CN110015744A - Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine - Google Patents
Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine Download PDFInfo
- Publication number
- CN110015744A CN110015744A CN201910350303.9A CN201910350303A CN110015744A CN 110015744 A CN110015744 A CN 110015744A CN 201910350303 A CN201910350303 A CN 201910350303A CN 110015744 A CN110015744 A CN 110015744A
- Authority
- CN
- China
- Prior art keywords
- water
- fenton
- pollutant
- added
- reaction system
- 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.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
- C02F1/763—Devices for the addition of such compounds in gaseous form
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/02—Specific form of oxidant
- C02F2305/026—Fenton's reagent
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine, the present invention relates to a kind of method for treating water, and there are H in order to solve existing Fenton system for handling for it2O2Consumption is big, the problem that iron throwing amount is more and pollutant removal is poor.Method for treating water: one, the pH value of pending water is adjusted in 2.0~4.0 ranges；Two, ferrous salt is then added into pending water, stirs pending water, and hydrogenperoxide steam generator is added；Three, hypochlorite solutions are added or are passed through chlorine, makes 1~15mg/L of concentration of effective chlorine in system, carries out reinforcing reaction, to remove water pollutant.The present invention can be improved 30%~50% to the removal rate of pollutant using the method that free chlorine strengthens Fenton's reaction system removal water pollutant, so that the dosage of hydrogen peroxide or persulfate is reduced 20%~50%, the dosage of ferrous iron or other metal salts is made to reduce 30%~60%.
Description
Technical field
The present invention relates to a kind of method for treating water, and in particular to strengthens Fenton/class Fenton's reaction system using free chlorine and goes
Except the method for water pollutant.
Background technique
Fenton's reaction is by ferrous ion (Fe2+) and hydrogen peroxide (H2O2) composition a kind of advanced chemical oxidation technology,
The hydroxyl radical free radical (HO) of strong oxidizing property can be generated, oxidation reaction can occur with hardly degraded organic substance in aqueous solution to broken
Its bad structure, therefore have a wide range of applications in multiple fields.Fenton reagent is to be sent out by French scientist Fenton in 1894
It is existing, have many advantages, such as applied widely, the small, strong antijamming capability of pollution and is swift in response.In Fenton's reaction, H2O2In Fe2 +The hydroxyl radical free radical (HO) with strong oxidizing property can be generated under catalysis, and generate Fe3+, Fe3+Can also and H2O2Reaction, it is raw
At Fe2+.Entire reaction process realizes Fe2+And Fe3+Between circulation, and continuously generate living radical (HO,
HOO·).HO electron affinity energy power is high, with non-selectivity can quickly aoxidize various organic compounds, be oxidized rapidly for
CO2Or H2O is converted into other organic matters being readily biodegradable.Class Fenton's reaction system refers to using Fenton reagent, changes one
A little conditions (such as ultraviolet lighting, electric Fenton) or the reaction for being doped with metal (copper, zinc, zirconium) other than iron etc..
Fenton's reaction, which has waste water difficult for biological degradation, toxic wastewater and Biostatic waste water, to be stablized, effectively removes
Function can handle different types of waste water because it is swift in response, applied widely, degrade a variety of polysaccharide polymers the advantages that,
More and more attention are at home and abroad obtained.
But there are H for individual Fenton system for handling2O2The disadvantages of consumption is big, and iron throwing amount is more, at high cost, pH narrow application range.
Summary of the invention
The purpose of the present invention is to solve existing Fenton system for handling, there are H2O2Consumption is big, and iron throwing amount is more and pollutes
The poor problem of object removal effect, and provide and strengthen Fenton/class Fenton's reaction system removal water pollutant using free chlorine
Method.
The present invention follows these steps to realize using the method that free chlorine strengthens Fenton's reaction system removal water pollutant:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, ferrous salt is then added into pending water, stirs pending water, and hydrogenperoxide steam generator is added；
Three, (quick) addition hypochlorite solutions or be passed through chlorine again, make the concentration 1 of effective chlorine in system~
15mg/L carries out reinforcing reaction, to remove water pollutant.
The present invention follows these steps to realize using the method that free chlorine strengthens class Fenton's reaction system removal water pollutant:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, transition metal salt is then added into pending water, stirs pending water, and single persulfate is added or crosses two sulphur
Hydrochlorate；
Three, (quick) addition hypochlorite solutions or be passed through chlorine again, make the concentration 1 of effective chlorine in system~
15mg/L carries out reinforcing reaction, to remove water pollutant；
Wherein transition metal salt described in step 2 be one of ferrous salt, mantoquita, zinc salt, zirconates, cobalt salt, manganese salt or
The a variety of mixtures of person.
Fenton or Fenton-like itself of the present invention can generate the strong free radical of oxidation, certainly such as hydroxyl
By base, potentiometric titrations etc..But the stability of hydroxyl radical free radical, potentiometric titrations is poor, Css in the solution
It is low.After free chlorine (hypochlorite or chlorine) is added in system, pass through free chlorine and chloride ion and hydroxyl radical free radical and sulfuric acid
The reaction of root free radical generates a large amount of Cl, ClO, Cl2The high Kinds of Free Radicals of equal Css, thus improve Fenton
Degradation effect of the system to pollutant.
The present invention using free chlorine strengthen Fenton's reaction system remove water pollutant method compared to individual Fenton/
Fenton-like can be improved 30%~50% to the removal rate of pollutant, subtract the dosage of hydrogen peroxide or persulfate
Few 20%~50%, so that the dosage of ferrous iron or other metal salts is reduced 30%~60%, the reaction time is made to shorten 2~10
Times.
Specific implementation method
Specific embodiment 1: present embodiment strengthens the side of Fenton's reaction system removal water pollutant using free chlorine
Method follows these steps to implement:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, ferrous salt is then added into pending water, stirs pending water, and hydrogenperoxide steam generator is added；
Three, (quick) addition hypochlorite solutions or be passed through chlorine again, make the concentration 1 of effective chlorine in system~
15mg/L carries out reinforcing reaction, to remove water pollutant.
After present embodiment adds hydrogenperoxide steam generator, hypochlorite solutions are added in 1~30min or are passed through chlorine
Gas.
Ferrous salt described in present embodiment is frerrous chloride, ferrous nitrate or ferrous sulfate.
Pending water can be trade effluent, the life of high COD, high phosphorus waste water, high ammonia nitrogen or high chroma in present embodiment
Sewage or landfill leachate etc. living.Its pollutant kind include all kinds of antibiotic, synthetic musk, anodyne, depressor,
Contraceptive, somnifacient, slimming drugs, hair jelly, hair dye and fungicide etc..
It can make to drink using the method that free chlorine strengthens Fenton's reaction system removal water pollutant using present embodiment
The removal rate of trace contaminant reduces by 60%~90% up to COD content in 80% or more or sewage in the water of source.
Specific embodiment 2: the present embodiment is different from the first embodiment in that when pending water is to drink source
Water, the throwing amount of hydrogen peroxide is 0.5~5mg/L in step 2.
Pollutant concentration in present embodiment drinking water is lower, and general COD concentration is in 0.001~10mg/L range
It is interior.Hydrogen peroxide is to add in form of an aqueous solutions.
Specific embodiment 3: the present embodiment is different from the first and the second embodiment in that working as the COD of pending water
When concentration is greater than 10mg/L, step 2 controls the mass concentration ratio of additional amount (mg/L) and COD of hydrogen peroxide in pending water
For 0.1~1:1.
High COD in present embodiment, high phosphorus waste water, can be the trade effluent of high ammonia nitrogen or high chroma, sanitary sewage or
Person's landfill leachate etc..Its pollutant kind include all kinds of antibiotic, synthetic musk, anodyne, depressor, contraceptive,
Somnifacient, slimming drugs, hair jelly, hair dye and fungicide etc..
Specific embodiment 4: ferrous in step 2 unlike one of present embodiment and specific embodiment one to three
Salt and hydrogen peroxide (Fe:H2O2) molar ratio be 0.5~1:3.
Specific embodiment 5: being stirred in step 2 unlike one of present embodiment and specific embodiment one to four
Speed be 100~1000r/min.
Specific embodiment 6: step 3 unlike one of present embodiment and specific embodiment one to five strengthen it is anti-
The time answered is 5~60min.
Specific embodiment 7: present embodiment strengthens class Fenton's reaction system removal water pollutant using free chlorine
Method follows these steps to implement:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, transition metal salt is then added into pending water, stirs pending water, and single persulfate is added or crosses two sulphur
Hydrochlorate；
Three, (quick) addition hypochlorite solutions or be passed through chlorine again, make the concentration 1 of effective chlorine in system~
15mg/L carries out reinforcing reaction, to remove water pollutant；
Wherein transition metal salt described in step 2 be one of ferrous salt, mantoquita, zinc salt, zirconates, cobalt salt, manganese salt or
The a variety of mixtures of person.
Peroxydisulfate described in present embodiment is potassium persulfate, sodium persulfate or peroxy-disulfuric acid ammonia, single over cure
Hydrochlorate is permonosulphuric acid potassium, permonosulphuric acid sodium or permonosulphuric acid ammonia, and mantoquita is stannous chloride, cuprous nitrate or cuprous sulfate.
Specific embodiment 8: present embodiment from unlike specific embodiment seven in step 2 when single over cure is added
When hydrochlorate, make 20~50:1 of equivalent molar ratio of transition metal salt and single persulfate.
Specific embodiment 9: present embodiment from unlike specific embodiment seven in step 2 when two sulphur were added
When hydrochlorate, make 5~50:1 of equivalent molar ratio of transition metal salt and peroxydisulfate.
Specific embodiment 10: present embodiment pending water unlike specific embodiment one or seven is to drink ground
Table water, Drinking Water, sanitary sewage or industrial wastewater.
Embodiment one: the present embodiment strengthens the method for Fenton's reaction system removal water pollutant by following using free chlorine
Step is implemented:
One, include the trace contaminants such as atrazine, nitrobenzene, Iopromide, pollutant in surface water to be processed after measured
Concentration is 2.0mg/L；
Two, the dosage for determining hydrogen peroxide is 2.0mg/L；
Three, the dosage for determining ferrous sulfate is 0.6mg/L；
Four, the pH value for adjusting pending water is 2.5；
Five, ferrous sulfate is then added into pending water, pending water is stirred with the revolving speed of 500r/min, peroxide is added
Change hydrogen solution；
Six, the hypochlorite stock solution that effective chlorine density is 10% is rapidly joined again, makes the concentration of effective chlorine in system
For 2.5mg/L, carry out strengthening reaction 15min, to remove water pollutant.
The present embodiment can make the removal rate of trace contaminant in drinking water up to 85% or more.
Embodiment two: the present embodiment strengthens the method for Fenton's reaction system removal water pollutant by following using free chlorine
Step is implemented:
One, the concentration of COD is 500mg/L in waste water from dyestuff to be processed；
Two, taking the ratio between hydrogen peroxide and the mass concentration of COD is 0.5:1, determines that the dosage of hydrogen peroxide is 250mg/
L；
Three, it is 0.5:3 according to the ratio between molar concentration of divalent iron salt and hydrogen peroxide, determines the dosage of divalent iron salt
(70mg/L)；
Four, the pH value for adjusting pending water is 3；
Five, divalent iron salt is then added into pending water, pending water is stirred with the revolving speed of 1000r/min, was added
Hydrogen peroxide solution；
Six, hypochlorite solutions are rapidly joined again, are made the concentration 10mg/L of effective chlorine in system, are carried out reinforcing reaction
30min, to remove water pollutant.
The present embodiment, which can make to handle COD content in water, reduces by 80%.
Embodiment three: the present embodiment strengthens the method for Fenton's reaction system removal water pollutant by following using free chlorine
Step is implemented:
One, the concentration through COD in sanitary sewage to be processed is 200mg/L；
Two, taking the ratio between hydrogen peroxide and the mass concentration of COD is 0.75:1, determines that the dosage of hydrogen peroxide is 150mg/
L；
Three, it is 0.75:3 according to the ratio between molar concentration of divalent iron salt and hydrogen peroxide, determines the dosage of divalent iron salt
(62mg/L)；
Four, the pH value for adjusting pending water is 3.5；
Five, divalent iron salt is then added into pending water, pending water is stirred with the revolving speed of 750r/min, peroxide is added
Change hydrogen solution；
Six, it is quickly passed through chlorine again, makes the concentration 5mg/L of effective chlorine in system, carries out strengthening reaction 20min, thus
Remove water pollutant.
The present embodiment can make COD content in sanitary sewage reduce by 90%.
Example IV: the present embodiment strengthens the method for Fenton's reaction system removal water pollutant by following using free chlorine
Step is implemented:
One, it is 35mg/L that pending water, which is ammonia-nitrogen content, and COD content is the sewage of farm of 100mg/L；
Two, taking the ratio between hydrogen peroxide and the mass concentration of COD is 0.5:1, determines that the dosage of hydrogen peroxide is 50mg/L；
Three, it is 0.75:3 according to the ratio between molar concentration of ferrous iron and hydrogen peroxide, determines ferrous dosage；
Four, the pH value for adjusting pending water is 3.0；
Five, divalent iron salt is then added into pending water, pending water is stirred with the revolving speed of 500r/min, peroxide is added
Change hydrogen solution；
Six, hypochlorite solutions are rapidly joined again, are made the concentration 7.5mg/L of effective chlorine in system, are carried out reinforcing reaction
30min, to remove water pollutant.
The present embodiment, which can make ammonia nitrogen in sewage content reduce by 80%, COD content, reduces by 75%.
Embodiment five: the present embodiment is pressed using the method that free chlorine strengthens class Fenton's reaction system removal water pollutant
Column step is implemented:
One, pending water be drink surface water, it includes trace contaminant mainly have Iopromide, Diclofenac, card
Horse Xiping etc., concentration are about 2.5mg/L；
Two, the dosage for determining single persulfate is 3mg/L；
Three, it is 1.5:3 according to the ratio between cobalt chloride and the molar concentration of single persulfate, determines the dosage of cobalt chloride；
Four, the pH value for adjusting pending water is 3.5；
Five, cobalt chloride then being added into pending water, pending water being stirred with the revolving speed of 1000r/min, single mistake is added
Sulfate liquor；
Six, hypochlorite solutions are rapidly joined again, are made the concentration 2mg/L of effective chlorine in system, are carried out reinforcing reaction
15min, to remove water pollutant.
The present embodiment can make the removal rate of trace contaminant in drinking water up to 85% or more.
Embodiment six: the present embodiment is pressed using the method that free chlorine strengthens class Fenton's reaction system removal water pollutant
Column step is implemented:
One, pending water be drink surface water, it includes trace contaminant mainly have Iopromide, Diclofenac, card
Horse Xiping etc., concentration are about 2.5mg/L；
Two, the dosage for determining single persulfate is 3mg/L；
Three, the dosage for determining cuprous salt is 0.85mg/L；
Four, the pH value for adjusting pending water is 3.0；
Five, cuprous salt is then added into pending water, pending water is stirred with the revolving speed of 1000r/min, be added single
Persulfate solution；
Six, hypochlorite solutions are rapidly joined again, are made the concentration 2mg/L of effective chlorine in system, are carried out reinforcing reaction
10min, to remove water pollutant.
The present embodiment can make the removal rate of trace contaminant in drinking water up to 90% or more.
Embodiment seven: the present embodiment is pressed using the method that free chlorine strengthens class Fenton's reaction system removal water pollutant
Column step is implemented:
One, the concentration for measuring COD in landfill leachate to be processed is 1000mg/L；
Two, taking the ratio between peroxydisulfate and the mass concentration of COD is 0.5:1, i.e. the dosage of peroxydisulfate is
500mg/L；
It three, is 0.5:3 according to the ratio between molar concentration of divalent iron salt and peroxydisulfate；
Four, the pH value for adjusting pending water is 3.0；
Five, divalent iron salt is then added into pending water, pending water is stirred with the revolving speed of 1000r/min, was added
Dithionate solution；
Six, hypochlorite solutions are rapidly joined again, are made the concentration 15mg/L of effective chlorine in system, are carried out reinforcing reaction
40min, to remove water pollutant.
The present embodiment, which can make to handle COD content in water, reduces by 85%.
Claims (10)
1. strengthening the method for Fenton's reaction system removal water pollutant using free chlorine, it is characterised in that this method presses following step
It is rapid to realize:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, ferrous salt is then added into pending water, stirs pending water, and hydrogenperoxide steam generator is added；
Three, hypochlorite solutions are added or are passed through chlorine, make 1~15mg/L of concentration of effective chlorine in system, are carried out strong
Change reaction, to remove water pollutant.
2. the method according to claim 1 for strengthening Fenton's reaction system removal water pollutant using free chlorine, special
Sign is that when pending water be drinking water, and the throwing amount of hydrogen peroxide is 0.5~5mg/L in step 2.
3. the method according to claim 1 for strengthening Fenton's reaction system removal water pollutant using free chlorine, special
Sign be when the COD concentration of pending water be greater than 10mg/L when, step 2 control pending water in hydrogen peroxide additional amount with
The mass concentration ratio of COD is 0.1~1:1.
4. the method according to claim 1 for strengthening Fenton's reaction system removal water pollutant using free chlorine, special
Sign is in step 2 that the molar ratio of ferrous salt and hydrogen peroxide is 0.5~1:3.
5. the method according to claim 1 for strengthening Fenton's reaction system removal water pollutant using free chlorine, special
Sign is that the speed stirred in step 2 is 100~1000r/min.
6. the method according to claim 1 for strengthening Fenton's reaction system removal water pollutant using free chlorine, special
The time that sign is that step 3 strengthens reaction is 5~60min.
7. strengthening the method for class Fenton's reaction system removal water pollutant using free chlorine, it is characterised in that this method is by following
Step is realized:
One, the pH value of pending water is adjusted in 2.0~4.0 ranges；
Two, transition metal salt is then added into pending water, stirs pending water, and single persulfate or peroxy-disulfuric acid is added
Salt；
Three, hypochlorite solutions are added or are passed through chlorine, make 1~15mg/L of concentration of effective chlorine in system, are carried out strong
Change reaction, to remove water pollutant；
Wherein transition metal salt described in step 2 is one of ferrous salt, mantoquita, zinc salt, zirconates, cobalt salt, manganese salt or more
Kind mixture.
8. the method according to claim 7 for strengthening class Fenton's reaction system removal water pollutant using free chlorine,
Be characterized in that in step 2 making when single persulfate is added the equivalent molar ratio 20 of transition metal salt and single persulfate~
50:1.
9. the method according to claim 7 for strengthening class Fenton's reaction system removal water pollutant using free chlorine,
Be characterized in that in step 2 making when peroxydisulfate is added the equivalent molar ratio 5 of transition metal salt and peroxydisulfate~
50:1.
10. the method for removal water pollutant according to claim 1 or claim 7, it is characterised in that pending water is to drink ground
Table water, Drinking Water, sanitary sewage or industrial wastewater.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910350303.9A CN110015744A (en) | 2019-04-28 | 2019-04-28 | Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910350303.9A CN110015744A (en) | 2019-04-28 | 2019-04-28 | Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN110015744A true CN110015744A (en) | 2019-07-16 |
Family
ID=67192735
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201910350303.9A Pending CN110015744A (en) | 2019-04-28 | 2019-04-28 | Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN110015744A (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110627176A (en) * | 2019-09-19 | 2019-12-31 | 陕西驭腾实业有限公司 | COD (chemical oxygen demand) degrading agent and method for degrading COD in wastewater |
| CN110723803A (en) * | 2019-10-22 | 2020-01-24 | 哈尔滨工业大学 | Method for removing pollutants in water by using high-valence ferric salt composite reagent |
| CN112777716A (en) * | 2020-12-09 | 2021-05-11 | 北京理工大学 | Method for photocatalytic degradation of trace organic macromolecules in surface water |
| CN114477418A (en) * | 2022-01-29 | 2022-05-13 | 哈尔滨工业大学 | Method for removing organic pollutants in water by zero-valent iron reinforced hypochlorite |
| CN115571967A (en) * | 2022-09-09 | 2023-01-06 | 哈尔滨工业大学 | Method for treating salt-containing organic wastewater by using inorganic anion reinforced copper-containing catalyst Fenton system |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6994793B2 (en) * | 2002-04-19 | 2006-02-07 | Hydro-Trace Incorporated | Process for remediating ground water containing one or more nitrogen compounds |
| CN101792205A (en) * | 2010-02-10 | 2010-08-04 | 哈尔滨工业大学 | Fenton and Fenton-like system fortifier and using method thereof |
| CN106745656A (en) * | 2017-01-17 | 2017-05-31 | 华侨大学 | It is a kind of to strengthen the method that iron/peroxy-monosulfate homogeneous system removes organic pollutants |
-
2019
- 2019-04-28 CN CN201910350303.9A patent/CN110015744A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6994793B2 (en) * | 2002-04-19 | 2006-02-07 | Hydro-Trace Incorporated | Process for remediating ground water containing one or more nitrogen compounds |
| CN101792205A (en) * | 2010-02-10 | 2010-08-04 | 哈尔滨工业大学 | Fenton and Fenton-like system fortifier and using method thereof |
| CN106745656A (en) * | 2017-01-17 | 2017-05-31 | 华侨大学 | It is a kind of to strengthen the method that iron/peroxy-monosulfate homogeneous system removes organic pollutants |
Non-Patent Citations (6)
| Title |
|---|
| 严建华等主编: "《能源与环境研究进展》", 31 October 2008, 浙江大学出版社 * |
| 侯艳君: "《臭氧/金属氧化物催化降解水中有机物的研究》", 30 June 2013, 黑龙江大学出版社 * |
| 刘希涛等编著: "《活化过硫酸盐在环境污染控制中的应用》", 31 May 2018, 中国环境科学出版社 * |
| 斯图(STROO,H.F.）等: "《地下水氯代烃污染羽原位修复》", 31 March 2015, 地质出版社 * |
| 田晓宇: "Fenton-NaClO法联用深度处理造纸废水实验研究", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》 * |
| 高金龙: "萃取-Fenton-次氯酸钠氧化联合处理咖啡因废水", 《工业水处理》 * |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110627176A (en) * | 2019-09-19 | 2019-12-31 | 陕西驭腾实业有限公司 | COD (chemical oxygen demand) degrading agent and method for degrading COD in wastewater |
| CN110723803A (en) * | 2019-10-22 | 2020-01-24 | 哈尔滨工业大学 | Method for removing pollutants in water by using high-valence ferric salt composite reagent |
| CN112777716A (en) * | 2020-12-09 | 2021-05-11 | 北京理工大学 | Method for photocatalytic degradation of trace organic macromolecules in surface water |
| CN114477418A (en) * | 2022-01-29 | 2022-05-13 | 哈尔滨工业大学 | Method for removing organic pollutants in water by zero-valent iron reinforced hypochlorite |
| CN115571967A (en) * | 2022-09-09 | 2023-01-06 | 哈尔滨工业大学 | Method for treating salt-containing organic wastewater by using inorganic anion reinforced copper-containing catalyst Fenton system |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN110015744A (en) | Strengthen Fenton/class Fenton's reaction system removal water pollutant method using free chlorine | |
| Manoli et al. | Enhanced oxidative transformation of organic contaminants by activation of ferrate (VI): Possible involvement of FeV/FeIV species | |
| Chen et al. | Molecular-level comparison study on microwave irradiation-activated persulfate and hydrogen peroxide processes for the treatment of refractory organics in mature landfill leachate | |
| Kang et al. | Pre-oxidation and coagulation of textile wastewater by the Fenton process | |
| Arslan | Treatability of a simulated disperse dye-bath by ferrous iron coagulation, ozonation, and ferrous iron-catalyzed ozonation | |
| Catalkaya et al. | Color, TOC and AOX removals from pulp mill effluent by advanced oxidation processes: A comparative study | |
| Mohajeri et al. | Influence of Fenton reagent oxidation on mineralization and decolorization of municipal landfill leachate | |
| Pawar et al. | An overview of the Fenton process for industrial wastewater | |
| Dehghani et al. | The effect of aeration on advanced coagulation, flotation and advanced oxidation processes for color removal from wastewater | |
| CN104891719A (en) | Method for pre-treating organic industrial wastewater based on ferric-carbon micro-electrolysis activated persulfate | |
| CN107311291A (en) | The method of sulfite oxidation degraded organic pollutants is combined using heterogeneous iron-based material under aeration condition | |
| Kattel et al. | Ferrous ion-activated persulphate process for landfill leachate treatment: removal of organic load, phenolic micropollutants and nitrogen | |
| CN105036293A (en) | Method for removing organic pollutants in water by ferrate reinforced ozone oxidation | |
| Wang et al. | 2, 4, 6-Trichlorophenol-promoted catalytic wet oxidation of humic substances and stabilized landfill leachate | |
| Huang et al. | Improved oxidation of refractory organics in concentrated leachate by a Fe 2+-enhanced O 3/H 2 O 2 process | |
| Zhu et al. | Application of ferrous hydrogen peroxide for treatment of DSD-acid manufacturing process wastewater | |
| CN109987693A (en) | The method that dithionite activate persistent organic pollutants in persulfate processing waste water | |
| Kilic et al. | Landfill Leachate Treatment by Fenton and Fenton‐L ike Oxidation Processes | |
| Tosik et al. | Color removal and improvement of biodegradability of wastewater from dyes production using ozone and hydrogen peroxide | |
| CN109368764A (en) | A kind of method for treating water for strengthening persulfate oxidation | |
| Shi et al. | Combined reduction/precipitation, chemical oxidation, and biological aerated filter processes for treatment of electroplating wastewater | |
| De Sena et al. | Assessment of polyacrylamide degradation using advanced oxidation processes and ferrate (VI) oxidation | |
| Süzen et al. | Removal of reactive black 5 dye using fenton oxidation from aqueous solutions and optimization of response surface methodology | |
| CN108558086B (en) | Combined process for removing hexavalent selenium in water | |
| CN113603205B (en) | Method for accelerating degradation of organic pollutants by potassium permanganate |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190716 |
|
| RJ01 | Rejection of invention patent application after publication |