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CN110237818A - A kind of preparation method and application of nitrogen sulphur codope charcoal - Google Patents

A kind of preparation method and application of nitrogen sulphur codope charcoal Download PDF

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Publication number
CN110237818A
CN110237818A CN201910516949.XA CN201910516949A CN110237818A CN 110237818 A CN110237818 A CN 110237818A CN 201910516949 A CN201910516949 A CN 201910516949A CN 110237818 A CN110237818 A CN 110237818A
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charcoal
nitrogen sulphur
nitrogen
preparation
sulphur codope
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CN110237818B (en
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严丽丽
郭锐税
饶品华
王润锴
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Shanghai University of Engineering Science
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Shanghai University of Engineering Science
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    • 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
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • 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
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28054Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J20/28057Surface area, e.g. B.E.T specific surface area
    • B01J20/28059Surface area, e.g. B.E.T specific surface area being less than 100 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/24Nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/0234Nitrogen-, phosphorus-, arsenic- or antimony-containing compounds
    • B01J31/0271Nitrogen-, phosphorus-, arsenic- or antimony-containing compounds also containing elements or functional groups covered by B01J31/0201 - B01J31/0231
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/61310-100 m2/g
    • 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
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • 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
    • B01J2220/4875Sorbents characterised by the starting material used for their preparation the starting material being a waste, residue or of undefined composition
    • B01J2220/4887Residues, wastes, e.g. garbage, municipal or industrial sludges, compost, animal manure; fly-ashes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
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  • Environmental & Geological Engineering (AREA)
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  • Life Sciences & Earth Sciences (AREA)
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  • Hydrology & Water Resources (AREA)
  • Materials Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Carbon And Carbon Compounds (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The present invention relates to a kind of preparation method and application of nitrogen sulphur codope charcoal, carry out pyrolysis processing after biological carbon feedstock is crushed, and mesh screen is crossed after cooling;Nitrogen sulphur source is mixed, then nitrogen atmosphere calcination processing with charcoal, nitrogen sulphur codope charcoal is prepared.Compared with prior art, modification biological charcoal prepared by the present invention not only has good absorption property, moreover it is possible to pass through phthalic acid ester in activation persulfate efficient degradation water.The features such as modification biological charcoal of invention has raw material cheap and easy to get, and preparation process is simple, environmentally protective, the removal of organic pollutant suitable for water process.

Description

A kind of preparation method and application of nitrogen sulphur codope charcoal
Technical field
The present invention relates to field of environment protection, a kind of preparation method more particularly, to nitrogen sulphur codope charcoal and answer With.
Background technique
Charcoal be by high temperature pyrolysis organic substance, such as agricultural residue, animal waste or xylophyta, generation Granular charcoal, and improvement environment aspect is produced and is applied to, soil is usually applied to improve soil property or storage Carbon.Charcoal has large surface area, complicated pore structure and changeable surface composition, therefore is considered a kind of efficient Adsorbent.Charcoal is nontoxic, harmless, and raw material is extensive, cheap, can largely prepare, and surface oxygen functional group is more, and easy surface changes Property.It is modified to its surface with the method for nonmetal doping, the absorption property of Carbon Materials can not only be improved, can also be increased certainly By the generation of base, there are catalysis potentiality, and preparation method is simple, operation is easy, and success rate is high, less energy consumption, for going to remove water Organic pollutant phthalic acid ester effect in body is fine.
Sulphur plays the role of plant growth very important as the nutrient for being only second to nitrogen, phosphorus and potassium.Meanwhile sulphur Plant growth regulating, removing toxic substances and it is degeneration-resistant etc. during also function to certain effect, be an important factor for influencing plant quality, The importance of growth and metabolic process to plant is self-evident.Currently, the whole world about more than 70 the soil of a countries and regions deposit The a lack of sulfur or potential a lack of sulfur the phenomenon that, a lack of sulfur can bring about great losses to agricultural production, to influence quality of agricultural product, and right Ecological environment causes potential threat.The charcoal for the nitrogen sulfur doping being related in the present invention phthalic acid in effectively removing water While this environmental contaminants of ester, unlimited potential also is provided for application in the soil.
Currently, the preparation and its application in organic pollutant removal that have not been reported nitrogen sulphur codope charcoal.For example, Chinese patent CN109052364A discloses a kind of preparation method and application of porous nitrogen sulphur codope carbon nanosheet material of two dimension, Preparation method includes the following steps: that (1) stirs gelatin with chitosan and foaming agent with certain proportion in 50~80 DEG C of water The gel of formation is precipitated in excessive solidification liquid at gel and forms cavernous body by 0.1~2h;The foaming agent potassium carbonate, alkali Formula magnesium carbonate or melamine;(2) gel that step (1) is formed is precipitated in excessive solidification liquid and forms cavernous body;Then Cavernous body is placed in 330 DEG C~400 DEG C Muffle furnaces, heat preservation 0.5~4h of calcination processing carries out foaming and pre- carbonization, obtains pre- carbon Change material;(3) the resulting pre- char-forming material of step (2) is ground uniformly with certain proportion and thiocarbamide, obtained mixture is existed Calcination processing obtains the porous nitrogen sulphur codope carbon nanosheet material of two dimension under protective atmosphere.But the two dimension that the patent is prepared Porous nitrogen sulphur codope carbon nanosheet is used primarily as lithium ion battery lithium anode protection materials.
Summary of the invention
It is raw that it is an object of the present invention to overcome the above-mentioned drawbacks of the prior art and provide a kind of nitrogen sulphur codopes The preparation method of object charcoal.
The purpose of the present invention can be achieved through the following technical solutions:
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
Pyrolysis processing is carried out after biological carbon feedstock is crushed, is then cooled down, obtained charcoal crosses mesh screen;
Nitrogen sulphur source is mixed, then calcination processing with charcoal, nitrogen sulphur codope charcoal is prepared.
Preferably, biological carbon feedstock is animals and plants waste.
It is further preferred that biological carbon feedstock includes peanut shell, rice husk, corn stover, cocoanut shell or animal excrements.
Preferably, the temperature control of pyrolysis is 200-700 DEG C, and the processing time is 1-3h, heating rate is 3-5 DEG C/min, The above processing occurs under conditions of nitrogen protection, and stringent limitation cannot have oxygen.The charcoal handled through the above scheme Surface can generate the new functional groups such as a large amount of sulfur oxide, thiophenic sulfur, pyrroles's nitrogen, pyridine nitrogen and graphene nitrogen, to the charcoal Absorption and catalytic performance have very big facilitation.
Preferably, it is 100-300 mesh that charcoal, which crosses grit number,.
Preferably, nitrogen sulphur source includes thiocarbamide, cysteine ??acid, sulfonamide or thioacetamide.
Preferably, nitrogen sulphur source and charcoal mass ratio are 0.1-0.9.
Preferably, the temperature control of calcining is, not less than 350 DEG C or more, preferably 350 DEG C, is 1-3h, rises the processing time Warm rate is 1-3 DEG C/min, and the above processing occurs to carry out under conditions of nitrogen protection.When temperature is controlled in the temperature range It is interior, temperature is especially controlled to the substance decomposition that can make at 350 DEG C nitrogenous sulphur source, be supported on charcoal surface and hole it is interior Portion.
Nitrogen sulphur codope charcoal, which is prepared, can be used for removing organic pollutant in water body, can be changed using this kind Property charcoal remove plasticizer phthalic acid ester.
Preferably, phthalic acid ester removal experiment is carried out under conditions of 25 DEG C of isothermal vibrations.
Preferably, phthalic acid ester pH value of solution is 5-7.
Preferably, the removal effect of phthalic acid ester can reach 90% or more.
Compared with prior art, the invention has the following advantages that
1. the present invention is using agricultural wastes as raw material, preparation method is simple, low in cost;
2. charcoal is doped with nitrogen and element sulphur by the present invention, the existing forms of nitrogen have 3 kinds, are pyridine nitrogen, pyrroles respectively Nitrogen and graphene nitrogen;The existing forms of sulphur have 2 kinds, are thiophenic sulfur respectively and the sulphur that is oxidized;The wherein sulphur of pyridine nitrogen and oxidation Presence enhance the absorption property of modification biological charcoal, graphene nitrogen and thiophenic sulfur provide activation persulfuric acid for modification biological charcoal The potentiality of salt.
3. the modification biological charcoal specific surface area that the present invention obtains is 1.46-28.28m2g-1, surface sulfur content is 0.5- 6.59%, nitrogen content 16.42-21.8%, by activating potassium peroxydisulfate, the removal rate of phthalic acid ester is reached as high as 96.75%;
4. the present invention realizes the substance by pyrolytic as nitrogen source sulphur source, by nitrogen and sulfur doping in charcoal, Modified charcoal adsorption capacity also has phthalic acid ester in the water that can degrade by activation persulfate while enhancing New capability.The present invention provides not only a kind of preparation method of charcoal nonmetal doping, is also useless containing phthalic acid ester The improvement of water provides a kind of efficient material.
Specific embodiment
The present invention is described in detail combined with specific embodiments below.Following embodiment will be helpful to the technology of this field Personnel further understand the present invention, but the invention is not limited in any way.It should be pointed out that the ordinary skill of this field For personnel, without departing from the inventive concept of the premise, various modifications and improvements can be made.These belong to the present invention Protection scope.
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
(1) biological carbon feedstock, such as peanut shell, rice husk, corn stover, cocoanut shell or animal excrements etc. are crushed laggard Row pyrolysis processing, control control heating rate is 3-5 DEG C/min in treatment process, and temperature is risen to 200-700 DEG C, handles 1- Then 3h cools down, whole process, which strictly limits, cannot oxygen, carries out under conditions of nitrogen protection, so that being prepared Biological carbon surface can generate the new functional groups such as a large amount of sulfur oxide, thiophenic sulfur, pyrroles's nitrogen, pyridine nitrogen and graphene nitrogen, it is right The charcoal that the absorption of the charcoal and catalytic performance have very big facilitation to obtain crosses the mesh screen of 100-300 mesh;
(2) nitrogen sulphur source, such as thiocarbamide, cysteine ??acid, sulfonamide or thioacetamide are mixed with charcoal, nitrogen sulphur source with Charcoal mass ratio is 0.1-0.9, then calcination processing, should control heating rate be in the process 1-3 DEG C/min, and be warming up to not low In 350 DEG C of isothermal holding 1-3h, equally stringent limitation cannot there should be oxygen in the process, be carried out under conditions of nitrogen protection, The substance decomposition for making nitrogenous sulphur source is supported on the surface of charcoal and the inside in hole, and nitrogen sulphur codope charcoal is prepared.
Nitrogen sulphur codope charcoal, which is prepared, can be used for removing organic pollutant in aqueous solution, can use this kind Charcoal removes plasticizer phthalic acid ester.Removal experiment is carried out under conditions of 25 DEG C of isothermal vibrations, O-phthalic Acid esters pH value of solution is 5-7, and removal effect can reach 90% or more.
More detailed case study on implementation below, by following case study on implementation further illustrate technical solution of the present invention with And the technical effect that can be obtained.
Embodiment 1
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
(1) preparation of charcoal:
Peanut shell is cleaned up, with being placed in Muffle furnace for pulverizer coarse crushing, control heating rate be 4 DEG C/ Temperature is risen to 375 DEG C of pyrolysis 1h, Temperature fall by min, and the entire treatment process in Muffle furnace needs to control in nitrogen protection Under atmosphere, burned charcoal is crossed to the mesh screen of 300 mesh.
(2) preparation of nitrogen sulphur codope charcoal:
Thiocarbamide and the charcoal for crossing mesh screen are uniformly mixed with the mass ratio of 0.1:1, heating rate is controlled in Muffle furnace Temperature is risen into 350 DEG C of calcining 1h, Temperature fall for 2 DEG C/min, the entire treatment process in Muffle furnace needs to control in nitrogen Under gas shielded atmosphere, deionized water clean the surface is then used, 60 DEG C are dried for standby.
(3) removal of diethyl phthalate
It is 20mg L that modified charcoal 100mg, which is added to the 20mL concentration containing 10mg potassium peroxydisulfate,-1Adjacent benzene two In the brown conical flask of formic acid diethylester, ultrasonic 3min, 25 DEG C of constant temperature oscillations in constant temperature oscillator, reaction 2h sampling.By sample Product measure phthalic acid diethyl in sample supernatant with high performance liquid chromatography after 0.22 μm of nylon filter filtering The content of ester, calculating removal rate is 97.3%.
Embodiment 2
Embodiment 2 is the change case of embodiment 1, and variation place is that the cracking temperature of charcoal in step (1) is 200, 450,700 DEG C, removal rate is shown in Table 1.
Table 1
Pyrolysis temperature (DEG C) 200 450 700
Diethyl phthalate removal rate (%) 80.2 83.7 30.2
Embodiment 3
Embodiment 3 is the change case of embodiment 1, and variation place is that the mass ratio of step (2) thiocarbamide and charcoal is 0.3,0.5,0.7,0.9, removal rate is shown in Table 2.
Table 2
The mass ratio of thiocarbamide and charcoal 0.3 0.5 0.7 0.9
Diethyl phthalate removal rate (%) 83.7 45.8 30.6 20.3
Embodiment 4
Embodiment 4 is the change case of embodiment 1, and variation place is that the grit number of crossing of charcoal in step (1) is 100 Hes 200 mesh, removal rate are shown in Table 3.
Table 3
Charcoal mesh number 100 200
Diethyl phthalate removal rate (%) 83.7 92.8
Embodiment 5
Embodiment 5 is the change case of embodiment 1, and variation place is that step (1) charcoal was pyrolyzed the mesh screen of 300 mesh, The removal of repefral and dibutyl phthalate is respectively used in step (3), removal rate is shown in Table 4.
Table 4
Pollutant kind Repefral Diethyl phthalate Dibutyl phthalate
Removal rate (%) 93.3 96.7 85.6
Embodiment 6
Embodiment 6 is the change case of embodiment 1, and variation place is that step (2) changes half Guang into as the thiocarbamide of nitrogen sulphur source One of propylhomoserin, sulfonamide or thioacetamide.
Table 5
Embodiment 7
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
(1) preparation of charcoal:
Rice husk is cleaned up, with being placed in Muffle furnace for pulverizer coarse crushing, control heating rate is 3 DEG C/min Temperature is risen into 200 DEG C of pyrolysis 3h, Temperature fall, the entire treatment process in Muffle furnace needs to control in nitrogen protection atmosphere Under, burned charcoal is crossed to the mesh screen of 100 mesh.
(2) preparation of nitrogen sulphur codope charcoal:
Cysteine ??acid and the charcoal for crossing mesh screen are uniformly mixed with the mass ratio of 0.5:1, heating is controlled in Muffle furnace Temperature is risen to 400 DEG C of calcining 1h, Temperature fall for 1 DEG C/min by rate, and the entire treatment process in Muffle furnace needs to control Under nitrogen protection atmosphere, deionized water clean the surface is then used, 60 DEG C are dried for standby.
(3) removal of diethyl phthalate
It is 20mg L that modified charcoal 100mg, which is added to the 20mL concentration containing 10mg potassium peroxydisulfate,-1Adjacent benzene two In the brown conical flask of formic acid diethylester, ultrasonic 3min, 25 DEG C of constant temperature oscillations in constant temperature oscillator, reaction 2h sampling.By sample Product measure phthalic acid diethyl in sample supernatant with high performance liquid chromatography after 0.22 μm of nylon filter filtering The content of ester, calculating removal rate is 93.5%.
Embodiment 8
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
(1) preparation of charcoal:
Cocoanut shell is cleaned up, with being placed in Muffle furnace for pulverizer coarse crushing, control heating rate be 5 DEG C/ Temperature is risen to 600 DEG C of pyrolysis 2h, Temperature fall by min, and the entire treatment process in Muffle furnace needs to control in nitrogen protection Under atmosphere, burned charcoal is crossed to the mesh screen of 200 mesh.
(2) preparation of nitrogen sulphur codope charcoal:
Thiocarbamide and the charcoal for crossing mesh screen are uniformly mixed with the mass ratio of 0.7:1, heating rate is controlled in Muffle furnace Temperature is risen into 450 DEG C of calcining 2h, Temperature fall for 3 DEG C/min, the entire treatment process in Muffle furnace needs to control in nitrogen Under gas shielded atmosphere, deionized water clean the surface is then used, 60 DEG C are dried for standby.
(3) removal of diethyl phthalate
It is 20mg L that modified charcoal 100mg, which is added to the 20mL concentration containing 10mg potassium peroxydisulfate,-1Adjacent benzene two In the brown conical flask of formic acid diethylester, ultrasonic 3min, 25 DEG C of constant temperature oscillations in constant temperature oscillator, reaction 2h sampling.By sample Product measure phthalic acid diethyl in sample supernatant with high performance liquid chromatography after 0.22 μm of nylon filter filtering The content of ester, calculating removal rate is 92.5%.
Embodiment 9
A kind of preparation method of nitrogen sulphur codope charcoal, comprising:
(1) preparation of charcoal:
Animal excrements are cleaned up, with being placed in Muffle furnace for pulverizer coarse crushing, controlling heating rate is 5 DEG C/temperature rises to 700 DEG C of pyrolysis 1h by min, Temperature fall, the entire treatment process in Muffle furnace needs to control protects in nitrogen It protects under atmosphere, burned charcoal is crossed to the mesh screen of 300 mesh.
(2) preparation of nitrogen sulphur codope charcoal:
Thioacetamide and the charcoal for crossing mesh screen are uniformly mixed with the mass ratio of 0.9:1, controls and rises in Muffle furnace Temperature is risen to 350 DEG C of calcining 3h, Temperature fall for 3 DEG C/min by warm rate, and the entire treatment process in Muffle furnace needs to control Then system uses deionized water clean the surface, 60 DEG C are dried for standby under nitrogen protection atmosphere.
(3) removal of diethyl phthalate
It is 20mg L that modified charcoal 100mg, which is added to the 20mL concentration containing 10mg potassium peroxydisulfate,-1Adjacent benzene two In the brown conical flask of formic acid diethylester, ultrasonic 3min, 25 DEG C of constant temperature oscillations in constant temperature oscillator, reaction 2h sampling.By sample Product measure phthalic acid diethyl in sample supernatant with high performance liquid chromatography after 0.22 μm of nylon filter filtering The content of ester, calculating removal rate is 95.6%.
Comparative example 1
Comparative example 1 is the comparative example of embodiment 1, and comparison place is, does not carry out carrying out nitrogen sulphur to charcoal in step (2) Codoping modified, diethyl phthalate removal rate is 20.3%, and the removal capacity of unmodified charcoal is co-doped with lower than nitrogen sulphur The removal capacity of miscellaneous charcoal.
Comparative example 2
Comparative example 1 is the comparative example of embodiment 1, and comparison place is, potassium peroxydisulfate, adjacent benzene two are not added in step (3) The removal rate of formic acid diethylester is 56.8%, and nitrogen sulphur codope charcoal has the function of activating persulfate.
In the description of this specification, the description of reference term " one embodiment ", " example ", " specific example " etc. means Particular features, structures, materials, or characteristics described in conjunction with this embodiment or example are contained at least one implementation of the invention In example or example.In the present specification, schematic expression of the above terms may not refer to the same embodiment or example. Moreover, particular features, structures, materials, or characteristics described can be in any one or more of the embodiments or examples to close Suitable mode combines.
The above description of the embodiments is intended to facilitate ordinary skill in the art to understand and use the invention. Person skilled in the art obviously easily can make various modifications to these embodiments, and described herein general Principle is applied in other embodiments without having to go through creative labor.Therefore, the present invention is not limited to the above embodiments, ability Field technique personnel announcement according to the present invention, improvement and modification made without departing from the scope of the present invention all should be of the invention Within protection scope.

Claims (10)

1. a kind of preparation method of nitrogen sulphur codope charcoal, which is characterized in that this method comprises:
Pyrolysis processing is carried out after biological carbon feedstock is crushed, mesh screen is crossed after cooling;Nitrogen sulphur source is mixed with charcoal, then calcines place Reason, is prepared nitrogen sulphur codope charcoal.
2. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the charcoal Raw material is animals and plants waste.
3. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1 or 2, which is characterized in that the life Object carbon feedstock includes peanut shell, rice husk, corn stover, cocoanut shell or animal excrements.
4. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the pyrolysis Temperature control is 200-700 DEG C, and the processing time is 1-3h, heating rate is 3-5 DEG C/min, is carried out in a nitrogen atmosphere.
5. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the charcoal Crossing grit number is 100-300 mesh.
6. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the nitrogen sulphur source Including thiocarbamide, cysteine ??acid, sulfonamide or thioacetamide.
7. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the nitrogen sulphur source It is 0.1-0.9 with charcoal mass ratio.
8. a kind of preparation method of nitrogen sulphur codope charcoal according to claim 1, which is characterized in that the calcining Temperature control is, not less than 350 DEG C, preferably 350 DEG C, the processing time is 1-3h, heating rate is 1-2 DEG C/min, the above processing Process carries out under the conditions of nitrogen atmosphere.
9. nitrogen sulphur codope charcoal answering in Organic Pollutants In Water removal is prepared in method as described in claim 1 With.
10. a kind of application of nitrogen sulphur codope charcoal according to claim 9, which is characterized in that the nitrogen sulphur is co-doped with Miscellaneous charcoal is added in the aqueous solution containing phthalic acid ester and a small amount of potassium peroxydisulfate, is placed in constant temperature oscillator, 25 DEG C of perseverances Temperature concussion, adsorb and degrade organic matter therein.
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Cited By (12)

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CN111925806A (en) * 2020-07-20 2020-11-13 华东理工大学 Sulfur-doped nano ferroferric oxide/biochar composite material as well as preparation method and application thereof
CN111925806B (en) * 2020-07-20 2021-10-29 华东理工大学 Sulfur-doped nano ferroferric oxide/biochar composite material as well as preparation method and application thereof
CN112023967A (en) * 2020-08-14 2020-12-04 中南大学 Selenium and nitrogen co-doped biochar catalytic material as well as preparation method and application thereof
CN112316967A (en) * 2020-10-21 2021-02-05 江苏中烟工业有限责任公司 Preparation method of nitrogen-sulfur double-doped biochar material for degrading phenol in water
CN112717975A (en) * 2020-12-09 2021-04-30 迪天环境技术南京股份有限公司 Heteroatom-loaded biomass charcoal material and application thereof
CN113385173A (en) * 2021-06-26 2021-09-14 昆明理工大学 Preparation method and application of coral stacked biomass charcoal-based catalyst
CN115925125A (en) * 2022-01-24 2023-04-07 重庆交通大学 Ecological floating bed device for landscape water body restoration treatment
CN114653391A (en) * 2022-03-11 2022-06-24 大连工业大学 Preparation method of carbon-based catalytic membrane with high selectivity and contamination resistance
CN114653391B (en) * 2022-03-11 2023-10-03 大连工业大学 Preparation method of carbon-based catalytic film with high selectivity and pollution resistance
CN116161640A (en) * 2022-09-09 2023-05-26 广东容钠新能源科技有限公司 Spherical long-circulation stable biomass hard carbon material, preparation method and application
CN115746864A (en) * 2022-11-01 2023-03-07 中国农业科学院农业资源与农业区划研究所 Biochar-based soil conditioner for coastal saline-alkali soil and preparation method thereof
CN115746864B (en) * 2022-11-01 2024-07-23 中国农业科学院农业资源与农业区划研究所 Biochar-based soil modifier for coastal saline-alkali soil and preparation method thereof
CN115990502A (en) * 2023-01-10 2023-04-21 吉林大学 Nitrogen-sulfur co-doped modified biochar material and application thereof
CN116081902A (en) * 2023-04-07 2023-05-09 湖南迪亚环境工程股份有限公司 Kitchen wastewater treatment method
CN117299152A (en) * 2023-11-27 2023-12-29 鲁东大学 Preparation method of sulfur-doped biochar
CN117299152B (en) * 2023-11-27 2024-03-12 鲁东大学 Preparation method of sulfur-doped biochar

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