CN101073764A - Plastic-skeleton bentonite bentonite composite adsorbent and its production - Google Patents
Plastic-skeleton bentonite bentonite composite adsorbent and its production Download PDFInfo
- Publication number
- CN101073764A CN101073764A CN 200710035221 CN200710035221A CN101073764A CN 101073764 A CN101073764 A CN 101073764A CN 200710035221 CN200710035221 CN 200710035221 CN 200710035221 A CN200710035221 A CN 200710035221A CN 101073764 A CN101073764 A CN 101073764A
- Authority
- CN
- China
- Prior art keywords
- bentonite
- preparation
- plastic
- skeleton
- composite adsorbent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Abstract
The invention is concerned with the plastic framework-style bentonite composite sorbent and the preparation method. The crude bentonite or the character-changed bentonite is the main material for the composite sorbent, the thermoplastic macromolecule polymer is as the framework connecting material and also add the assistant selective material, the blowing hole-make material by the working procedure such as mixture, model melt extrude, dryness and cut grain. The preparation method is dry preparation method with simple process and without secondary pollution, the product can adjust the powder intensity, the size of the hole, the porosity, the density and the adsorbing selectivity according to the change of the selected group and dosage. The sorbent is not easy pulverization in water which can use for waste water dispose with heavy metal ion and organic infectant.
Description
One, technical field
The present invention relates to a kind of adsorbent that is applicable to water and wastewater treatment, particularly a kind of plastic-skeleton bentonite bentonite composite adsorbent.
Two, background technology
Bentonite is to be the claystone of Main Ingredients and Appearance with the montmorillonite, and its mineral composition and structure make it show the property of many excellences, and the title of " omnipotent clay " is arranged.Its application is extensive, and in recent years, along with the continuous reinforcement of environmental protection, for reducing the environmental improvement cost, exploitation and the application of bentonite as water and wastewater treatment sorbing material paid much attention in the whole world.Bentonite is the absorption and the cation exchange property of its excellence as the basis of water and wastewater treatment sorbing material, and wide material sources, and low price is expected to replace expensive charcoal absorption material.But, many researchs show, bentonite is as the sorbing material of water and wastewater treatment, or the material that uses in water environment, because its natural dilatancy, dispersiveness, suspension, make bentonite meet water and easily disperse pulp, follow-up Separation of Solid and Liquid difficulty, and be difficult to reclaim usefulness again, therefore, restricted the industrial applications of bentonite as water and wastewater treatment sorbing material, many bentonite adsorption productions can only rest on the laboratory research stage.
When bentonite uses as water and wastewater treatment sorbing material, mainly comprise natural montmorillonite, modified alta-mud and composite bentonite three major types.Natural montmorillonite generally can be used for handling the lower waste water of pollution level.Modified alta-mud and composite bentonite are in order to improve bentonitic adsorption treatment efficient or to handle and need process bentonite product after the processing to natural montmorillonite at different pollutants.Modified alta-mud generally can make by activation methods such as acidization, oxidizing process, reducing process, roasting method and hydrogenization methods, or by introducing inorganic or organic compound makes.Composite bentonite is by adding new material, bringing into play the bentonite product of each material composition effect simultaneously.Under many situations, people absolutely do not separate modified alta-mud and composite bentonite, but both are general.Relevant modification of China or composite bentonite patent are more, as patent " a kind of sodium bentonite ore composite water disposal agent and preparation thereof and application " (patent No. 200410067506.0), " a kind of preparation method of natural bentone material used to treat sewage " (patent No. 00123368.8), " a kind of sun-nonionic organobentonite wastewater treatment preparation methods " (patent No. 200310122774.3), " a kind of inorganic-organic composite bentonite wastewater treatment preparation methods " (patent No. 200410018109.4), " preparation method of bentonite composite water purifying agent (type) " (patent No. 89109200.5), " production technology of bentone adsorbent " (patent No. 96122367.7), " a kind of modified bentonite chromium remover and manufacture method thereof " (patent No. 200510021343.7), " be used for bentonite base composite material of water treatment and preparation method thereof " (patent No. 200510036985.4), " ferro-nickel modified bentonite in use for processing water and preparation method thereof " (patent No. 200610046853.4), " be used for bentonite of water purification and preparation method thereof " (patent No. 200610014052.X), or the like.These patented technologies mainly are to improve efficient and the selectivity of bentonite in water treatment by modification or complex method.
But these patented technologies exist uses a large amount of chemical agents, and preparation is easy to generate secondary pollution under solution environmental, preparation process more complicated (comprising drying, mixing, reaction, ageing, filtration etc.), preparation time is long, generally needs several hrs, even tens hours.Cause that preparation efficiency is low, cost is high, problem such as be difficult to apply.
Three, summary of the invention
Purpose of the present invention mainly is the problem that exists at above-mentioned bentone adsorbent, provide a kind of chance water not disperse pulp, be easy to Separation of Solid and Liquid, preparation is simple, and has high strength, high porosity, high adsorption activity, is easy to the plastic-skeleton bentonite bentonite composite adsorbent of reclaiming.
The present invention is achieved through the following technical solutions, and described technical scheme may further comprise the steps:
(1) batching: with dried natural montmorillonite or modified alta-mud 45～80wt%, thermoplastic polyester 20～40wt%, assisted selective absorption raw material 0～30wt%, the ratio of foaming pore-creating raw material 0～10wt% is prepared burden.
(2) batch mixing: earlier dried natural montmorillonite or modified alta-mud and assisted selective absorption raw material were mixed in high-speed mixer 15～30 minutes in described ratio, and then the adding thermoplastic polyester mixed 15～20 minutes, add foaming pore-creating raw material at last and continue to mix 5～10 minutes, get final product discharging.
(3) plasticizing is extruded: described batch mixing is joined the twin-screw plastic extruder plastify and extrude, the operating temperature of each section of control extruder is: 160～190 ℃ of transportation sections, 180～200 ℃ of fluxing zones, 200～220 ℃ of melt zones, 200～230 ℃ of extruding zones, the main-machine screw speed setting is 40～200 rev/mins, and obtaining diameter is the fine strip shape product of 2～5mm, and this product is put into the tank cooling.
(4) drying: with the air dry of cooled fine strip shape product or use heated-air drying, baking temperature is controlled at below the thermoplastic polyester softening temperature.
(5) pelletizing: dried fine strip shape product is adopted automatic pelleter pelletizing, obtain partical.
Wherein, described bentonite is natural montmorillonite or modified alta-mud.
Described thermoplastic polyester is the one or more combination in polyethylene, polypropylene, the polyvinyl chloride.
Described assisted selective absorption raw material is the one or more combination in flyash, charcoal, activated carbon, slag, blast furnace slag, diatomite, medical stone, zeolite, the gangue.
Described foaming pore-creating raw material is the one or more combination in Celogen Az, sodium acid carbonate, the carbonic hydroammonium.
Described drying is that natural montmorillonite or modified alta-mud is dry under 100～150 ℃, makes its water content less than 2%; Assisted selective absorption raw material drying is handled back (making its water content less than 2%) and is handled after the screening of 100 mesh sieves; Foaming pore-creating raw material is a mealy solid particle; Thermoplastic polyester can be granular or powdery.
Prepare plastic-skeleton bentonite bentonite composite adsorbent according to the method described above and belong to dry preparation process, preparation process is simple, do not produce secondary pollution, and the preparation product can be regulated its granule strength, pore-size, porosity, density and adsorptive selectivity according to the variation of selected component and consumption thereof, thereby improves the adaptability and the practicality of bentone adsorbent product.
Four, the specific embodiment
Embodiment 1
Get natural montmorillonite 45wt%, assisted selective absorption raw meal coal ash and each 10wt% of slag, add in the high-speed mixer, stirred 30 minutes, then add thermoplastic polyester polyethylene 30wt%, continue to stir 15 minutes, add foaming pore-creating raw material Celogen Az 5wt% at last, stirred again 15 minutes.Then the sample that mixes is added in the feeding funnel of twin-screw plastic extruder; treat that each section of twin-screw plastic extruder reaches heating-up temperature (160 ℃ of the transportation sections that set; 180 ℃ of fluxing zones; 200 ℃ of melt zones, 220 ℃ of compression extruding zones), start main frame and extrude; obtain the fine strip shape product; it carries out drying after directly entering the tank cooling, send automatic pelleter pelletizing again, obtains the 3mm granulated sorbent at last.
This plastic-skeleton bentonite bentonite composite adsorbent not efflorescence in water is used for effluent containing heavy metal ions such as Treatment of Copper, chromium, lead, reaches more than 90% through the clearance of heavy metal ions in wastewater after the single treatment.With the absorbing copper ion is example, and this compound adsorbent can reach 26mg/g to the adsorption capacity of copper ion, adsorbs saturated after can continue after the regeneration to use.
Embodiment 2
Get natural montmorillonite 80wt%, add in the high-speed mixer, stirred 30 minutes, then add thermoplastic polyester polypropylene 20wt%, continue to stir 15 minutes.Then the sample that mixes is added in the feeding funnel of twin-screw plastic extruder; treat that each section of twin-screw plastic extruder reaches heating-up temperature (180 ℃ of the transportation sections that set; 190 ℃ of fluxing zones; 220 ℃ of melt zones, 220 ℃ of compression extruding zones), start main frame and extrude; obtain the fine strip shape product; it carries out drying after directly entering the tank cooling, send automatic pelleter pelletizing again, obtains the 3mm granulated sorbent at last.
This plastic-skeleton bentonite bentonite composite adsorbent not efflorescence in water is used for effluent containing heavy metal ions such as Treatment of Copper, chromium, lead, reaches more than 90% through the clearance of heavy metal ions in wastewater after the single treatment.With the absorbing copper ion is example, and this compound adsorbent can reach 20mg/g to the adsorption capacity of copper ion, adsorbs saturated after can continue after the regeneration to use.
Embodiment 3
Get natural montmorillonite 60wt%, assisted selective absorption raw material activated carbon and each 5wt% of blast furnace slag, add in the high-speed mixer, stirred 30 minutes, then add thermoplastic polyester polyvinyl chloride 25wt%, continue to stir 15 minutes, add foaming pore-creating raw material sodium acid carbonate 5wt% at last, stirred again 15 minutes.Then the sample that mixes is added in the feeding funnel of twin-screw plastic extruder; treat that each section of twin-screw plastic extruder reaches heating-up temperature (190 ℃ of the transportation sections that set; 200 ℃ of fluxing zones; 220 ℃ of melt zones, 230 ℃ of compression extruding zones), start main frame and extrude; obtain the fine strip shape product; it carries out drying after directly entering the tank cooling, send automatic pelleter pelletizing again, obtains the 3mm granulated sorbent at last.
This plastic-skeleton bentonite bentonite composite adsorbent not efflorescence in water is used for effluent containing heavy metal ions such as Treatment of Copper, chromium, lead, reaches more than 90% through the clearance of heavy metal ions in wastewater after the single treatment.With the absorbing copper ion is example, and this compound adsorbent can reach 28mg/g to the adsorption capacity of copper ion, adsorbs saturated after can continue after the regeneration to use.
Claims (9)
1, a kind of plastic-skeleton bentonite bentonite composite adsorbent and preparation method thereof is characterized in that: may further comprise the steps,
(1) batching: with dried natural montmorillonite or modified alta-mud 45～80wt%, thermoplastic polyester 20～40wt%, assisted selective absorption raw material 0～30wt%, the ratio of foaming pore-creating raw material 0～10wt% is prepared burden,
(2) batch mixing: earlier dried natural montmorillonite or modified alta-mud and assisted selective absorption raw material were mixed in high-speed mixer 15～30 minutes in described ratio, and then the adding thermoplastic polyester mixed 15～20 minutes, adding foaming pore-creating raw material at last continues to mix 5～10 minutes, get final product discharging
(3) plasticizing is extruded: described batch mixing is joined the twin-screw plastic extruder plastify and extrude, the operating temperature of each section of control extruder is: 160～190 ℃ of transportation sections, 180～200 ℃ of fluxing zones, 200～220 ℃ of melt zones, 200～230 ℃ of extruding zones, the main-machine screw speed setting is 40～200 rev/mins, obtaining diameter is the fine strip shape product of 2～5mm, this product is put into the tank cooling
(4) drying: with the air dry of cooled fine strip shape product or use heated-air drying, baking temperature is controlled at below the thermoplastic polyester softening temperature,
(5) pelletizing: dried fine strip shape product is adopted automatic pelleter pelletizing, obtain partical.
2, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described bentonite is natural montmorillonite or modified alta-mud.
3, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described thermoplastic polyester is the one or more combination in polyethylene, polypropylene, the polyvinyl chloride.
4, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described assisted selective absorption raw material is the one or more combination in flyash, charcoal, activated carbon, slag, blast furnace slag, diatomite, medical stone, zeolite, the gangue.
5, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described foaming pore-creating raw material is the one or more combination in Celogen Az, sodium acid carbonate, the carbonic hydroammonium.
6, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof, it is characterized in that: described dried natural montmorillonite or modified alta-mud are that natural montmorillonite or modified alta-mud is dry under 100～150 ℃, make its water content less than 2%.
7, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described auxiliary absorption raw material is after drying is handled, to make its water content less than 2%, handles after the screening of 100 mesh sieves.
8, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described foaming pore-creating raw material is a mealy solid particle.
9, plastic-skeleton bentonite bentonite composite adsorbent according to claim 1 and preparation method thereof is characterized in that: described thermoplastic polyester is granular or powdery.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100352212A CN100486687C (en) | 2007-06-21 | 2007-06-21 | Plastic-skeleton bentonite bentonite composite adsorbent and its production |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100352212A CN100486687C (en) | 2007-06-21 | 2007-06-21 | Plastic-skeleton bentonite bentonite composite adsorbent and its production |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101073764A true CN101073764A (en) | 2007-11-21 |
| CN100486687C CN100486687C (en) | 2009-05-13 |
Family
ID=38975126
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2007100352212A Expired - Fee Related CN100486687C (en) | 2007-06-21 | 2007-06-21 | Plastic-skeleton bentonite bentonite composite adsorbent and its production |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN100486687C (en) |
Cited By (22)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102423682A (en) * | 2011-12-07 | 2012-04-25 | 南京工业大学 | Adsorbent for removing antibiotics from water body, and preparation method and application of adsorbent |
| CN102464373A (en) * | 2011-10-20 | 2012-05-23 | 常州亚环环保科技有限公司 | Method for removing benzopyrene from drinking water |
| CN102814489A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using bentonite |
| CN103007900A (en) * | 2012-11-27 | 2013-04-03 | 安徽皖东化工有限公司 | Preparation method of kieselguhr modified absorbent resin |
| CN103666376A (en) * | 2013-11-11 | 2014-03-26 | 青岛佰众化工技术有限公司 | High oil-adsorption compound and preparation method thereof |
| CN104556342A (en) * | 2015-01-26 | 2015-04-29 | 东南大学 | Medicament for restoring hexavalent chromium contaminated soil and underground water and preparation method of medicament |
| CN104607039A (en) * | 2015-01-20 | 2015-05-13 | 济南木齐健康科技有限公司 | Composite material with anti-bacterial and purifying functions and preparation method of composite material |
| CN104907039A (en) * | 2015-05-21 | 2015-09-16 | 安徽凤凰滤清器股份有限公司 | Composite volcanic rock absorbent |
| CN104907043A (en) * | 2015-05-21 | 2015-09-16 | 安徽凤凰滤清器股份有限公司 | Modified volcanic rock adsorbent capable of recovering carbon monoxide |
| CN104923178A (en) * | 2015-05-21 | 2015-09-23 | 安徽凤凰滤清器股份有限公司 | Modified volcanic-rock acid-resistant adsorbent |
| CN105110392A (en) * | 2015-09-11 | 2015-12-02 | 武汉理工大学 | Quick purifying agent for nonselective heavy metal wastewater |
| CN105540699A (en) * | 2016-01-26 | 2016-05-04 | 苏州能华节能环保科技有限公司 | Nanometer phosphorus-free water treatment material and preparation method thereof |
| CN105753119A (en) * | 2016-03-16 | 2016-07-13 | 山东五洲检测有限公司 | Oily wastewater treating agent and preparation method and application thereof |
| CN106116022A (en) * | 2016-07-14 | 2016-11-16 | 胡大苇 | A kind of ammonia nitrogen processing method in acid waste water containing heavy metal |
| CN107042097A (en) * | 2017-05-25 | 2017-08-15 | 中持新兴环境技术中心（北京）有限公司 | A kind of material and its application method for being used to adsorb halogenated organic compounds |
| CN108479731A (en) * | 2018-04-23 | 2018-09-04 | 杭州鼎好新材料有限公司 | A kind of absorption heavy metal ion porous polyethylene ball and preparation method thereof |
| CN109370786A (en) * | 2018-11-06 | 2019-02-22 | 枞阳县毛巾有限责任公司 | A kind of diatomite towel washing agent and preparation method thereof |
| CN111514864A (en) * | 2020-05-07 | 2020-08-11 | 滨州学院 | Organic polluted wastewater treating agent and preparation method and application method thereof |
| CN111732148A (en) * | 2020-06-29 | 2020-10-02 | 河海大学 | System for retrieve phosphate in follow surface eutrophic water |
| CN112126574A (en) * | 2020-09-29 | 2020-12-25 | 安徽明光酒业有限公司 | Method for improving clarity of soft white spirit base wine |
| CN113499636A (en) * | 2021-06-30 | 2021-10-15 | 桐乡市健民过滤材料有限公司 | Formaldehyde-removing color-changing framework and preparation method thereof |
| WO2024060354A1 (en) * | 2022-09-23 | 2024-03-28 | 全椒科利德电子材料有限公司 | Preparation method for and preparation system of high-purity ammonia |
-
2007
- 2007-06-21 CN CNB2007100352212A patent/CN100486687C/en not_active Expired - Fee Related
Cited By (29)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102464373A (en) * | 2011-10-20 | 2012-05-23 | 常州亚环环保科技有限公司 | Method for removing benzopyrene from drinking water |
| CN102423682A (en) * | 2011-12-07 | 2012-04-25 | 南京工业大学 | Adsorbent for removing antibiotics from water body, and preparation method and application of adsorbent |
| CN102814489A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using bentonite |
| CN103007900A (en) * | 2012-11-27 | 2013-04-03 | 安徽皖东化工有限公司 | Preparation method of kieselguhr modified absorbent resin |
| CN103666376B (en) * | 2013-11-11 | 2016-06-29 | 青岛佰众化工技术有限公司 | A kind of high oil suction complex and preparation method thereof |
| CN103666376A (en) * | 2013-11-11 | 2014-03-26 | 青岛佰众化工技术有限公司 | High oil-adsorption compound and preparation method thereof |
| CN104607039A (en) * | 2015-01-20 | 2015-05-13 | 济南木齐健康科技有限公司 | Composite material with anti-bacterial and purifying functions and preparation method of composite material |
| CN104556342B (en) * | 2015-01-26 | 2016-06-01 | 东南大学 | The reparation medicament of hexavalent chromium polluted soil and underground water and preparation method |
| CN104556342A (en) * | 2015-01-26 | 2015-04-29 | 东南大学 | Medicament for restoring hexavalent chromium contaminated soil and underground water and preparation method of medicament |
| CN104907039A (en) * | 2015-05-21 | 2015-09-16 | 安徽凤凰滤清器股份有限公司 | Composite volcanic rock absorbent |
| CN104907043A (en) * | 2015-05-21 | 2015-09-16 | 安徽凤凰滤清器股份有限公司 | Modified volcanic rock adsorbent capable of recovering carbon monoxide |
| CN104923178A (en) * | 2015-05-21 | 2015-09-23 | 安徽凤凰滤清器股份有限公司 | Modified volcanic-rock acid-resistant adsorbent |
| CN105110392A (en) * | 2015-09-11 | 2015-12-02 | 武汉理工大学 | Quick purifying agent for nonselective heavy metal wastewater |
| CN105110392B (en) * | 2015-09-11 | 2017-12-05 | 武汉理工大学 | A kind of non-selective heavy metal wastewater thereby fast purification agent |
| CN105540699A (en) * | 2016-01-26 | 2016-05-04 | 苏州能华节能环保科技有限公司 | Nanometer phosphorus-free water treatment material and preparation method thereof |
| CN105753119A (en) * | 2016-03-16 | 2016-07-13 | 山东五洲检测有限公司 | Oily wastewater treating agent and preparation method and application thereof |
| CN106116022A (en) * | 2016-07-14 | 2016-11-16 | 胡大苇 | A kind of ammonia nitrogen processing method in acid waste water containing heavy metal |
| CN106116022B (en) * | 2016-07-14 | 2019-02-01 | 胡大苇 | A kind of ammonia nitrogen processing method in acid waste water containing heavy metal |
| CN107042097B (en) * | 2017-05-25 | 2019-06-21 | 中持新兴环境技术中心（北京）有限公司 | It is a kind of for adsorbing the material and its application method of halogenated organic compounds |
| CN107042097A (en) * | 2017-05-25 | 2017-08-15 | 中持新兴环境技术中心（北京）有限公司 | A kind of material and its application method for being used to adsorb halogenated organic compounds |
| CN108479731A (en) * | 2018-04-23 | 2018-09-04 | 杭州鼎好新材料有限公司 | A kind of absorption heavy metal ion porous polyethylene ball and preparation method thereof |
| CN109370786B (en) * | 2018-11-06 | 2021-09-10 | 山东凯大新型材料科技有限公司 | Diatomite towel detergent and preparation method thereof |
| CN109370786A (en) * | 2018-11-06 | 2019-02-22 | 枞阳县毛巾有限责任公司 | A kind of diatomite towel washing agent and preparation method thereof |
| CN111514864A (en) * | 2020-05-07 | 2020-08-11 | 滨州学院 | Organic polluted wastewater treating agent and preparation method and application method thereof |
| CN111732148A (en) * | 2020-06-29 | 2020-10-02 | 河海大学 | System for retrieve phosphate in follow surface eutrophic water |
| CN111732148B (en) * | 2020-06-29 | 2022-06-10 | 河海大学 | System for retrieve phosphate in follow surface eutrophic water |
| CN112126574A (en) * | 2020-09-29 | 2020-12-25 | 安徽明光酒业有限公司 | Method for improving clarity of soft white spirit base wine |
| CN113499636A (en) * | 2021-06-30 | 2021-10-15 | 桐乡市健民过滤材料有限公司 | Formaldehyde-removing color-changing framework and preparation method thereof |
| WO2024060354A1 (en) * | 2022-09-23 | 2024-03-28 | 全椒科利德电子材料有限公司 | Preparation method for and preparation system of high-purity ammonia |
Also Published As
| Publication number | Publication date |
|---|---|
| CN100486687C (en) | 2009-05-13 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN100486687C (en) | Plastic-skeleton bentonite bentonite composite adsorbent and its production | |
| CN111632575B (en) | Composite adsorbent and preparation method thereof | |
| Papandreou et al. | Copper and cadmium adsorption on pellets made from fired coal fly ash | |
| Katsou et al. | Use of ultrafiltration membranes and aluminosilicate minerals for nickel removal from industrial wastewater | |
| Reddad et al. | Cadmium and lead adsorption by a natural polysaccharide in MF membrane reactor: experimental analysis and modelling | |
| CN1272074C (en) | Super fine active compound adsorptive indoor air purifying agent | |
| Guo et al. | Magnesium hydroxide with higher adsorption capacity for effective removal of Co (II) from aqueous solutions | |
| US9120082B2 (en) | Modified adsorbent for capturing heavy metals in aqueous solution | |
| CN101585563A (en) | New composite water purifying agent and a preparation method thereof | |
| CN103071451A (en) | Modified attapulgite clay capable of purifying heavy metal ions in waste water and preparation method thereof | |
| CN1669632A (en) | Method for preparing active fly ash phosphorus adsorbent | |
| CN105712739A (en) | Magnetic biological ceramsite prepared from waste incineration fly ash, and preparation method thereof | |
| CN103523848B (en) | The made charcoal of Pinus massoniana Lamb wood chip removes method and the application of sulfa antibiotics in water body | |
| PL195988B1 (en) | Sorbent, method for producing the same and use of the same for immobilisation of heavy metals and phosphates | |
| CN114931929A (en) | Iron-based sludge/plastic composite biochar adsorbing material, and preparation method and application thereof | |
| CN103084154A (en) | Method for activated carbon regeneration by yeast combined chemical process | |
| CN111729654A (en) | Preparation method and application of modified pagodatree leaf biochar | |
| CN102000541A (en) | Spongy bentonite-based composite adsorbing material and preparation method thereof | |
| Wu et al. | Succinic acid-assisted modification of a natural zeolite and preparation of its porous pellet for enhanced removal of ammonium in wastewater via fixed-bed continuous flow column | |
| CN111036170B (en) | Water purification sludge composite adsorbent and application thereof | |
| CN102503053B (en) | Early-strength sludge modifier for landfill treatment and application thereof | |
| CN103127922B (en) | A kind of production method of adsorbent | |
| Perera et al. | Low-cost treatment method for organic matter and nutrients in landfill leachate | |
| CN101318737B (en) | Baking-free stephanoporate water slag filtering material and preparation method thereof | |
| CN1238275C (en) | Filter material having phosphor adsorbing and biological membrane function and its preparing method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20090513 Termination date: 20180621 |