CN103801259B - A kind of flyash composite filter material and its preparation method and application - Google Patents

A kind of flyash composite filter material and its preparation method and application Download PDF

Info

Publication number
CN103801259B
CN103801259B CN201410029547.4A CN201410029547A CN103801259B CN 103801259 B CN103801259 B CN 103801259B CN 201410029547 A CN201410029547 A CN 201410029547A CN 103801259 B CN103801259 B CN 103801259B
Authority
CN
China
Prior art keywords
flyash
composite filter
filter material
silicate
silica
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.)
Expired - Fee Related
Application number
CN201410029547.4A
Other languages
Chinese (zh)
Other versions
CN103801259A (en
Inventor
葛海卿
尚百雨
马雪英
李建勇
程东惠
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.)
Beijing Union Green Technology Group Co ltd
Original Assignee
BEIJING AURORA ENVIRONMENTAL PROTECTION SCITECH INSTITUTE Co 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 BEIJING AURORA ENVIRONMENTAL PROTECTION SCITECH INSTITUTE Co Ltd filed Critical BEIJING AURORA ENVIRONMENTAL PROTECTION SCITECH INSTITUTE Co Ltd
Priority to CN201410029547.4A priority Critical patent/CN103801259B/en
Publication of CN103801259A publication Critical patent/CN103801259A/en
Application granted granted Critical
Publication of CN103801259B publication Critical patent/CN103801259B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The invention provides a kind of flyash composite filter material, it is mixed with by particle diameter 120-160 object flyash, atlapulgite, silica and silicate to form.Flyash composite filter material of the present invention is a kind of surperficial porcelain and has the material of a large amount of hole, has the adsorptivity of flyash and the adsorptivity of micropore thing simultaneously, and has flocculability; Polluter is had to the effect of adsorption-decomposition function simultaneously, the disposal ability to pollutant can be improved significantly.The present invention also provides the method for the flyash composite filter material described in preparation, and the method technique is simple, and can not produce secondary pollution.The present invention also provides described flyash composite filter material as the application of water treatment agent in sewage purification.Flyash composite filter material of the present invention can be used for integrated treatment municipal sewage; Treatment effect is good, and removal efficiency is more than 99%, and the flco of generation is few, and precipitation is fast.

Description

A kind of flyash composite filter material and its preparation method and application
Technical field
The present invention relates to a kind of inorganic composite materials, especially a kind of flyash composite filter material, and preparation method thereof and application in sewage purification.
Technical background
Flyash is the thin ash collected from the flue gas after coal combustion, is the primary solids discarded object that coal-burning power plant discharges.Flyash is one of industrial residue that the current discharge capacity of China is larger, and along with the development of power industry, the flyash discharge capacity of coal-burning power plant increases year by year, and a large amount of flyash does not add process, will produce airborne dust, atmosphere pollution; River can be caused to silt up if enter water system, and toxic chemical substance wherein also can work the mischief to human body and biology.But the specific surface of flyash is large, and particle diameter is little, between 0.1-10 μm, there is a lot of micropore, can be a lot of with the surperficial courtyard of adsorption molecule effect in hole, superpose with avoiding the produced absorption field of force at micropore internal face, absorption affinity strengthens, and can reach absorption at low pressures saturated.On the other hand, in flyash molecular structure, there is a large amount of Si-O and AL-O active groups, can combine with adsorbate chemical bond or ion, thus produce absorption.Its suction-operated comprises physical absorption and chemisorbed two aspect, can suspension, coloring matter in absorption effluent.Reduce colourity, adsorb and remove the aerobic substance in decontaminated water.
Summary of the invention
Technical problem to be solved by this invention is to provide a kind of sewage treating material, and raw material sources are wide, and cost is low, stable performance.This technology can make turbidity of sewage effectively be reduced to can the level of discharge water, does not have secondary pollution.
Above-mentioned purpose of the present invention is achieved through the following technical solutions:
There is provided a kind of flyash composite filter material, it is mixed with by particle diameter 120-160 object flyash, atlapulgite, silica and silicate to form.
The preferred flyash composite filter material of the present invention, each raw material components is counted by weight: flyash 60-80 part, atlapulgite 5-15 part, silica 5-20 part, silicate 5 parts.
The present invention is preferred flyash composite filter material further, and each raw material components is counted by weight: flyash 65-75 part, atlapulgite 10-15 part, silica 5 ~ 15 parts, silicate 5 parts.
The most preferred flyash composite filter material of the present invention, each raw material components is counted by weight: 72 parts, flyash, atlapulgite 10 parts, silica 13 parts, silicate 5 parts.
Described silica preferred size was the powder after 200 order-1000 mesh sieves.
The preferred aluminium magensium silicate of described silicate, aluminosilicate or polysilicate, most preferably polysilicate.
The present invention also provides the method for the flyash composite filter material described in preparation, comprises the following steps:
1) first soaked with clear water in sedimentation basin by flyash, removing surface dust, pull flyash out, draining dries;
2) flyash of step 1) process is added obtained fly ash grain in comminutor;
3) to step 2) add atlapulgite, silica and silicate in described ratio in the fly ash grain that obtains and prepare hybrid particles;
4) be dispersed in water by the hybrid particles that step 3) obtains, the addition of water accounts for the 15%-20% of total quality of material, forms solution, add expanding agent, be uniformly mixed rear dropping ethyl orthosilicate, reaction 3-5 hour, filter, vacuum drying obtains preliminary composite filter material;
5) preliminary composite filter material step 4) obtained is dried and is removed moisture, then roasting 3-4 hour at 200-250 DEG C in 3-5 hour at 120-160 DEG C, i.e. obtained described flyash composite filter material.
Expanding agent described in step 4) is preferably 3,4,5-trimethoxybenzoic acid, and addition is 2% of described liquor capacity.
Ethyl orthosilicate addition described in step 4) is preferably 0.5% of described liquor capacity.
The present invention also provides described flyash composite filter material as the application of water treatment agent in sewage purification.
In composite filter material obtained by the inventive method, flyash forms the particle that particle diameter is less than 6 millimeters, described atlapulgite, silica and silicate are wrapped in the surface of flyash and through sintering the porcelain layer forming adsorptivity micropore, therefore flyash composite filter material of the present invention is a kind of surperficial porcelain and has the material of a large amount of hole.Compared with prior art, flyash composite filter material of the present invention has following several respects beneficial effect:
1. composite filter material of the present invention has the adsorptivity of flyash and the adsorptivity of micropore thing simultaneously, and has flocculability.The active material of flocculating property is solidificated in micropore, can slow releasing, and make the oxidized degraded of pollutant be adsorbed in micropore, the shortcoming of luxus consumption flocculant when avoiding disposing of sewage, can save the consumption of flocculant.
2. composite filter material of the present invention, is fired by flyash, silicate and atlapulgite compound and forms, have triplen, polluter is had to the effect of adsorption-decomposition function simultaneously, significantly enhance the pollutant disposal ability of flyash.
3. the technique prepared of composite filter material of the present invention is simple, and can not produce secondary pollution.
4. combined filtration process range of the present invention is wide, can integrated treatment municipal sewage; Treatment effect is good, and removal efficiency is more than 99%, and the flco of generation is few, and precipitation is fast.
Detailed description of the invention
Embodiment 1
Soaked with clear water in sedimentation basin by flyash, removing surface dust, pull flyash out, draining dries;
The flyash processed is added obtained fly ash grain in comminutor, form the particle that particle diameter is less than 6 millimeters;
Each raw material is mixed (kilogram) according to following weight:
Flyash 65, atlapulgite 10, the silica 20 crossing 200 order-500 mesh sieve granularities, polysilicate 5 prepare hybrid particles;
Hybrid particles is dispersed in water, the addition of water accounts for 15% of total quality of material, form solution, 3,4,5-trimethoxybenzoic acid is added by the amount of described liquor capacity 2%, be uniformly mixed the ethyl orthosilicate of rear dropping liquor capacity 0.5%, react 4 hours, filter, vacuum drying obtains preliminary composite filter material;
Preliminary composite filter material is dried and within 3 hours, is removed moisture, then roasting 3 hours at 250 DEG C at 120 DEG C, i.e. obtained described flyash composite filter material 1.
Embodiment 2
Soaked with clear water in sedimentation basin by flyash, removing surface dust, pull flyash out, draining dries;
The flyash processed is added obtained fly ash grain in comminutor, form the particle that particle diameter is less than 4 millimeters;
Each raw material is mixed (kilogram) according to following weight:
Flyash 72, atlapulgite 8, the silica 15 crossing 500-800 mesh sieve granularity, aluminosilicate 5 prepare hybrid particles
Hybrid particles is dispersed in water, the addition of water accounts for 20% of total quality of material, form solution, 3,4,5-trimethoxybenzoic acid is added by the amount of described liquor capacity 2%, be uniformly mixed the ethyl orthosilicate of rear dropping liquor capacity 0.5%, react 4 hours, filter, vacuum drying obtains preliminary composite filter material;
Preliminary composite filter material is dried and within 4 hours, is removed moisture, then roasting 4 hours at 200 DEG C at 160 DEG C, i.e. obtained described flyash composite filter material 2.
Embodiment 3
Soaked with clear water in sedimentation basin by flyash, removing surface dust, pull flyash out, draining dries;
The flyash processed is added obtained fly ash grain in comminutor, form the particle that particle diameter is less than 4 millimeters;
Each raw material is mixed (kilogram) according to following weight:
Flyash 70, atlapulgite 12, the silica 13 crossing 800-1000 mesh sieve granularity, polysilicate 5 prepare hybrid particles
Hybrid particles is dispersed in water, the addition of water accounts for 20% of total quality of material, form solution, 3,4,5-trimethoxybenzoic acid is added by the amount of described liquor capacity 2%, be uniformly mixed the ethyl orthosilicate of rear dropping liquor capacity 0.5%, react 5 hours, filter, vacuum drying obtains preliminary composite filter material;
Preliminary composite filter material is dried and within 5 hours, is removed moisture, then roasting 4 hours at 220 DEG C at 140 DEG C, i.e. obtained described flyash composite filter material 3.
Experimental example
1. concrete-agitating station equipment washing water Treatment for Reuse.Trucd mixer is scrubbed after being separated sandstone with water aggregate separated machine, introduce tank, add the composite water disposal agent of the embodiment 1 of process water yield 2-3%.Due to the Adsorption and flocculation effect of composite, pulp-water deposits flocculation very soon, makes water become simple and easy with being separated of mud.The washing water water examination of reclaiming meets the reinforcement of concrete water quality standard, and testing result is in table 1:
Table 1
2. adopt the surface water of embodiment 2 pairs of organic micro-pollutions to process, SDBS(DBSA man) content is 2.1mg/l, the composite water disposal agent of 3% is dropped in 1L contaminant water, add 1.5mg ozone simultaneously, oscillation treatment is after 40 minutes, SDBS residual volume is only 0.039mg/l, and degradation rate reaches 98%.
3. the process of city domestic sewage, adopts embodiment 3, experiment condition: regulate the pH of water inlet at 7-8, temperature is at 24-30 DEG C, and filler dosage 10%, in sewage, major pollutants clearance is as follows: COD93.6%, NH 4-N92.7%, TN67.4%, TP52.5%.
The invention provides a kind of flyash composite filter material, it is mixed with by particle diameter 120-160 object flyash, atlapulgite, silica and silicate to form.Flyash composite filter material of the present invention is a kind of surperficial porcelain and has the material of a large amount of hole, has the adsorptivity of flyash and the adsorptivity of micropore thing simultaneously, and has flocculability; Polluter is had to the effect of adsorption-decomposition function simultaneously, the disposal ability to pollutant can be improved significantly.The present invention also provides the method for the flyash composite filter material described in preparation, and the method technique is simple, and can not produce secondary pollution.The present invention also provides described flyash composite filter material as the application of water treatment agent in sewage purification.Flyash composite filter material of the present invention can be used for integrated treatment municipal sewage; Treatment effect is good, and removal efficiency is more than 99%, and the flco of generation is few, and precipitation is fast.

Claims (8)

1. a flyash composite filter material, is characterized in that: it is mixed with by particle diameter 120-160 object flyash, atlapulgite, silica and silicate to form; Each raw material components is counted by weight: flyash 60-80 part, atlapulgite 5-15 part, silica 5-20 part, silicate 5 parts;
The described silica powder that to be granularity be after 200 order-1000 mesh sieves;
Described silicate is aluminium magensium silicate, aluminosilicate or polysilicate.
2. flyash composite filter material according to claim 1, is characterized in that: each raw material components is counted by weight: flyash 65-75 part, atlapulgite 10-15 part, silica 5-15 part, silicate 5 parts.
3. flyash composite filter material according to claim 1, is characterized in that: each raw material components is counted by weight: 72 parts, flyash, atlapulgite 10 parts, silica 13 parts, silicate 5 parts.
4. flyash composite filter material according to claim 1, is characterized in that: described silicate is polysilicate.
5. prepare the method for flyash composite filter material according to claim 1, comprise the following steps:
1) first soaked with clear water in sedimentation basin by flyash, removing surface dust, pull flyash out, draining dries;
2) by step 1) flyash that processed adds obtained fly ash grain in comminutor;
3) to step 2) add atlapulgite, silica and silicate in described ratio in the fly ash grain that obtains and prepare hybrid particles;
4) by step 3) hybrid particles that obtains is dispersed in water, and the addition of water accounts for the 15%-20% of total quality of material, forms solution, add expanding agent, be uniformly mixed rear dropping ethyl orthosilicate, reaction 3-5 hour, filter, vacuum drying obtains preliminary composite filter material;
5) by step 4) the preliminary composite filter material that obtains dries and removes moisture, then roasting 3-4 hour at 200-250 DEG C in 3-5 hour, be i.e. obtained described flyash composite filter material at 120-160 DEG C.
6. method according to claim 5, is characterized in that: step 4) described expanding agent is 3,4,5-trimethoxybenzoic acid, addition is 2% of described liquor capacity.
7. method according to claim 5, is characterized in that: step 4) described in ethyl orthosilicate addition be 0.5% of described liquor capacity.
8. flyash composite filter material according to claim 1 is as the application of water treatment agent in sewage purification.
CN201410029547.4A 2014-01-22 2014-01-22 A kind of flyash composite filter material and its preparation method and application Expired - Fee Related CN103801259B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410029547.4A CN103801259B (en) 2014-01-22 2014-01-22 A kind of flyash composite filter material and its preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410029547.4A CN103801259B (en) 2014-01-22 2014-01-22 A kind of flyash composite filter material and its preparation method and application

Publications (2)

Publication Number Publication Date
CN103801259A CN103801259A (en) 2014-05-21
CN103801259B true CN103801259B (en) 2015-12-02

Family

ID=50698933

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410029547.4A Expired - Fee Related CN103801259B (en) 2014-01-22 2014-01-22 A kind of flyash composite filter material and its preparation method and application

Country Status (1)

Country Link
CN (1) CN103801259B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105561732B (en) * 2015-12-17 2018-09-04 山东省环境保护科学研究设计院 A kind of exhaust gas device for deep cleaning
CN105435734B (en) * 2015-12-17 2018-08-07 济南正骐生物科技有限公司 A kind of Combined gas purifier
CN105999847A (en) * 2016-06-28 2016-10-12 安徽国能亿盛环保科技有限公司 Filter material for sewage purification and preparation method thereof
CN106268693A (en) * 2016-09-08 2017-01-04 合肥智慧殿投资管理有限公司 A kind of filtering material for sewage disposal and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1611450A (en) * 2003-10-31 2005-05-04 中国石油化工股份有限公司 Waste water purifying agent, and its preparing method and use
US20070210006A1 (en) * 2006-03-10 2007-09-13 Council Of Scientific And Industrial Research Surface-Modified Zeolite and Process for Synthesis Thereof for Sequestration of Anions
CN101239748A (en) * 2007-02-05 2008-08-13 冯英昌 Coal ash activation chemical synthesis technique, preparation of fast flocculant by applying the coal ash and use thereof
CN101274172A (en) * 2007-12-27 2008-10-01 江苏正本净化节水科技实业有限公司 Composite filtering material for activating and regenerating coal ash and production method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1611450A (en) * 2003-10-31 2005-05-04 中国石油化工股份有限公司 Waste water purifying agent, and its preparing method and use
US20070210006A1 (en) * 2006-03-10 2007-09-13 Council Of Scientific And Industrial Research Surface-Modified Zeolite and Process for Synthesis Thereof for Sequestration of Anions
CN101239748A (en) * 2007-02-05 2008-08-13 冯英昌 Coal ash activation chemical synthesis technique, preparation of fast flocculant by applying the coal ash and use thereof
CN101274172A (en) * 2007-12-27 2008-10-01 江苏正本净化节水科技实业有限公司 Composite filtering material for activating and regenerating coal ash and production method thereof

Also Published As

Publication number Publication date
CN103801259A (en) 2014-05-21

Similar Documents

Publication Publication Date Title
US20220126267A1 (en) Co-pyrolyzed sludge biochar modified by lanthanum carbonate, preparation method and use thereof
CN102190345B (en) Method for enriching low-concentration heavy metal in water by recyclable magnesium hydroxide adsorbent
Nie et al. Novel recycling of incinerated sewage sludge ash (ISSA) and waste bentonite as ceramsite for Pb-containing wastewater treatment: Performance and mechanism
CN103801259B (en) A kind of flyash composite filter material and its preparation method and application
CN109482135B (en) Preparation method and application of calcium silicate adsorption material
CN110586031A (en) Preparation method of modified sludge carbon material
CN104722282B (en) A kind of synthetic method of the Fly ash bead magnetic adsorbent of Chitosan-coated
CN104888717A (en) Modified vermiculite mercury removal adsorbent, preparation method and application thereof
CN108889280A (en) A kind of preparation method of flyash-chitosan composite particle adsorbent material
CN107473467A (en) A kind of method of hexavalent chromium in Adsorption industrial wastewater
CN113786804B (en) Preparation method and application of magnetic porous composite material for adsorbing heavy metals
CN108067185A (en) A kind of preparation of high-efficient sewage water treatment absorbent and production method
CN114213140B (en) Coal gangue-based ceramsite for phosphorus adsorption, preparation method thereof and water treatment equipment
CN106345398A (en) Preparation method of modified coal ash adsorbent
CN103263891A (en) Method for preparing modified fly ash for effectively treating heavy metal waste water
KR101420498B1 (en) The covering material development for purifying the sea polluted sediments and using thereof
Qin et al. Role of minerals in mushroom residue on its adsorption capability to Cd (II) from aqueous solution
CN115624952B (en) Novel carbon material and preparation method and application thereof
CN108579670B (en) Method for removing phosphorus by using argil
CN102327893B (en) Material for removing lead in heavy-metal soil leacheate as well as preparation method and application thereof
CN102872805A (en) Composite adsorbing material for removing heavy chromate in water and preparation method thereof
CN108295810B (en) Preparation and application of nano-pore carbon-calcium composite material for quickly and efficiently removing organic pollutants
CN105692771A (en) Material for treating wastewater containing heavy metal
CN112844303A (en) Water purification sludge/sodium silicate composite adsorbent, preparation method thereof and application thereof in treating ammonia nitrogen in water body
Li et al. Distribution and speciation of heavy metals in two different sludge composite conditioning and deep dewatering processes

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
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20201028

Address after: 102200 8222, floor 2, building 1, east of Gulou South Street, Chengbei street, Changping District, Beijing

Patentee after: Beijing union Green Technology Group Co.,Ltd.

Address before: 100080, room 9, No. 1708 West Fourth Ring Road, Haidian District, Beijing

Patentee before: BEIJING AURORA ENVIRONMENTAL PROTECTION SCITECH INSTITUTE Co.,Ltd.

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: 20151202