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 PDFInfo
- 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
Links
- 239000010881 fly ash Substances 0.000 title claims abstract description 80
- 239000000463 material Substances 0.000 title claims abstract description 55
- 239000002131 composite material Substances 0.000 title claims abstract description 49
- 238000002360 preparation method Methods 0.000 title abstract description 6
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000002245 particle Substances 0.000 claims abstract description 23
- BPQQTUXANYXVAA-UHFFFAOYSA-N Orthosilicate Chemical compound [O-][Si]([O-])([O-])[O-] BPQQTUXANYXVAA-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 18
- 238000000034 method Methods 0.000 claims abstract description 17
- 239000010865 sewage Substances 0.000 claims abstract description 13
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 10
- -1 atlapulgite Substances 0.000 claims abstract description 6
- 238000000746 purification Methods 0.000 claims abstract description 5
- SJSOFNCYXJUNBT-UHFFFAOYSA-N 3,4,5-trimethoxybenzoic acid Chemical group COC1=CC(C(O)=O)=CC(OC)=C1OC SJSOFNCYXJUNBT-UHFFFAOYSA-N 0.000 claims description 10
- 239000002994 raw material Substances 0.000 claims description 10
- BOTDANWDWHJENH-UHFFFAOYSA-N Tetraethyl orthosilicate Chemical compound CCO[Si](OCC)(OCC)OCC BOTDANWDWHJENH-UHFFFAOYSA-N 0.000 claims description 7
- 239000000428 dust Substances 0.000 claims description 6
- IWPZKOJSYQZABD-UHFFFAOYSA-N 3,4,5-trimethoxybenzoic acid Natural products COC1=CC(OC)=CC(C(O)=O)=C1 IWPZKOJSYQZABD-UHFFFAOYSA-N 0.000 claims description 5
- 238000004062 sedimentation Methods 0.000 claims description 5
- 238000001291 vacuum drying Methods 0.000 claims description 5
- 229910000323 aluminium silicate Inorganic materials 0.000 claims description 3
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 3
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical group [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- 239000004411 aluminium Substances 0.000 claims description 2
- 238000006243 chemical reaction Methods 0.000 claims description 2
- 239000000843 powder Substances 0.000 claims description 2
- 230000000694 effects Effects 0.000 abstract description 8
- 239000003344 environmental pollutant Substances 0.000 abstract description 5
- 231100000719 pollutant Toxicity 0.000 abstract description 5
- 229910052573 porcelain Inorganic materials 0.000 abstract description 4
- 238000000354 decomposition reaction Methods 0.000 abstract description 3
- 238000001556 precipitation Methods 0.000 abstract description 3
- 238000010521 absorption reaction Methods 0.000 description 6
- 235000019580 granularity Nutrition 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- HFQQZARZPUDIFP-UHFFFAOYSA-M sodium;2-dodecylbenzenesulfonate Chemical compound [Na+].CCCCCCCCCCCCC1=CC=CC=C1S([O-])(=O)=O HFQQZARZPUDIFP-UHFFFAOYSA-M 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000005406 washing Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 229910018557 Si O Inorganic materials 0.000 description 1
- 239000011149 active material Substances 0.000 description 1
- 239000002156 adsorbate Substances 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 231100000481 chemical toxicant Toxicity 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000004040 coloring Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 230000003311 flocculating effect Effects 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 description 1
- 229910003471 inorganic composite material Inorganic materials 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 230000010355 oscillation Effects 0.000 description 1
- 230000002787 reinforcement Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- LIVNPJMFVYWSIS-UHFFFAOYSA-N silicon monoxide Inorganic materials [Si-]#[O+] LIVNPJMFVYWSIS-UHFFFAOYSA-N 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
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
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.
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)
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)
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 |
-
2014
- 2014-01-22 CN CN201410029547.4A patent/CN103801259B/en not_active Expired - Fee Related
Patent Citations (4)
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 |