CN105253946B - Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof - Google Patents

Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof Download PDF

Info

Publication number
CN105253946B
CN105253946B CN201510745137.4A CN201510745137A CN105253946B CN 105253946 B CN105253946 B CN 105253946B CN 201510745137 A CN201510745137 A CN 201510745137A CN 105253946 B CN105253946 B CN 105253946B
Authority
CN
China
Prior art keywords
activated carbon
potassium hydroxide
adsorption bed
superelevation
bed
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201510745137.4A
Other languages
Chinese (zh)
Other versions
CN105253946A (en
Inventor
闫亮
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
PowerChina Huadong Engineering Corp Ltd
Original Assignee
PowerChina Huadong Engineering Corp Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by PowerChina Huadong Engineering Corp Ltd filed Critical PowerChina Huadong Engineering Corp Ltd
Priority to CN201510745137.4A priority Critical patent/CN105253946B/en
Publication of CN105253946A publication Critical patent/CN105253946A/en
Application granted granted Critical
Publication of CN105253946B publication Critical patent/CN105253946B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The present invention provides a kind of multistage charcoal absorption bed system based on selective absorption cleaning principle, including being arranged in the first activated carbon adsorption bed of sorption channel leading portion and being arranged in the second activated carbon adsorption bed of sorption channel back segment, first activated carbon adsorption bed carries high meso-hole structure activated carbon, second activated carbon adsorption bed carries superelevation microcellular structure activated carbon, the present invention also provides the preparation method of above-mentioned multistage charcoal absorption bed system, the present invention has treatment effeciency high, reduced investment, it is low to run standing charges, energy consumption is low, the advantages of applied widely, especially it is when plurality of organic pollutants in water being present, also it can preferably carry out selectivity and complete adsorption cleaning by batch.

Description

Multistage charcoal absorption bed system and its preparation based on selective absorption cleaning principle Method
Technical field
The present invention relates to a kind of multistage activated carbon adsorption bed cleaning system, is primarily adapted for use in water supply and drainage treatment technology neck Domain, it can be applied to raw water and the deep purifying processing engineering of sewage.
Background technology
Along with China's rapid development of economy, the species and usage amount of organic matter are continuously increased.Organic matter makes extensively By the use of inevitably entering through various channels as in the water body of drinking water source, river, reservoir, lake as water source By different degrees of Organic Pollution.And the artificial synthesized small organic molecule using phenols as representative, can result in water body Permanent contact scar and intractability is very big.Organic matter can also constantly accumulate in water body and soil, then pass through food chain Into organism and it is progressively enriched with, finally enters human body, toxic action is produced to the mankind.In addition in water body generally existing with humic Natural macromolecular organic matter based on acid, natural macromolecular organic matter are by molecular weight is different, chemical characteristic is different a variety of groups Divide what is formed, its presence can dramatically increase the formation of carcinogenicity DBPs.At present, in general organic matter treatment technology Including flocculation, there is treating capacity deficiency, cost height etc. when being handled applied to organic pollution in method for oxidation and biological treatment Problem.Therefore, therefore the effective organic matter treatment technology of exploiting economy is the key of pollution control in water.
Activated carbon is a kind of porous sorbing material for being process by physico-chemical process based on carbon, With the characteristics of internal voids structure is flourishing, specific surface area is big and adsorption capacity is strong.Therefore it is net in various improvement water quality and raising In the further treatment technique of water effect, active carbon adsorption technology be make up the most ripe method of the problem of conventional hydraulic art is present it One.Active carbon adsorption technology has just been used to remove the smelly and taste in water early in the 1920s abroad.Activated carbon pair The removal of organic matter is mainly the suction-operated of internal various holes, thus the distribution of pores structures shape of activated carbon it to not With the removal effect of molecular size organic pollution.The internal void of activated carbon can be generally divided into macropore, mesoporous and micropore.It is living Property charcoal suction-operated depend on intermolecular force, the absorption that chemical bond force and electrostatic attraction are formed, the institute of material Changed automatically with producing concentration on two-phase interface, key be to be present between adsorbent and adsorbate these three are different Active force, these three active forces form respectively physical absorption, chemisorbed and exchange adsorption, and they constitute the suction of activated carbon Attached characteristic.
Through patent retrieval, the research using multistage activated carbon adsorption bed processing organic pollutants is less both at home and abroad.This Outside, for now, charcoal absorption application is primarily present natural macromolecular organic matter and small organic molecule competitive Adsorption, small Molecular organic polymerizate, which easily blocks activated carbon space, makes the regeneration difficulty of saturated activity charcoal, for natural macromolecular organic matter The problem of rate of adsorption is slow.Therefore design one kind is needed badly to be directed at the feasible effective charcoal absorption of variety classes organic matter Reason system, to better meet Organic Pollutants In Water process demand.
The content of the invention
Present invention technical problems to be solved first are to provide a kind of multistage activity based on selective absorption cleaning principle Charcoal adsorbs bed system, and its treatment effeciency is high, is applicable Some Organic Pollutants is removed, and different types of organic pollution can be entered Row selective absorption, while good regenerating active carbon efficiency is provided.
Technical scheme is used by the present invention solves above-mentioned technical problem:Multistage based on selective absorption cleaning principle Charcoal absorption bed system, including be arranged in the first activated carbon adsorption bed of sorption channel leading portion and be arranged in sorption channel back segment The second activated carbon adsorption bed, first activated carbon adsorption bed carries high meso-hole structure activated carbon, second activated carbon Adsorbent bed carries superelevation microcellular structure activated carbon, the high meso-hole structure activated carbon can adsorption cleaning natural macromolecular it is organic Thing, the superelevation microcellular structure activated carbon being capable of the artificial synthesized small organic molecules of adsorption cleaning.
While using above-mentioned technical proposal, the present invention can also be used or combined using technology further below Scheme:
The high meso-hole structure activated carbon is arranged closely in the first activated carbon adsorption bed with bulk form, and the superelevation is micro- Pore structure activated carbon is arranged closely in the second activated carbon adsorption bed with bulk form.
The superelevation microcellular structure activated carbon can suppress artificial synthesized small organic molecule and occur to gather under aerobic state Close reaction.
The BET specific surface area of the high meso-hole structure activated carbon is 1696 m2/g, and mesopore volume is 0.672 cm3/g, always Pore volume is 1.025 cm3/g, and mesoporous ratio is 65.6%.
The BET specific surface area of the superelevation microcellular structure activated carbon is 1476 m2/g, and micro pore volume is 0.683 cm3/g, Total pore volume is 0.841 cm3/g, and micropore ratio is 81.3%.
The multi-stage absorption system of the present invention by the way of multi-stage absorption, is specifically divided into leading portion during adsorption cleaning And back segment, leading portion carry out adsorption cleaning using high meso-hole structure activated carbon, high meso-hole structure activated carbon possesses net suitable for absorption Change the physicochemical properties of natural macromolecular organic matter, be capable of effective removal natural macromolecular organic pollution of selectivity, from And it effectively prevent competitive Adsorption of the natural macromolecular organic matter with artificial synthesized small organic molecule in back segment adsorbent bed and make With greatly improving adsorption efficiency of the back segment adsorbent bed for small organic molecule, back segment is entered using superelevation microcellular structure activated carbon Row adsorption cleaning, superelevation microcellular structure activated carbon can not only effectively remove artificial synthesized small molecule organic pollution, and living Property charcoal possessed superelevation micropore structure can effectively suppress artificial synthesized small organic molecule and be sent out under aerobic state Raw polymerisation, so as to substantially increase the regeneration efficiency of activated carbon.
Another technical problem to be solved by this invention is to provide the above-mentioned multistage based on selective absorption cleaning principle The preparation method of charcoal absorption bed system, the preparation method include preparing high meso-hole structure activated carbon and superelevation micropore first The step of structure-activity charcoal, the step of preparing high meso-hole structure activated carbon be:
(1)Anthracite is crushed, crosses 28-40 mesh sieves;Potassium hydroxide pellet is crushed;It is 1 according to mass ratio:4 will be smokeless Coal uniformly mixes with potassium hydroxide;The ratio of a ml deionized water is added according to every gram of potassium hydroxide simultaneously, by deionized water Add to anthracite and potassium hydroxide mixture, mixture is changed into pureed;
(2)Mixture is positioned in tubular type activation furnace, mixing placement 12 hours under 110 oC;
(3)Anthracite after placement is activated 2 hours under 800oC, and whole process is passed through nitrogen to ensure inert atmosphere, Specific nitrogen flow rate is maintained at 400ml/min;
(4)Then under argon atmosphere, gained activated carbon is heat-treated 20 hours under 900oC;
(5)Then the potassium hydroxide of the hydrochloric acid wash residual activated carbon surface of 5 mol/L concentration is utilized;Then using go from It is 6.5-7 that sub- water washs to pH repeatedly, prepares activated carbon;
(6)The activated carbon of preparation is dried under 105oC, crushed, packaging is put into stand-by in sealing container;
The physicochemical properties of obtained product are as shown in table 1.
Table 1
Prepare superelevation microcellular structure activated carbon the step of be:
(1)Anthracite is crushed, crosses 28-40 mesh sieves;Potassium hydroxide pellet is crushed;It is 1 according to mass ratio:2 will be smokeless Coal uniformly mixes with potassium hydroxide;The ratio of a ml deionized water is added according to every gram of potassium hydroxide simultaneously, by deionized water Add to anthracite and potassium hydroxide mixture, mixture is changed into pureed;
(2)Mixture is positioned in tubular type activation furnace, mixing placement 12 hours under 110 oC;
(3)Anthracite after placement is activated 2 hours under 650oC, and whole process is passed through nitrogen to ensure inert atmosphere, Specific nitrogen flow rate is maintained at 400ml/min;
(4)Then the potassium hydroxide of the hydrochloric acid wash residual activated carbon surface of 5 mol/L concentration is utilized;Then using go from It is 6.5-7 that sub- water washs to pH repeatedly, prepares activated carbon;
(5)The activated carbon of preparation is dried under 105oC, crushed, packaging is put into stand-by in sealing container;
The physicochemical properties of obtained product are as shown in table 2.
Table 2
After the above step is finished, respectively by obtained high meso-hole structure activated carbon and superelevation microcellular structure activated carbon with block The form of shape structure and compact arranged mode are respectively charged into the first activated carbon adsorption bed and the second activated carbon adsorption bed, then will First activated carbon adsorption bed and the second activated carbon adsorption bed are sequentially arranged in sorption channel, form the multistage charcoal absorption Bed system.
The beneficial effects of the invention are as follows:
1st, place the high meso-hole structure activated carbon of preparation in leading portion adsorbent bed, such a activated carbon it is mesoporous(20-500Å) Ratio reaches 66%, and because the molecular size of most natural macromolecular organic matters is between 20-60, therefore activated carbon is non- The absorption of natural macromolecular organic matter is very suitable for, secondly, the total acid-base value and zero potential of activated carbon surface can be with from table 1 It was found that activated carbon surface possesses considerable basic functionality, thus by the basic functionality of activated carbon surface with it is natural big Neutralization of acid with base between the acidic carboxypolymer of molecular organic, activated carbon can be effectively improved for natural macromolecular organic matter Suction-operated.By above-mentioned effect, activated carbon can be good at the natural macromolecular organic contamination in selective absorption water body Thing.Therefore, for water body when by multistage activated carbon adsorption bed, natural macromolecular organic pollution can be by the adsorbent bed of front end Activated carbon effectively removes.
2nd, water flows into back segment activated carbon adsorption bed after flowing through front end absorption, and the high micropore knot of preparation is placed in this section of adsorbent bed Structure activated carbon, its specific surface area reach 1476 m2/g, therefore it is small in water body so as to effectively remove to provide enough adsorption potentials Molecular organic pollutants.Further, since the micropore of such a activated carbon(0-20Å)Ratio reaches 81%, therefore can ensure absolutely mostly The adsorbed organic pollutions of number are all unimolecule state, and polymerisation and the polymer that is formed due to excessive size then not It can be tightly held by activated carbon, so as to effectively suppress generation of the polymerisation in activated carbon surface, and it is organic due to unimolecule state Pollutant is easy to be resolved out during regenerating active carbon, therefore can greatly improve activity using such a activated carbon The regeneration efficiency of charcoal, the cost performance that increase activated carbon uses.
3rd, the present invention has the advantages for the treatment of effeciency height, reduced investment, operation standing charges are low, energy consumption is low, applied widely, It is that also can preferably carry out selectivity to complete adsorption cleaning by batch especially when plurality of organic pollutants in water be present.
Brief description of the drawings
Fig. 1 is the preparation flow figure of leading portion adsorbent bed carrying activated carbon.
Fig. 2 is the preparation flow figure of back segment adsorbent bed carrying activated carbon.
Fig. 3 is the structural representation of the multistage charcoal absorption bed system of the present invention.
Embodiment
Embodiment 1, prepare high meso-hole structure activated carbon.
As shown in figure 1, the high mesoporous activated carbon of suitable natural macromolecular organic matter absorption uses ball milling using anthracite as raw material Machine crushes anthracite, crosses 28-40 mesh sieves, the raw material of fineness needed for collection.Granular sodium hydroxide is ground into afterwards powdered. It is 1 according still further to mass ratio:4 uniformly mix anthracite with potassium hydroxide.One milliliter is added according to every gram of potassium hydroxide simultaneously to go The ratio of ionized water, deionized water is added to anthracite and potassium hydroxide mixture, mixture is changed into pureed.Then will be mixed Compound is positioned in tubular type activation furnace, mixing placement 12 hours under 110 oC.Anthracite after placement is activated under 800oC 2 hours, and whole process is passed through nitrogen to ensure inert atmosphere, and specific nitrogen flow rate is maintained at 400ml/min.Then in argon atmospher Under enclosing, gained activated carbon is heat-treated 20 hours under 900oC.Then the hydrochloric acid wash residual activated carbon of 5 mol/L concentration is utilized The potassium hydroxide on surface, and it is 6.5-7 to be washed repeatedly to pH using deionized water.Activated carbon will be prepared afterwards under 105oC Drying, then obtained activated carbon is crushed, packaging is put into stand-by in sealing container.
Embodiment 2, prepare superelevation microcellular structure activated carbon.
As shown in Fig. 2 the high microporous activated carbon of suitable synthesized micromolecule organic matter absorption uses ball milling using anthracite as raw material Machine crushes anthracite, crosses 28-40 mesh sieves, the raw material of fineness needed for collection.Granular sodium hydroxide is ground into afterwards powdered. It is 1 according still further to mass ratio:2 uniformly mix anthracite with potassium hydroxide.One milliliter is added according to every gram of potassium hydroxide simultaneously to go The ratio of ionized water, deionized water is added to anthracite and potassium hydroxide mixture, mixture is changed into pureed.Then will be mixed Compound is positioned in tubular type activation furnace, mixing placement 12 hours under 110 oC.Anthracite after placement is activated under 650oC 2 hours, and whole process is passed through nitrogen to ensure inert atmosphere, and specific nitrogen flow rate is maintained at 400ml/min.Then 5 are utilized The potassium hydroxide of the hydrochloric acid wash residual activated carbon surface of mol/L concentration, and it is 6.5- to be washed repeatedly to pH using deionized water 7.Activated carbon will be prepared afterwards to dry under 105oC, then obtained activated carbon will be crushed, and packaging, which is put into sealing container, to be treated With.
Embodiment 3, the multistage charcoal absorption bed system based on selective absorption cleaning principle.
The multistage charcoal absorption bed system of the present invention includes the first activated carbon adsorption bed 1 for being arranged in sorption channel leading portion With the second activated carbon adsorption bed 2 for being arranged in sorption channel back segment, first activated carbon adsorption bed 1 carries high meso-hole structure Activated carbon 3, second activated carbon adsorption bed 2 carry superelevation microcellular structure activated carbon 4, the high meso-hole structure activated carbon 3 Can adsorption cleaning natural macromolecular organic matter, the superelevation microcellular structure activated carbon 4 being capable of artificial synthesized small point of adsorption cleaning Sub- organic matter.The high meso-hole structure activated carbon 3 is arranged closely in the first activated carbon adsorption bed 1 with bulk form, described super High microcellular structure activated carbon 4 is arranged closely in the second activated carbon adsorption bed 2 with bulk form.The superelevation microcellular structure activity Charcoal 4 can also suppress artificial synthesized small organic molecule and polymerisation occurs under aerobic state.
The physicochemical properties of the high meso-hole structure activated carbon 3 are as shown in table 1.
Table 1
The physicochemical properties of the superelevation microcellular structure activated carbon 4 are as shown in table 2.
Table 2
BET specific surface area (m2/g) Micro pore volume (cm3/g) Total pore volume (cm3/g) Micropore ratio (%)
Activated carbon 1476 0.683 0.841 81.3
As shown in figure 3, the water body containing plurality of organic pollutants after conventional processing technique is handled, is flowed into based on selection The multistage charcoal absorption bed system of property adsorption cleaning principle.Multistage charcoal absorption bed system is in place in the first activity of leading portion Place the high meso-hole structure activated carbon 3 of preparation in charcoal adsorbent bed 1, such a activated carbon it is mesoporous(20-500Å)Ratio reaches 66%, Because the molecular size of most natural macromolecular organic matters is between 20-60, therefore activated carbon is very suitable for naturally The absorption of larger molecular organicses, secondly as activated carbon possesses the total alkalinity and zero potential on high surface, so activated carbon surface Possesses considerable basic functionality, therefore the acidity for the basic functionality and natural macromolecular organic matter for passing through activated carbon surface Neutralization of acid with base between carboxyl, suction-operated of the activated carbon for natural macromolecular organic matter can be effectively improved.Pass through Above-mentioned effect, activated carbon can be good at the natural macromolecular organic pollution in selective absorption water body.Therefore, day in water body Right macromolecular organic pollution can be trapped effective removal in the adsorbent bed of front end.
Subsequent water body flows into the second activated carbon adsorption bed 2 for being arranged in back segment after front end is adsorbed, and is put in this section of adsorbent bed The high microcellular structure activated carbon 4 of the suitable synthesized micromolecule organic matter absorption of preparation is put, its specific surface area reaches 1476 m2/g, Therefore enough adsorption potentials can be provided so as to effectively remove the small molecule organic pollution in water body.Further, since such a activity The micropore of charcoal(0-20Å)Ratio reaches 81%, therefore can ensure that most adsorbed organic pollutions are all unimolecule shape State, and polymerisation and the polymer that is formed be because excessive size can not be then tightly held by activated carbon, so as to effectively suppress polymerization React the generation in activated carbon surface.And due to the organic pollution of unimolecule state be easy to during regenerating active carbon by Parse, therefore the regeneration efficiency of activated carbon can greatly be improved using such a activated carbon, the property that increase activated carbon uses Valency ratio.
Finally, water body safety dumping after the selective absorption purification of multistage activated carbon adsorption bed.
Arrow represents water (flow) direction in figure.

Claims (4)

1. the multistage charcoal absorption bed system based on selective absorption cleaning principle, it is characterised in that:The absorption bed system Including being arranged in the first activated carbon adsorption bed of sorption channel leading portion and being arranged in the second charcoal absorption of sorption channel back segment Bed, first activated carbon adsorption bed carry high meso-hole structure activated carbon, the activated carbon table of first activated carbon adsorption bed Face possesses basic functionality, and second activated carbon adsorption bed carries superelevation microcellular structure activated carbon, the high meso-hole structure Activated carbon can adsorption cleaning natural macromolecular organic matter, the superelevation microcellular structure activated carbon can adsorption cleaning it is artificial synthesized Small organic molecule;The BET specific surface area of the superelevation microcellular structure activated carbon is 1476m2/ g, micro pore volume 0.683cm3/ G, total pore volume 0.841cm3/ g, micropore ratio are 81.3%, and the BET specific surface area of the high meso-hole structure activated carbon is 1696m2/ g, mesopore volume 0.672cm3/ g, total pore volume 1.025cm3/ g, mesoporous ratio are 65.6%.
2. the multistage charcoal absorption bed system based on selective absorption cleaning principle, its feature exist as claimed in claim 1 In the high meso-hole structure activated carbon is arranged closely in the first activated carbon adsorption bed with bulk form, the superelevation micropore knot Structure activated carbon is arranged closely in the second activated carbon adsorption bed with bulk form.
3. the multistage charcoal absorption bed system based on selective absorption cleaning principle, its feature exist as claimed in claim 1 In the superelevation microcellular structure activated carbon can suppress artificial synthesized small organic molecule and polymerization occurs under aerobic state instead Should.
4. the preparation method of the multistage charcoal absorption bed system based on selective absorption cleaning principle, the preparation method are used for The multistage charcoal absorption bed system based on selective absorption cleaning principle any one of claim 1-3 is prepared, its It is characterised by, methods described including the step of preparing high meso-hole structure activated carbon and superelevation microcellular structure activated carbon, is prepared first The step of high meso-hole structure activated carbon is,
(1)Anthracite is crushed, crosses 28-40 mesh sieves;Potassium hydroxide pellet is crushed;It is 1 according to mass ratio:4 by anthracite with Potassium hydroxide uniformly mixes;The ratio of a ml deionized water is added according to every gram of potassium hydroxide simultaneously, deionized water is added To anthracite and potassium hydroxide mixture, mixture is set to be changed into pureed;
(2)Mixture is positioned in tubular type activation furnace, mixing placement 12 hours at 110 DEG C;
(3)Anthracite after placement is activated 2 hours at 800 DEG C, and whole process is passed through nitrogen to ensure inert atmosphere, specifically Nitrogen flow rate is maintained at 400ml/min;
(4)Then under argon atmosphere, gained activated carbon is heat-treated 20 hours at 900 DEG C;
(5)Then the potassium hydroxide of the hydrochloric acid wash residual activated carbon surface of 5mol/L concentration is utilized;Then deionized water is utilized It is 6.5-7 to wash repeatedly to pH, prepares activated carbon;
(6)The activated carbon of preparation is dried at 105 DEG C, crushed, packaging is put into stand-by in sealing container;
Prepare superelevation microcellular structure activated carbon the step of be:
(1)Anthracite is crushed, crosses 28-40 mesh sieves;Potassium hydroxide pellet is crushed;It is 1 according to mass ratio:2 by anthracite with Potassium hydroxide uniformly mixes;The ratio of a ml deionized water is added according to every gram of potassium hydroxide simultaneously, deionized water is added To anthracite and potassium hydroxide mixture, mixture is set to be changed into pureed;
(2)Mixture is positioned in tubular type activation furnace, mixing placement 12 hours at 110 DEG C;
(3)Anthracite after placement is activated 2 hours at 650 DEG C, and whole process is passed through nitrogen to ensure inert atmosphere, specifically Nitrogen flow rate is maintained at 400ml/min;
(4)Then the potassium hydroxide of the hydrochloric acid wash residual activated carbon surface of 5mol/L concentration is utilized;Then deionized water is utilized It is 6.5-7 to wash repeatedly to pH, prepares activated carbon;
(5)The activated carbon of preparation is dried at 105 DEG C, crushed, packaging is put into stand-by in sealing container;
After the above step is finished, obtained high meso-hole structure activated carbon and superelevation microcellular structure activated carbon are tied with bulk respectively The form of structure and compact arranged mode are respectively charged into the first activated carbon adsorption bed and the second activated carbon adsorption bed, then by first Activated carbon adsorption bed and the second activated carbon adsorption bed are sequentially arranged in sorption channel, form the multistage activated carbon adsorption bed system System.
CN201510745137.4A 2015-11-05 2015-11-05 Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof Active CN105253946B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510745137.4A CN105253946B (en) 2015-11-05 2015-11-05 Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510745137.4A CN105253946B (en) 2015-11-05 2015-11-05 Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof

Publications (2)

Publication Number Publication Date
CN105253946A CN105253946A (en) 2016-01-20
CN105253946B true CN105253946B (en) 2018-04-03

Family

ID=55093950

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510745137.4A Active CN105253946B (en) 2015-11-05 2015-11-05 Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof

Country Status (1)

Country Link
CN (1) CN105253946B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112456679A (en) * 2020-11-18 2021-03-09 安徽汇泽通环境技术有限公司 Device and method for treating disinfection byproducts by mesoporous carbon reinforced carbon sand filter
CN112661233A (en) * 2020-12-22 2021-04-16 北京元泰达环保科技有限公司 System and process for removing heavy metal ions in water
CN114890495B (en) * 2022-05-11 2023-03-21 中国科学院生态环境研究中心 Method for determining competitive organic matters influencing activated carbon adsorption of micropollutants in water

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101439857A (en) * 2008-12-11 2009-05-27 武汉科技大学 Mesoporous activated carbon and preparation process thereof
CN101767891A (en) * 2008-12-29 2010-07-07 上海轻工业研究所有限公司 Integrative wastewater treatment device of ozone and active carbon
CN101993068A (en) * 2010-10-27 2011-03-30 北京化工大学 Preparation method of porous structured active carbon
JP5249983B2 (en) * 2010-04-05 2013-07-31 株式会社エヌ・ティ・ティ・ドコモ Radio base station apparatus, mobile terminal apparatus and cell selection method
CN103626175A (en) * 2013-12-17 2014-03-12 中国科学院新疆理化技术研究所 Method for preparing activated carbon from coal tar residues and application thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5249983A (en) * 1975-10-20 1977-04-21 Nippon Soda Co Ltd Adsorption method with active carbon

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101439857A (en) * 2008-12-11 2009-05-27 武汉科技大学 Mesoporous activated carbon and preparation process thereof
CN101767891A (en) * 2008-12-29 2010-07-07 上海轻工业研究所有限公司 Integrative wastewater treatment device of ozone and active carbon
JP5249983B2 (en) * 2010-04-05 2013-07-31 株式会社エヌ・ティ・ティ・ドコモ Radio base station apparatus, mobile terminal apparatus and cell selection method
CN101993068A (en) * 2010-10-27 2011-03-30 北京化工大学 Preparation method of porous structured active carbon
CN103626175A (en) * 2013-12-17 2014-03-12 中国科学院新疆理化技术研究所 Method for preparing activated carbon from coal tar residues and application thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
用无烟煤制备高比表面积活性炭的研究;李东艳等;《稀有金属材料与工程》;20070831;第36卷(第S1期);第583-586页 *

Also Published As

Publication number Publication date
CN105253946A (en) 2016-01-20

Similar Documents

Publication Publication Date Title
CN104289185B (en) The granule filter material and preparation method thereof of heavy metal in a kind of Adsorption water
CN106745645B (en) Preparation method and application of nano zero-valent iron composite material
Wang et al. Adsorption of heavy metal onto biomass-derived activated carbon
CN103041787B (en) Preparation method of crosslinked chitosan-manganese dioxide composite adsorbing material
Xu et al. Nitrate adsorption by stratified wheat straw resin in lab-scale columns
CN101314123B (en) Magnetic biological adsorption agent and preparation method thereof
CN109608655B (en) Difunctional group MOFs material and preparation method and application thereof
CN110508243B (en) Preparation method and application of biomass-based porous carbon loaded iron floc adsorption material
CN105253946B (en) Multistage charcoal absorption bed system based on selective absorption cleaning principle and preparation method thereof
CN105413660A (en) Nanosilicon dioxide structure-based high-heavy metal ion adsorption chelating agent and preparation method thereof
CN111298769B (en) Preparation method and application of lanthanum-modified sycamore biochar
CN105771916A (en) Bentonite particles, bentonite particle adsorption column and method for removing phosphorus in natural water body
CN111889077A (en) Preparation of modified magnetic zeolite imidazole framework material and adsorption of trace amount of ceftazidime in water
CN104971687A (en) Efficient compound iron-based phosphorous-removing adsorbent as well as preparation method, application method and regeneration method thereof
CN104128161B (en) A kind of amino modified activated coke heavy metal absorbent and preparation method thereof
CN108970589B (en) Hydrotalcite-based composite gel ball and preparation method and application thereof
CN107376857A (en) It is a kind of to be used to adsorb compound hydrogel material of heavy metal and preparation method thereof
CN105944681A (en) Preparation method and application of potassium carboxylate base porous carbon material
CN102614826B (en) Modified expanded perlite for treating low-concentration ammonia-nitrogen wastewater and wastewater treatment method
CN100582023C (en) Method for removing lead from industrial wastewater with magnetic biological adsorption agent
CN112007694A (en) Embedded catalyst, preparation method thereof and application thereof in wastewater denitrification
CN104761018A (en) Method for carrying out water treatment by using active carbon
CN102040291B (en) Claystone-activated carbon fiber water purification and filtration system
CN114471466B (en) Amino-modified corncob-derived nitrogen-doped nano zero-valent iron/biochar as well as preparation method and application thereof
CN113304734B (en) Preparation method, product and application of modified lignite

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant