CN105921125A - Attapulgite clay/sodium alginate composite heavy metal absorbent and preparation method thereof - Google Patents

Attapulgite clay/sodium alginate composite heavy metal absorbent and preparation method thereof Download PDF

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Publication number
CN105921125A
CN105921125A CN201610432403.2A CN201610432403A CN105921125A CN 105921125 A CN105921125 A CN 105921125A CN 201610432403 A CN201610432403 A CN 201610432403A CN 105921125 A CN105921125 A CN 105921125A
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attapulgite
sodium alginate
glutaraldehyde
preparation
attapulgite clay
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万怀新
蔡沐芳
彭勇刚
郑先进
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JIANGSU MAI GE ADSORBENT Co Ltd
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JIANGSU MAI GE ADSORBENT Co Ltd
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/24Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Analytical Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Engineering & Computer Science (AREA)
  • Hydrology & Water Resources (AREA)
  • Dispersion Chemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Inorganic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention relates to the field of environmental governance, in particular to a heavy metal absorbent and a preparation method thereof. The preparation method comprises the following steps: modifying attapulgite clay powder by using an aminosilane coupling agent to obtain attapulgite clay modified by a silane coupling agent; then dispersing the attapulgite clay in a glutaraldehyde solution, and fully stirring to obtain attapulgite clay modified by glutaraldehyde; and dropwise adding an acid solution of sodium alginate in suspension liquid of the attapulgite clay modified by the glutaraldehyde, heating and fully reacting to obtain a sodium alginate grafted and crosslinked attapulgite clay heavy metal absorbing material. By a mode of covalent bonds, the sodium alginate is grafted and crosslinked to the surface of the attapulgite clay, and in a using process, the sodium alginate cannot drop easily.

Description

A kind of compound heavy metal absorbent of attapulgite clay/sodium alginate and preparation method thereof
Technical field
The present invention relates to field of environmental improvement, be specifically related to a kind of heavy metal absorbent and preparation method thereof.
Background technology
Along with global economy and the development of society, environmental pollution is day by day serious, and wherein industrial wastewater is as main environomental pollution source, It it is a great problem perplexing countries in the world for a long time.Heavy metal ion in industrial wastewater has strong carcinogenic, teratogenesis, cause Mutation effect, constitutes serious threat to health and ecological environment, the most strictly controls the pollution of heavy metal wastewater thereby to closing Important.
Traditional process for treating heavy-metal waste water mainly has chemical precipitation method, ion exchange, membrane separation process etc., and these methods are led to Being commonly present that investment is big, energy consumption high, operating cost is high, be easily generated secondary pollution problems, application is restricted.Absorption method is profit With the pollutant in adsorbent water, thus the method purifying waste water, there is simple to operate, feature fast and effectively, obtain It is widely applied.How to obtain adsorbent cheap, that high adsorption capacity, adsorptive selectivity are high, have become as research and development Focus.
Summary of the invention
The present invention provides the adsorbing material of a kind of heavy metal ion, and component includes attapulgite, ammonium alginate, and attapulgite and Ammonium alginate is connected by chemical bond,
Present invention also offers the preparation method of a kind of above-mentioned adsorbing material, concretely comprise the following steps:
(1) attapulgite powder body is scattered in organic solvent, dropping amino silicane coupling agent after being uniformly dispersed, 70~100 DEG C Reaction 6~10h;Reaction is filtered after terminating, vacuum drying, obtains silane coupler modified attapulgite,
Wherein, attapulgite powder body is 1:10~1:30 with the mass ratio of organic solvent,
Organic solvent is toluene or dimethylbenzene,
The amino silicane coupling agent of dropping is 1:1 with the mass ratio of attapulgite powder body,
Amino silicane coupling agent be gamma-aminopropyl-triethoxy-silane, γ-aminopropyltrimethoxysilane, N-β-(aminoethyl)- γ-aminopropyltriethoxy dimethoxysilane, N-(β-aminoethyl)-γ-aminopropyltrimethoxysilane, N-(β-aminoethyl)-γ-ammonia Propyl-triethoxysilicane, γ-aminopropyltriethoxy diethoxy silane or γ-aminopropyltriethoxy dimethoxysilane;
(2) attapulgite modified it is scattered in what step (1) obtained in glutaraldehyde solution, filters after being sufficiently stirred for, washs, Vacuum drying, obtains the attapulgite that glutaraldehyde is modified,
Wherein, the Solute mass fraction of glutaraldehyde solution is 5%,
Attapulgite modified and the glutaraldehyde solution mass ratio added is 1:10~1:25,
Whipping temp is 30~40 DEG C;
(3) sodium alginate joined in acid solution and stir, obtaining the acid solution of sodium alginate;Step (2) will be obtained To the modified attapulgite of glutaraldehyde be made into suspension;The acid solution of sodium alginate is added drop-wise to the attapulgite that glutaraldehyde is modified Suspension in, be stirred and heated to 30~45 DEG C after dropping, react 3~5h, centrifugation, fully wash, remove The sodium alginate of non-covalent cross-linking, obtains the attapulgite heavy-metal adsorption material of sodium alginate graft crosslinking,
Wherein, acid solution be Solute mass fraction be the acetum of 1%, sodium alginate content in its acid solution be 0.5~ 1.5g/100ml,
The attapulgite of glutaraldehyde modification concentration in its suspension is 1~2g/100ml,
During dropping, the weight ratio controlling the sodium alginate attapulgite modified with glutaraldehyde is 1:1~1:2.
The beneficial effects of the present invention is: present invention effect based on glutaraldehyde, by the way of covalent bond, sodium alginate is grafted Being linked to attapulgite's surface, both adhesions are strong, and in use sodium alginate is difficult to come off from carrier surface and freely roll into a ball Poly-, heavy metal is polluted and is embodied good absorption property.
Detailed description of the invention
Embodiment 1
(1) during 10g attapulgite is scattered in 100mL toluene, ultrasonic disperse 30min, under stirring condition, dropping 10g γ- Aminopropyl triethoxysilane, after dripping, is heated to 70 DEG C, reacts 10h, and reaction is filtered after terminating, vacuum drying, i.e. Obtain attapulgite modified by silane coupling agent;
(2) by molten for the glutaraldehyde that the attapulgite modified 150mL of being dispersed in Solute mass fraction is 5% that obtains in step (1) In liquid, after 30 DEG C of reaction 3h, filter, after deionized water repeatedly washs, vacuum drying, obtain the attapulgite that glutaraldehyde is modified;
(3) sodium alginate joined in the acetum that Solute mass fraction is 1% and stir 3 hours, obtaining sodium alginate Acid solution, wherein the content of sodium alginate is 0.5g/100ml,
The attapulgite that the glutaraldehyde obtained in step (2) is modified is made into the suspension that concentration is 1g/100ml,
It is 1:1 according to the weight ratio of sodium alginate with the attapulgite of glutaraldehyde modification, the acid solution of sodium alginate is added drop-wise to penta 2 In the suspension of the attapulgite that aldehyde is modified, after dropping, it is stirred and heated to 30 DEG C, reacts 5h, centrifugation, fully wash Wash, obtain the attapulgite heavy-metal adsorption material of sodium alginate graft crosslinking.
Embodiment 2
(1) during 10g attapulgite is scattered in 200mL toluene, ultrasonic disperse 20min, under stirring condition, dropping 10g γ- Aminopropyl trimethoxysilane, after dripping, is heated to 80 DEG C, reacts 8h, and reaction is filtered after terminating, and vacuum drying to obtain final product Attapulgite modified by silane coupling agent;
(2) by molten for the glutaraldehyde that the attapulgite modified 100mL of being dispersed in Solute mass fraction is 5% that obtains in step (1) In liquid, after 30 DEG C of reaction 4h, filter, after deionized water repeatedly washs, vacuum drying, obtain the attapulgite that glutaraldehyde is modified;
(3) sodium alginate joined in the acetum that Solute mass fraction is 1% and stir 3 hours, obtaining sodium alginate Acid solution, wherein the content of sodium alginate is 1g/100ml,
The attapulgite that the glutaraldehyde obtained in step (2) is modified is made into the suspension that concentration is 1.5g/100ml,
It is 1:1.5 according to the weight ratio of sodium alginate with the attapulgite of glutaraldehyde modification, the acid solution of sodium alginate is added drop-wise to penta In the suspension of the attapulgite of dialdehyde, after dropping, it is stirred and heated to 40 DEG C, reaction 4h, centrifugation, fully Washing, obtains the attapulgite heavy-metal adsorption material of sodium alginate graft crosslinking.
Embodiment 3
(1) during 10g attapulgite is scattered in 250mL toluene, ultrasonic disperse 20min, under stirring condition, drip 10g N- β-(aminoethyl)-γ-aminopropyltriethoxy dimethoxysilane, after dripping, is heated to 90 DEG C, reacts 7h, after reaction terminates Filter, vacuum drying, obtain attapulgite modified by silane coupling agent;
(2) by molten for the glutaraldehyde that the attapulgite modified 200mL of being dispersed in Solute mass fraction is 5% that obtains in step (1) In liquid, after 30 DEG C of reaction 3h, filter, after deionized water repeatedly washs, vacuum drying, obtain the attapulgite that glutaraldehyde is modified;
(3) sodium alginate joined in the acetum that Solute mass fraction is 1% and stir 3 hours, obtaining sodium alginate Acid solution, wherein the content of sodium alginate is 1g/100ml,
The attapulgite that the glutaraldehyde obtained in step (2) is modified is made into the suspension that concentration is 1g/100ml,
It is 1:1.5 according to the weight ratio of sodium alginate with the attapulgite of glutaraldehyde modification, the acid solution of sodium alginate is added drop-wise to penta In the suspension of the attapulgite of dialdehyde, after dropping, it is stirred and heated to 35 DEG C, reaction 4h, centrifugation, fully Washing, obtains the attapulgite heavy-metal adsorption material of sodium alginate graft crosslinking.
Comparative example 1
(1) during 10g attapulgite is scattered in 200mL toluene, ultrasonic disperse 20min, under stirring condition, dropping 10g γ- Aminopropyl trimethoxysilane, after dripping, is heated to 80 DEG C, reacts 8h, and reaction is filtered after terminating, and vacuum drying to obtain final product Attapulgite modified by silane coupling agent;
(2) sodium alginate joined in the acetum that Solute mass fraction is 1% and stir 3 hours, obtaining sodium alginate Acid solution, wherein the content of sodium alginate is 1g/100ml,
Attapulgite modified it is made into the suspension that concentration is 1.5g/100ml by what step (1) obtained,
It is 1:1.5 according to sodium alginate and attapulgite modified weight ratio, the acid solution of sodium alginate is added drop-wise to modified attapulgite In the suspension of soil, after dropping, it is stirred and heated to 40 DEG C, reacts 4h, centrifugation, fully wash, obtain alginic acid The attapulgite heavy-metal adsorption material that sodium is modified.
Taking each 0.5g of the compound adsorbent in the various embodiments described above, comparative example, the heavy metal copper ion concentration joining 1L is In the water of 0.1g/L, after adsorbing 1h under room temperature (25 DEG C), detect the concentration of residual copper ion in solution and calculate absorption Amount, concrete detection data are as shown in table 1:
Table 1
Embodiment Embodiment 2 Embodiment 3 Comparative example 1
Adsorbance (mg/g) 86.4 85.2 82.6 67.8

Claims (9)

1. attapulgite clay/sodium alginate Compound Heavy Metals adsorbent, it is characterised in that: described absorbent component includes attapulgite Soil, ammonium alginate, and attapulgite and ammonium alginate connected by chemical bond.
2. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 1, it is characterised in that: institute The step stating preparation method is,
(1) attapulgite powder body is scattered in organic solvent, dropping amino silicane coupling agent after being uniformly dispersed, 70~100 DEG C Reaction 6~10h;Reaction is filtered after terminating, vacuum drying, obtains silane coupler modified attapulgite;
(2) attapulgite modified it is scattered in what step (1) obtained in glutaraldehyde solution, filters after being sufficiently stirred for, washs, Vacuum drying, obtains the attapulgite that glutaraldehyde is modified;
(3) sodium alginate joined in acid solution and stir, obtaining the acid solution of sodium alginate;Step (2) will be obtained To the modified attapulgite of glutaraldehyde be made into suspension;The acid solution of sodium alginate is added drop-wise to the attapulgite that glutaraldehyde is modified Suspension in, be stirred and heated to 30~45 DEG C after dropping, react 3~5h, centrifugation, fully wash, obtain The attapulgite heavy-metal adsorption material of sodium alginate graft crosslinking.
3. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly the organic solvent described in (1) is toluene or dimethylbenzene, and attapulgite powder body is 1:10~1 with the mass ratio of organic solvent: 30。
4. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly the amino silicane coupling agent described in (1) is gamma-aminopropyl-triethoxy-silane, γ-aminopropyltrimethoxysilane, N-β -(aminoethyl)-γ-aminopropyltriethoxy dimethoxysilane, N-(β-aminoethyl)-γ-aminopropyltrimethoxysilane, N-(β-ammonia second Base)-gamma-aminopropyl-triethoxy-silane, γ-aminopropyltriethoxy diethoxy silane or γ-aminopropyltriethoxy dimethoxysilane, The amino silicane coupling agent of dropping is 1:1 with the mass ratio of attapulgite powder body.
5. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly the Solute mass fraction of the glutaraldehyde solution described in (2) is 5%.
6. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly, in (2), the mass ratio of the attapulgite modified and glutaraldehyde solution of addition is 1:10~1:25.
7. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly the acid solution described in (3) be Solute mass fraction be the acetum of 1%, sodium alginate is content in described acid solution It is 0.5~1.5g/100ml.
8. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly, in (3), the attapulgite of glutaraldehyde modification concentration in its suspension is 1~2g/100ml.
9. the preparation method of attapulgite clay/sodium alginate Compound Heavy Metals adsorbent as claimed in claim 2, it is characterised in that: step Suddenly, in (3), during dropping, the weight ratio controlling the sodium alginate attapulgite modified with glutaraldehyde is 1:1~1:2.
CN201610432403.2A 2016-06-16 2016-06-16 Attapulgite clay/sodium alginate composite heavy metal absorbent and preparation method thereof Pending CN105921125A (en)

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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106630131A (en) * 2016-10-25 2017-05-10 南京大学宜兴环保研究院 Preparation method of modified attapulgite particles and method for accelerating granulation of anaerobic sludge by modified attapulgite particles
CN106732445A (en) * 2016-11-30 2017-05-31 无锡龙盈环保科技有限公司 A kind of silica modified heavy metal wastewater thereby adsorbent and preparation method thereof
CN106987306A (en) * 2017-06-05 2017-07-28 蚌埠市江淮粮油有限公司 It is a kind of to reduce the rape oil-pressing method of water content
CN107022411A (en) * 2017-06-05 2017-08-08 蚌埠市江淮粮油有限公司 A kind of preparation method of giving off a strong fragrance rapeseed oil
CN107583600A (en) * 2017-10-18 2018-01-16 上海纳米技术及应用国家工程研究中心有限公司 Preparation method of improved silica hydrogel and products thereof and application
CN109012621A (en) * 2016-12-07 2018-12-18 天津市金鳞水处理科技有限公司 A kind of heavy metal ion adsorbed and detection type compound water congealing glue fiber
CN109289788A (en) * 2016-12-07 2019-02-01 天津市金鳞水处理科技有限公司 Heavy metal ion adsorbed and detection type composite hydrogel
CN110841609A (en) * 2019-12-11 2020-02-28 广西科技大学 Preparation method of high-molecular-weight heavy metal adsorbent
CN112007617A (en) * 2019-05-29 2020-12-01 西南科技大学 Preparation method of shaddock peel/attapulgite composite material

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060021927A1 (en) * 2002-03-29 2006-02-02 Council Of Scientific And Industrial Research Process for the preparation of arsenic free water, apparatus therefor, method for the manufacture of porous ceramics for use in pressure filtration to produce arsenic free water
CN101733076A (en) * 2009-12-31 2010-06-16 四川大学 Modified attapulgite adsorbent for tannery wastewater treatment and preparation method thereof
CN101942167A (en) * 2010-09-10 2011-01-12 天津工业大学 Nanometer clay-containing high absorptive hydrogel as well as preparation method and application thereof
CN102114412A (en) * 2011-01-19 2011-07-06 常州大学 Chitosan-grafted and modified attapulgite clay absorbing material and preparation method thereof
CN102952792A (en) * 2012-11-12 2013-03-06 淮阴工学院 Preparation method of beta-glucosidase immobilized by sodium alginate loaded with attapulgite

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060021927A1 (en) * 2002-03-29 2006-02-02 Council Of Scientific And Industrial Research Process for the preparation of arsenic free water, apparatus therefor, method for the manufacture of porous ceramics for use in pressure filtration to produce arsenic free water
CN101733076A (en) * 2009-12-31 2010-06-16 四川大学 Modified attapulgite adsorbent for tannery wastewater treatment and preparation method thereof
CN101942167A (en) * 2010-09-10 2011-01-12 天津工业大学 Nanometer clay-containing high absorptive hydrogel as well as preparation method and application thereof
CN102114412A (en) * 2011-01-19 2011-07-06 常州大学 Chitosan-grafted and modified attapulgite clay absorbing material and preparation method thereof
CN102952792A (en) * 2012-11-12 2013-03-06 淮阴工学院 Preparation method of beta-glucosidase immobilized by sodium alginate loaded with attapulgite

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
LINHUI ZHU ET AL.: ""Synthesis of Sodium Alginate Graft Poly (Acrylic Acid-Co-2-Acrylamido-2-Methyl-1-Propane Sulfonic Acid)/Attapulgite Hydrogel Composite and the Study of its Adsorption"", 《POLYMER-PLASTICS TECHNOLOGY AND ENGINEERING》 *
徐婷婷等: ""缓释铜的凹土/海藻酸钠复合微球的制备及性能测试"", 《化工进展》 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106630131A (en) * 2016-10-25 2017-05-10 南京大学宜兴环保研究院 Preparation method of modified attapulgite particles and method for accelerating granulation of anaerobic sludge by modified attapulgite particles
CN106732445A (en) * 2016-11-30 2017-05-31 无锡龙盈环保科技有限公司 A kind of silica modified heavy metal wastewater thereby adsorbent and preparation method thereof
CN109012621A (en) * 2016-12-07 2018-12-18 天津市金鳞水处理科技有限公司 A kind of heavy metal ion adsorbed and detection type compound water congealing glue fiber
CN109289788A (en) * 2016-12-07 2019-02-01 天津市金鳞水处理科技有限公司 Heavy metal ion adsorbed and detection type composite hydrogel
CN106987306A (en) * 2017-06-05 2017-07-28 蚌埠市江淮粮油有限公司 It is a kind of to reduce the rape oil-pressing method of water content
CN107022411A (en) * 2017-06-05 2017-08-08 蚌埠市江淮粮油有限公司 A kind of preparation method of giving off a strong fragrance rapeseed oil
CN107583600A (en) * 2017-10-18 2018-01-16 上海纳米技术及应用国家工程研究中心有限公司 Preparation method of improved silica hydrogel and products thereof and application
CN112007617A (en) * 2019-05-29 2020-12-01 西南科技大学 Preparation method of shaddock peel/attapulgite composite material
CN112007617B (en) * 2019-05-29 2022-03-04 西南科技大学 Preparation method of shaddock peel/attapulgite composite material
CN110841609A (en) * 2019-12-11 2020-02-28 广西科技大学 Preparation method of high-molecular-weight heavy metal adsorbent
CN110841609B (en) * 2019-12-11 2023-04-11 广西科技大学 Preparation method of high-molecular-weight heavy metal adsorbent

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Application publication date: 20160907