CN101045594A - Strong oxidation sewage treatment process - Google Patents
Strong oxidation sewage treatment process Download PDFInfo
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- CN101045594A CN101045594A CN 200710090389 CN200710090389A CN101045594A CN 101045594 A CN101045594 A CN 101045594A CN 200710090389 CN200710090389 CN 200710090389 CN 200710090389 A CN200710090389 A CN 200710090389A CN 101045594 A CN101045594 A CN 101045594A
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- 239000010865 sewage Substances 0.000 title claims abstract description 30
- 238000000034 method Methods 0.000 title claims abstract description 25
- 230000003647 oxidation Effects 0.000 title claims description 14
- 238000007254 oxidation reaction Methods 0.000 title claims description 14
- 241000894006 Bacteria Species 0.000 claims abstract description 5
- 239000000126 substance Substances 0.000 claims abstract description 5
- 238000006243 chemical reaction Methods 0.000 claims description 34
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 24
- 239000000463 material Substances 0.000 claims description 14
- 238000005516 engineering process Methods 0.000 claims description 13
- 238000002156 mixing Methods 0.000 claims description 11
- 239000002351 wastewater Substances 0.000 claims description 8
- 239000003814 drug Substances 0.000 claims description 6
- 238000004062 sedimentation Methods 0.000 claims description 5
- 230000000694 effects Effects 0.000 claims description 4
- 230000005672 electromagnetic field Effects 0.000 claims description 4
- 238000006864 oxidative decomposition reaction Methods 0.000 claims description 4
- 206010020843 Hyperthermia Diseases 0.000 claims description 3
- 230000007613 environmental effect Effects 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- 230000036031 hyperthermia Effects 0.000 claims description 3
- 239000011259 mixed solution Substances 0.000 claims description 3
- 239000002699 waste material Substances 0.000 claims description 3
- 230000003139 buffering effect Effects 0.000 claims description 2
- 230000015556 catabolic process Effects 0.000 claims description 2
- 230000001112 coagulating effect Effects 0.000 claims description 2
- 238000006731 degradation reaction Methods 0.000 claims description 2
- 238000006479 redox reaction Methods 0.000 claims description 2
- 238000006555 catalytic reaction Methods 0.000 claims 2
- 238000000354 decomposition reaction Methods 0.000 claims 1
- 239000002198 insoluble material Substances 0.000 claims 1
- 239000003403 water pollutant Substances 0.000 claims 1
- 230000001590 oxidative effect Effects 0.000 abstract description 3
- 241000195493 Cryptophyta Species 0.000 abstract description 2
- 230000005684 electric field Effects 0.000 abstract 1
- 239000007800 oxidant agent Substances 0.000 abstract 1
- 239000007787 solid Substances 0.000 abstract 1
- 230000003851 biochemical process Effects 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 208000027418 Wounds and injury Diseases 0.000 description 1
- 150000004945 aromatic hydrocarbons Chemical class 0.000 description 1
- 230000008953 bacterial degradation Effects 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 230000005669 field effect Effects 0.000 description 1
- 238000005189 flocculation Methods 0.000 description 1
- 230000016615 flocculation Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 208000014674 injury Diseases 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 230000000050 nutritive effect Effects 0.000 description 1
- 210000000056 organ Anatomy 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 230000003534 oscillatory effect Effects 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 230000001766 physiological effect Effects 0.000 description 1
- 230000035790 physiological processes and functions Effects 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
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- Water Treatment By Electricity Or Magnetism (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
A strong oxidizing process for treating sewage features that under the existence of particular oxidant and energy converting substances and the frequency-converting strong electric field, the moleculae of harmful substances in the sewage are cracked and decomposed to become the harmless gas or solid deposit to be separated out, and the bacteria and algae are killed.
Description
Technical field: strong oxidation sewage treatment process can be widely used in environmental protection fields such as industrial sewage, hospital sewage, middle water treatment and sub-district landscape water processing, and application space is more widely arranged
Background technology: strong oxidation sewage treatment process is that technology such as oxygenant, Conversion of energy material, frequency conversion strong-electromagnetic field, emulation automatization are arranged is the comprehensive water treatment technology of one
Summary of the invention: strong oxidation sewage treatment process is to add specific oxygenant, Conversion of energy material in sewage, through a kind of novel water technology of frequency conversion strong-electromagnetic field effect.Its ultimate principle is:
1, many pollutant dissolutions are arranged in water in the sewage, be difficult to be adsorbed by flocculation agent or coagulating sedimentation is removed from water body, also difficult what is by bacterial degradation simultaneously.Therefore; Strong oxidation sewage treatment process has proposed the oxygenolysis new technology under high temperature, high pressure, in order to promote the development of sewage disposal technology;
2, according to the ultimate principle of chemical reaction, not all reactant molecule collides mutually and can both react, and the effective collision of having only energy to be higher than the activated molecule of a certain threshold value just can react.Therefore; Strong oxidation sewage treatment process adopts the frequency conversion strong-electromagnetic field to improve reaction activity, impels the pollutent of difficult degradation to be decomposed;
3, well-known, chemical reaction equilibrium constant K is the function of temperature T, have only the variation of T just to cause K ° change, and most of oxidative decomposition is thermo-negative reaction.Therefore; The raising temperature of reaction must help reaction and move to decomposing direction.In strong oxidation sewage treatment process, added the Conversion of energy material, this kind material has very strong receptivity to hertzian wave, wave energy can be converted into heat energy, moment produces localized hyperthermia, high pressure on its surface, impel temperature of reaction raising, environmental change, the oxidative decomposition of part non-polar molecule is taken place.
4, because oxygenant self has certain redox-potential, according to energy this spy (Nerst) formula, redox-potential is the function of temperature, improving the temperature redox-potential must increase, thereby makes some become possibility under the envrionment conditions of the oxidizing reaction that can not take place under normal temperature, the normal pressure at strong oxidation sewage treatment process.Therefore; Under the acting in conjunction of strong frequency-conversion electromagnetic field, oxygenant, Conversion of energy material and medicament, oxidative decomposition more completely all can take place in the most of objectionable impurities in the water body (comprising polar molecule and non-polar molecule) under high temperature, condition of high voltage, reach innoxious purpose.
In addition, strong oxidation sewage treatment process also can be killed microorganisms such as bacterium in the water, algae in sewage disposal.Its action principle is because oxygenant violent oxygenizement and frequency conversion strong-electromagnetic field radiation organism in the frequency conversion strong-electromagnetic field, causes the heat effect of bio-tissue organ and the promoter action of the physiological effect that produces and inhibition, injury.The polar molecule of forming cell adds in oxidation, intensification, the oscillatory process outside, causes the histocyte imbalance, change so the disorderly concurrent sick reason of physiological function takes place organism, so that dead.
Existing water technologies such as different and available coagulation precipitation, biochemical treatment, film processing on the ultimate principle of this technology.
The ultimate principle of the various biochemical water treatment technologies that are widely adopted at present is to cultivate, breed a large amount of bacteriums that can decompose, absorb pollutent sewage is carried out purifying treatment in sewage, but lack the required nutritive ingredient of bacterial reproduction in most of process spent water, can not satisfy the basic demand of biochemical process, simultaneously, all biochemical process all can not bear the impact of high density pollution thing, much less many pollutents can not be decomposed by bacterium, therefore the use of biochemical process are limited to.
Traditional coagulation-settlement process can only be removed suspended substance and the more water-fast pollutents in the water body, and many organic pollutants (producing the principal pollutant of COD) can not effectively be removed, therefore at present usually as a processing links in the water treatment process.
The film processing is the new technology based on mechanical filter, effective various ions in the water body of place to go, but " film " of its key is a kind of organic compound, very easily damaged by the organic substances such as aromatic hydrocarbon in the water body, and very high to the water inlet requirement, the difficult what of the general enterprise of working cost is accepted.
In sewage treatment process, add oxygenant and be used in practice, but up to the present do not see the report that under localized hyperthermia, condition of high voltage, uses.
Description of drawings: Fig. 1 is seen in this technical process: 1, waste water, 2, grid, 3, equalizing tank, 4, Conversion of energy material, 5,1# mixing tank, 6, oxygenant, 7,2# mixing tank, 8, medicament, 9, frequency conversion strong-electromagnetic field, 10, sedimentation and filtration equipment, 11, device for dehydrating sladge waste.
Embodiment:
Sewage is removed bulk foreign material such as bigger sandstone, wooden unit, plastics through grid; Then enter equalizing tank, sewage obtains the buffering of the water yield and water quality in equalizing tank; The sewage that comes out from equalizing tank enters 1
#Mixing tank, and 1
#Adding the Conversion of energy material in the mixing tank mixes; Mixed solution is by entering 2 subsequently
#Mixing tank, and to wherein adding oxygenant; Mixed solution promotes by the frequency conversion strong-electromagnetic field through sump pump, and direct physical-chemical reaction and pyro-oxidation-reduction reaction take place in the frequency conversion strong-electromagnetic field, and the resultant of these reactions changes the heavy flco thing of speed into; The sewage (SS≤1500mg/L), enter sedimentation and filtration equipment, but water outlet qualified discharge or utilization again that have the heavy flco thing of a large amount of speed; Mud goes out the mud cake outward transport through device for dehydrating sladge waste.
Claims (4)
- Current sewage treatment process can be divided into basically based on the biochemical processing process of bacterium with based on the medicament oxidation processing technique under materialization treatment process, film processing and the normal temperature of coagulating sedimentation.And strong oxidation frequency-conversion electromagnetic field sewage treatment process is characterised in that:
- 1, technology characteristics: in sewage, add behind oxygenant, Conversion of energy material, the medicament effect by electromagnetic field (or forceful electric power magnetic), make sewage (waste water) under oxygenant, Conversion of energy material, medicament, high temperature, highly compressed acting in conjunction, reach water treatment process, technology that sewage (waste water) purifies purpose.
- 2, process mechanism: adopt electromagnetic field to improve reaction activity, impel the pollutent of difficult degradation to be decomposed; In technology, added the Conversion of energy material, this kind material has very strong receptivity to hertzian wave, wave energy can be converted into heat energy, moment produces localized hyperthermia, high pressure on its surface, impel temperature of reaction raising, environmental change, the oxidative decomposition of part non-polar molecule is taken place, and violent chemical oxidation decomposition reaction and catalyzed reaction take place, make water pollutant change into insoluble material or gas is separated from water.
- 3, technical process: waste water is removed the bulk foreign material through grid; Then enter equalizing tank, obtain the buffering of the water yield and water quality; Waste water enters thorough mixing in the mixing tank after coming out to add the Conversion of energy material from equalizing tank; Waste water enters thorough mixing in the mixing tank after coming out to add oxygenant from mixing tank; After waste water came out to add medicament from mixing tank, direct physical-chemical reaction, pyro-oxidation-reduction reaction, catalyzed reaction took place by strong-electromagnetic field in mixed solution in strong-electromagnetic field, and the resultant of these reactions changes the heavy flco thing of speed into; The waste water (SS≤1500mg/L), enter sedimentation and filtration equipment, but water outlet qualified discharge or utilization again that have the heavy flco thing of a large amount of speed; Mud goes out the mud cake outward transport through device for dehydrating sladge waste.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 200710090389 CN101045594A (en) | 2007-04-10 | 2007-04-10 | Strong oxidation sewage treatment process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN 200710090389 CN101045594A (en) | 2007-04-10 | 2007-04-10 | Strong oxidation sewage treatment process |
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| Publication Number | Publication Date |
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| CN101045594A true CN101045594A (en) | 2007-10-03 |
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| CN 200710090389 Pending CN101045594A (en) | 2007-04-10 | 2007-04-10 | Strong oxidation sewage treatment process |
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Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102020391A (en) * | 2010-12-23 | 2011-04-20 | 北京拓峰科技开发有限责任公司 | Novel process for coking wastewater treatment |
| CN102120667A (en) * | 2010-01-11 | 2011-07-13 | 刘恩来 | Water treatment system with catalytic tower |
| CN101774722B (en) * | 2009-02-16 | 2011-09-07 | 北京拓峰科技开发有限责任公司 | Novel industrial sewage treatment process |
| CN102336508A (en) * | 2011-10-18 | 2012-02-01 | 东莞市高能磁电技术有限公司 | Method and system for quickly dehydrating and recycling municipal sewage sludge |
| CN102489501A (en) * | 2011-11-17 | 2012-06-13 | 常州浩瀚新材料科技有限公司 | Process suitable for integrated safe restoration of soil pollution |
| CN101805070B (en) * | 2009-02-16 | 2012-07-25 | 胡德錄 | Electromagnetic fluid reaction device |
-
2007
- 2007-04-10 CN CN 200710090389 patent/CN101045594A/en active Pending
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101774722B (en) * | 2009-02-16 | 2011-09-07 | 北京拓峰科技开发有限责任公司 | Novel industrial sewage treatment process |
| CN101805070B (en) * | 2009-02-16 | 2012-07-25 | 胡德錄 | Electromagnetic fluid reaction device |
| CN102120667A (en) * | 2010-01-11 | 2011-07-13 | 刘恩来 | Water treatment system with catalytic tower |
| CN102020391A (en) * | 2010-12-23 | 2011-04-20 | 北京拓峰科技开发有限责任公司 | Novel process for coking wastewater treatment |
| CN102336508A (en) * | 2011-10-18 | 2012-02-01 | 东莞市高能磁电技术有限公司 | Method and system for quickly dehydrating and recycling municipal sewage sludge |
| CN102336508B (en) * | 2011-10-18 | 2014-09-17 | 东莞市高能磁电技术有限公司 | Method and system for quickly dehydrating and recycling municipal sewage sludge |
| CN102489501A (en) * | 2011-11-17 | 2012-06-13 | 常州浩瀚新材料科技有限公司 | Process suitable for integrated safe restoration of soil pollution |
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Owner name: BEIJING DAGU TIME ENVIRONMENTAL PROTECTION TECHNO Free format text: FORMER OWNER: HU DE Effective date: 20071214 |
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Effective date of registration: 20071214 Address after: Beijing city Haidian District Xitucheng Road No. 31 13-5-402 post encoding: 100088 Applicant after: Beijing Dagu Shidai Protection Science and Technology Co., Ltd. Address before: Beijing city Haidian District Xitucheng Road No. 31 13-5-402 post encoding: 100088 Applicant before: Hu Delu |
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