CN106947486A - A kind of attapulgite activated carbon from activated sludge soil remediation material and preparation method thereof - Google Patents

A kind of attapulgite activated carbon from activated sludge soil remediation material and preparation method thereof Download PDF

Info

Publication number
CN106947486A
CN106947486A CN201710239445.9A CN201710239445A CN106947486A CN 106947486 A CN106947486 A CN 106947486A CN 201710239445 A CN201710239445 A CN 201710239445A CN 106947486 A CN106947486 A CN 106947486A
Authority
CN
China
Prior art keywords
attapulgite
soil remediation
preparation
activated sludge
activated carbon
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201710239445.9A
Other languages
Chinese (zh)
Other versions
CN106947486B (en
Inventor
姚超
左士祥
刘文杰
王灿
刘展
李霞章
姚群
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.)
CHANGZHOU NAOU NEW MATERIAL TECHNOLOGY Co Ltd
Original Assignee
CHANGZHOU NAOU NEW MATERIAL TECHNOLOGY 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 CHANGZHOU NAOU NEW MATERIAL TECHNOLOGY Co Ltd filed Critical CHANGZHOU NAOU NEW MATERIAL TECHNOLOGY Co Ltd
Priority to CN201710239445.9A priority Critical patent/CN106947486B/en
Publication of CN106947486A publication Critical patent/CN106947486A/en
Application granted granted Critical
Publication of CN106947486B publication Critical patent/CN106947486B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09KMATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/02Soil-conditioning materials or soil-stabilising materials containing inorganic compounds only
    • C09K17/04Soil-conditioning materials or soil-stabilising materials containing inorganic compounds only applied in a physical form other than a solution or a grout, e.g. as granules or gases

Landscapes

  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Soil Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Processing Of Solid Wastes (AREA)
  • Carbon And Carbon Compounds (AREA)

Abstract

The invention belongs to the higher value application field of biomass resource, more particularly to a kind of attapulgite activated carbon from activated sludge soil remediation material and preparation method thereof.Using attapulgite and the vegetable seed dregs of fat as raw material, attapulgite/carbon composite is prepared using a step high temperature pyrolytic cracking (HTP) first, obtained attapulgite/absorbent charcoal composite material is then handled by acid activation.

Description

A kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof
Technical field
The invention belongs to the higher value application field of biomass resource, more particularly to a kind of attapulgite-biomass active Charcoal soil remediation material and preparation method thereof.
Background technology
The development as resource-conserving and environment-friendly society becomes the higher value application of industrial solid castoff resource Gesture.The vegetable seed dregs of fat are a kind of accessory substance after vegetable seed oil expression, the one kind belonged in biomass industrial solid castoff.According to statistics, 14,000,000 tons of China's rapeseed yield in 2016, this will undoubtedly produce a large amount of vegetable seed dregs of fat solid waste.
Current processing method is that these vegetable seed dregs of fat are used as into vegetable fertilizer, but this does not realize biomass industry The higher value application level of solid waste resource.It is carbon source using the vegetable seed dregs of fat, is the high level of vegetable seed dregs of fat solid waste Change to utilize and open a new direction, but the easy coking in pyrolytic process of the vegetable seed dregs of fat, so as to have a strong impact on its charing production The specific surface area and pore structure of thing.
The content of the invention
The present invention is intended to provide a kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof, its skill Art scheme is, using attapulgite and the vegetable seed dregs of fat as raw material, to prepare attapulgite/charcoal using a step high temperature pyrolytic cracking (HTP) first and be combined Material, is then handled by acid activation and attapulgite/absorbent charcoal composite material is made.
Concretely comprise the following steps:
(1) the vegetable seed dregs of fat and attapulgite powder are uniformly mixed, then gained mixture is placed under inert atmosphere hot Solution, is made attapulgite/carbon composite,
Wherein, the vegetable seed dregs of fat and the mass ratio of attapulgite powder are 0.5~3:1,
Inert atmosphere is nitrogen, is pyrolyzed to react 2~5 hours under the conditions of 450~650 DEG C;
(2) attapulgite/carbon composite obtained by step (1) is added in acid solution and carries out hydro-thermal process, i.e., Attapulgite/absorbent charcoal composite material is made,
Wherein, the mass ratio of attapulgite/carbon composite and acid solution is 0.1~0.3:1, acid solution be hydrogen from Sub- concentration is hydrochloric acid solution, sulfuric acid solution or the salpeter solution of 3~10 mol/Ls,
Hydro-thermal process is, hydro-thermal reaction 6~12 hours under the conditions of 150~180 DEG C.
The beneficial effects of the present invention are:
1st, the present invention is based on the protein and amino acid enriched in the cereal and oil industry solid waste vegetable seed dregs of fat, using its work The active group that the activated carbon prepared by organic carbon source has been rich in the nitrogen of raw material itself, P elements are formed, so as to be conducive to Heavy metal ion in curing soil, it is to avoid this pollution of part heavy metal to soil surrounding environment;
2nd, the present invention adds 1-dimention nano attapulgite in vegetable seed dregs of fat pyrolytic process, using a step high temperature pyrolysis legal system During standby attapulgite/carbon composite, the coking problem in vegetable seed dregs of fat pyrolytic process can be effectively prevented, so as to improve activity The specific surface area of Carbon Materials, improves its pore structure;The technique has the advantages that with low cost, technique is simple;
3rd, the present invention is using the pyrolysis of the specific organic carbon source vegetable seed dregs of fat, and the Carbon Materials changed into are with similar to zigzag Pattern is coated on attapulgite surface (as shown in Figure 1), increases the specific surface area of composite;
4th, the present invention carries out acidifying hydro-thermal process to obtained attapulgite/carbon composite, so there is 2 aspect effects Really:1. inorganic acid can activate the active group of charcoal material surface;2. the vegetable seed dregs of fat can effectively be removed and be pyrolyzed the raw material of wood-charcoal to be formed Original metal impurities ion in material.This 2 aspect effect is all conducive to strengthening suction of the composite to heavy metal in soil ion Attached and solidification.
Brief description of the drawings
Fig. 1 schemes for the TEM of attapulgite/absorbent charcoal composite material prepared in the embodiment of the present invention 4.
Embodiment
Embodiment 1
1st, 1.0 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, are then placed in gained mixture Under nitrogen atmosphere, it is pyrolyzed 6 hours under the conditions of temperature is 450 DEG C, attapulgite/carbon composite is made;
2nd, take attapulgite/carbon composite obtained by 1.0 kilograms of steps 1 to be added to 10.0 kilograms of hydrogen ion concentrations to be In the hydrochloric acid solution of 3.0 mol/Ls, the hydro-thermal process 6 hours under the conditions of temperature is 180 DEG C is filtered, washs, dried, that is, is made Attapulgite/absorbent charcoal composite material.
Embodiment 2
1st, 6.0 kilograms of vegetable seed dregs of fat and 2 kilograms of attapulgite powders are uniformly mixed, gained mixture is then placed in nitrogen Under gas atmosphere, it is pyrolyzed 2 hours under the conditions of temperature is 650 DEG C, attapulgite/carbon composite is made;
2nd, take attapulgite/carbon composite obtained by 2.0 kilograms of steps 1 to be added to 6.7 kilograms of hydrogen ion concentrations to be In the sulfuric acid solution of 10.0 mol/Ls, the hydro-thermal process 12 hours under the conditions of temperature is 150 DEG C is filtered, washs, dried, that is, makes Obtain attapulgite/absorbent charcoal composite material.
Embodiment 3
1st, 3.5 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, are then placed in gained mixture Under nitrogen atmosphere, it is pyrolyzed 4 hours under the conditions of temperature is 550 DEG C, attapulgite/carbon composite is made;
2nd, it is 6.5 to take attapulgite/carbon composite obtained by 1.0 kilograms of steps 1 to be added to 5.0 kilograms of hydrogen ion concentrations In the salpeter solution of mol/L, the hydro-thermal process 9 hours under the conditions of temperature is 165 DEG C filters, washs, dried, that is, is made recessed Convex rod stone/absorbent charcoal composite material.
Embodiment 4
1st, 4.0 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, are then placed in gained mixture Under nitrogen atmosphere, it is pyrolyzed 3 hours under the conditions of temperature is 600 DEG C, attapulgite/carbon composite is made;
2nd, it is 5.0 to take attapulgite/carbon composite obtained by 1.0 kilograms of steps 1 to be added to 4.0 kilograms of hydrogen ion concentrations In the salpeter solution of mol/L, the hydro-thermal process 10 hours under the conditions of temperature is 170 DEG C filters, washs, dried, that is, is made recessed Convex rod stone/absorbent charcoal composite material.
Comparative example 1
Compared to above-described embodiment 4, remove " addition attapulgite powder " this process, other process conditions are constant:
4.0 kilograms of vegetable seed dregs of fat are placed under nitrogen atmosphere, are pyrolyzed 3 hours under the conditions of temperature is 600 DEG C, then by it It is added in the salpeter solution that 4.0 kilograms of hydrogen ion concentrations are 5.0 mol/Ls, the hydro-thermal process 10 under the conditions of temperature is 170 DEG C Hour, filtering, washing, dry, i.e., obtained absorbent charcoal material.
Comparative example 2
On the basis of comparative example 1, the vegetable seed dregs of fat are replaced with into the equal glucose of phosphorus content, also entered with reference to comparative example 1 Row is sufficiently pyrolyzed and hydro-thermal process.
Comparative example 3
On the basis of comparative example 1, the vegetable seed dregs of fat are replaced with into the equal cellulose of phosphorus content, also entered with reference to comparative example 1 Row is sufficiently pyrolyzed and hydro-thermal process.
Comparative example 4
Compared to above-described embodiment 4, remove " hydro-thermal process " this process, other process conditions are constant:
4.0 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, gained mixture is then placed in nitrogen Under gas atmosphere, it is pyrolyzed 3 hours under the conditions of temperature is 600 DEG C, attapulgite/carbon composite is made.
Soil remediation performance evaluation
Pb and Cd ions in fixed-contamination soil are repaired using chemical passivation method:1.0 kilograms of same contaminated soils are taken, Attapulgite/absorbent charcoal composite material (5%, mass ratio) obtained by addition embodiment and comparative example is mixed with contaminated soil It is even, under room temperature (25 DEG C), after the 60% of holding maximum water holding capacity cultivates 14 days, deionized water elution is added, until eluting Water reaches 10L, and the soil natural eluted is air-dried, and tests and analyzes,
Pedotheque is analyzed:Soil after reparation and not repaired blank soil are used 1:1 (mol ratio) HNO3/ H2O2Clear up, and the heavy metal in digestion solution is determined using atom flame spectrophotometer (AAS) (Jena, Germany, novAA350) Concentration, you can draw the content of beary metal after repairing or in blank soil,
Heavy metals immobilization rate=(quality of corresponding heavy metal in the quality of heavy metal in soil/blank soil after reparation) × 100%
Testing result such as following table:
Pb curing degrees Cd curing degrees
Embodiment 1 41.5 51.6
Embodiment 2 42.3 54.2
Embodiment 3 42.7 53.6
Embodiment 4 44.7 55.8
Comparative example 1 29.5 37.9
Comparative example 2 5.3 5.8
Comparative example 3 4.6 5.0
Comparative example 4 27.8 32.4

Claims (7)

1. a kind of attapulgite-activated carbon from activated sludge soil remediation material, it is characterised in that:Described soil remediation material be with Attapulgite and the vegetable seed dregs of fat are raw material, prepare attapulgite/carbon composite, Ran Houtong using a step high temperature pyrolytic cracking (HTP) first Made from peracid activation process.
2. a kind of preparation method of attapulgite as claimed in claim 1-activated carbon from activated sludge soil remediation material, its feature It is:The preparation method is,
(1) the vegetable seed dregs of fat and attapulgite powder are uniformly mixed, then gained mixture is placed under inert atmosphere and is pyrolyzed, system Obtain attapulgite/carbon composite;
(2) attapulgite/carbon composite obtained by step (1) is added in acid solution and carries out hydro-thermal process, that is, be made Attapulgite/absorbent charcoal composite material.
3. the preparation method of attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material, its feature exists In:In step (1), the vegetable seed dregs of fat are 0.5~3 with the mass ratio of attapulgite powder:1.
4. the preparation method of attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material, its feature exists In:In step (1), it is pyrolyzed to react 2~5 hours under the conditions of 450~650 DEG C.
5. the preparation method of attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material, its feature exists In:In step (2), the mass ratio of attapulgite/carbon composite and acid solution is 0.1~0.3:1.
6. the preparation method of attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material, its feature exists In:Acid solution described in step (2) is the hydrochloric acid solution, sulfuric acid solution or nitric acid that hydrogen ion concentration is 3~10 mol/Ls Solution.
7. the preparation method of attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material, its feature exists In:Hydro-thermal process described in step (2) is, hydro-thermal reaction 6~12 hours under the conditions of 150~180 DEG C.
CN201710239445.9A 2017-04-13 2017-04-13 A kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof Active CN106947486B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710239445.9A CN106947486B (en) 2017-04-13 2017-04-13 A kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710239445.9A CN106947486B (en) 2017-04-13 2017-04-13 A kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof

Publications (2)

Publication Number Publication Date
CN106947486A true CN106947486A (en) 2017-07-14
CN106947486B CN106947486B (en) 2019-10-01

Family

ID=59475855

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710239445.9A Active CN106947486B (en) 2017-04-13 2017-04-13 A kind of attapulgite-activated carbon from activated sludge soil remediation material and preparation method thereof

Country Status (1)

Country Link
CN (1) CN106947486B (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108949188A (en) * 2018-08-02 2018-12-07 佛山皖阳生物科技有限公司 A kind of preparation method of antibacterial passivator
CN110016355A (en) * 2019-04-17 2019-07-16 南京三聚生物质新材料科技有限公司 A kind of biomass carbonated method and utilize soil conditioner made from this method
CN110156012A (en) * 2019-06-04 2019-08-23 北方民族大学 Active carbon and the method for preparing active carbon using recycled wood materials
CN110947364A (en) * 2019-12-12 2020-04-03 甘肃农业大学 Heavy metal contaminated soil remediation agent and application thereof
CN111004069A (en) * 2019-12-31 2020-04-14 群发(广东)生物科技有限公司 Method for preparing novel organic fertilizer
CN111019404A (en) * 2019-11-29 2020-04-17 淮阴工学院 Modified attapulgite for rubber reinforcement and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005255737A (en) * 2004-03-09 2005-09-22 Sumitomo Osaka Cement Co Ltd Method for producing heavy metal adsorbent from waste and heavy metal adsorbent obtained by the method
CN103301807A (en) * 2013-06-07 2013-09-18 常州大学 Preparation method of high-efficiency composite attapulgite/rice hull activated carbon purified water material
CN103316633A (en) * 2013-06-13 2013-09-25 常州大学 Preparation method of attapulgite/porous carbon composite material
CN103920459A (en) * 2013-01-16 2014-07-16 江苏正本净化节水科技实业有限公司 Method for preparing efficient adsorption composite material by taking silicate clay and rice husk as raw materials

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005255737A (en) * 2004-03-09 2005-09-22 Sumitomo Osaka Cement Co Ltd Method for producing heavy metal adsorbent from waste and heavy metal adsorbent obtained by the method
CN103920459A (en) * 2013-01-16 2014-07-16 江苏正本净化节水科技实业有限公司 Method for preparing efficient adsorption composite material by taking silicate clay and rice husk as raw materials
CN103301807A (en) * 2013-06-07 2013-09-18 常州大学 Preparation method of high-efficiency composite attapulgite/rice hull activated carbon purified water material
CN103316633A (en) * 2013-06-13 2013-09-25 常州大学 Preparation method of attapulgite/porous carbon composite material

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
刘文杰等: ""凹凸棒石/脱硅稻壳炭复合材料吸附Pb2+、Cu2+、Ni2+的对比研究", 《化工新型材料》 *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108949188A (en) * 2018-08-02 2018-12-07 佛山皖阳生物科技有限公司 A kind of preparation method of antibacterial passivator
CN110016355A (en) * 2019-04-17 2019-07-16 南京三聚生物质新材料科技有限公司 A kind of biomass carbonated method and utilize soil conditioner made from this method
CN110156012A (en) * 2019-06-04 2019-08-23 北方民族大学 Active carbon and the method for preparing active carbon using recycled wood materials
CN111019404A (en) * 2019-11-29 2020-04-17 淮阴工学院 Modified attapulgite for rubber reinforcement and preparation method thereof
CN110947364A (en) * 2019-12-12 2020-04-03 甘肃农业大学 Heavy metal contaminated soil remediation agent and application thereof
CN111004069A (en) * 2019-12-31 2020-04-14 群发(广东)生物科技有限公司 Method for preparing novel organic fertilizer

Also Published As

Publication number Publication date
CN106947486B (en) 2019-10-01

Similar Documents

Publication Publication Date Title
CN106947486A (en) A kind of attapulgite activated carbon from activated sludge soil remediation material and preparation method thereof
CN104258809B (en) Modified biomass charcoal and the restorative procedure of heavy-metal contaminated soil
CN105731752B (en) A method of charcoal is prepared using excess sludge and hazelnut shell copyrolysis
CN103833274B (en) A kind of heavy metal contamination soil consolidator and using method thereof
WO2016176906A1 (en) Method for producing canna indica biochar capable of adsorbing ammonia nitrogen and cadmium simultaneously
CN107983314A (en) A kind of biological carbon composite of sodium alginate-calcium ion modification and preparation method thereof and purposes
CN103464101A (en) Resource utilization method of plant bamboo reed after restoring heavy metal contaminated soil
CN105170091A (en) Preparation method of iron-modified reed biological carbon, and application of iron-modified reed biological carbon in treatment of phosphorus wastewater
CN104549154B (en) The preparation method of the charcoal of cadmium in the safe adsorbed water body of energy
CN106744936A (en) A kind of method that biomass cauline leaf separation prepares absorbent charcoal material
CN105753608A (en) Preparation method and application of novel iron-based biochar
CN105174254B (en) A kind of method that activated carbon and furfural are prepared by raw material of corncob
CN109704327A (en) The method that bio-oil makes multiple hole carbon material
CN112209378A (en) Waste vinasse biochar, preparation method thereof and application of waste vinasse biochar as soil conditioner
CN105536698A (en) Preparation method of papermaking sludge activated biochar
CN103480330B (en) Biomass-modified adsorbent for adsorbing coking wastewater, and preparation method and application thereof
CN110586030A (en) Preparation method of modified charcoal capable of adsorbing and fixing cadmium and copper in soil by cyclic utilization of heat
CN105776796A (en) Method of reducing heavy metal bio-availability through pig manure pyrolysis and biochar application of pig manure
CN116851432A (en) Method for repairing petroleum and zinc polluted saline-alkali soil by phosphoric acid modified magnetic biochar
CN106744952B (en) The method that sewage sludge prepares modified active coke
CN109761213A (en) Porous doping nitrogen sulphur phosphorus carbon material of one kind and its preparation method and application
CN110655137B (en) Fly ash-based high-salinity organic wastewater purification and biomass catalytic pyrolysis combined treatment process
CN110976503A (en) Modified attapulgite and preparation method and application thereof
DE112022000781T5 (en) EXPANDED GRAPHITE AND METHOD FOR THE PRODUCTION THEREOF
CN112691640B (en) Coprinus comatus mushroom dreg porous carbon adsorbent and preparation method and application thereof

Legal Events

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