CN105727881B - A kind of alkali modification attapulgite clay adsorbent and preparation method thereof - Google Patents

A kind of alkali modification attapulgite clay adsorbent and preparation method thereof Download PDF

Info

Publication number
CN105727881B
CN105727881B CN201610200746.6A CN201610200746A CN105727881B CN 105727881 B CN105727881 B CN 105727881B CN 201610200746 A CN201610200746 A CN 201610200746A CN 105727881 B CN105727881 B CN 105727881B
Authority
CN
China
Prior art keywords
attapulgite
mud
alkali modification
alkali
attapulgite clay
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
CN201610200746.6A
Other languages
Chinese (zh)
Other versions
CN105727881A (en
Inventor
陈禧
魏东洋
贺涛
陈隽
桑燕鸿
张恒军
周雯
檀笑
朱家亮
徐丹
王龙乐
林冬红
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.)
South China Institute of Environmental Science of Ministry of Ecology and Environment
Original Assignee
South China Institute of Environmental Science of Ministry of Ecology and Environment
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 South China Institute of Environmental Science of Ministry of Ecology and Environment filed Critical South China Institute of Environmental Science of Ministry of Ecology and Environment
Priority to CN201610200746.6A priority Critical patent/CN105727881B/en
Publication of CN105727881A publication Critical patent/CN105727881A/en
Application granted granted Critical
Publication of CN105727881B publication Critical patent/CN105727881B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/10Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
    • B01J20/12Naturally occurring clays or bleaching earth
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4806Sorbents characterised by the starting material used for their preparation the starting material being of inorganic character
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Analytical Chemistry (AREA)
  • Dispersion Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention discloses a kind of alkali modification attapulgite clay adsorbent and preparation method thereof, which is by using alkali compounds, lime and attapulgite mix, and alkali modification attapulgite clay adsorbent material is obtained after calcining.The alkali modification attapulgite clay adsorbent includes following material by weight:Purify 12 parts of attapulgite;0.5 1 parts of alkali compounds;12 parts of lime.The heavy metal ion and its compound that the sorbent material can be used in Adsorption aqueous solution, the material can be also used for the soil remediation on farmland simultaneously, for improveing the heavy metal ion in acid soil and absorption passivation polluted soil, the part physicochemical property of agricultural land soil is adjusted.

Description

A kind of alkali modification attapulgite clay adsorbent and preparation method thereof
Technical field
The invention belongs to technical field of sewage, more particularly to a kind of modification attapulgite clay adsorbent material in a huge sum of money Belong to waste water and the application in polluted soil improvement, the invention further relates to the preparation methods of the adsorbent.
Background technology
Water is for the survival of mankind and development important substance basis, but with human progress and industrial expansion, Heavy metal pollution problem becomes getting worse.Heavy metal pollution refers to the environmental pollution as caused by heavy metal and its compound, The Absolute emissions amount of heavy metal accounts for about the 66.33% of waste water total amount in middle discharge of wastewater.Its main source is mining engineering, discards Discharge, sewage irrigation, the percolate using heavy metals exceeding standard product and garbage loading embeading.These enter natural water and soil Heavy metal, it is difficult to eliminate naturally.Heavy metal pollution mainly generates two big harm in nature:First, in nature, that is, food chain It builds up, eventually results in organism lesion or death.Second is that influence agricultural production, it was reported that China is annual because attaching most importance to Metallic pollution and cause more than 1,000 ten thousand tons of grain drop in production, in addition also up to 12,000,000 tons every year of contaminated by heavy metals grain, is closed Meter economic loss is at least up to 20,000,000,000 yuan.
Heavy metal ion conventional method in removal water body mainly has two big kinds:First, based technique for in-situ remediation;Second is that dystopy Recovery technique.Contaminated soil is mainly digged up and focused on by showering technology, is mainly had ablution, is burned Processing, heat treating process etc., but excavation and transport of the showering technology due to being related to earth volume, there is time-consuming, costs The problems such as height, inefficiency, and depth contaminated soil cannot be handled and there is the soil below economic value and building.It is former Position recovery technique be at the scene under the conditions of the method directly repaired to contaminated soil.Based technique for in-situ remediation is as a kind of technique Simply, soil remediation new technology easy to operate, is gradually approved by people, receives extensive attention.
Attapulgite as a kind of mineral resources of rich reserves in China, in water process be a kind of development cost it is cheap, Effective environmental-protection adsorption new material.Its unique porous type chain layered crystal structure, leads to large number of duct and seam For gap through in entire crystalline material, natural huge specific surface area determines that it has good adsorptivity, natural concave convex rod One layer of tradable cation and hydroxyl are contained in native surface, can with aqueous solution or in the form of an ion existing heavy metal occur from Sub- exchange interaction forms coordinate bond, so as to be passivated or Adsorption aqueous solution in heavy metal.However natural concave convex rod is former Shape soil contains a large amount of impurity, and duct permeability is poor, influences its absorption property, and need to pass through purification and appropriate modification could obtain Better absorption property.
Invention content
It is an object of the invention to overcome the deficiencies of the prior art and provide a kind of systems of alkali modification concave convex rod sorbent material Preparation Method and its application.
The purpose of the present invention is realized by the following method:
A kind of alkali modification attapulgite material is by using after alkali compounds, lime and purification attapulgite mix, passes through It crosses calcining and obtains alkali modification attapulgite clay adsorbent material.
A kind of alkali modification attapulgite clay adsorbent includes following material by weight:
Purify 1-2 parts of attapulgite
0.5-1 parts of alkali compounds
1-2 parts of lime
A kind of preparation method of alkali modification attapulgite clay adsorbent, includes the following steps:
(1) it purifies:Natural attapulgite using mechanical means is rolled, crushes, grind, is sieved with 100 mesh sieve, by adding Enter distilled water, mud in suspension be made, then carry out ultrasonic disperse 10min, discard lower sediment, in reservation suspension carry out from The heart controls rotating speed 4000r/min, centrifuges 15min.Retain sediment, it is for use to be transferred to beaker;
(2) modifying agent:By highly basic powder and lime with mass ratio 1:1 or 0.5:1 ratio mixes, and obtains alkaline mixt, That is modifying agent;
(3) it is modified:The modifying agent that the purification attapulgite that step (1) is prepared is prepared with step (2) is with 2:1 Ratio mixing after obtain mixture, after while the mixture is stirred continuously add in distilled water carry out mix, be made outstanding Mud scum is starched, and is constantly stirred on magnetic stirring apparatus, to be added to finish, and continues stirring to obtain mixing mud to uniformly mixed;
(4) pH is adjusted:In the case where being stirred continuously, hydrochloric acid is constantly instilled in mixing mud made from step (3), while with essence The pH of close pH test paper method control mud is 8 or so, continues to stir 15min or so or until being uniformly mixed;
(5) it centrifuges:Mud made from step (4) is centrifuged on centrifuge, control rotating speed is in 4000r/min;From In heart 15min, then solid sediment is washed with distilled water 3 times, continues to centrifuge, dry, then ground 100 mesh Sieve;
(6) it calcines:The solid dried object that (5) obtain is calcined, at 350 DEG C~450 DEG C, calcining 1h, natural cooling, Alkali modification attapulgite sorbing material can be obtained, divulge information or carries out sealing preservation after drying in drying box.
Preferably, above-mentioned steps (1) are replaced with:(1) it purifies:Natural attapulgite is ground using mechanical means Pressure, broken, grinding, sieve with 100 mesh sieve, and by adding in distilled water, mud in suspension are made, then carries out dispersant dispersion 10min, abandons Sub-cloud precipitates, and suspension is centrifuged in reservation, controls rotating speed 4000r/min, centrifuges 15min.Retain sediment, be transferred to Beaker is for use.
Preferably, the dispersant is calgon or Sodium Polyacrylate or sodium metasilicate.
More preferably, the dispersant is nonylphenol polyoxyethylene ether, octyl phenol polyoxyethylene ether, phenethyl phenol polyoxy second It is one or more in alkene ether, fatty alcohol polyoxyethylene ether, polyoxyethylene alkylphenol ether.
More preferably, the dispersant be composite dispersing agent, ingredient by it is following by weight:Nonyl pheno Ether, sodium metasilicate, sodium carboxymethylcellulose, active carbon nanoparticles, polyoxyethylene alkylphenol ether mixture, volume mixture ratio For:1:(2-3):1:1:0.5.
Advantageous effect
The heavy metal ion and its compound that the sorbent material can be used in Adsorption aqueous solution, while the material is also It can be used for the soil remediation on farmland, for improveing the heavy metal ion in acid soil and absorption passivation polluted soil, Adjust the part physicochemical property of agricultural land soil.
Specific embodiment
The present invention is described in further detail with reference to embodiment, for going for the heavy metal ion in aqueous solution It removes, inventive formulation and production method are as follows, can reach effect as scheduled:
Embodiment 1:
(1) it purifies:Natural attapulgite using mechanical means is rolled, crushes, grind, is sieved with 100 mesh sieve, by adding Enter distilled water, mud in suspension be made, then carry out ultrasonic disperse 10min, discard lower sediment, in reservation suspension carry out from The heart controls rotating speed 4000r/min, centrifuges 15min.Retain sediment, it is for use to be transferred to beaker;
(2) by calcium hydroxide and lime in mass ratio 0.5:1 ratio mixes, and obtains alkali modification mixture, i.e. modifying agent B.
(3) it is modified:The modifying agent that the purification attapulgite that step (1) is prepared is prepared with step (2) is with 2:1 Ratio mixing after obtain mixture, after while the mixture is stirred continuously add in distilled water carry out mix, be made outstanding Mud scum is starched, and is constantly stirred on magnetic stirring apparatus, to be added to finish, and continues stirring to obtain mixing mud to uniformly mixed;
(4) pH is adjusted:In the case where being stirred continuously, hydrochloric acid is constantly instilled in mixing mud made from step (3), while with essence The pH of close pH test paper method control mud is 8 or so, continues to stir 15min or so or until being uniformly mixed;
(5) it centrifuges:Mud made from step (4) is centrifuged on centrifuge, control rotating speed is in 4000r/min;From In heart 15min, then solid sediment is washed with distilled water 3 times, continues to centrifuge, dry, then ground 100 mesh Sieve;
(6) it calcines:The solid dried object that (5) obtain is calcined, at 350 DEG C~450 DEG C, calcining 1h, natural cooling, Aeration-drying carries out sealing preservation in drying box after drying, you can obtains alkali modification attapulgite sorbing material.
Preferably, above-mentioned steps (1) are replaced with:(1) it purifies:Natural attapulgite is ground using mechanical means Pressure, broken, grinding, sieve with 100 mesh sieve, and by adding in distilled water, mud in suspension are made, then carries out dispersant dispersion 10min, abandons Sub-cloud precipitates, and suspension is centrifuged in reservation, controls rotating speed 4000r/min, centrifuges 15min.Retain sediment, be transferred to Beaker is for use.
To obtain the alkali modification attapulgite to the Adsorption effect of the heavy metal ion in aqueous solution and to soil Improved effect, spy have done the scheme of being implemented as follows:
(1) cadmium-ion solution of 1g/L and the solution of lead ion solution is respectively configured, is then mixed and made into the mixed of 500mg/L Close solution.The mixed liquor 100ml of six parts of lead ions and cadmium ion is accurately measured respectively, is put into 250ml volumetric flasks
(2) weigh 6 parts of alkali modification attapulgite clay adsorbent material respectively, quality be respectively 0.025g, 0.05g, 0.1g, 0.15g, 0.2g, 0.25g are put into conical flask, and room temperature concussion absorption is for 24 hours.
(3) after concussion absorption, 2h is stood, supernatant 20ml is taken, 15min is centrifuged under 4000r/min, using national standard Method measures concentration of heavy metal ion.
1 alkali modification concave convex rod sorbing material of embodiment absorption heavy metal effect situation is shown in Table 1
Table 1
Embodiment 2
To obtain alkali modification attapulgite clay adsorbent material in improvement acid soil, recovery field biological characteristic performance is special The domestic experiment acid soil in Xuyi County of Jiangsu Province is picked up from selection, and the pH value of initial soil is non-Suitable agricultural kind between 4-5 The acid soil of plant.
This is used to improveing acid soil alkali modification attapulgite sorbing material manufacturing process as follows:
(1) by broken concave convex rod undisturbed soil in mass ratio 1:10 add in distilled water, are mixed into mud and are being stirred continuously Lower progress ultrasonic disperse 10-15min, discards sediment, and suspension is centrifuged in reservation, control rotating speed in 4000r/min, from Heart 15min obtains mud A.
(2) modifying agent:By calcium hydroxide and lime with mass ratio 1:1 is mixed, and obtains alkaline mixt, i.e. modifying agent B;
(3) it is modified:The modifying agent that the purification attapulgite that step (1) is prepared is prepared with step (2) is with 2:1 Ratio mixing after obtain mixture, after while the mixture is stirred continuously add in distilled water carry out mix, control turn Speed in 60-120r/min per minute, mud in suspension is made, it is to be added to finish, continue stirring to obtain mixing mud to being uniformly mixed;
(4) pH is adjusted:In the case where being stirred continuously, hydrochloric acid is constantly instilled in mixing mud made from step (3), while with essence The pH of close pH test paper control mud is 8 or so, continues to stir 15min or so or until being uniformly mixed;
(5) it centrifuges:Mud made from step (4) is centrifuged on centrifuge, control rotating speed is in 4000r/min;From In heart 15min, then solid sediment is washed with distilled water 3 times, continues to centrifuge, then at 105 DEG C dry 4h or It is that gravity-flow ventilation is dried, then grinds, sieve with 100 mesh sieve.
(6) it calcines:The solid dried object that (5) obtain is calcined, at 400 DEG C, calcines 1h, natural cooling, you can obtain Alkali modification attapulgite sorbing material is obtained, divulge information or carries out sealing preservation after drying in drying box.
To obtain alkali modification attapulgite clay adsorbent to the implementation result on acid soil improvement, spy has done the side of being implemented as follows Case:
(1) moisture content for measuring acid soil is 18.2%, accurately weighs 5 parts of experiment soil, and every part of soil sample presses practical 10g Dry soil samples, which calculates, to be weighed, and is put into 50ml small beakers, then number 1-0,1-1,1-2,1-3,1-4,1-5.
(2) it is concave-convex for the fully dried alkali modification of 0.0g, 0.3g, 0.9g, 1.5g, 1.8g, 2.1g that quality is weighed respectively Stick earth adsorbing sample is put by number in experiment soil, every part of style respectively stirring twice, i.e., with glass bar clockwise and the inverse time Respectively stirring is primary for needle, turns over shape.
PH is measured by National Standard Method after sample opening is continuously cultivated 3 days, it is as a result as follows:
Alkali modification attapulgite clay adsorbent material improvement acid soil effect situation is shown in Table 2 in embodiment 2:
Table 2
Finally it should be noted that:The above embodiments are merely illustrative of the technical solutions of the present invention, rather than its limitations;Although The present invention is described in detail with reference to the foregoing embodiments, it will be understood by those of ordinary skill in the art that:It still may be used To modify to the technical solution recorded in previous embodiment or carry out equivalent replacement to which part technical characteristic;And These modifications are replaced, the spirit and model of technical solution of the embodiment of the present invention that it does not separate the essence of the corresponding technical solution It encloses.

Claims (1)

1. a kind of alkali modification attapulgite clay adsorbent is by using attapulgite, alkali compounds and lime mix, after calcining It obtains, it is characterised in that:The alkali modification attapulgite clay adsorbent includes following material by weight,
Purify 1-2 parts of attapulgite
0.5-1 parts of alkali compounds
1-2 parts of lime;
A kind of preparation method of alkali modification attapulgite clay adsorbent, includes the following steps:
(1) it purifies:Natural attapulgite using mechanical means is rolled, crushes, grind, is sieved with 100 mesh sieve, is steamed by adding in Mud in suspension is made in distilled water, then carries out ultrasonic disperse 10min, discards lower sediment, and suspension is centrifuged in reservation, control Rotating speed 4000r/min processed centrifuges 15min;Retain sediment, it is for use to be transferred to beaker;
(2) modifying agent:By highly basic powder and lime with mass ratio 1:1 or 0.5:1 ratio mixes, and obtains alkaline mixt, that is, changes Property agent;
(3) it is modified:The modifying agent that the purification attapulgite that step (1) is prepared is prepared with step (2) is with 2:1 ratio Example mixing after obtain mixture, after while the mixture is stirred continuously add in distilled water carry out mix, suspension mud is made Slurry, is constantly stirred on magnetic stirring apparatus, to be added to finish, and continues stirring to obtain mixing mud to uniformly mixed;
(4) pH is adjusted:In the case where being stirred continuously, hydrochloric acid is constantly instilled, while use Accurate pH in mixing mud made from step (3) The pH of test paper method control mud is 8, continues to stir 15min or until being uniformly mixed;
(5) it centrifuges:Mud made from step (4) is centrifuged on centrifuge, control rotating speed is in 4000r/min;Centrifugation In 15min, then solid sediment is washed with distilled water 3 times, continues to centrifuge, dry, then grinding sieves with 100 mesh sieve;
(6) it calcines:The solid dried object that (5) obtain is calcined, at 350 DEG C~450 DEG C, calcines 1h, natural cooling, ventilation Drying carries out sealing preservation in drying box after drying, you can obtains alkali modification attapulgite sorbing material.
CN201610200746.6A 2016-03-31 2016-03-31 A kind of alkali modification attapulgite clay adsorbent and preparation method thereof Expired - Fee Related CN105727881B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610200746.6A CN105727881B (en) 2016-03-31 2016-03-31 A kind of alkali modification attapulgite clay adsorbent and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610200746.6A CN105727881B (en) 2016-03-31 2016-03-31 A kind of alkali modification attapulgite clay adsorbent and preparation method thereof

Publications (2)

Publication Number Publication Date
CN105727881A CN105727881A (en) 2016-07-06
CN105727881B true CN105727881B (en) 2018-06-19

Family

ID=56252723

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610200746.6A Expired - Fee Related CN105727881B (en) 2016-03-31 2016-03-31 A kind of alkali modification attapulgite clay adsorbent and preparation method thereof

Country Status (1)

Country Link
CN (1) CN105727881B (en)

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106242906A (en) * 2016-08-11 2016-12-21 晋鼎明 A kind of potted plant Epipremnum aureum (Linde et Andre) (Bunting.) dedicated substrate
CN106890720A (en) * 2017-03-30 2017-06-27 兰州坤仑环保科技有限公司 A kind of alkali chelates the preparation method of palygorskite base heavy metal passivating material
CN106904624A (en) * 2017-04-14 2017-06-30 明光市外泰高分子材料有限公司 A kind of method for strengthening attapulgite stickiness
CN106957560A (en) * 2017-04-28 2017-07-18 明光市飞洲新材料有限公司 A kind of coating additive using attapulgite as carrier and preparation method thereof
CN106900768A (en) * 2017-04-28 2017-06-30 明光市飞洲新材料有限公司 A kind of vegetable insecticide and preparation method thereof
CN109761241A (en) * 2018-12-27 2019-05-17 济南大学 A method of utilizing alkaline matter activated clays pore-creating
CN110372075B (en) * 2019-05-14 2022-03-25 山东环瑞生态科技有限公司 Efficient defluorination medicament and application thereof
CN112877322B (en) * 2021-02-22 2022-06-21 杭州楠大环保科技有限公司 Perishable garbage biodegradation method based on microbial phase change
CN113307280B (en) * 2021-06-23 2023-01-06 西北师范大学 Method for normalizing quality of attapulgite product
CN114433008B (en) * 2022-01-17 2024-01-23 常州大学 Preparation method of attapulgite composite material for adsorption separation of methanol/dimethyl carbonate
CN114907058B (en) * 2022-04-15 2022-12-02 浙江碧水量子科技有限公司 Water purification component for reducing total phosphorus and preparation method and application thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005040685A (en) * 2003-07-25 2005-02-17 Sumitomo Osaka Cement Co Ltd Heavy metal adsorbent material and heavy metal treatment method
CN102019166A (en) * 2010-12-11 2011-04-20 上海纳米技术及应用国家工程研究中心有限公司 Method for preparing modified attapulgite clay adsorbing material
CN103736444A (en) * 2013-12-31 2014-04-23 常州大学 Preparation method and application of hydrothermally solidified attapulgite clay filtering material

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005040685A (en) * 2003-07-25 2005-02-17 Sumitomo Osaka Cement Co Ltd Heavy metal adsorbent material and heavy metal treatment method
CN102019166A (en) * 2010-12-11 2011-04-20 上海纳米技术及应用国家工程研究中心有限公司 Method for preparing modified attapulgite clay adsorbing material
CN103736444A (en) * 2013-12-31 2014-04-23 常州大学 Preparation method and application of hydrothermally solidified attapulgite clay filtering material

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
改性凹凸棒土去除废水磷酸根的研究;杨立春 等;《资源节约与环保》;20131231(第9期);全文 *

Also Published As

Publication number Publication date
CN105727881A (en) 2016-07-06

Similar Documents

Publication Publication Date Title
CN105727881B (en) A kind of alkali modification attapulgite clay adsorbent and preparation method thereof
CN107115840B (en) Carbon-based composite material for repairing arsenic-cadmium contaminated soil and application thereof
CN105733596B (en) A kind of soil conditioner and preparation method thereof for heavy metal passivation
CN107398251B (en) Preparation and application for the floatability magnetic hollow material that water body and heavy metal in soil remove
CN106800933A (en) A kind of passivator repaired for farmland soil heavy metals combined pollution and its preparation and application
CN107011918B (en) A kind of sulfhydrylation bentonite of restoration of soil polluted by heavy metal and preparation method thereof
CN105536739B (en) Synchronous heavy metal adsorption mineralizer for repairing water body and its bed mud and preparation method thereof
CN1275884C (en) Bayer process red mud matrix improvement technology
CN108178605A (en) A kind of Preparation method and use of the residual mud baking-free ceramicite of high absorption property water supply plant
CN105693067B (en) A kind of method that purification plant sludge recycling prepares bed mud covering material
CN106623400A (en) Method for remedying heavy metal contaminated soil through passivation
CN110484267A (en) A kind of mineral soil conditioner and preparation method thereof using flyash production
CN106478012A (en) A kind of sludge curing agent and preparation method thereof
CN105854808A (en) Composite adsorbing material based on straw and coal gangue and preparation method thereof
CN113426402B (en) Preparation method and application of lanthanum-aluminum multi-element composite mineral phosphorus removal material
CN109097064A (en) A kind of acid soil improving agent
CN109092247A (en) The preparation method of modified mulberry bar biomass carbon adsorbent
CN105126760A (en) Heavy metal poly-hole adsorption material and preparation method thereof
CN111575012A (en) Composite material for passivating soil heavy metal nickel and preparation and application methods thereof
KR20190048515A (en) Adsorbent for removal of arsenic containing mine drainage sludge, method for preparing the same, and arsenic removal method using the same
CN105499265B (en) Waste water-base drilling liquid solid formation land resource method
CN109574104B (en) Bimetal wind wave resistant phosphorus locking material and preparation method and application thereof
CN109695059B (en) Preparation method of gypsum whisker
CN108273829B (en) Method for reducing alkalinity of Bayer process red mud
CN107321298B (en) The preparation method of modified magnetite and its application in heavy metal pollution reparation

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
CB03 Change of inventor or designer information
CB03 Change of inventor or designer information

Inventor after: Chen Xi

Inventor after: Xu Dan

Inventor after: Wang Longle

Inventor after: Lin Donghong

Inventor after: Wei Dongyang

Inventor after: He Tao

Inventor after: Chen Juan

Inventor after: Sang Yanhong

Inventor after: Zhang Hengjun

Inventor after: Zhou Wen

Inventor after: Tanxiao

Inventor after: Zhu Jialiang

Inventor before: Wei Dongyang

Inventor before: Xia Xiaodong

Inventor before: Wang Xin

Inventor before: He Tao

Inventor before: Ma Xiaozhou

Inventor before: Sang Yanhong

Inventor before: Zhou Wen

Inventor before: Yi Hao

Inventor before: Lei Yutao

Inventor before: Fang Xiaohang

GR01 Patent grant
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: 20180619