CN1260141C - Pollution removing medicament for drinking water - Google Patents
Pollution removing medicament for drinking water Download PDFInfo
- Publication number
- CN1260141C CN1260141C CN 200410043762 CN200410043762A CN1260141C CN 1260141 C CN1260141 C CN 1260141C CN 200410043762 CN200410043762 CN 200410043762 CN 200410043762 A CN200410043762 A CN 200410043762A CN 1260141 C CN1260141 C CN 1260141C
- Authority
- CN
- China
- Prior art keywords
- permanganate
- tap water
- ferrate
- present
- depollution
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
The present invention relates to a pollution removing medicine for drinking water, particularly to a high-ferrum and high-manganese compounding medicine. The present invention is composed of components of the weight percentage: 0.1 to 90% of ferrate, 0 to 70% of permanganate and 0.1 to 30% of assistants. The present invention can be stored for a long time. Because permanganate and stable ferric salt are contained in the compound medicine, the good catalytic oxidation action and the good synergistic action among all components in the high-ferrum and high-manganese compound medicine and the specific property of the ferric salt (+6 valence) in water can be fully performed. The ferric salt (+6 valence) can oxidize and destroy organic substances, and the reaction product is ferric salt (+3 valence), which has no side effect to a human body. Coagulant with good efficiency can be generated to absorb colloid impurities and organic substances. Thus, the effects of enhancing coagulation and filtration can be obtained.
Description
Technical field:
The present invention relates to a kind of medicament that is used for the tap water depollution, particularly a kind of compound tap water depollution medicament.
Background technology:
Recent two decades comes, tap water depollution technology becomes one of focus of water treatment research, the employing method generally is to add organic pollutant in the methods removal water such as absorption method, Biological Pretreatment, chemical pre-oxidation treatment on existing conventional treatment process basis in the at present extensive water technology, in the hope of obtaining safety, qualified tap water.Wherein chemical preoxidation is one of wherein important technology, has the advantage of economical and efficient.The oxygenant that pre-oxidation treatment technology adopts at present mainly contains Cl
2, O
3, ClO
2, KMnO
4, H
2O
2Deng, it is few that chemical pre-oxidation treatment advantage is taken up an area of, and the reaction times is short, generally is subjected to Temperature Influence smaller, and their shortcoming is: some oxygenant (O
3, ClO
2) can not preserve, need on-site preparation, complicated operation; Expense costliness (O
3); Present result of study is thought, some oxygenant (Cl
2, O
3Deng) with water in organism reaction in, produce harmful by product.These methods both can be used separately, also can and require according to condition of water quality to adopt and other treatment process coupling, so often can obtain better treatment effect.The environment protection of China is backward relatively and funds are relatively limited, has determined that to reinforcement and the advanced treatment of contaminated drinking water source in water treatment process all be an important task in quite over a long time.The polluted water strengthening treatment process of wherein seeking economical and efficient has very important meaning for today China national conditions and polluted-water.
Summary of the invention:
The purpose of this invention is to provide a kind of tap water depollution medicament, it is enhanced coagulation, intensive filtration in polluted water is handled, have efficient, safety, economy,, easy handling management little and realize that automatic control advantage, this technology are the strengthening treatment process that China goes out in tap water depollution field independent studies temperature and organic loading variable effect.Tap water depollution medicament of the present invention is made up of following component in percentage by weight: ferrate 0.1~90%, permanganate 0~70% and assistant agent 0.1~30%.Tap water depollution medicament can be made up of following component in percentage by weight optimization: ferrate 20~45%, permanganate 40~60% and assistant agent 10~30%.High ferrimanganic compound (CFP) can be preserved the long period.Owing to contain permanganate and comparatively stable ferric salt composition in the compound, thereby given full play to good catalyzed oxidation and the synergy between various compositions in the high ferrimanganic compound (CFP), and ferric salt (+6 valency) reacts distinctive character in water: oxidation and destruction organism, reaction product is originally as molysite (+3 valency), without any side effects to human body, generate the good coagulating agent of usefulness, adsorb colloidal impurity and organism, reach the effect of enhanced coagulation, intensive filtration.High ferrimanganic compound (CFP) itself is natural sterilizing agent, can make full use of its high price strong oxidizing property break virus and bacterium, and from present result of study, its deactivation efficient is better than HClO and OCl
-, the generation of sterilization accessory substance is much smaller than disinfection byproduct (DBP) that chlorine disinfectant produced.High ferrimanganic compound (CFP) in enhanced coagulation, intensive filtration, removal turbidity, colourity, algae, smell flavor, remove micro quantity organic pollutant and mutagenesis active substance in the water, reduce haloform antecedent and haloform growing amount, replace prechlorination, reduce and have excellent performance aspect the consumption of coagulating agent, its a lot of aspects of depollution performance surpass ozone pre-treatment depollution effect, precipitate simultaneously and filter after water in bacterium almost be killed.Using at present chlorine only to add a spot of sterilizing agent in the output water under as the condition of sterilizing agent, just can keep the wholesomeness of output water in outer net, avoid disinfection byproduct (DBP) to produce in a large number.
Embodiment:
Embodiment one: present embodiment is made up of following component in percentage by weight: ferrate 0.1~90%, permanganate 0~70% and assistant agent 0.1~30%.Described assistant agent is a kind of or any several mixture in ferric sulfate, calcium oxide, calcium hydroxide, sodium hydroxide, potassium hydroxide, phosphoric acid salt, superoxide, hypochlorite, oxymuriate, special clay, Tai-Ace S 150 and the polyaluminium sulfate.One or more mixture in montmorillonite, Peng Run soil, Attapulgite, zeolite and the diatomite of described special clay after for activation.The described position that adds is at the front end of coagulation process or at the front end of filtration process.The described form that adds perhaps adds with solid form for to add with liquid form.Describedly add the active drug dosage that pharmaceutical quantities is 0.1~100mg/L.Described ferrate is for being potassium ferrate or Na2Fe04.Described permanganate is potassium permanganate or sodium permanganate.
Embodiment two: present embodiment is made up of following component in percentage by weight: ferrate 70~90%, assistant agent 10~30%.
Embodiment three: present embodiment is made up of following component in percentage by weight: ferrate 20~45%, permanganate 40~60%, assistant agent 10~30%.
Embodiment four: present embodiment is made up of following component in percentage by weight: ferrate 25~30%, permanganate 50~55%, assistant agent 20~30%.Surface water body 3 classes, it is 0.1~5% that high ferrimanganic compound (CFP) is mixed with mass concentration, dosage is 0.1~10mg/L, be added in the preceding water body of coagulation, filter back delivery turbidity clearance improves 30%~50%, and the organic pollutant removal rate improves 30%~50%, and consuming amount of concrete saves 10~15%, haloform antecedent and haloform growing amount reduce significantly, and toxicology detects index and is negative.
Embodiment five: present embodiment is made up of following component in percentage by weight: ferrate 35~40%, permanganate 42~48%, assistant agent 12~25%.Surface water body 4 classes, it is 0.1~5% that high ferrimanganic compound (CFP) is mixed with mass concentration, dosage is 0.1~40mg/L, be added in the preceding water body of coagulation, filter back delivery turbidity clearance improves 30%~50%, the organic pollutant removal rate improves 30%~50%, and consuming amount of concrete saves 10~15%, and haloform antecedent and haloform growing amount reduce significantly.
Embodiment six: present embodiment is made up of following component in percentage by weight: ferrate 80%, assistant agent 20%.
Embodiment seven: present embodiment is made up of following component in percentage by weight: ferrate 25%, permanganate 50%, assistant agent 25%.
Claims (6)
1, tap water depollution medicament is characterized in that it is made up of following component in percentage by weight: ferrate 20~45%, permanganate 40~60% and assistant agent 10~30%.
2, tap water depollution medicament according to claim 1 is characterized in that described assistant agent is one or more the mixture in ferric sulfate, calcium oxide, calcium hydroxide, sodium hydroxide, potassium hydroxide, phosphoric acid salt, superoxide, hypochlorite, oxymuriate, special clay, Tai-Ace S 150 and the polyaluminium sulfate.
3, tap water depollution medicament according to claim 2 is characterized in that one or more the mixture in montmorillonite, Peng Run soil, Attapulgite, zeolite and the diatomite after described special clay is for activation.
4, tap water depollution medicament according to claim 1 is characterized in that the described active drug dosage that pharmaceutical quantities is 0.1~100mg/L that adds.
5, tap water depollution medicament according to claim 1 is characterized in that described ferrate is potassium ferrate or Na2Fe04.
6, tap water depollution medicament according to claim 1 is characterized in that described permanganate is potassium permanganate or sodium permanganate.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 200410043762 CN1260141C (en) | 2004-07-30 | 2004-07-30 | Pollution removing medicament for drinking water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 200410043762 CN1260141C (en) | 2004-07-30 | 2004-07-30 | Pollution removing medicament for drinking water |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1597544A CN1597544A (en) | 2005-03-23 |
CN1260141C true CN1260141C (en) | 2006-06-21 |
Family
ID=34665434
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 200410043762 Expired - Fee Related CN1260141C (en) | 2004-07-30 | 2004-07-30 | Pollution removing medicament for drinking water |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1260141C (en) |
Families Citing this family (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100457646C (en) * | 2006-05-19 | 2009-02-04 | 北京工业大学 | Composite dephosphorizing coagulant dedicated for drinking water |
CN100420636C (en) * | 2006-11-24 | 2008-09-24 | 北京工业大学 | Coagulation method for removing trace phosphorus in water |
CN101503242B (en) * | 2009-03-13 | 2011-04-20 | 哈尔滨工业大学 | Water treatment medicament removing pollution by using intermediate state manganese strengthened potassium permanganate |
CN102381779B (en) * | 2011-11-02 | 2013-08-28 | 哈尔滨工业大学 | Method for controlling production of algae chlorinated disinfection byproduct by using potassium permanganate and calcium ion |
CN102515327B (en) * | 2011-12-28 | 2013-07-17 | 樊继健 | Composite water treatment agent, and preparation method thereof |
CN103121745A (en) * | 2013-02-01 | 2013-05-29 | 西京学院 | Water treatment compound agent based on potassium ferrate and preparation method of water treatment compound agent |
CN103204575A (en) * | 2013-04-25 | 2013-07-17 | 韶关市雅鲁环保实业有限公司 | Processing process of water discharged out of tailing pool of lead-zinc ore concentrating mill |
CN103204576A (en) * | 2013-04-25 | 2013-07-17 | 韶关市雅鲁环保实业有限公司 | Treating agent for water discharged out of tailing pool of lead-zinc ore concentrating mill |
CN104176810B (en) * | 2013-05-20 | 2016-07-06 | 新昌县中发环保材料有限公司 | A kind of high-efficiency multi-function remover and preparation method thereof |
CN103723772B (en) * | 2014-01-15 | 2014-12-17 | 哈尔滨工业大学 | Preparation method of composite ferrate reagent |
CN103787482B (en) * | 2014-03-05 | 2016-01-20 | 南京农业大学 | A kind of method simultaneously removing phosphorus and endocrine disrupter in water |
CN107021582B (en) * | 2017-06-22 | 2020-10-02 | 南阳理工学院 | Landfill leachate pretreatment process |
CN107445282A (en) * | 2017-08-30 | 2017-12-08 | 河海大学 | Ruthenium joint high price iron removes the method for treating water of depollution |
CN110282688A (en) * | 2019-07-09 | 2019-09-27 | 浙江大学常州工业技术研究院 | Chemical engineering sewage inorganic agent |
-
2004
- 2004-07-30 CN CN 200410043762 patent/CN1260141C/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
CN1597544A (en) | 2005-03-23 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN1260141C (en) | Pollution removing medicament for drinking water | |
CN101755838B (en) | Compound powdery deodorant bacterial poison eliminating agent and preparation method thereof | |
KR101355178B1 (en) | Water treating agent of food wastewater and for removing green algae, red algae and odors | |
CN102771516A (en) | Disinfectant for pond water body | |
CN110563191B (en) | Method for removing organic micropollutants in drinking water by utilizing persulfate reinforced ferric salt coagulation process | |
CN107117765B (en) | A kind of drinking water purification device and purifying treatment method | |
CN1807288A (en) | Method for deep treatment of bromine ion-containing drinking water | |
CN103503922A (en) | Disinfection powder for hospital wastewater disinfection | |
CN1321907C (en) | Pollution removing composite medicament for water disposal | |
CN102229444A (en) | Running water preoxidation medicament | |
CN1319871C (en) | Pollution removing medicament for water disposal | |
CN1927730A (en) | Method of controlling alga in reservoir by chemical agent | |
CN101475245A (en) | Swimming pool water disinfection method | |
CN106186115A (en) | A kind of water quality cleansing agent of high-efficiency environment friendly and preparation method thereof | |
CN1762845A (en) | Composite medicament for water disposal | |
CN108101145A (en) | A kind of new substrate modifier used for aquiculture and preparation method thereof | |
CN1321908C (en) | Pollution removing composite medicament | |
CN106241901A (en) | A kind of inorganic water purification agent | |
KR101355177B1 (en) | Water treating agent for removing green algae, red algae and odors in water | |
CN105036287A (en) | Ferrate (VI) effervescent tablets for water treatment and preparation method thereof | |
KR100476610B1 (en) | Water treatment agent for removing nutritive salts and method for using the same | |
CN221420931U (en) | Drinking water disinfection treatment device | |
KR20120138416A (en) | Water treatment agent for removing taste and odors, and green algae in water, method for preparing the same and using method thereof | |
CN108925485B (en) | Oxygen-increasing sterilization disinfection water-changing-free ecological fish tank | |
CN102630606B (en) | Synthesis of biological preparation enriching ammonia nitrogen content in natural water body and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
C17 | Cessation of patent right | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20060621 |