CN109110901B - Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride - Google Patents

Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride Download PDF

Info

Publication number
CN109110901B
CN109110901B CN201811020504.4A CN201811020504A CN109110901B CN 109110901 B CN109110901 B CN 109110901B CN 201811020504 A CN201811020504 A CN 201811020504A CN 109110901 B CN109110901 B CN 109110901B
Authority
CN
China
Prior art keywords
zero
valent iron
heavy metal
iron fluoride
fluoride
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.)
Active
Application number
CN201811020504.4A
Other languages
Chinese (zh)
Other versions
CN109110901A (en
Inventor
张礼知
彭星
王谦
贾法龙
廖敏子
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.)
Central China Normal University
Original Assignee
Central China 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 Central China Normal University filed Critical Central China Normal University
Priority to CN201811020504.4A priority Critical patent/CN109110901B/en
Publication of CN109110901A publication Critical patent/CN109110901A/en
Application granted granted Critical
Publication of CN109110901B publication Critical patent/CN109110901B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

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
    • 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
    • C02F2101/22Chromium or chromium compounds, e.g. chromates

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)
  • Removal Of Specific Substances (AREA)
  • Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)

Abstract

The invention relates to a method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride. The zero-valent iron fluoride is characterized in that: part of the hydroxyl groups on the surface of the zero-valent iron are replaced by fluorine or fluorine-containing groups and sulfonic acid surfactant groups. The using method comprises the following steps: and adding the zero-valent iron fluoride into a heavy metal pollutant water body to remove heavy metals. The zero-valent iron fluoride provided by the invention has the advantages of good transmission capability, high electron selectivity, high utilization rate, higher pollutant removal efficiency, simple operation, economy and high efficiency when being used for removing heavy metal pollutants.

Description

Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride
Technical Field
The invention belongs to the field of environmental material preparation and pollutant remediation in water, and particularly relates to preparation of zero-valent iron fluoride and application of the zero-valent iron fluoride in pollutant removal.
Background
Compared with other chromium pollution remediation technologies, the zero-valent iron technology has the characteristics of low cost, environmental friendliness, simplicity in operation and the like, and is increasingly emphasized in the field of remediation of heavy metal chromium-polluted water bodies. After more than 20 years of basic research and application development, the zero-valent iron technology has excellent effect on treating heavy metal chromium ions in some practical water bodies, but the wide application of the zero-valent iron technology still has challenges. For example, micron-sized zero-valent iron has a problem of low activity, which is manifested by low electron transfer efficiency, poor electron selectivity, slow dissolution of ferrous ions, and the like. The reasons for this problem are: during the preparation, storage or use process of the zero-valent iron, a ferrite/hydroxide shell layer is generated on the surface of the zero-valent iron, and a typical core-shell structure is formed. Although the existence of the shell layer can prevent the continuous oxidation of the zero-valent iron, the contact of the zero-valent iron and the pollutants can be possibly hindered, the electron transfer and mass transfer processes of the system are influenced, and the pollutant removal efficiency of the zero-valent iron is further reduced; in addition, hydroxyl on the surface of the zero-valent iron is a hydrophilic group and is easy to combine with water molecules, so that the surface of the zero-valent iron is surrounded by the water molecules, and electrons generated by corrosion of the zero-valent iron are directly transferred to the water molecules instead of pollutants. In response to the above problems, researchers have developed various improvement strategies to improve the activity and electron selectivity of zero-valent iron. For example, researchers prepare nanoscale zero-valent iron to replace micron-sized zero-valent iron for removing pollutants, the shell layer of the nanoscale zero-valent iron is relatively thin, and the reduction capability and the reaction rate of the nanoscale zero-valent iron are found to be high, so that heavy metals can be efficiently removed; applying a weak magnetic field or pre-magnetizing the zero-valent iron in advance to generate a non-uniform induction magnetic field on the surface of the zero-valent iron, so that the thickening of a shell layer in the reaction process can be slowed down, the corrosion effect of the zero-valent iron is strengthened, more iron ions are generated, and the efficiency of removing heavy metal pollutants by the zero-valent iron is improved; the shell layer part on the surface of the zero-valent iron can be removed by the methods of acid washing, hydrogen pretreatment, ultrasonic treatment and the like, so that the zero-valent iron is directly exposed in the water body, and the pollutant removing efficiency of the zero-valent iron is further improved; the sulfuration modification method is adopted to prepare the sulfuration zero-valent iron, and the pollutant removal capability and the electron selectivity of the zero-valent iron can be obviously improved. However, the above zero-valent iron improvement techniques involve complicated operations, require additional equipment, or fail to improve the electron selectivity of zero-valent iron.
Disclosure of Invention
The invention aims to provide the fluorinated zero-valent iron with simple operation and low cost, and the preparation method and the application thereof.
In order to achieve the purpose, the technical scheme adopted by the invention is as follows:
provided is a fluorinated zero-valent iron, wherein a part of hydroxyl groups on the surface of the zero-valent iron are replaced by fluorine or fluorine-containing groups, and sulfonic acid surfactant groups.
Provides a preparation method of novel zero-valent iron fluoride, which mainly comprises the following steps: firstly, preparing a fluorine-containing substance solution, then mixing a sulfonic acid surfactant solution with a certain concentration, and adding zero-valent iron to perform a modification reaction to obtain the zero-valent iron fluoride material.
According to the scheme, the concentration of the fluorine source substance solution is 0.001-1M, the concentration of the stable transmission agent solution is 0.0001-0.001M, and the dosage of the zero-valent iron is 0.56-5.6 g/L.
According to the scheme, the modification reaction time is 0.5-2.5h, and the modification reaction temperature is 20-27 ℃. According to the scheme, after the modification reaction, the post-treatment is carried out: washing with deionized water and ethanol for several times, and vacuum drying.
According to the scheme, the fluoride comprises perfluorocarboxylic acid, hydrofluoric acid, sodium fluoride and the like.
According to the scheme, the sulfonic acid surfactant comprises sodium tridecyl sulfonate, sodium dodecyl benzene sulfonate, sodium petroleum sulfonate and the like.
The method for efficiently removing the heavy metal pollutants based on the zero-valent iron fluoride is characterized in that the zero-valent iron fluoride is added into a heavy metal pollutant water body to remove the heavy metals.
According to the scheme, when the heavy metal is removed, the pollutants are stirred or not stirred.
According to the scheme, the adding amount of the zero-valent iron fluoride is 0.5-3 g/L.
The invention has the beneficial effects that:
the fluorine-containing group of the fluorinated zero-valent iron obtained by the invention partially replaces hydroxyl on the surface of the zero-valent iron, so that the electronic selectivity of the material for removing pollutants is weakened, and the electronic selectivity is greatly improved, meanwhile, the hydrophobic property of the material can be enhanced by matching with the addition of part of sulfonic acid surfactant groups as a stable transmission agent, the charge distribution on the surface of the zero-valent iron is changed, and the stability and the transmission capability of the modified fluorinated zero-valent iron, namely the migration capability in a water body, are remarkably improved, as shown in figure 1. As can be seen from the attached figure 2, the corrosion potential of the modified material is more negative, which shows that the material is easier to corrode, can release electrons more quickly, is high in selectivity of removing electrons for heavy metal pollutants, high in utilization rate, can remove heavy metal ions more economically and efficiently, does not need to control the dissolved oxygen of a system, and has the heavy metal removal rate of more than 99%.
The whole modification process of the obtained zero-valent iron fluoride is simple to operate and has low requirements on instruments and equipment.
Drawings
FIG. 1 is a graph showing the contact angle results of original zero-valent iron (A) and zero-valent iron (B) after modification in example 3;
FIG. 2 is a Tafel plot of zero-valent iron before and after modification in example 3, wherein: a, original zero-valent iron, and b, the modified zero-valent iron in the embodiment;
FIG. 3 is a graph showing the chromium removal effect of virgin zero-valent iron and modified zero-valent iron of example 1, example 2 and example 3.
Detailed Description
Example 1, first 50mL of 0.01M sodium fluoride solution was prepared and added to a 100mL beaker, 0.005M sodium petroleum sulfonate solution was added and 0.56g of zero-valent iron was added. Reacting for 60min at 25 ℃, washing for 3 times by using deionized water and ethanol respectively, filtering a sample, and drying for 18h at 25 ℃ in a vacuum drying oven; under the aerobic condition, the rotating speed is 200 r/min, the initial concentration of hexavalent chromium is 2mg/L, the adding amount of the zero-valent iron fluoride is 2g/L, after 90min of reaction, the removal rate of chromium reaches 99%, the electron selectivity of the original zero-valent iron is about 2.3%, the electron selectivity after modification reaches 23%, and the removal rate of chromium after 5 times of circulation still reaches 95%.
Example 2, first, 50mL of 1M hydrofluoric acid solution was prepared and added to a 100mL beaker, 0.001M sodium dodecylbenzenesulfonate solution was added, and 3g of zero-valent iron was added. Reacting for 90min at 25 ℃, then washing for 3 times by using deionized water and ethanol respectively, and filtering and drying a sample for 12h at 25 ℃ in a vacuum drying oven; under the aerobic condition, the rotating speed is 200 r/min, the initial concentration of hexavalent chromium is 10mg/L, the adding amount of the zero-valent iron fluoride is 2g/L, the removal rate of chromium reaches 99 percent after reaction for 30min, the electron selectivity of the original zero-valent iron is about 2.3 percent, the electron selectivity after modification reaches 25 percent, and the removal rate of chromium after 5 times of circulation still reaches 93 percent.
Example 3A 0.05M trifluoroacetic acid solution (50 mL) was prepared in a 100mL beaker, and a 0.0001M sodium tridecylsulfonate solution was added thereto, followed by addition of 5.6g of zero-valent iron. Reacting at 25 ℃ for 120min, washing with deionized water and ethanol for 3 times respectively, filtering the sample, and drying in a vacuum drying oven at 25 ℃ for 16 h; under the aerobic condition, the rotating speed is 200 r/min, the initial concentration of hexavalent chromium is 5mg/L, the adding amount of the zero-valent iron fluoride is 2g/L, the removal rate of chromium reaches 99 percent after the reaction is carried out for 30min, the electron selectivity of the original zero-valent iron is about 2.3 percent, the electron selectivity after the modification is as high as 32 percent, and the removal rate of chromium after 5 times of circulation is still as high as 96 percent.
The zero-valent iron of examples 1-3 above was micron-sized zero-valent iron.
The contact angle results of the original zero-valent iron and the modified zero-valent iron (B) are shown in a graph of FIG. 1; the Tafel plot of zero-valent iron before and after modification is shown in FIG. 2; the chromium removal effect of the original zero-valent iron and the modified zero-valent iron of example 1, example 2 and example 3 is shown in fig. 3.
The results show that: the fluorine-containing group of the fluorinated zero-valent iron obtained by the invention partially replaces hydroxyl on the surface of the zero-valent iron, so that the hydrophilic performance of the material is weakened, and meanwhile, the addition of the matched sulfonic acid surfactant not only obviously improves the stability and the transmission capability of the zero-valent iron, but also enhances the hydrophobic performance of the material, as shown in figure 1; as can be seen from the attached figure 2, the corrosion potential of the modified material is more negative, which indicates that the material is easier to corrode and can release electrons more quickly; the electronic selectivity of the modified zero-valent iron fluoride material for removing pollutants (the proportion of the number of electrons used for removing pollutants in the total number of electrons released in the zero-valent iron corrosion process is determined by the valence state change and mass conservation of iron and pollutants) is greatly improved (the electronic selectivity of original zero-valent iron is about 2.3%, the electronic selectivity of the modified zero-valent iron fluoride in embodiment 3 of the invention is about 32%, and the capacity of removing heavy metals is greatly improved, as shown in fig. 3.

Claims (9)

1. A zero-valent iron fluoride, characterized by: part of hydroxyl groups on the surface of the micron-sized zero-valent iron are replaced by fluorine or fluorine-containing groups and sulfonic acid surfactant groups.
2. The method for producing zero-valent iron fluoride according to claim 1, wherein: the method mainly comprises the following steps: firstly, preparing a fluorine source substance solution, then mixing a sulfonic acid surfactant solution with a certain concentration, and adding micron-sized zero-valent iron for modification reaction to obtain a zero-valent iron fluoride material, wherein the concentration of the fluorine source substance solution is 0.001-1M, the concentration of the sulfonic acid surfactant solution is 0.0001-0.001M, and the using amount of the zero-valent iron is 0.56-5.6 g/L.
3. The method of claim 2, wherein: the modification reaction time is 0.5-2.5h, and the modification reaction temperature is 20-27 ℃.
4. The method of claim 2, wherein: carrying out post-treatment after the modification reaction: washing with deionized water and ethanol for several times, and vacuum drying.
5. The method of claim 2, wherein: the fluorine source substance is selected from one or more of perfluorocarboxylic acid, hydrofluoric acid and sodium fluoride.
6. The method of claim 2, wherein: the sulfonic acid surfactant is one or more of tridecyl sodium sulfonate, sodium dodecyl benzene sulfonate and petroleum sodium sulfonate.
7. The method for efficiently removing heavy metal pollutants based on the zero-valent iron fluoride according to claim 1, which is characterized in that: the method comprises the step of adding the zero-valent iron fluoride according to claim 1 into a heavy metal pollutant water body to remove heavy metals.
8. The method of claim 7, wherein: when the heavy metal is removed, the pollutants are stirred or not stirred.
9. The method of claim 7, wherein: the addition amount of the zero-valent iron fluoride is 0.5-3 g/L.
CN201811020504.4A 2018-09-03 2018-09-03 Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride Active CN109110901B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811020504.4A CN109110901B (en) 2018-09-03 2018-09-03 Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811020504.4A CN109110901B (en) 2018-09-03 2018-09-03 Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride

Publications (2)

Publication Number Publication Date
CN109110901A CN109110901A (en) 2019-01-01
CN109110901B true CN109110901B (en) 2021-07-20

Family

ID=64860563

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811020504.4A Active CN109110901B (en) 2018-09-03 2018-09-03 Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride

Country Status (1)

Country Link
CN (1) CN109110901B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110422957B (en) * 2019-08-09 2022-03-01 华中师范大学 Method and device for treating hydrofluoric acid wastewater by coupling zero-valent iron technology with lime precipitation technology
CN110713242B (en) * 2019-08-09 2020-12-01 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
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

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104310726A (en) * 2014-09-30 2015-01-28 湖南大学 Method for removing heavy metal chromium in bottom mud by using modified nano zero-valent iron
CN108002518A (en) * 2017-12-16 2018-05-08 傲自然成都生物科技有限公司 A kind of bioelectrochemical system and purification method for purifying drinking water nitrate

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US10266424B2 (en) * 2016-07-07 2019-04-23 Terra-Hydrochem, Inc. Method for recycling oilfield and other wastewater

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104310726A (en) * 2014-09-30 2015-01-28 湖南大学 Method for removing heavy metal chromium in bottom mud by using modified nano zero-valent iron
CN108002518A (en) * 2017-12-16 2018-05-08 傲自然成都生物科技有限公司 A kind of bioelectrochemical system and purification method for purifying drinking water nitrate

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
Engineered iron/iron oxide functionalized membranes for selenium and other toxic metal removal from power plant scrubber water;Minghui Gui etal.;《Journal of Membrane Science》;20150420;第488卷;第79-91页第2.2、2.6节,第80页左栏第2、4段 *

Also Published As

Publication number Publication date
CN109110901A (en) 2019-01-01

Similar Documents

Publication Publication Date Title
CN109110901B (en) Method for efficiently removing heavy metal pollutants based on zero-valent iron fluoride
CN108940335B (en) Advanced redox water treatment method based on nitrogen-doped nuclear shell structure magnetic field recoverable iron-carbon material
CN104262536B (en) A kind of activity/controllable oxidization Graphene surface ion imprinted polymer and preparation method thereof and application
CN103862037B (en) The preparation of biomaterial embedding Zero-valent Iron-tri-iron tetroxide double nano system and pre-treatment way
CN107930629A (en) The preparation method of support type charcoal catalysis material
CN102258980B (en) Method for preparing sulfured magnetic chitosan and method for treating waste water containing heavy metals by using sulfured magnetic chitosan
CN111167513B (en) Flexible electro-catalytic membrane for removing nitrate in water and preparation method and application thereof
CN103332766A (en) Water and waste water purification method for improving reactivity of zero-valent iron through magnetic field pretreatment
CN113943030B (en) Biomass carbon-coated nano zero-valent iron composite material for treating chlorobenzene-polluted water body by activating peroxymonosulfate and preparation and application thereof
CN109850865A (en) A kind of preparation method and applications of the sodium alginate carbon aerogels of iron load
CN105776371A (en) Preparation method of loaded type nano iron underground water remediation agent
CN112958108B (en) Preparation method and application of magnetic oxygen-deficient nano cage-shaped iron-manganese composite catalyst
Peng et al. Recovery and separation of vanadium and chromium by two-step alkaline leaching enhanced with an electric field and H2O2
CN111036297A (en) Carbon fiber modified based on iron alginate, preparation method and application
CN106334518A (en) Recyclable magnetic phosphorus adsorbent and preparation method thereof
CN105668757A (en) Graphene/sodium alginate globules modified by nano zero-valent iron and preparing method and application thereof
CN105502558A (en) Preparation method for activated sludge and nano iron-copper composite material
CN110201699B (en) CuO-CN peroxide composite catalyst for advanced oxidation technology and preparation method and application thereof
CN108383208B (en) Method for treating organic wastewater by virtue of micro-battery-Fenton-like system
CN112892609A (en) Light-controlled slow-release double-network hydrogel catalyst for efficiently reducing Cr (VI)
CN104549365A (en) Ternary alloy-reduced graphene composite material catalyst and preparation method thereof
CN113788515B (en) Heterogeneous electro-Fenton cathode material for industrial wastewater treatment, preparation method and application
CN106001093B (en) Remediation method for heavy metal pollution of alkaline soil
CN108500030A (en) A kind of Na2The method that EDTA couples heavy metal in Zero-valent Iron removal medical refuse burning flyash
CN110713242B (en) Zero-valent iron material Fe @ iron fluoride and preparation method thereof

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
EE01 Entry into force of recordation of patent licensing contract

Application publication date: 20190101

Assignee: Wuhan Nanwang Environmental Protection Technology Research Co.,Ltd.

Assignor: CENTRAL CHINA NORMAL University

Contract record no.: X2023980053268

Denomination of invention: A method for efficient removal of heavy metal pollutants based on zero valent iron fluoride

Granted publication date: 20210720

License type: Common License

Record date: 20231220

EE01 Entry into force of recordation of patent licensing contract