CN102302926A - Composite modified layered double-metal hydroxide and method for preparing same - Google Patents
Composite modified layered double-metal hydroxide and method for preparing same Download PDFInfo
- Publication number
- CN102302926A CN102302926A CN 201110166964 CN201110166964A CN102302926A CN 102302926 A CN102302926 A CN 102302926A CN 201110166964 CN201110166964 CN 201110166964 CN 201110166964 A CN201110166964 A CN 201110166964A CN 102302926 A CN102302926 A CN 102302926A
- Authority
- CN
- China
- Prior art keywords
- metal
- hydroxide
- metal hydroxide
- composite modified
- double
- 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
Images
Abstract
The invention belongs to the technical field of novel materials and water pollution treatment agents and particularly relates to a composite modified layered double-metal hydroxide and a method for preparing the same. The composite modified layered double-metal hydroxide and the method for preparing the same mainly solve the technical problem that heavy metal cations and organic pollutants in sewage cannot be cooperatively adsorbed by a layered double-metal hydroxide material. The composite modified layered double-metal hydroxide provided by the invention is made by commonly modifying a layered double-metal hydroxide through an anionic surfactant and a metal complexing agent. According to the invention, the insertion amount of both the surfactant and the metal complexing agent is large, and the surfactant and the metal complexing agent are evenly inserted between layers of the layered double-metal hydroxide through a structural reconstruction method and an ion-exchange method step by step so as to realize composite modification.
Description
Technical field
The invention belongs to new material and water and pollute the inorganic agent technical field, be specifically related to a kind of composite modified stratiform double-metal hydroxide and preparation method thereof.
Background technology
China has a large population, water resource lacks, and water resources ownership per capita is 1/4 of a world average level only, is one of 13 poor-water states in the world.A large amount of town domestic sewages and various industrial wastewater are unprocessed and directly discharge or do not have a qualified discharge; Make underground water receive pollution to a certain degree; Deteriorating water quality; And the trend that increases the weight of is year by year arranged; The water that is on the rise pollutes, and has not only reduced the function of use of water body, the contradiction of further having aggravated shortage of water resources; The strategy of sustainable development to China is implementing has been brought serious negative effect, but also seriously threatens city dweller's safe drinking water and the people's health.In real work, focus on after various industrial wastewaters are normal mixed, cause containing simultaneously in the waste water a large amount of heavy metals and various organic pollution.
What processing waste water was commonly used at present is absorption method; Its great advantage is that equipment is simple, easy to operate; The saturated renewable use in back of adsorbents adsorb; Adsorbate also can be recycled; But present adsorbents adsorb function singleness promptly can only be adsorbed a kind of in heavy metal or the organic pollution, and two kinds of pollutants are simultaneously and deposit often in the water; For this reason, be badly in need of exploitation can be simultaneously the effectively new material and the new technology of heavy metal and organic pollution in the adsorption treatment waste water.
The hydroxide with hydrotalcite layered structure that the laminated type bimetal hydroxide compound is made up of bivalent metal ion and trivalent metal ion is claimed mixed metal hydroxides again; The laminated type bimetal hydroxide compound has the shepardite lamellar structure; Laminate is owing to trivalent metal ion isomorphous substitution bivalent metal ion has positive charge; Anionic electric charge of the object that interlayer can exchange and laminate positive charge balance; Make the laminated type bimetal hydroxide compound be electroneutral; The laminated type bimetal hydroxide compound has bigger anion-exchange capacity (AEC; 2-3meq/g); Acceptant object anion; Therefore the metal that can be used to exist with the anion form in the adsorbed water body is (like Cr (VI); As (V), Se (IV) etc.) and organic pollution.
Summary of the invention
The present invention is primarily aimed at that heavy metal cation and organic pollution can not be by the technical problems of the collaborative absorption of stratiform bimetal hydroxide laminate material in the sewage; A kind of composite modified stratiform bimetal hydroxide compound and preparation method thereof is provided, has can be used for environmental wastewater and handle.
The present invention for realizing the technical scheme that above-mentioned purpose is taked is:
The composite modified stratiform double-metal hydroxide of the present invention be by anion surfactant and metal chelating agent to layered double hydroxide common modification process;
The general structure of wherein said layered double hydroxide is: [M (II)
(1-x)M (III)
x(OH)
2] (A)
X/nMH
2O, wherein: M (II) is a bivalent metal ion, and M (III) is a trivalent metal ion, and A is-n valency anion, n=1~2, x is the molal quantity of M in every mole of layered double hydroxide (III), x=0.2~0.4; M is the molal quantity of the interlayer crystallization water in every mole of layered double hydroxide, m=0.5~6;
The general formula of said composite modified stratiform double-metal hydroxide is: [M (II)
(1-x)M (III)
x(OH)
2] (A)
a(SAA)
b(Complexation)
cMH
2O, wherein: M (II) is a bivalent metal ion; M (III) is a trivalent metal ion; A is-n valency anion; N=1~2; X is the molal quantity of M (III) in every mole of modified layered double-metal hydroxide, x=0.35~0.51; M=0.5~6; SAA is the anion of anion surfactant, and Complexation is the metal chelating agent anion, a=0.05~0.40; B=0.03~0.17; C=0.02~0.14.
The preparation method of the composite modified stratiform double-metal hydroxide of the present invention may further comprise the steps:
1) earlier with the layered double hydroxide calcining, calcined product is scattered in the anionic surfactant solution, the pH value of regulation system is 9~11 again, under nitrogen protection, the stirrings 10~72 hours down of 20~70 ℃ of constant temperature, processes dispersion;
2) metal chelating agent is added in the dispersion, regulating pH value is 5.5~6.5, and under nitrogen protection, constant temperature stirred 3~12 hours down for 50~80 ℃, suction filtration, washing, dry sediment get composite modified stratiform double-metal hydroxide.
Preferred bivalent metal ion M (II) is Mg in the composite modified stratiform double-metal hydroxide of the present invention
2+, Zn
2+, Fe
2+, Ni
2+Or Ca
2+Trivalent metal ion M (III) is Al
3+, Cr
3+, Fe
3+Or Co
3+-n valency anion A is Cl
-, OH
-, NO
3 -, CO
3 2-Or SO
4 2-Anion surfactant is lauryl sodium sulfate C
12H
25SO
4Na; Metal chelating agent is disodium ethylene diamine tetraacetate C
10H
14N
2Na
2O
82H
2O.
Preferred, in the layered double-metal hydroxide, M (II) is Mg
2+M (III) is Al
3+A is Cl
-
Further, bivalent metal ion of the present invention is 2~4: 1 with the amount of substance ratio of trivalent metal ion.
Layered double hydroxide calcining heat according to the invention is 400~500 ℃.
The calcined product of layered double-metal hydroxide is 1: 0.25~1 with the ratio of the amount of substance of anion surfactant.
The calcined product of layered double-metal hydroxide is 1: 0.25~1 with the ratio of the amount of substance of metal chelating agent.
The temperature of said dry sediment is 40~80 ℃.
The present invention utilizes D/max-γ Type B X-ray powder diffraction appearance; Under the condition of 0.2 ° of voltage 40kV, electric current 100mA, Cu target K α radiation, 4 °/min of sweep speed, scanning step; In 2 ° of-70 ° of scopes, record the X-ray powder diffraction of layered double hydroxide of the present invention and modified layered double-metal hydroxide, through same diffraction maximum (d before and after the modification in the collection of illustrative plates
003) displacement, prove that anion surfactant anion and metal chelating agent anion among the present invention have inserted the interlayer of layered double hydroxide.
Simultaneously, the present invention also utilizes Nicolet USA 5DX fourier-transform infrared absorption spectrometer at resolution ratio 1cm
-1Condition under, detect at 400-4000cm
-1The layered double hydroxide in the scope and the infrared spectrum of modified layered double-metal hydroxide: the existence form that compares the provable modified layered double-metal hydroxide interlayer anion of difference of the two collection of illustrative plates.3600-3500cm
-1Scope is the hydrogen bond stretching vibration absworption peak of hydroxyl on the laminate; 3000cm
-1The place is the hydrogen bond absworption peak between intermediary water and other anion; 1800-1000cm
-1Scope is the stretching vibration peak of interlayer anion; 1000-400cm
-1Scope is the vibration absorption peak that metal cation and oxygen form covalent bond.
The content of metallic element Mg and Al in layered double hydroxide of the present invention and the modified layered double-metal hydroxide (wt%) measure through IRIS ADVANTAGE type inductive coupling plasma emission spectrograph by mass percent; C, H, N, S content (wt%) are measured through Vario ELIII type elemental analyser.Amount (n) by the wt% countable entity matter of each element.Layered double hydroxide [Mg
(1-x)Al
x(OH)
2] (Cl)
xMH
2O or modified layered double-metal hydroxide [Mg
(1-x)Al
x(OH)
2] (Cl)
a(C
12H
25SO
4)
b(C
10H
14N
2O
8)
cMH
2The x value can be by n (Mg): n (Al)=2 (1-x) among the O: x draws; [Mg
(1-x)Al
x(OH)
2] (Cl)
xMH
2M=[n among the O (H) (1-x)-2n (Mg)]/(2n (Mg)); [Mg
(1-x)Al
x(OH)
2] (Cl)
a(C
12H
25SO
4)
b(C
10H
14N
2O
8)
cMH
2C=n among the O (N) (1-x)/(2n (Mg)), b=n (S) (1-x)/n (Mg), a=x-b-2c, m=[n (H) is n (Mg) (1-x)-(25b+14c+2)]/(2n (Mg)).
The present invention is the main body with synthetic layered double hydroxide easy, that have layer structure, band structure positive charge; With anion surfactant and metal chelating agent is object; Prepared composite modified stratiform double-metal hydroxide; Can utilize the nonpolar action of surfactant to dissolve organic pollution in the sewage; Utilize the special stability of metal chelating agent effectively to remove heavy metal ion in the water, thereby realize of collaborative, the effectively absorption of composite modified stratiform double-metal hydroxide heavy metal in the water body and organic pollution.The modified layered double-metal hydroxide method of preparation NEW TYPE OF COMPOSITE is simple among the present invention, and cost is lower, has played positive role for layered double hydroxide in the application aspect the water treatment.Therefore; Compared with prior art the present invention has following beneficial effect: 1, existing modification to layered double hydroxide is single modification (at layered double hydroxide interlayer or insertion surfactant or insertion metal chelating agent); And the present invention proposes surfactant and metal chelating agent are all inserted the layered double hydroxide interlayer, realize composite modified through structural remodeling method and ion-exchange substep; 2, the insertion amount of surfactant of the present invention and metal chelating agent is all bigger, and surfactant and metal chelating agent anion molal quantity can reach 0.17 and 0.14 respectively in every mole of composite modified stratiform double-metal hydroxide; 3, preparation method of the present invention is simple, and cost is low.
Description of drawings
Fig. 1 is the powder x-ray diffraction figure of modification front and back laminated type bimetal hydroxide compound among the embodiment of the invention 1-3, and wherein a is the powder x-ray diffraction figure of embodiment 1 laminate bimetal hydroxide compound; B is the powder x-ray diffraction figure of embodiment 2 laminate bimetal hydroxide compounds; C is the powder x-ray diffraction figure of embodiment 3 laminate bimetal hydroxide compounds; D is the powder x-ray diffraction figure of modified layered bimetal hydroxide compound among the embodiment 1; E is the powder x-ray diffraction figure of modified layered bimetal hydroxide compound among the embodiment 2; F is the powder x-ray diffraction spectrogram of modified layered bimetal hydroxide compound among the embodiment 3;
Fig. 2 is the infrared spectrum of modification front and back laminated type bimetal hydroxide compound among the embodiment of the invention 1-3, and wherein a is the infrared spectrum of embodiment 1 laminate bimetal hydroxide compound; B is the infrared spectrum of embodiment 2 laminate bimetal hydroxide compounds; C is the infrared spectrum of embodiment 3 laminate bimetal hydroxide compounds; D is the infrared spectrum of modified layered bimetal hydroxide compound among the embodiment 1; E is the infrared spectrum of modified layered bimetal hydroxide compound among the embodiment 2; F is the infrared spectrum of modified layered bimetal hydroxide compound among the embodiment 3.
The specific embodiment
Embodiment 1
1) with layered double hydroxide [Mg
0.78Al
0.22(OH)
2] (Cl)
0.220.5H
2O gets calcined product 300mg and is scattered in the lauryl sodium sulfate (C that 30mL concentration is 0.1mol/L 500 ℃ of calcinings
12H
25SO
4Na, SDS) in the aqueous solution, using the NaOH solution regulation system pH value of 0.01mol/L is 9, under nitrogen protection, the stirring 42 hours down of 70 ℃ of constant temperature, processes dispersion;
2) get the disodium ethylene diamine tetraacetate (C that concentration is 0.06mol/L
10H
14N
2Na
2O
82H
2O, Na
2-EDTA) solution 33mL adds in the dispersion, and using the HCl of 0.01mol/L to regulate pH value is 6.5, under nitrogen protection, the stirring 8 hours down of 80 ℃ of constant temperature, suction filtration, washing, sediment dries to constant weight at 80 ℃, promptly gets composite modified stratiform double-metal hydroxide [Mg
0.64Al
0.36(OH)
2] (Cl)
0.1(C
12H
25SO
4)
0.12(C
10H
14N
2O
8)
0.070.7H
2O.
A is the powder x-ray diffraction figure of present embodiment laminated type bimetal hydroxide compound among Fig. 1, and d is the powder x-ray diffraction figure of modified layered bimetal hydroxide compound in the present embodiment; Relatively a and d curve can be known, the 0.772nm of the interlamellar spacing of layered double hydroxide before by modification becomes 2.752nm after the modification (with C
12H
25SO
4 -Molecular length 2.23nm+ laminate thickness 0.48nm=2.71nm basically identical) and 1.343nm (with C
10H
14N
2O
8 2-Molecular length 0.91nm+ laminate thickness 0.48nm=1.39nm basically identical), illustrate in the modified layered bimetal hydroxide compound and inserted C
12H
25SO
4 -And C
10H
14N
2O
8 2-
A is the infrared spectrum of present embodiment laminate bimetal hydroxide compound among Fig. 2, and d is the infrared spectrum of modified layered bimetal hydroxide compound in the present embodiment; Relatively a and d curve can be known, have increased by 2850~2965cm after the layered double hydroxide modification
-1Absworption peak (CH
2The contraction vibration peak) ,~1229cm
-1Absworption peak (SO
4Vibration peak) and 1400~1600cm
-1Absworption peak (COO
-The contraction vibration peak), illustrating in the modified layered bimetal hydroxide compound has increased C
12H
25SO
4 -And C
10H
14N
2O
8 2-Ion.
Embodiment 2
1) with layered double hydroxide [Mg
0.65Al
0.35(OH)
2] (Cl)
0.352.7H
2O gets calcined product 280mg and is scattered in the lauryl sodium sulfate (C that 30mL concentration is 0.15mol/L 450 ℃ of calcinings
12H
25SO
4Na, SDS) in the aqueous solution, using the NaOH solution regulation system pH value of 0.01mol/L is 9.5, under nitrogen protection, the stirring 52 hours down of 50 ℃ of constant temperature, processes dispersion;
2) get the disodium ethylene diamine tetraacetate (C that concentration is 0.2mol/L
10H
14N
2Na
2O
82H
2O, Na
2-EDTA) solution 30mL adds in the dispersion, and using the HCl of 0.01mol/L to regulate pH value is 6, under nitrogen protection, the stirring 4 hours down of 50 ℃ of constant temperature, suction filtration, washing, sediment dries to constant weight at 60 ℃, promptly gets composite modified stratiform double-metal hydroxide [Mg
0.49Al
0.51(OH)
2] (Cl)
0.1(C
12H
25SO
4)
0.17(C
10H
14N
2O
8)
0.122.3H
2O.
B is the powder x-ray diffraction figure of present embodiment laminated type bimetal hydroxide compound among Fig. 1, and e is the powder x-ray diffraction figure of modified layered bimetal hydroxide compound in the present embodiment; Relatively b and e curve can be known, the 0.772nm of the interlamellar spacing of layered double hydroxide before by modification becomes 2.984nm after the modification (with C
12H
25SO
4 -Molecular length 2.23nm+ laminate thickness 0.48nm=2.71nm basically identical) and 1.390nm (with C
10H
14N
2O
8 2-Molecular length 0.91nm+ laminate thickness 0.48nm=1.39nm is consistent), illustrate in the modified layered bimetal hydroxide compound and inserted C
12H
25SO
4 -And C
10H
14N
2O
8 2-
B is the infrared spectrum of present embodiment laminate bimetal hydroxide compound among Fig. 2, and e is the infrared spectrum of modified layered bimetal hydroxide compound in the present embodiment; Relatively b and e curve can be known, have increased by 2850~2965cm after the layered double hydroxide modification
-1Absworption peak (CH
2The contraction vibration peak) ,~1229cm
-1Absworption peak (SO
4Vibration peak) and 1400~1600cm
-1Absworption peak (COO
-The contraction vibration peak), illustrating in the modified layered bimetal hydroxide compound has increased C
12H
25SO
4 -And C
10H
14N
2O
8 2-Ion.
Embodiment 3
1) with layered double hydroxide [Mg
0.68Al
0.32(OH)
2] (Cl)
0.323H
2O gets calcined product 250mg and is scattered in the lauryl sodium sulfate (C that 30mL concentration is 0.1mol/L 500 ℃ of calcinings
12H
25SO
4Na, SDS) in the aqueous solution, using the NaOH solution regulation system pH value of 0.01mol/L is 10, under nitrogen protection, the stirring 48 hours down of 30 ℃ of constant temperature, processes dispersion;
2) get the disodium ethylene diamine tetraacetate (C that concentration is 0.2mol/L
10H
14N
2Na
2O
82H
2O, Na
2-EDTA) solution 25mL adds in the dispersion, and using the HCl of 0.01mol/L to regulate pH value is 5.5, under nitrogen protection, the stirring 6 hours down of 70 ℃ of constant temperature, suction filtration, washing, sediment dries to constant weight at 55 ℃, promptly gets composite modified stratiform double-metal hydroxide [Mg
0.52Al
0.48(OH)
2] (Cl)
0.07(C
12H
25SO
4)
0.13(C
10H
14N
2O
8)
0.143.5H
2O.
C is the powder x-ray diffraction figure of present embodiment laminated type bimetal hydroxide compound among Fig. 1, and f is the powder x-ray diffraction figure of modified layered bimetal hydroxide compound in the present embodiment; Relatively c and f curve can be known, the 0.767nm of the interlamellar spacing of layered double hydroxide before by modification becomes 2.752nm after the modification (with C
12H
25SO
4 -Molecular length 2.23nm+ laminate thickness 0.48nm=2.71nm basically identical) and 1.401nm (with C
10H
14N
2O
8 2-Molecular length 0.91nm+ laminate thickness 0.48nm=1.39nm basically identical), illustrate in the modified layered bimetal hydroxide compound and inserted C
12H
25SO
4 -And C
10H
14N
2O
8 2-
C is the infrared spectrum of present embodiment laminate bimetal hydroxide compound among Fig. 2, and f is the infrared spectrum of modified layered bimetal hydroxide compound in the present embodiment; Relatively c and f curve can be known, have increased by 2850~2965cm after the layered double hydroxide modification
-1Absworption peak (the contraction vibration peak of CH2) ,~1229cm
-1Absworption peak (SO
4Vibration peak) and 1400~1600cm
-1Absworption peak (the contraction vibration peak of COO-), illustrating in the modified layered bimetal hydroxide compound has increased C
12H
25SO
4 -And C
10H
14N
2O
8 2-Ion.
Claims (8)
1. composite modified stratiform double-metal hydroxide, it is characterized in that by anion surfactant and metal chelating agent to layered double hydroxide common modification process;
Wherein: the general formula of said composite modified stratiform double-metal hydroxide is: [M (II)
(1-x)M (III)
x(OH)
2] (A)
a(SAA)
b(Complexation)
cMH
2O, wherein: M (II) is a bivalent metal ion; M (III) is a trivalent metal ion; A is-n valency anion; N=1~2; X is the molal quantity of M (III) in every mole of modified layered double-metal hydroxide, x=0.35~0.51; M=0.5~6; SAA is the anion of anion surfactant, and Complexation is the metal chelating agent anion, a=0.05~0.40; B=0.03~0.17; C=0.02~0.14.
2. the preparation method of the described composite modified stratiform double-metal hydroxide of claim 1 is characterized in that may further comprise the steps:
1) earlier with the layered double hydroxide calcining, calcined product is scattered in the anionic surfactant solution, the pH value of regulation system is 9~11 again, under nitrogen protection, the stirrings 10~72 hours down of 20~70 ℃ of constant temperature, processes dispersion;
2) metal chelating agent is added in the dispersion, regulating pH value is 5.5~6.5, and under nitrogen protection, constant temperature stirred 3~12 hours down for 50~80 ℃, suction filtration, washing, dry sediment get composite modified stratiform double-metal hydroxide.
3. a kind of composite modified stratiform double-metal hydroxide according to claim 1 is characterized in that described bivalent metal ion M (II) is Mg
2+, Zn
2+, Fe
2+, Ni
2+Or Ca
2+Described trivalent metal ion M (III) is Al
3+, Cr
3+, Fe
3+, or Co
3+Described-n valency anion A is Cl
-, OH
-, NO
3 -, CO
3 2-Or SO
4 2-Said anion surfactant is lauryl sodium sulfate C
12H
25SO
4Na; Said metal chelating agent is disodium ethylene diamine tetraacetate C
10H
14N
2Na
2O
82H
2O.
4. a kind of composite modified stratiform double-metal hydroxide according to claim 1 is characterized in that the described bivalent metal ion and the amount of substance ratio of trivalent metal ion are 2~4: 1.
5. the preparation method of a kind of composite modified stratiform double-metal hydroxide according to claim 2 is characterized in that described layered double hydroxide calcining heat is 400~500 ℃.
6. the preparation method of a kind of composite modified stratiform double-metal hydroxide according to claim 2, the calcined product that it is characterized in that described layered double hydroxide is 1: 0.25~1 with the ratio of the amount of substance of anion surfactant.
7. the preparation method of a kind of composite modified stratiform double-metal hydroxide according to claim 2, the calcined product that it is characterized in that described layered double hydroxide is 1: 0.25~1 with the ratio of the amount of substance of metal chelating agent.
8. the preparation method of a kind of composite modified stratiform double-metal hydroxide according to claim 2, the temperature that it is characterized in that described dry sediment is 40~80 ℃.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201110166964 CN102302926A (en) | 2011-06-21 | 2011-06-21 | Composite modified layered double-metal hydroxide and method for preparing same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 201110166964 CN102302926A (en) | 2011-06-21 | 2011-06-21 | Composite modified layered double-metal hydroxide and method for preparing same |
Publications (1)
Publication Number | Publication Date |
---|---|
CN102302926A true CN102302926A (en) | 2012-01-04 |
Family
ID=45376895
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 201110166964 Pending CN102302926A (en) | 2011-06-21 | 2011-06-21 | Composite modified layered double-metal hydroxide and method for preparing same |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN102302926A (en) |
Cited By (14)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102583631A (en) * | 2012-03-02 | 2012-07-18 | 北京化工大学 | Method of adopting laminar duplex-metal hydroxide to recycle heavy metal ions in sewage |
CN102976278A (en) * | 2012-12-19 | 2013-03-20 | 青岛科技大学 | Laminar bimetal hydroxide and preparation method thereof |
CN103570114A (en) * | 2013-10-24 | 2014-02-12 | 上海大学 | Reduction treatment method for nitrates in water |
CN106669592A (en) * | 2016-12-07 | 2017-05-17 | 常州大学 | Preparation method of iron-nickel loaded nano calcium peroxide used for micro-polluted water treatment |
CN107570106A (en) * | 2017-10-17 | 2018-01-12 | 西南大学 | A kind of ferrimanganic class layered double-hydroxide, preparation method and application |
CN108609708A (en) * | 2018-04-28 | 2018-10-02 | 孙法峰 | A kind of preparation method of sewage disposal polymeric silicicacid modified hydrotalcite material |
CN108837803A (en) * | 2018-06-28 | 2018-11-20 | 东北农业大学 | A kind of layered double-hydroxide loads the preparation method of biological carbon composite |
CN109908965A (en) * | 2019-03-21 | 2019-06-21 | 长治学院 | CuBr2@Zr-MOF catalyst and the preparation method and application thereof |
CN110191926A (en) * | 2016-11-15 | 2019-08-30 | Scg化学有限公司 | The modified layered double-hydroxide in surface |
CN110433765A (en) * | 2019-08-18 | 2019-11-12 | 桂林理工大学 | The preparation method and applications of EDTA intercalation ferrimanganic layered double hydroxide |
CN110736778A (en) * | 2019-06-04 | 2020-01-31 | 黑龙江大学 | Preparation method of three-dimensional layered CoAl bimetal hydroxide nano material and application of three-dimensional layered CoAl bimetal hydroxide nano material in detection of heavy metal ions in water body |
CN112063386A (en) * | 2020-09-25 | 2020-12-11 | 中科院过程工程研究所南京绿色制造产业创新研究院 | Layered double-metal hydroxide composite material and preparation method and application thereof |
CN112188883A (en) * | 2019-05-03 | 2021-01-05 | 威博特依株式会社 | Novel metal layered hydroxide complex and method for preparing same |
CN112316924A (en) * | 2020-10-20 | 2021-02-05 | 中科院过程工程研究所南京绿色制造产业创新研究院 | Coal gangue-based porous composite material and preparation method and application thereof |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1974399A (en) * | 2006-11-28 | 2007-06-06 | 山东大学 | Rod hydrotalcite-like compound and its prepn process |
CN101993101A (en) * | 2010-10-15 | 2011-03-30 | 农业部环境保护科研监测所 | Preparation and application of layered double hydroxides with diethylenetriaminepentaacetic acid intercalation |
-
2011
- 2011-06-21 CN CN 201110166964 patent/CN102302926A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1974399A (en) * | 2006-11-28 | 2007-06-06 | 山东大学 | Rod hydrotalcite-like compound and its prepn process |
CN101993101A (en) * | 2010-10-15 | 2011-03-30 | 农业部环境保护科研监测所 | Preparation and application of layered double hydroxides with diethylenetriaminepentaacetic acid intercalation |
Non-Patent Citations (2)
Title |
---|
《中国博士学位论文全文数据库工程科技I辑》 20081215 刘春霞 层状双金属氢氧化物及其药物插层纳米杂化物的制备与性能研究 53-57 1-8 , 第12期 * |
《稀有金属材料与工程》 20100831 Zhang Feng et al Surface Properties of Mg/Al-Layered Double Hydroxides and Their Modified Products 194-197 2,5-8 第39卷, * |
Cited By (20)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102583631B (en) * | 2012-03-02 | 2013-10-30 | 北京化工大学 | Method of adopting laminar duplex-metal hydroxide to recycle heavy metal ions in sewage |
CN102583631A (en) * | 2012-03-02 | 2012-07-18 | 北京化工大学 | Method of adopting laminar duplex-metal hydroxide to recycle heavy metal ions in sewage |
CN102976278A (en) * | 2012-12-19 | 2013-03-20 | 青岛科技大学 | Laminar bimetal hydroxide and preparation method thereof |
CN102976278B (en) * | 2012-12-19 | 2014-03-19 | 青岛科技大学 | Laminar bimetal hydroxide and preparation method thereof |
CN103570114A (en) * | 2013-10-24 | 2014-02-12 | 上海大学 | Reduction treatment method for nitrates in water |
CN110191926A (en) * | 2016-11-15 | 2019-08-30 | Scg化学有限公司 | The modified layered double-hydroxide in surface |
US11242460B2 (en) | 2016-11-15 | 2022-02-08 | Scg Chemicals Co., Ltd. | Surface modified layered double hydroxide |
CN106669592A (en) * | 2016-12-07 | 2017-05-17 | 常州大学 | Preparation method of iron-nickel loaded nano calcium peroxide used for micro-polluted water treatment |
CN106669592B (en) * | 2016-12-07 | 2019-10-11 | 常州大学 | The preparation method of iron nickel load nanometer calper calcium peroxide for micro-polluted water treatment |
CN107570106A (en) * | 2017-10-17 | 2018-01-12 | 西南大学 | A kind of ferrimanganic class layered double-hydroxide, preparation method and application |
CN108609708A (en) * | 2018-04-28 | 2018-10-02 | 孙法峰 | A kind of preparation method of sewage disposal polymeric silicicacid modified hydrotalcite material |
CN108609708B (en) * | 2018-04-28 | 2022-01-25 | 孙法峰 | Preparation method of polymerized silicic acid modified hydrotalcite material for sewage treatment |
CN108837803A (en) * | 2018-06-28 | 2018-11-20 | 东北农业大学 | A kind of layered double-hydroxide loads the preparation method of biological carbon composite |
CN109908965A (en) * | 2019-03-21 | 2019-06-21 | 长治学院 | CuBr2@Zr-MOF catalyst and the preparation method and application thereof |
CN112188883A (en) * | 2019-05-03 | 2021-01-05 | 威博特依株式会社 | Novel metal layered hydroxide complex and method for preparing same |
CN110736778A (en) * | 2019-06-04 | 2020-01-31 | 黑龙江大学 | Preparation method of three-dimensional layered CoAl bimetal hydroxide nano material and application of three-dimensional layered CoAl bimetal hydroxide nano material in detection of heavy metal ions in water body |
CN110433765A (en) * | 2019-08-18 | 2019-11-12 | 桂林理工大学 | The preparation method and applications of EDTA intercalation ferrimanganic layered double hydroxide |
CN112063386A (en) * | 2020-09-25 | 2020-12-11 | 中科院过程工程研究所南京绿色制造产业创新研究院 | Layered double-metal hydroxide composite material and preparation method and application thereof |
CN112316924A (en) * | 2020-10-20 | 2021-02-05 | 中科院过程工程研究所南京绿色制造产业创新研究院 | Coal gangue-based porous composite material and preparation method and application thereof |
CN112316924B (en) * | 2020-10-20 | 2023-05-23 | 中科南京绿色制造产业创新研究院 | Gangue-based porous composite material and preparation method and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102302926A (en) | Composite modified layered double-metal hydroxide and method for preparing same | |
Wang et al. | The synergistic elimination of uranium (VI) species from aqueous solution using bi-functional nanocomposite of carbon sphere and layered double hydroxide | |
CN103723868A (en) | Water purifier | |
Ren et al. | Comparison of Cd2+ adsorption onto amphoteric, amphoteric-cationic and amphoteric-anionic modified magnetic bentonites | |
Zhao et al. | Selectively capacitive recovery of rare earth elements from aqueous solution onto Lewis base sites of pyrrolic-N doped activated carbon electrodes | |
CN108160026A (en) | One kind absorbs the method with restoring Cr (VI) based on iron magnesia-alumina hydrotalcite | |
CN109289762B (en) | Preparation method of manganese-activated amorphous iron-based adsorbent | |
CN102583631A (en) | Method of adopting laminar duplex-metal hydroxide to recycle heavy metal ions in sewage | |
CN102464810A (en) | Hydroxyapatite-chitosan (HA-CTS) composite material for treating waste water and preparation method thereof | |
CN102351225A (en) | Method for preparing chloride ion treating medicament | |
CN105126742A (en) | Method for treating fluorine-containing wastewater by using modified kaolin adsorbent | |
CN105289562B (en) | Heavy metal wastewater thereby recoverying and utilizing method | |
CN106669592B (en) | The preparation method of iron nickel load nanometer calper calcium peroxide for micro-polluted water treatment | |
CN103464123A (en) | Preparation method of CTMAB/CPAM/bentonite compound intercalation materials | |
Jiang et al. | An electrochemically induced dual-site adsorption composite film of Ni-MOF derivative/NiCo LDH for selective bromide-ion extraction | |
Ou et al. | Fabrication of nickel-iron layered double hydroxides using nickel plating wastewater via electrocoagulation, and its use for efficient dye removal | |
CN110394154B (en) | Preparation method and application of moso bamboo charcoal/FeMn-LDH composite material | |
Xiong et al. | Fabrication of phosphorus doping porous carbon derived from bagasse for highly-efficient removal of La3+ ions via capacitive deionization | |
Yao et al. | Construction of lignin-based nano-adsorbents for efficient and selective recovery of tellurium (IV) from wastewater | |
Li et al. | Reuse of secondary aluminum ash: Study on removal of fluoride from industrial wastewater by mesoporous alumina modified with citric acid | |
Zhu et al. | Construction of Bi12O17Cl2/ZnO-CN Z-scheme photocatalyst with ZIF-8 as precursor to remove antibiotics and Cr (VI) under visible light: Optimization, mechanism and degradation path | |
CN102942242B (en) | Preparation method of nanometer iron-copper-carbon micro electrolysis material for organic waste water treatment | |
CN102317213B (en) | Water purification material, water purification method, phosphate fertilizer precursor, and method for manufacturing a phosphate fertilizer precursor | |
Zheng et al. | A dual-cycle regeneration to recover high-value and high-purity FePO4 from real wastewater for Li-battery application | |
Zhang et al. | Incorporation of edge-N into La-doped hierarchical carbon framework enables high-efficiency phosphate electrosorption: Boosting accessible active centers and bridging charge transfer paths |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20120104 |