CN108911101A - A method of based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron - Google Patents

A method of based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron Download PDF

Info

Publication number
CN108911101A
CN108911101A CN201810662373.3A CN201810662373A CN108911101A CN 108911101 A CN108911101 A CN 108911101A CN 201810662373 A CN201810662373 A CN 201810662373A CN 108911101 A CN108911101 A CN 108911101A
Authority
CN
China
Prior art keywords
zero
valent iron
oxalic acid
ball milling
metal ion
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.)
Granted
Application number
CN201810662373.3A
Other languages
Chinese (zh)
Other versions
CN108911101B (en
Inventor
张礼知
胡月
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Huazhong Normal University
Central China Normal University
Original Assignee
Huazhong Normal University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Huazhong Normal University filed Critical Huazhong Normal University
Priority to CN201810662373.3A priority Critical patent/CN108911101B/en
Publication of CN108911101A publication Critical patent/CN108911101A/en
Application granted granted Critical
Publication of CN108911101B publication Critical patent/CN108911101B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • C02F1/705Reduction by metals
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Abstract

The present invention relates to a kind of methods based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron.This method is:Ball milling oxalic acid Zero-valent Iron is added in the aqueous solution containing heavy metal ion, the removal of heavy metal ion is carried out.The method of the ball milling oxalic acid Zero-valent Iron is that oxalic acid and Zero-valent Iron are prepared by solid-phase ball milling method, and the ability of heavy-metal ion removal significantly increases, and solves the problems, such as that Zero-valent Iron heavy-metal ion removal activity is low.The improvement that is simple, at low cost, environmental-friendly, can be widely used for various heavy polluted underground water of the preparation method of oxalic acid Zero-valent Iron provided by the invention.

Description

A method of based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron
Technical field
The invention belongs to Environmental Chemistry fields, and in particular to be based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron Method, be applicable to the processing of the fields such as printing and dyeing, industry waste water.
Background technique
Dosage is continuous in industrial or agricultural, science and technology, daily life for heavy metal (chromium, arsenic, lead, cadmium, copper, nickel, zinc, tin, mercury etc.) Increase, and can be discharged into environment with various channels, Heavy Metals In Environment total amount is caused to continue to increase.Heavy metal pollution is easily long-pending Tired, irreversible, toxicity is big, metabolism slowly and easily enrichment the features such as, seriously endanger human health.Therefore, develop green high-efficient Heavy metal pollution control technology is extremely urgent.
Relative to other heavy metal pollution recovery techniques, zero-valent iron technology has environmental-friendly, removal various heavy etc. Feature is widely used in the improvement of waste water and polluted underground water over 20 years.But zeroth order iron surface is easy to by water and oxygen institute Oxidation, one layer of ferriferous oxide of Surface Creation form unique core shell architecture.And the official of the thickness of ferriferous oxide shell and its surface The absorption and reduction for all affecting heavy metal can be rolled into a ball, the thickness effect electron transfer rate of oxide layer aoxidizes the function of layer surface Group influences the absorption of heavy metal, to decide that electronics that Zero-valent Iron is transmitted out is used for the ratio of reducing heavy metal, i.e. electronics Selectivity.Researcher has developed a variety of methods to eliminate the negative effect of shell, for example, using pickling, reducing agent reduction and The modes (part) such as ultrasound removing remove Zero-valent Iron surface crust, or apply the corrosion rate etc. that low-intensity magnetic field accelerates Zero-valent Iron.This A little methods reduce the thickness of oxide layer simply by pretreatment, but oxide layer generates again during removing removing heavy metals, So being also difficult to solve the problems, such as that Zero-valent Iron removal heavy metal activity is not high by the removal of oxide layer.
Summary of the invention
The technical problem to be solved by the present invention is to provide a kind of based on ball milling oxalic acid in view of the deficiencies of the prior art The method of the efficient heavy-metal ion removal of Zero-valent Iron.
The present invention be solve the problems, such as it is set forth above used by technical solution be:
A method of based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron, ball milling oxalic acid Zero-valent Iron is added Enter in the aqueous solution containing heavy metal ion, carries out the removal of heavy metal ion, the ball milling oxalic acid Zero-valent Iron is by oxalic acid It is prepared with Zero-valent Iron by solid-phase ball milling method.
According to the above scheme, it is washed after the oxalic acid and Zero-valent Iron ball milling, vacuum drying obtains oxalic acid Zero-valent Iron.It is described Washing be washing after alcohol wash.
According to the above scheme, the oxalic acid accounts for the molar percentage of Zero-valent Iron and is:0.2-2.0%.
According to the above scheme, the Ball-milling Time:0.5-5h, rotational speed of ball-mill 300-800r/min.
According to the above scheme, the partial size, pattern of the Zero-valent Iron, purity and resting period no requirement (NR).Zero-valent Iron can be micron Grade, can also be nanoscale.
According to the above scheme, the oxalic acid purity is technical grade or more.
According to the above scheme, the dosage of the ball milling oxalic acid Zero-valent Iron is 1-5g/L.
According to the above scheme, the concentration of heavy metal ion is 2-50ppm, and reaction temperature is 10-30 DEG C, and reaction pH is 4- 8。
According to the above scheme, it is shaken in removal process with shaking table, comes into full contact with heavy metal ion and Zero-valent Iron.Using shaking table Shaking purpose is to come into full contact with heavy metal ion and Zero-valent Iron.If preferable effect can also be obtained without concussion.
According to the above scheme, the heavy metal includes but is not limited to chromium, mercury, silver, lead, nickel.
Technical principle of the invention (see Fig. 1):
Zeroth order iron surface covers one layer of hydroxyl, and poor to the adsorption capacity of heavy metal ion, more Zero-valent Irons are by water and oxygen Gas is aoxidized, so Zero-valent Iron surface hydroxyl is unfavorable for the absorption to heavy metal ion.After oxalic acid and Zero-valent Iron ball-milling treatment, Oxalate replaces surface hydroxyl and with chemical bonds to zeroth order iron surface, and this in-situ modification is in the ironing surface oxalate of zeroth order Zeroth order iron surface can be stable in the presence of.Zeroth order iron surface oxalic acidization can promote the adsorption capacity to heavy metal ion, to mention The electronics of high Zero-valent Iron is used for the ratio of reducing heavy metal ion, and the electronics for reducing Zero-valent Iron reacts consumption with water or oxygen Amount, is achieved in the efficient removal of heavy metal ion.Experiments verify that being used to remove different heavy metal ion all has high work Property.
The advantage of the invention is that:
1, the present invention is based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron, method is simple, easy to operate, can be obvious Promote the removal of heavy metal ion.
2, Zero-valent Iron is cheap, environmental-friendly, can be widely used in practical Heavy Metal Pollution Control.
3, method of the invention has universal removal ability to different heavy metal ion.
Detailed description of the invention
The preparation principle figure of Fig. 1 ball milling oxalic acid Zero-valent Iron;
1 ball milling of Fig. 2 embodiment prepares oxalic acid Zero-valent Iron and Zero-valent Iron except directly addition oxalic acid activity comparison during chromium Figure;
Cr VI effect picture in 2 ball milling oxalic acid Zero-valent Iron pollution administration water body of Fig. 3 embodiment;
Mercury effect picture in 3 ball milling oxalic acid Zero-valent Iron polluted-water of Fig. 4 embodiment;
Silver-colored effect picture in 4 ball milling oxalic acid Zero-valent Iron pollution administration water body of Fig. 5 embodiment;
Lead effect picture in 5 ball milling oxalic acid Zero-valent Iron pollution administration water body of Fig. 6 embodiment;
Nickel effect picture in 6 ball milling oxalic acid Zero-valent Iron pollution administration water body of Fig. 7 embodiment;
Specific embodiment
Carry out the summary of the invention that the present invention will be described in detail below by specific implementation case, described specific embodiment is only used To explain the present invention, it is not intended to limit the present invention.
1 ball milling of embodiment prepares oxalic acid Zero-valent Iron and Zero-valent Iron except addition oxalic acid effect contrast figure direct during chromium
5.6g Zero-valent Iron (partial size is up to 80 μm) and 0.126g oxalic acid (containing two water) are put into ball grinder, revolving speed is 550r/min, Ball-milling Time 2h, the alcohol of sample washing later wash vacuum drying and obtain oxalic acid Zero-valent Iron Fe/Ox (n= 1.0%).Chromate waste water, pH value of solution 6.5 are simulated with the potassium bichromate solution 30mL that hexavalent chromium concentration is 20mg/L, temperature is 25 DEG C, Fe/Ox sample 0.1g is added, is put into the shaking table that revolving speed is 150r/min, periodically samples, spectrophotometry surveys solution sexavalence Chromium concn.As control experiment, by the 0.097g Fe contained in theoretical amount in 0.1g Fe/Ox (n=1.0%) sample and 0.003g oxalic acid (concentration of oxalic acid 0.79mmol/L) is added in chrome liquor, and adjusting pH value of solution is 6.5.As further check experiment, Different oxalic acid amount (system medium-height grass acid concentration is respectively 0.01,0.1mol/L) conducts are added again while 0.1g Zero-valent Iron is added Control experiment, adjusting pH value of solution is 6.5, and other conditions are constant, as a result see Fig. 2.Oxalic acid Zero-valent Iron 120min of the invention is almost Completely remove chromium;And directly 0.003g oxalic acid is added except in chromium system, reaction 120min only eliminates about 10%;With oxalic acid Amount is sequentially increased, except chromium activity is enhanced, but still substantially less than oxalic acid Zero-valent Iron.
The above-mentioned oxalic acid Zero-valent Iron for absolutely proving the present invention and preparing by using oxalic acid and Zero-valent Iron solid-phase ball milling method, can Realize the efficient removal of chromium.
Cr VI effect picture in 2 ball milling oxalic acid Zero-valent Iron pollution administration water body of embodiment
By 5.6g Zero-valent Iron (partial size is up to 160 μm) and different oxalic acid amounts, (molar ratio of oxalic acid and Zero-valent Iron is followed successively by: 0%, 0.2%, 0.5%, 1.0%, 2.0%) it is put into ball grinder, revolving speed 550r/min, Ball-milling Time 2h, sample washing Alcohol washes vacuum drying and obtains oxalic acid Zero-valent Iron, i.e. Fe/Ox (n=0.0%, 0.2%, 0.5%, 1.0%, 2.0%).Use sexavalence The potassium bichromate solution 30mL that chromium concn is 20mg/L simulates chromate waste water, and pH value of solution 5.2, temperature is 30 DEG C, and Fe/Ox is added Sample 0.1g is put into the shaking table that revolving speed is 150r/min, periodically samples, and spectrophotometry surveys solution hexavalent chromium concentration, as a result sees Fig. 3.Non- oxalic acid Zero-valent Iron only eliminates 10% in 120min, and oxalic acid Zero-valent Iron is greatly improved except chromium rate, And being sequentially increased with ball milling oxalic acid amount illustrates that the modification of different oxalic acid is attained by the height of chromium except chromium rate is sequentially increased Effect removal.
3 ball milling oxalic acid Zero-valent Iron pollution administration Mercury in Water Body effect picture of embodiment
5.6g Zero-valent Iron (partial size is up to 80 μm) and 0.126g oxalic acid (containing two water) are put into ball grinder, revolving speed is 550r/min, Ball-milling Time 2h, washing alcohol wash vacuum drying and obtain oxalic acid Zero-valent Iron, i.e. Fe/Ox (n=1.0%).Use mercury The mercuric chloride solution 30mL that concentration is 5mg/L simulates mercury waste water, and pH value of solution 7.0, temperature is 25 DEG C, and Fe/Ox sample is added 0.1g, is put into the shaking table that revolving speed is 150r/min, periodically samples, and surveys mercury in solution with inductive coupling plasma emission spectrograph Concentration, while using non-oxalic acid Zero-valent Iron as control experiment, as a result see Fig. 4.Non- oxalic acid Zero-valent Iron is slowly gone in 120min The removal of mercury, and oxalic acid Zero-valent Iron has completely removed mercury in 10min.Illustrate that oxalic acid Zero-valent Iron can reach efficiently going for mercury It removes.
Silver-colored effect picture in 4 ball milling oxalic acid Zero-valent Iron pollution administration water body of embodiment
5.6g Zero-valent Iron (partial size is up to 40 μm) and 0.126g oxalic acid (containing two water) are put into ball grinder, revolving speed is 550r/min, Ball-milling Time 2h, washing alcohol wash vacuum drying and obtain oxalic acid Zero-valent Iron, i.e. Fe/Ox (n=1.0%).With silver The silver nitrate solution 30mL that concentration is 5mg/L simulates silver waste water, and pH value of solution 6.5, temperature is 25 DEG C, and Fe/Ox sample is added 0.1g is put into the shaking table that revolving speed is 150r/min, periodically samples, surveys silver concentration in solution, while being with non-oxalic acid Zero-valent Iron As a result Fig. 5 is shown in control experiment.Non- oxalic acid Zero-valent Iron can slowly go desilver in 120min, and oxalic acid Zero-valent Iron exists Silver has been completely removed in 10min.Illustrate that oxalic acid Zero-valent Iron can reach the efficient removal of silver.
Lead effect picture in 5 ball milling oxalic acid Zero-valent Iron pollution administration water body of embodiment
5.6g Zero-valent Iron (partial size is up to 80 μm) and 0.126g oxalic acid (containing two water) are put into ball grinder, revolving speed is 550r/min, Ball-milling Time 1h, washing alcohol wash vacuum drying and obtain oxalic acid Zero-valent Iron, i.e. Fe/Ox (n=1.0%).Use lead The lead nitrate solution 30mL that concentration is 10mg/L simulates lead waste water, and pH value of solution 6.5, temperature is 25 DEG C, and Fe/Ox sample is added 0.1g is put into the shaking table that revolving speed is 150r/min, periodically samples, surveys lead concentration in solution, while being with non-oxalic acid Zero-valent Iron As a result Fig. 6 is shown in control experiment.The rate constant of oxalic acid Zero-valent Iron removal lead is 2 times of non-oxalic acid Zero-valent Iron, illustrates oxalic acid The efficient removal of lead can be reached by changing Zero-valent Iron.
Nickel effect picture in 6 ball milling oxalic acid Zero-valent Iron pollution administration water body of embodiment
5.6g Zero-valent Iron (partial size is up to 160 μm) and 0.252g oxalic acid (containing two water) are put into ball grinder, revolving speed is 800r/min, Ball-milling Time 4h, sample wash vacuum drying through washing alcohol and obtain oxalic acid Zero-valent Iron, i.e. Fe/Ox (n= 2.0%).Nickel waste water is simulated with the nickel chloride solution 50mL that nickel concentration is 20mg/L, Fe/Ox sample is added in pH value of solution 8 0.05g is put into the shaking table that revolving speed is 400r/min, 10 DEG C of temperature, periodically samples, survey in solution and remain nickel concentration, while with not Oxalic acid Zero-valent Iron is control experiment, as a result sees Fig. 7.Oxalic acid Zero-valent Iron eliminates 98% in 40min, and non-oxalic acidization zero Valence iron only eliminates 60% in 90min, illustrates that oxalic acid Zero-valent Iron can reach the efficient removal of nickel.

Claims (10)

1. a kind of method based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron, it is characterised in that:By ball milling oxalic acid Change Zero-valent Iron to be added in the aqueous solution containing heavy metal ion, carries out the removal of heavy metal ion, the ball milling oxalic acidization zero Valence iron is that oxalic acid and Zero-valent Iron are prepared by solid-phase ball milling method.
2. according to the method described in claim 1, it is characterized in that:Through washing after the oxalic acid and Zero-valent Iron ball milling, vacuum is dry It is dry to obtain oxalic acid Zero-valent Iron.
3. according to the method described in claim 1, it is characterized in that:The molar percentage that the oxalic acid accounts for Zero-valent Iron is: 0.2-2.0%.
4. according to the method described in claim 1, it is characterized in that:The Ball-milling Time:0.5-5h, rotational speed of ball-mill 300- 800r/min。
5. according to the method described in claim 1, it is characterized in that:Partial size, pattern, purity and the resting period of the Zero-valent Iron No requirement (NR).
6. according to the method described in claim 1, it is characterized in that:The oxalic acid purity is technical grade or more.
7. according to the method described in claim 1, it is characterized in that:The dosage of the ball milling oxalic acid Zero-valent Iron is 1-5g/ L。
8. according to the method described in claim 1, it is characterized in that:The concentration of heavy metal ion is 2-50ppm, reaction temperature Degree is 10-30 DEG C, and reaction pH is 4-8.
9. according to the method described in claim 1, it is characterized in that:Shaken in removal process with shaking table, make heavy metal ion and Zero-valent Iron comes into full contact with.
10. according to the method described in claim 1, it is characterized in that:The heavy metal includes but is not limited to chromium, and mercury is silver-colored, Lead, nickel.
CN201810662373.3A 2018-06-25 2018-06-25 Method for efficiently removing heavy metal ions based on ball milling oxalic acid zero-valent iron Active CN108911101B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810662373.3A CN108911101B (en) 2018-06-25 2018-06-25 Method for efficiently removing heavy metal ions based on ball milling oxalic acid zero-valent iron

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810662373.3A CN108911101B (en) 2018-06-25 2018-06-25 Method for efficiently removing heavy metal ions based on ball milling oxalic acid zero-valent iron

Publications (2)

Publication Number Publication Date
CN108911101A true CN108911101A (en) 2018-11-30
CN108911101B CN108911101B (en) 2021-06-04

Family

ID=64422374

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810662373.3A Active CN108911101B (en) 2018-06-25 2018-06-25 Method for efficiently removing heavy metal ions based on ball milling oxalic acid zero-valent iron

Country Status (1)

Country Link
CN (1) CN108911101B (en)

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110201992A (en) * 2019-05-16 2019-09-06 常熟理工学院 A kind of detoxification of chromium-polluted soil
CN110606538A (en) * 2019-07-30 2019-12-24 华中师范大学 Method for removing pollutants based on efficient reduction of borated zero-valent iron
CN110713242A (en) * 2019-08-09 2020-01-21 中国科学院地理科学与资源研究所 Zero-valent iron material Fe @ iron fluoride and preparation method thereof
CN112062259A (en) * 2020-09-23 2020-12-11 中国环境科学研究院 Method for degrading organic pollutants by using interface-targeted activated persulfate
CN112079417A (en) * 2020-09-23 2020-12-15 华中师范大学 Surface humation zero-valent iron and preparation method and application thereof
CN112139508A (en) * 2020-09-23 2020-12-29 中国科学院地理科学与资源研究所 Amphoteric surface micron zero-valent iron, and preparation method and application thereof
CN112250156A (en) * 2020-10-16 2021-01-22 中国环境科学研究院 Silicification modified zero-valent iron and preparation method and application thereof
CN114291992A (en) * 2021-12-29 2022-04-08 华中师范大学 Preparation combination for removing municipal sludge antibiotic resistance genes and application
US20220118516A1 (en) * 2020-10-16 2022-04-21 Chinese Research Academy Of Environmental Sciences Silicified modified zero-valent iron and its preparation method and application
CN115159598A (en) * 2022-07-27 2022-10-11 湖北省生态环境科学研究院(省生态环境工程评估中心) Preparation method and application of sodium oxalate doped modified nano zero-valent iron
CN115403124A (en) * 2022-09-09 2022-11-29 浙江工业大学绍兴研究院 Method for efficiently removing heavy metal pollutants by ball milling of sargassum acidized zero-valent iron composite material
CN115432796A (en) * 2022-09-08 2022-12-06 浙江工业大学绍兴研究院 Method for efficiently removing heavy metals in water body based on lignosulfonate-modified cobalt-doped zero-valent iron composite material
CN115583712A (en) * 2022-11-09 2023-01-10 华中师范大学 Method for removing halohydrocarbon and heavy metal composite pollutants in water body by oxalic acid modified zero-valent iron and hydrotalcite physical mixture
CN117509847A (en) * 2023-11-09 2024-02-06 华中师范大学 Method for removing water bacteria and antibiotic resistance genes of copper ion coupled zero-valent iron

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20040069720A1 (en) * 2002-05-29 2004-04-15 Clausen Christian A. Contaminant removal from natural resources
WO2010057225A3 (en) * 2008-11-11 2011-04-21 Afrisam (South Africa) (Pty) Ltd ADDITIVES FOR Cr (VI) REDUCTION IN CEMENT, SLAGS, MORTARS, CONCRETE, WASTE WATER AND MINING INDUSTRY WASTE
CN104667865A (en) * 2014-12-31 2015-06-03 浙江工业大学 Ferric-carbon complex as well as preparation and application thereof
CN104846271A (en) * 2015-04-27 2015-08-19 同济大学 Particle-reinforced iron-based composite material and ball milling preparation method and application thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20040069720A1 (en) * 2002-05-29 2004-04-15 Clausen Christian A. Contaminant removal from natural resources
WO2010057225A3 (en) * 2008-11-11 2011-04-21 Afrisam (South Africa) (Pty) Ltd ADDITIVES FOR Cr (VI) REDUCTION IN CEMENT, SLAGS, MORTARS, CONCRETE, WASTE WATER AND MINING INDUSTRY WASTE
CN104667865A (en) * 2014-12-31 2015-06-03 浙江工业大学 Ferric-carbon complex as well as preparation and application thereof
CN104846271A (en) * 2015-04-27 2015-08-19 同济大学 Particle-reinforced iron-based composite material and ball milling preparation method and application thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
GU, YAWEI ET AL: "Mechanochemically Sulfidated Microscale Zero Valent Iron: Pathways, Kinetics, Mechanism, and Efficiency of Trichloroethylene Dechlorination", 《ENVIRONMENTAL SCIENCE & TECHNOLOGY》 *
YU-HENG OU ET AL: "Short-chain organic acids increase the reactivity of zerovalent iron nanoparticles toward polychlorinated aromatic pollutants", 《CHEMICAL ENGINEERING JOURNAL》 *

Cited By (19)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110201992B (en) * 2019-05-16 2021-05-11 常熟理工学院 Detoxification method of chromium-contaminated soil
CN110201992A (en) * 2019-05-16 2019-09-06 常熟理工学院 A kind of detoxification of chromium-polluted soil
CN110606538A (en) * 2019-07-30 2019-12-24 华中师范大学 Method for removing pollutants based on efficient reduction of borated zero-valent iron
CN110713242A (en) * 2019-08-09 2020-01-21 中国科学院地理科学与资源研究所 Zero-valent iron material Fe @ iron fluoride and preparation method thereof
CN112062259B (en) * 2020-09-23 2021-11-30 中国环境科学研究院 Method for degrading organic pollutants by using interface-targeted activated persulfate
CN112139508A (en) * 2020-09-23 2020-12-29 中国科学院地理科学与资源研究所 Amphoteric surface micron zero-valent iron, and preparation method and application thereof
CN112079417A (en) * 2020-09-23 2020-12-15 华中师范大学 Surface humation zero-valent iron and preparation method and application thereof
CN112062259A (en) * 2020-09-23 2020-12-11 中国环境科学研究院 Method for degrading organic pollutants by using interface-targeted activated persulfate
CN112250156A (en) * 2020-10-16 2021-01-22 中国环境科学研究院 Silicification modified zero-valent iron and preparation method and application thereof
US11850664B2 (en) * 2020-10-16 2023-12-26 Chinese Research Academy Of Environmental Sciences Silicified modified zero-valent iron and its preparation method and application
US20220118516A1 (en) * 2020-10-16 2022-04-21 Chinese Research Academy Of Environmental Sciences Silicified modified zero-valent iron and its preparation method and application
CN114291992B (en) * 2021-12-29 2022-07-19 华中师范大学 Preparation combination for removing municipal sludge antibiotic resistance genes and application
CN114291992A (en) * 2021-12-29 2022-04-08 华中师范大学 Preparation combination for removing municipal sludge antibiotic resistance genes and application
CN115159598A (en) * 2022-07-27 2022-10-11 湖北省生态环境科学研究院(省生态环境工程评估中心) Preparation method and application of sodium oxalate doped modified nano zero-valent iron
CN115159598B (en) * 2022-07-27 2023-11-21 湖北省生态环境科学研究院(省生态环境工程评估中心) Preparation method and application of sodium oxalate doped modified nano zero-valent iron
CN115432796A (en) * 2022-09-08 2022-12-06 浙江工业大学绍兴研究院 Method for efficiently removing heavy metals in water body based on lignosulfonate-modified cobalt-doped zero-valent iron composite material
CN115403124A (en) * 2022-09-09 2022-11-29 浙江工业大学绍兴研究院 Method for efficiently removing heavy metal pollutants by ball milling of sargassum acidized zero-valent iron composite material
CN115583712A (en) * 2022-11-09 2023-01-10 华中师范大学 Method for removing halohydrocarbon and heavy metal composite pollutants in water body by oxalic acid modified zero-valent iron and hydrotalcite physical mixture
CN117509847A (en) * 2023-11-09 2024-02-06 华中师范大学 Method for removing water bacteria and antibiotic resistance genes of copper ion coupled zero-valent iron

Also Published As

Publication number Publication date
CN108911101B (en) 2021-06-04

Similar Documents

Publication Publication Date Title
CN108911101A (en) A method of based on the efficient heavy-metal ion removal of ball milling oxalic acid Zero-valent Iron
Chang et al. A review of the applications of ion floatation: Wastewater treatment, mineral beneficiation and hydrometallurgy
CN109384299B (en) Method for removing hexavalent chromium in water body by using sodium oxalate modified zero-valent iron
Hu et al. Adsorptive recovery of vanadium (V) from chromium (VI)-containing effluent by Zr (IV)-loaded orange juice residue
CN110606538A (en) Method for removing pollutants based on efficient reduction of borated zero-valent iron
CN105149334B (en) A kind of oxidation of chromium-polluted soil-chelating elution combined remediation method
Huang et al. Concentration and separation of vanadium from alkaline media by strong alkaline anion-exchange resin 717
CN106861615A (en) A kind of charcoal magnetic Fe3S4Composite nano adsorbent and preparation method and application
CN102616824A (en) Method for preparing ultrafine high-whiteness active barite powder
CN110387470A (en) The processing method and gained silica-alumina material of waste acetic acid and its application
CN105457599A (en) Synthesis of magnetic nano-adsorbent material and application method thereof to the treatment of heavy metal waste liquid
CN104959112A (en) Modified papermaking sludge adsorbent, and preparation method and application thereof
Ying et al. A cleaner and sustainable method to recover vanadium and chromium from the leaching solution based on solvent extraction
Han et al. Deep purification of copper from Cu (II)-EDTA acidic wastewater by Fe (III) replacement/diethyldithiocarbamate precipitation
CN106311186A (en) Preparation method of magnetic mercury removal adsorbent
Zhang et al. Super-efficient extraction of U (VI) by the dual-functional sodium vanadate (Na2V6O16· 2H2O) nanobelts
Ma et al. Novel technology for hydrogen sulfide purification via the slurry prepared from roasted vanadium steel slag
Tan et al. Ultrasonic-assisted preparation of interlaced layered hydrotalcite (U–Fe/Al-LDH) for high-efficiency removal of Cr (VI): Enhancing adsorption-coupled reduction capacity and stability
CN109206554A (en) A kind of ion imprinted polymer material of photo-reduction Cr VI and its preparation and application
CN106946375A (en) A kind of nano zero valence iron joint ion exchange resin goes the method for total nitrogen and application in water removal
CN102807293A (en) Resource treatment method of CODCr (chemical oxygen demand chromium) measurement waste liquid
CN107190155A (en) Vanadium, the method for chromium are extracted in a kind of mixed liquor from containing vanadium and chromium
CN110342628A (en) A kind of processing method that copper waste water is complexed
CN108793371A (en) A kind of Na2EDTA couples Fe0/Fe3O4The method that composite material removes Cr (VI) in water body
CN101746843A (en) Method for recycling heavy metal ion in water body by utilizing ion chelate fiber

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
GR01 Patent grant
GR01 Patent grant