CN102029144A - Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof - Google Patents
Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof Download PDFInfo
- Publication number
- CN102029144A CN102029144A CN2009102056481A CN200910205648A CN102029144A CN 102029144 A CN102029144 A CN 102029144A CN 2009102056481 A CN2009102056481 A CN 2009102056481A CN 200910205648 A CN200910205648 A CN 200910205648A CN 102029144 A CN102029144 A CN 102029144A
- Authority
- CN
- China
- Prior art keywords
- bamboo charcoal
- adsorbent
- sodium alginate
- dye
- heavy metal
- 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
Landscapes
- Water Treatment By Sorption (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention relates to an adsorbent for adsorbing heavy metal ions and dye in waste water, which is particularly suitable for reluctant printing and dying waste water simultaneously containing heavy metal ions and dye. In the invention, by utilizing the special microcellular structure of bamboo charcoal and the excellent adsorption property of chitosan and using sodium alginate as a cross linker, an adsorbent is developed, which takes the bamboo charcoal as the matrix to load the chitosan and can efficiently remove heavy metal ions and dye in the printing and dying waste water. The specific technical scheme comprises the steps of: after the bamboo charcoal is pretreated, mixing the bamboo charcoal with the sodium alginate by the mass ratio of 3:1, and putting and maintaining the mixture in a water bath at the constant temperature of 80-100DEG C for 14 hours to obtain a bamboo charcoal/ sodium alginate mixture; activating for 120-240min at the temperature of 105-110DEG C; mixing carbide and chitosan into paste by the mass ratio of 2:1, and then adding CH3COOH of certain volume into the paste; quickly stirring and drying; washing until pH is 7.0, and then drying in a drying oven at the temperature of 60DEG C; and smashing, and screening to obtain a BC(Bamboo Charcoal )/CTS (Chitosan) composite adsorbent. When the compound is mixed with FeSO4 by the ratio of 1:1, the adsorption effect of sulfur dye can be improved. The adsorbent is mainly used for treating waste water simultaneously containing heavy metal ions and dye.
Description
Technical field
The present invention relates to a kind of adsorbent that adsorbs heavy metal ions in wastewater and dyestuff, especially bigger to proportion metal ion and reluctant dyeing waste water, enter water body and the pollution that causes is adsorbed through various approach, can efficiently remove the heavy metal ion in the dyeing waste water and the adsorbent of dyestuff simultaneously.
Background technology
The improvement of heavy metal and waste water from dyestuff all is the focus that environmental protection industry (epi) is paid close attention to.Heavy metal can not be by biodegradation, and easily enrichment causes water pollution in water, finally is detrimental to health.Simultaneously, China's printing and dyeing industry mostly is small lot batch manufacture, and major part is intermittently operated, and waste water is discontinuity discharging, thereby the water quality and quantity excursion is very big, and waste water component complexity, concentration height, colourity are dark.The method of removing the heavy metal ion in anhydrating is a lot, and traditional processing method is to adopt chemical precipitation method, membrane filtration, ion-exchange, evaporation absorption method, absorption method and electrolysis etc., but all there is certain defective in these methods.Chemical precipitation method greatly, easily produces secondary pollution to the consumption of reagent; Evaporation absorption method energy consumption is too big; Though ion-exchange and active carbon adsorption effect are better, cost is too high.And traditional adsorbent is to the processing of dyeing waste water, have the advantages that investment is little, method is easy, cost is low, be fit to the processing of middle-size and small-size printing and dyeing mill waste water, it mainly is activated carbon, activated carbon only has absorption property preferably to water-soluble dyes such as the dye of positive ion, direct dyes, acid dyes, reactive dye, but can not remove the colloid hydrophobic dye in the water, and regeneration expense height, the application of activated carbon is restricted.Make a general survey of the production development process of domestic and international water treatment agent, development trend by low molecule to macromolecule, single type to compound, single function to multi-functional.
Bamboo charcoal is a focus in the raw material of wood-charcoal material research field in recent years, has flourishing microcosmic duct, mechanical strength is higher, absorption property is good, can be used as adsorbent, deodorant, conditioning agent, soil conditioner, preserving fruit and vegetable utilizing material, health care product, radioresistance and electromagnetic shielding material and industrial semi-conducting material etc., be a kind of novel function environment-friendly materials.But the easy stripping of the salt in the bamboo charcoal ash content can not be as the purification of water quality filter material of fish breeding water and live fish water, and frangible, re-uses shortcomings such as difficulty after the flushing.Shitosan is the positively charged big molecule of natural biological, easily film forming, nontoxic, corrosion-resistant, easily biological-degradable, anti-microbial property are good, can not cause secondary pollution and aboundresources, contain a large amount of hydroxyls and amino, can it be removed from solution by strong bonded such as hydrogen bond, covalent bond or coordinate bond and printing and dyeing organic molecule, tannic acid molecule, metal ions, have good absorption property.The present invention with sodium alginate as crosslinking agent, by the reformation of pore structure and the physical and chemical performance of hole surface chemical modification change bamboo charcoal, and be the matrix loading chitosan with renewable low-cost resource bamboo charcoal, the good adsorptivity of shitosan, easy film forming are combined with porous, the adsorptivity of bamboo charcoal, develop the efficient compound adsorbent of a kind of environment-friendly bamboo charcoal-shitosan (BC/CTS), this adsorbent has overcome active carbon influence that colourity, the adsorptive selectivity of water is big, regenerative process is complicated, the property is crisp, influence shortcomings such as the turbidity of water, difficult recovery.The adsorbent pore volume obviously increases, and specific area is far longer than chitosan particle, has improved its adsorption capacity to heavy metal ion and dyestuff greatly.
Summary of the invention
One of purpose of patent of the present invention provides a kind of adsorbent that adsorbs heavy metal ions in wastewater and dyestuff.Utilizing resourceful bamboo charcoal to be carrier, is material modified with shitosan, adds sodium alginate as crosslinking agent, preparation (BC/CTS) compound adsorbent.
Two of the purpose of patent of the present invention provides a kind of above-mentioned preparation of adsorbent method.
In order to realize one of foregoing invention patent purpose, the technical scheme that patent of the present invention adopted is: with the bamboo charcoal skeleton is carrier, on its surface, is prepared into the BC/CTS composite with chitosan loaded.Shitosan has excellent biological compatibility, avirulence, nonirritant, contains a large amount of primary amino radicals ,-NH on its strand
2Ionization takes place in group under acid condition, become the NH of positively charged
3 +, be natural polycationic compounds, contain a large amount of carboxyls on the sodium alginate strand, be natural polyanionic compound, under acid condition, shitosan and sodium alginate can form the polyelectrolyte composite membrane by positive and negative charge attraction.
In order to realize two of foregoing invention patent purpose, preparation of adsorbent method of the present invention may further comprise the steps:
1, bamboo charcoal is boiled repeatedly cleaning with deionized water, filter, oven dry is down sieved about 105-110 ℃, continues to dry to constant weight, places drier standby;
2, prepare certain density sodium alginate aqueous solution, standing and defoaming.The shitosan that adds bamboo charcoal and certain mass proportioning while stirring, the acetic acid that adds certain volume behind the furnishing pasty state, stir fast, make the even association reaction of bamboo charcoal, shitosan and sodium alginate, mixture is transferred in the different vessel as required, dry in 60 ℃ of baking ovens, washing is flooded to neutrality, continues oven dry in 60 ℃ of baking ovens, pulverizes, sieve, obtain the BC/CTS combination product of different-grain diameter;
3, with the BC/CTS combination product and the FeSO of different-grain diameter
4According to 1: 1 proportioning, make it constitute good flocculate, improve the adsorption effect of sulfur dye.
The specific embodiment
1, the preliminary treatment of bamboo charcoal: bamboo charcoal is boiled repeatedly to remove the residue on dust and bamboo charcoal surface with deionized water, filter, oven dry is down sieved about 105~110 ℃, continues to dry to constant weight, obtains product A;
2, the preparation of bamboo charcoal/sodium alginate mixture: place baking oven to dry to constant weight for 105~110 ℃ product A (60 order).Bamboo charcoal and sodium alginate by mass ratio be mix at 3: 1 after, constant temperature was placed 14 hours in 80~100 ℃ water-bath, obtained bamboo charcoal/sodium alginate mixture B;
3, activation preparation BC/CTS combination product: at N
2Under the atmosphere, mixture B under 105~110 ℃ of temperature, is activated 120~240min.And with the carbide that obtained with and the shitosan of certain mass proportioning, add the CH of certain volume behind the furnishing pasty state
3COOH, stir fast, make activation bamboo charcoal, shitosan association reaction, as required mixture is transferred in the different vessel, dry in 60 ℃ of baking ovens, washing is flooded to neutrality, in 60 ℃ of baking ovens, continue oven dry, pulverize, sieve, obtain the BC/CTS compound adsorbent of different-grain diameter, can Adsorption of Heavy Metal Ions, acid dyes, reactive dye, premetallized dye and a part of direct dyes.
4, the adsorption function of adsorbent is expanded: with the BC/CTS combination product and the FeSO of different-grain diameter
4According to 1: 1 proportioning, make it constitute good flocculate, can improve the hydrophobic dye adsorption effect of (comprise sulphur red brown BBR, vulcanize deep blue 3R, vulcanize red GGF, vulcanize dark brown GD etc.).Vulcanize alkaline reduzate by acidifying after, the pH value is about 4~5, dyestuff is separated out from solution, and the sulfuration raffinate after the acidifying is precipitated, sediment is recyclable hydrophobic dye after filtration.
5, the regeneration of BC/CTS compound adsorbent: adsorbent is eluted to no adsorbate with the slow vibration of 2% NaOH solution and detects, and then washs to neutral with watery hydrochloric acid, distilled water, dries, and reuses.
The beneficial effect of patent of the present invention is: adopt the blend method for coating to prepare the BC/CTS compound adsorbent, preparation process is simple to operate, energy consumption is low, pollution-free. The actual loading effect of shitosan is better in the composite of preparation, when its load capacity arrives 20%, the absorption effect increases significantly, wherein the quality proportioning of shitosan and sodium alginate is 10: 1 o'clock, compound adsorbent is better to the absorption performance of metal ion, acid dyes, effluent quality is good and more stable after treatment, can not generate spawn in water again simultaneously, causes secondary pollution. As compound adsorbent and FeSO4During according to 1: 1 proportioning, can consist of good flocculate, can improve the absorption effect of hydrophobic dye, simultaneously, vulcanize alkaline reduzate by acidifying after, dyestuff can be separated out from solution, sulfuration raffinate after the acidifying is precipitated, sediment is recyclable hydrophobic dye after filtration, has alleviated the pollution of dyestuff waste water, obtains good economic benefit and environmental benefit. The BC/CTS compound adsorbent is regenerated by sig water, and operating process is easy, quick, efficient is high, functional, reuses adsorption rate after three times and still can arrive originally more than 95%, and can not affect the turbidity of water in the processing procedure.
Claims (5)
1. a composite natural polymeric sorbent is characterized in that: contain a large amount of primary amino radicals ,-NH on the chitosan molecule chain
2Ionization takes place in group under acid condition, become the NH of positively charged
3 +, be natural polycationic compounds, contain a large amount of carboxyls on the sodium alginate strand, be natural polyanionic compound, under acid condition, shitosan and sodium alginate can form the polyelectrolyte composite membrane by positive and negative charge attraction.
2. a kind of composite natural polymeric sorbent according to claim 1 is characterized in that: being carrier with the bamboo charcoal, is material modified with shitosan, adds sodium alginate as crosslinking agent, preparation BC/CTS compound adsorbent.
3. a kind of composite natural polymeric sorbent according to claim 1 and 2, its preparation process condition feature is: bamboo charcoal is boiled repeatedly to remove the residue on dust and bamboo charcoal surface with deionized water, filter, oven dry is down sieved about 105~110 ℃, dries to constant weight, after crossing 60 orders, bamboo charcoal and sodium alginate by mass ratio be mix at 3: 1 after, constant temperature was placed 14 hours in 80~100 ℃ water-bath, obtained bamboo charcoal/sodium alginate mixture.At N
2Under the atmosphere, this mixture under 105~110 ℃ of temperature, is activated 120~240min.And be 2: 1 with carbide and the chitosan mass proportioning that is obtained, add the CH of certain volume behind the furnishing pasty state
3COOH stirs fast, makes activation bamboo charcoal, shitosan association reaction, dries in 60 ℃ of baking ovens, and washing is flooded to pH7.0, continues oven dry in 60 ℃ of baking ovens, pulverizes, and sieves, and obtains the BC/CTS compound adsorbent of different-grain diameter.
4. according to claim 1 or 2 or 3 described a kind of composite natural polymeric sorbents, with the BC/CTS combination product and the FeSO of different-grain diameter
4According to 1: 1 proportioning, constitute good flocculate, improve the adsorption effect of hydrophobic dye.Vulcanize alkaline reduzate by acidifying after, the pH value is about 4~5, dyestuff is separated out from solution, the sulfuration raffinate after the acidifying is precipitated recyclable hydrophobic dye.Adsorbent is eluted to no adsorbate with the slow vibration of 2% NaOH solution and detects, and then washs to neutral with watery hydrochloric acid, distilled water, dries, and reuses.
5. according to claim 1 or 2 or 3 or 4 described a kind of composite natural polymeric sorbents, its preparation of adsorbent method may further comprise the steps:
A) preliminary treatment of bamboo charcoal: bamboo charcoal is boiled repeatedly to remove the residue on dust and bamboo charcoal surface with deionized water, filter, oven dry is down sieved about 105~110 ℃, continues to dry to constant weight, obtains product A;
B) preparation of bamboo charcoal/sodium alginate mixture: place baking oven to dry to constant weight for 105~110 ℃ product A (60 order).Bamboo charcoal and sodium alginate by mass ratio be mix at 3: 1 after, constant temperature was placed 14 hours in 80~100 ℃ water-bath, obtained bamboo charcoal/sodium alginate mixture B;
C) activation preparation BC/CTS combination product: at N
2Under the atmosphere, mixture B under 105~110 ℃ of temperature, is activated 120~240min.And be 2: 1 with carbide and the chitosan mass proportioning that is obtained, add the CH of certain volume behind the furnishing pasty state
3COOH, stir fast, make activation bamboo charcoal, shitosan association reaction, mixture is transferred in the different vessel, dry in 60 ℃ of baking ovens, washing is flooded to neutrality, in 60 ℃ of baking ovens, continue oven dry, pulverize, sieve, obtain the BC/CTS compound adsorbent of different-grain diameter, can Adsorption of Heavy Metal Ions and acid dyes etc.Obtain the BC/CTS compound adsorbent of different-grain diameter, can Adsorption of Heavy Metal Ions and acid dyes etc.
D) adsorption function of adsorbent is expanded: with the BC/CTS combination product and the FeSO of different-grain diameter
4According to 1: 1 proportioning, make it constitute good flocculate, can improve the adsorption effect of hydrophobic dye.
E) regeneration of the recovery of dyestuff and adsorbent: vulcanize alkaline reduzate by acidifying after, the pH value is about 4~5, dyestuff is separated out from solution, and the sulfuration raffinate after the acidifying is precipitated, sediment is recyclable hydrophobic dye after filtration.Adsorbent is eluted to no adsorbate with the slow vibration of 2% NaOH solution and detects, and then washs to neutral with watery hydrochloric acid, distilled water, dries, and reuses.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2009102056481A CN102029144A (en) | 2009-09-29 | 2009-09-29 | Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2009102056481A CN102029144A (en) | 2009-09-29 | 2009-09-29 | Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof |
Publications (1)
Publication Number | Publication Date |
---|---|
CN102029144A true CN102029144A (en) | 2011-04-27 |
Family
ID=43882927
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2009102056481A Pending CN102029144A (en) | 2009-09-29 | 2009-09-29 | Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN102029144A (en) |
Cited By (28)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102658083A (en) * | 2012-04-28 | 2012-09-12 | 天津城市建设学院 | Modified sludge activated carbon for removing multiple heavy metals in sewage and sludge simultaneously |
CN102671555A (en) * | 2012-05-18 | 2012-09-19 | 江南大学 | Preparation method and application of chitosan and polyvinyl alcohol mixed film |
CN103007903A (en) * | 2012-12-26 | 2013-04-03 | 常州大学 | BC-PANI composite adsorbent for treating azo dye wastewater, and preparation method and applications thereof |
CN103232146A (en) * | 2013-05-18 | 2013-08-07 | 兰州理工大学 | Method for preparing modified flocculant of sodium alga acid |
CN103359816A (en) * | 2012-03-29 | 2013-10-23 | 江南大学 | Method for synthesizing modified sodium alginate flocculating agent and application of flocculating agent |
CN103464102A (en) * | 2013-09-23 | 2013-12-25 | 北京师范大学 | Porous composite adsorbing agent for removing stream substrate sludge contamination and preparation process of agent |
CN104720104A (en) * | 2015-02-11 | 2015-06-24 | 浙江中烟工业有限责任公司 | Filter tip addition agent for selectively reducing crotonaldehyde in smoke of cigarette and preparing method and application thereof |
CN105112059A (en) * | 2015-08-19 | 2015-12-02 | 中国科学院宁波材料技术与工程研究所 | Soil heavy mental fixing agent and preparation method therefor and application thereof |
CN105148855A (en) * | 2015-08-06 | 2015-12-16 | 莆田学院 | Magnetic chitosan bamboo charcoal composite material, preparation method and application thereof |
CN105417614A (en) * | 2015-11-20 | 2016-03-23 | 浙江省海洋水产研究所 | Heavy metal removal agent for mariculture water |
CN105642242A (en) * | 2016-01-07 | 2016-06-08 | 井冈山大学 | Preparation of modified bamboo charcoal based on lead ion adsorption and application method thereof |
CN106189193A (en) * | 2016-07-14 | 2016-12-07 | 安徽亳州喜宝鞋服有限公司 | A kind of compound polyurethane material of anti-pressure and abrasion-proof for footwear material and preparation method thereof |
CN106362703A (en) * | 2016-10-12 | 2017-02-01 | 四川大学 | Improved carageenan-chitosan polyelectrolyte microspheres as well as preparation method and application thereof |
CN106608665A (en) * | 2015-10-27 | 2017-05-03 | 华东理工大学 | Method for removal of heavy metal ions |
CN106745358A (en) * | 2016-11-25 | 2017-05-31 | 南宁市黑晶信息技术有限公司 | A kind of heavy metal-polluted water treatment agent and preparation method thereof |
CN108499546A (en) * | 2018-04-25 | 2018-09-07 | 安徽天顺环保设备股份有限公司 | A kind of preparation method of heavy metal absorbent |
CN108905982A (en) * | 2018-07-18 | 2018-11-30 | 广西南宁荣威德新能源科技有限公司 | It is a kind of for removing the preparation method of the adsorbent of aflatoxin in peanut oil |
CN108940219A (en) * | 2018-07-12 | 2018-12-07 | 浙江正洁环境科技有限公司 | A kind of anti-acid heavy metal absorbent and preparation method thereof |
CN109776764A (en) * | 2019-01-23 | 2019-05-21 | 北京化工大学 | A kind of super organic cross-linked polymeric object material, preparation method and application |
CN110304762A (en) * | 2019-07-10 | 2019-10-08 | 浙江海印数码科技有限公司 | A kind of processing method for the dyeing waste water that absorption-flocculation-UF membrane combines |
CN110749634A (en) * | 2019-10-21 | 2020-02-04 | 遵义师范学院 | NiO/BC composite material and preparation method thereof |
CN110749633A (en) * | 2019-10-21 | 2020-02-04 | 遵义师范学院 | Method for modifying electrode by NiO/BC composite material and application thereof |
CN111298774A (en) * | 2019-12-10 | 2020-06-19 | 佛山科学技术学院 | Preparation method of nano repair material for heavy metal polluted groundwater |
CN111302467A (en) * | 2020-04-08 | 2020-06-19 | 刘水平 | Flocculant capable of recovering dye, preparation method and application thereof |
CN111871367A (en) * | 2020-06-08 | 2020-11-03 | 武汉纺织大学 | Rush magnetic powder for dyeing wastewater treatment and preparation method and application thereof |
CN112441651A (en) * | 2019-08-27 | 2021-03-05 | 宁波方太厨具有限公司 | Water storage tank for steam box and preparation method and control method thereof |
CN112569908A (en) * | 2020-12-24 | 2021-03-30 | 镇江市和云工业废水处置有限公司 | Preparation method of adsorbent for heavy metal wastewater treatment |
CN116099509A (en) * | 2023-01-13 | 2023-05-12 | 安徽工业大学 | Sodium alginate/gelatin biochar multi-element composite material, preparation method and method for treating cadmium in water body |
-
2009
- 2009-09-29 CN CN2009102056481A patent/CN102029144A/en active Pending
Non-Patent Citations (2)
Title |
---|
王云燕: "竹炭-壳聚糖复合材料的制备及其性能研究", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》 * |
王云燕等: "竹炭-壳聚糖复合吸附剂的制备及其性能", 《福建林学院学报》 * |
Cited By (37)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103359816A (en) * | 2012-03-29 | 2013-10-23 | 江南大学 | Method for synthesizing modified sodium alginate flocculating agent and application of flocculating agent |
CN103359816B (en) * | 2012-03-29 | 2015-05-20 | 江南大学 | Method for synthesizing modified sodium alginate flocculating agent and application of flocculating agent |
CN102658083A (en) * | 2012-04-28 | 2012-09-12 | 天津城市建设学院 | Modified sludge activated carbon for removing multiple heavy metals in sewage and sludge simultaneously |
CN102658083B (en) * | 2012-04-28 | 2013-09-11 | 天津城市建设学院 | Modified sludge activated carbon for removing multiple heavy metals in sewage and sludge simultaneously |
CN102671555A (en) * | 2012-05-18 | 2012-09-19 | 江南大学 | Preparation method and application of chitosan and polyvinyl alcohol mixed film |
CN102671555B (en) * | 2012-05-18 | 2014-07-23 | 江南大学 | Preparation method and application of chitosan and polyvinyl alcohol mixed film |
CN103007903A (en) * | 2012-12-26 | 2013-04-03 | 常州大学 | BC-PANI composite adsorbent for treating azo dye wastewater, and preparation method and applications thereof |
CN103232146A (en) * | 2013-05-18 | 2013-08-07 | 兰州理工大学 | Method for preparing modified flocculant of sodium alga acid |
CN103464102A (en) * | 2013-09-23 | 2013-12-25 | 北京师范大学 | Porous composite adsorbing agent for removing stream substrate sludge contamination and preparation process of agent |
CN104720104B (en) * | 2015-02-11 | 2018-01-30 | 浙江中烟工业有限责任公司 | Additives of filter tip of crotonaldehyde and its preparation method and application in a kind of selectivity reducing cigarette fume |
CN104720104A (en) * | 2015-02-11 | 2015-06-24 | 浙江中烟工业有限责任公司 | Filter tip addition agent for selectively reducing crotonaldehyde in smoke of cigarette and preparing method and application thereof |
CN105148855A (en) * | 2015-08-06 | 2015-12-16 | 莆田学院 | Magnetic chitosan bamboo charcoal composite material, preparation method and application thereof |
CN105112059A (en) * | 2015-08-19 | 2015-12-02 | 中国科学院宁波材料技术与工程研究所 | Soil heavy mental fixing agent and preparation method therefor and application thereof |
CN105112059B (en) * | 2015-08-19 | 2019-02-22 | 中国科学院宁波材料技术与工程研究所 | A kind of heavy metal-polluted soil fixative and its preparation method and application |
CN106608665A (en) * | 2015-10-27 | 2017-05-03 | 华东理工大学 | Method for removal of heavy metal ions |
CN105417614A (en) * | 2015-11-20 | 2016-03-23 | 浙江省海洋水产研究所 | Heavy metal removal agent for mariculture water |
CN105642242A (en) * | 2016-01-07 | 2016-06-08 | 井冈山大学 | Preparation of modified bamboo charcoal based on lead ion adsorption and application method thereof |
CN106189193A (en) * | 2016-07-14 | 2016-12-07 | 安徽亳州喜宝鞋服有限公司 | A kind of compound polyurethane material of anti-pressure and abrasion-proof for footwear material and preparation method thereof |
CN106362703A (en) * | 2016-10-12 | 2017-02-01 | 四川大学 | Improved carageenan-chitosan polyelectrolyte microspheres as well as preparation method and application thereof |
CN106745358A (en) * | 2016-11-25 | 2017-05-31 | 南宁市黑晶信息技术有限公司 | A kind of heavy metal-polluted water treatment agent and preparation method thereof |
CN108499546A (en) * | 2018-04-25 | 2018-09-07 | 安徽天顺环保设备股份有限公司 | A kind of preparation method of heavy metal absorbent |
CN108940219A (en) * | 2018-07-12 | 2018-12-07 | 浙江正洁环境科技有限公司 | A kind of anti-acid heavy metal absorbent and preparation method thereof |
CN108905982A (en) * | 2018-07-18 | 2018-11-30 | 广西南宁荣威德新能源科技有限公司 | It is a kind of for removing the preparation method of the adsorbent of aflatoxin in peanut oil |
CN109776764A (en) * | 2019-01-23 | 2019-05-21 | 北京化工大学 | A kind of super organic cross-linked polymeric object material, preparation method and application |
CN109776764B (en) * | 2019-01-23 | 2020-06-02 | 北京化工大学 | Super-crosslinked organic polymer material, preparation method and application |
CN110304762A (en) * | 2019-07-10 | 2019-10-08 | 浙江海印数码科技有限公司 | A kind of processing method for the dyeing waste water that absorption-flocculation-UF membrane combines |
CN110304762B (en) * | 2019-07-10 | 2021-11-05 | 浙江海印数码科技有限公司 | Method for treating printing and dyeing wastewater by combining adsorption-flocculation-membrane separation |
CN112441651A (en) * | 2019-08-27 | 2021-03-05 | 宁波方太厨具有限公司 | Water storage tank for steam box and preparation method and control method thereof |
CN110749634A (en) * | 2019-10-21 | 2020-02-04 | 遵义师范学院 | NiO/BC composite material and preparation method thereof |
CN110749633A (en) * | 2019-10-21 | 2020-02-04 | 遵义师范学院 | Method for modifying electrode by NiO/BC composite material and application thereof |
CN111298774A (en) * | 2019-12-10 | 2020-06-19 | 佛山科学技术学院 | Preparation method of nano repair material for heavy metal polluted groundwater |
CN111302467A (en) * | 2020-04-08 | 2020-06-19 | 刘水平 | Flocculant capable of recovering dye, preparation method and application thereof |
CN111302467B (en) * | 2020-04-08 | 2020-12-01 | 湖州达立智能设备制造有限公司 | Flocculant capable of recovering dye, preparation method and application thereof |
CN111871367A (en) * | 2020-06-08 | 2020-11-03 | 武汉纺织大学 | Rush magnetic powder for dyeing wastewater treatment and preparation method and application thereof |
CN112569908A (en) * | 2020-12-24 | 2021-03-30 | 镇江市和云工业废水处置有限公司 | Preparation method of adsorbent for heavy metal wastewater treatment |
CN116099509A (en) * | 2023-01-13 | 2023-05-12 | 安徽工业大学 | Sodium alginate/gelatin biochar multi-element composite material, preparation method and method for treating cadmium in water body |
CN116099509B (en) * | 2023-01-13 | 2023-08-01 | 安徽工业大学 | Sodium alginate/gelatin biochar multi-element composite material, preparation method and method for treating cadmium in water body |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102029144A (en) | Adsorbent for adsorbing heavy metal ions and dye in waste water and preparation method thereof | |
Bashir et al. | Removal of heavy metal ions from aqueous system by ion-exchange and biosorption methods | |
Lu et al. | Fabrication of cross-linked chitosan beads grafted by polyethylenimine for efficient adsorption of diclofenac sodium from water | |
CN102527347B (en) | Magnetic chitosan/cationic surface active agent modified zeolite adsorbent and preparation method and application thereof | |
Purkayastha et al. | A comprehensive review on Cd (II) removal from aqueous solution | |
CN104226259B (en) | A kind of threonine modified attapulgite earth adsorbing and application thereof | |
CN101934223B (en) | Preparation method for composite crosslinked adsorbent for waste water treatment | |
Wong et al. | The removal of basic and reactive dyes using quartenised sugar cane bagasse | |
CN103447013A (en) | Method for preparing graphene/chitosan adsorbent and application method thereof | |
CN109126697B (en) | Natural material composite adsorbent and preparation method and application thereof | |
Kalkan et al. | Experimental Study to Remediate Acid Fuchsin Dye Using Laccase-Modified Zeolite from Aqueous Solutions. | |
De Souza et al. | Removal of Pb (II) from aqueous solution with orange sub-products chemically modified as biosorbent | |
CN100548470C (en) | Preparation method and application of biological adsorption material consisting of seaweed plants and chitosan | |
CN109647353A (en) | A kind of heavy metal containing sewage composite treating agent and its preparation method and application | |
CN101601991A (en) | Remove biomass adsorbent and preparation, application and the renovation process of lead ion in the waste water | |
CN113842883A (en) | Lanthanum-loaded iron carbon nanotube film material for environmental remediation and preparation method and application thereof | |
Shaikh | Adsorption of Pb (II) from wastewater by natural and synthetic adsorbents | |
CN103084154A (en) | Method for activated carbon regeneration by yeast combined chemical process | |
CN105944672A (en) | Preparation and application of phosphorus-hybridized functional activated-carbon absorption material | |
CN101337731B (en) | Method for removing cadmium in industrial wastewater by bio adsorbing agent | |
CN109126647A (en) | A kind of preparation method of graphene oxide-sodium alginate gel ball | |
CN1868576B (en) | Biological modification infusorial earth adsorbent, and its prepn. method | |
CN107337249A (en) | A kind of adsorption treatment method of heavy metal ion-containing waste water | |
Binupriya et al. | A novel method in utilization of bokbunja seed wastes from wineries in liquid-phase sequestration of reactive blue 4 | |
CN113351187B (en) | Heavy metal ion imprinted hydrogel ball and preparation method and application thereof |
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: 20110427 |