CN106947486B - 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
CN106947486B
CN106947486B CN201710239445.9A CN201710239445A CN106947486B CN 106947486 B CN106947486 B CN 106947486B CN 201710239445 A CN201710239445 A CN 201710239445A CN 106947486 B CN106947486 B CN 106947486B
Authority
CN
China
Prior art keywords
attapulgite
soil remediation
activated
carbon
activated sludge
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201710239445.9A
Other languages
Chinese (zh)
Other versions
CN106947486A (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

Abstract

The invention belongs to the higher value application field of biomass resource, in particular 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, then attapulgite/absorbent charcoal composite material as made from acid activation processing.

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, in particular to a kind of attapulgite-biomass active Charcoal soil remediation material and preparation method thereof.
Background technique
The development that the higher value application of industrial solid castoff resource has become resource-conserving and environment-friendly society becomes Gesture.The vegetable seed dregs of fat are a kind of by-products after vegetable seed oil expression, belong to one of biomass industrial solid castoff.According to statistics, 14,000,000 tons of China's rapeseed yield in 2016, this will undoubtedly generate a large amount of vegetable seed dregs of fat solid waste.
Current processing method is these vegetable seed dregs of fat to be used as to vegetable fertilizer, but this does not realize biomass industry The higher value application of solid waste resource is horizontal.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 opens a new direction, however the easy coking in pyrolytic process of the vegetable seed dregs of fat, it is produced to seriously affect its charing The specific surface area and pore structure of object.
Summary 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, skill Art scheme is that it is compound to prepare attapulgite/charcoal using a step high temperature pyrolytic cracking (HTP) first using attapulgite and the vegetable seed dregs of fat as raw material Then material is handled by acid activation and attapulgite/absorbent charcoal composite material is made.
Specific steps are as follows:
(1) the vegetable seed dregs of fat and attapulgite powder are uniformly mixed, then gained mixture is placed under inert atmosphere hot Attapulgite/carbon composite is made in solution,
Wherein, the mass ratio of the vegetable seed dregs of fat and attapulgite powder is 0.5~3:1,
Inert atmosphere is nitrogen, be pyrolyzed be 450~650 DEG C under the conditions of react 2~5 hours;
(2) the resulting attapulgite/carbon composite of 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 be 0.1~0.3:1, acid solution be hydrogen from Sub- concentration is hydrochloric acid solution, sulfuric acid solution or the nitric acid 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:
1, the present invention is based on protein and amino acid abundant in the cereal and oil industry solid waste vegetable seed dregs of fat, using its work The nitrogen and phosphorus element for being rich in raw material itself for the active carbon that organic carbon source is prepared is formed by active group, to be conducive to Heavy metal ion in curing soil avoids this pollution of part heavy metal to soil ambient enviroment;
2,1-dimention nano attapulgite is added in the present invention in vegetable seed dregs of fat pyrolytic process, using a step high temperature pyrolysis legal system When standby attapulgite/carbon composite, the coking problem in vegetable seed dregs of fat pyrolytic process can be effectively prevented, to improve activity The specific surface area of Carbon Materials improves its pore structure;The technique has many advantages, such as low in cost, simple process;
3, the present invention is pyrolyzed using the specific organic carbon source vegetable seed dregs of fat, and the Carbon Materials being converted to are zigzag to be similar to Pattern is coated on attapulgite surface (as shown in Fig. 1), increases the specific surface area of composite material;
4, the present invention carries out acidification hydro-thermal process to obtained attapulgite/carbon composite, there is 2 aspect effects in this way Fruit: 1. inorganic acid can activate the active group of charcoal material surface;2. can effectively remove the vegetable seed dregs of fat is pyrolyzed the raw material of wood-charcoal to be formed Original metal impurities ion in material.This 2 aspect effect is all conducive to enhance suction of the composite material to heavy metal ions in soil Attached and solidification.
Detailed description of the invention
Fig. 1 is attapulgite/absorbent charcoal composite material TEM figure prepared in the embodiment of the present invention 4.
Specific embodiment
Embodiment 1
1,1.0 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, is then placed in gained mixture It under nitrogen atmosphere, is pyrolyzed 6 hours under the conditions of temperature is 450 DEG C, attapulgite/carbon composite is made;
2, it takes the resulting attapulgite/carbon composite of 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, hydro-thermal process 6 hours under the conditions of temperature is 180 DEG C, it is filtered, washed, dries, obtain Attapulgite/absorbent charcoal composite material.
Embodiment 2
1,6.0 kilograms of vegetable seed dregs of fat and 2 kilograms of attapulgite powders are uniformly mixed, gained mixture is then placed in nitrogen It under gas atmosphere, is pyrolyzed 2 hours under the conditions of temperature is 650 DEG C, attapulgite/carbon composite is made;
2, it takes the resulting attapulgite/carbon composite of 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, hydro-thermal process 12 hours under the conditions of temperature is 150 DEG C, it is filtered, washed, dries, that is, make Obtain attapulgite/absorbent charcoal composite material.
Embodiment 3
1,3.5 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, is then placed in gained mixture It under nitrogen atmosphere, is pyrolyzed 4 hours under the conditions of temperature is 550 DEG C, attapulgite/carbon composite is made;
2, taking the resulting attapulgite/carbon composite of 1.0 kilograms of steps 1 to be added to 5.0 kilograms of hydrogen ion concentrations is 6.5 In the nitric acid solution of mol/L, hydro-thermal process 9 hours under the conditions of temperature is 165 DEG C, it is filtered, washed, dries, obtain recessed Convex stick stone/absorbent charcoal composite material.
Embodiment 4
1,4.0 kilograms of vegetable seed dregs of fat and 2.0 kilograms of attapulgite powders are uniformly mixed, is then placed in gained mixture It under nitrogen atmosphere, is pyrolyzed 3 hours under the conditions of temperature is 600 DEG C, attapulgite/carbon composite is made;
2, taking the resulting attapulgite/carbon composite of 1.0 kilograms of steps 1 to be added to 4.0 kilograms of hydrogen ion concentrations is 5.0 In the nitric acid solution of mol/L, hydro-thermal process 10 hours under the conditions of temperature is 170 DEG C, it is filtered, washed, dries, obtain recessed Convex stick 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 nitric acid 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, it is filtered, washed, dries, obtain 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, referring to comparative example 1 also into Row is adequately 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, referring to comparative example 1 also into Row is adequately 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 It under gas atmosphere, 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 ion in fixed-contamination soil is repaired using chemical passivation method: taking 1.0 kilograms of same contaminated soils, Attapulgite/absorbent charcoal composite material (5%, mass ratio) obtained by embodiment and comparative example is added to mix with contaminated soil It is even, under room temperature (25 DEG C), after keeping the 60% of maximum water holding capacity to cultivate 14 days, deionized water elution is added, until elution Water reaches 10L, and the soil natural eluted is air-dried, and tests and analyzes,
Pedotheque analysis: the soil after reparation and not repaired blank soil are used into 1:1 (molar ratio) HNO3/ H2O2Resolution, and using the heavy metal in atom flame spectrophotometer (AAS) (Jena, Germany, novAA350) measurement digestion solution Concentration, the content of beary metal after reparation that you can get it 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 is as follows:
Pb curing degree Cd curing degree
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: the soil remediation material be with Attapulgite and the vegetable seed dregs of fat are raw material, prepare attapulgite/carbon composite using a step high temperature pyrolytic cracking (HTP) first, then lead to Made from peracid is activated;
The acid activation processing is that attapulgite/carbon composite is added in acid solution to be lauched in 150~180 DEG C of conditions Thermal response 6~12 hours.
2. a kind of attapulgite as described in claim 1-activated carbon from activated sludge soil remediation material preparation method, feature It is: the preparation method is that,
(1) the vegetable seed dregs of fat and attapulgite powder are uniformly mixed, then gained mixture is placed under inert atmosphere and is pyrolyzed, made Obtain attapulgite/carbon composite;
(2) the resulting attapulgite/carbon composite of step (1) is added in acid solution and carries out hydro-thermal process, obtained Attapulgite/absorbent charcoal composite material.
3. attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material preparation method, feature exist In: in step (1), the mass ratio of the vegetable seed dregs of fat and attapulgite powder is 0.5~3:1.
4. attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material preparation method, feature exist In: in step (1), be pyrolyzed be 450~650 DEG C under the conditions of react 2~5 hours.
5. attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material preparation method, feature exist In: in step (2), the mass ratio of attapulgite/carbon composite and acid solution is 0.1~0.3:1.
6. attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material preparation method, feature exist 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. attapulgite as claimed in claim 2-activated carbon from activated sludge soil remediation material preparation method, feature exist 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 CN106947486A (en) 2017-07-14
CN106947486B true 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)

Families Citing this family (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
CN110156012B (en) * 2019-06-04 2020-12-25 北方民族大学 Activated carbon and method for preparing activated carbon by using waste edible oil
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

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
"凹凸棒石/脱硅稻壳炭复合材料吸附Pb2+、Cu2+、Ni2+的对比研究;刘文杰等;《化工新型材料》;20150531;第43卷(第5期);第170-171页 *

Also Published As

Publication number Publication date
CN106947486A (en) 2017-07-14

Similar Documents

Publication Publication Date Title
CN106947486B (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
Wang et al. Comparisons of biochar properties from wood material and crop residues at different temperatures and residence times
CN105731752B (en) A method of charcoal is prepared using excess sludge and hazelnut shell copyrolysis
WO2016176906A1 (en) Method for producing canna indica biochar capable of adsorbing ammonia nitrogen and cadmium simultaneously
CN110586030B (en) Preparation method of modified charcoal capable of adsorbing and fixing cadmium and copper in soil by cyclic utilization of heat
CN103833274A (en) Heavy metal-contaminated soil solidifying agent and application method thereof
CN105753608A (en) Preparation method and application of novel iron-based biochar
CN104150460B (en) The method of template synthesis high-ratio surface biomass carbon material
CN106744936A (en) A kind of method that biomass cauline leaf separation prepares absorbent charcoal material
CN105174254B (en) A kind of method that activated carbon and furfural are prepared by raw material of corncob
CN109336082B (en) Straw treatment method, biochar and preparation method and application thereof
Liu et al. Comparative analysis of the properties of biochars produced from different pecan feedstocks and pyrolysis temperatures
CN107128899A (en) A kind of preparation method of spherical nitrogen-doped carbon nano material
CN109704327A (en) The method that bio-oil makes multiple hole carbon material
CN112457853B (en) Zinc-rich biochar, preparation method thereof and application of zinc-rich biochar in passivation and remediation of heavy metal contaminated soil
CN110615437A (en) Comprehensive utilization method of lignite
CN105776796A (en) Method of reducing heavy metal bio-availability through pig manure pyrolysis and biochar application of pig manure
CN105536698A (en) Preparation method of papermaking sludge activated biochar
CN112209378A (en) Waste vinasse biochar, preparation method thereof and application of waste vinasse biochar as soil conditioner
CN102786967A (en) Method for preparing biochar from using sludge
CN107032352A (en) A kind of method that citrus peel residue prepares activated carbon from activated sludge
CN110627064B (en) Method for preparing nitrogen-doped activated carbon material by using plant asphalt as raw material
CN102516322B (en) Method for preparing levoglucosenone with magnetic solid phosphoric acid catalyst
CN109158083B (en) Preparation method and application of biomass-based carbon material

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