim 2 and flocculation filtration all-in-one, it is characterized in that, described every group of ring shape water distributor has two concentric(al) circles circumferences of cannon bone to become, the water distributing pore of opening on two concentric pipes passes through each tube hub line respectively, and angled with level, this angular range is 45 °--60 °.
7. a kind of strong oxidizing reaction according to claim 1 and flocculation filtration all-in-one is characterized in that, described filtrate is quartz sand or haydite.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201320191658 CN203229430U (en) | 2013-04-16 | 2013-04-16 | Strong oxidation reaction and flocculation filter integrated machine |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 201320191658 CN203229430U (en) | 2013-04-16 | 2013-04-16 | Strong oxidation reaction and flocculation filter integrated machine |
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| Publication Number | Publication Date |
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| CN203229430U true CN203229430U (en) | 2013-10-09 |
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| Application Number | Title | Priority Date | Filing Date |
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| CN 201320191658 Expired - Lifetime CN203229430U (en) | 2013-04-16 | 2013-04-16 | Strong oxidation reaction and flocculation filter integrated machine |
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104108807A (en) * | 2013-04-16 | 2014-10-22 | 山东山大华特科技股份有限公司 | Strong oxidation reaction and flocculation filter integrated machine |
| CN104496126A (en) * | 2014-12-19 | 2015-04-08 | 河南机电高等专科学校 | Novel sewage treatment equipment |
-
2013
- 2013-04-16 CN CN 201320191658 patent/CN203229430U/en not_active Expired - Lifetime
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104108807A (en) * | 2013-04-16 | 2014-10-22 | 山东山大华特科技股份有限公司 | Strong oxidation reaction and flocculation filter integrated machine |
| CN104108807B (en) * | 2013-04-16 | 2016-03-02 | 山东山大华特科技股份有限公司 | A kind of Strong oxdiative reaction and flocculation filtration all-in-one |
| CN104496126A (en) * | 2014-12-19 | 2015-04-08 | 河南机电高等专科学校 | Novel sewage treatment equipment |
| CN104496126B (en) * | 2014-12-19 | 2017-06-16 | 河南机电高等专科学校 | A kind of New foul water disposal facility |
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Legal Events
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|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| TR01 | Transfer of patent right |
Effective date of registration: 20210312 Address after: 250101 Huate building, Shanda Science Park, Yingxiu Road, high tech Development Zone, Jinan City, Shandong Province Patentee after: Shandong Shanda Huate Environmental Protection Technology Co.,Ltd. Address before: 250061 Huate Plaza, 17703 Jingshi Road, Lixia District, Jinan City, Shandong Province Patentee before: SHANDONG SHANDA HUATE TECHNOLOGY Co.,Ltd. |
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| TR01 | Transfer of patent right | ||
| CX01 | Expiry of patent term |
Granted publication date: 20131009 |
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| CX01 | Expiry of patent term |