CN106390926B - A kind of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials and the preparation method and application thereof - Google Patents
A kind of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials and the preparation method and application thereof Download PDFInfo
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- CN106390926B CN106390926B CN201610812764.XA CN201610812764A CN106390926B CN 106390926 B CN106390926 B CN 106390926B CN 201610812764 A CN201610812764 A CN 201610812764A CN 106390926 B CN106390926 B CN 106390926B
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Abstract
The invention discloses a kind of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials and the preparation method and application thereof.First by silkworm excrement and ZnCl2It is freeze-dried after solution mixing swelling, then silkworm excrement after freeze-drying is carried out to activation reaming reaction in protective gas, silkworm excrement base multi-stage porous Carbon Materials are obtained after then cleaning, be centrifuged and drying again, then be passed through O2Atmosphere prepares the O doping surfaces modification more materials of silkworm excrement base multi-stage porous charcoal in plasma reactor, which can be applied to pesticide and delay controlled release aspect.The present invention is at high temperature activated silkworm excrement using protection gas bar part; the modification of O doping surfaces is carried out to the material by way of plasma modification again; obtained Carbon Materials specific surface area with higher and controllable polar group containing O, can there is higher adsorption capacity and preferable slow-releasing and controlled-releasing action to pesticide.
Description
Technical field
The invention belongs to Carbon Materials technical fields, and in particular to O doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials and its
Preparation method and application.
Background technique
Pesticide can efficiently control the harm of disease, worm, grass and other harmful organisms to crops, it is as chemical prevention
Important means, play irreplaceable role in agricultural production.However, pesticide only a small amount of in specific time can arrive
Up to crop target site, and most of pesticide is directly released into natural environment and causes pesticide utilization efficiency low.This part is not
The pesticide for playing drug effect can cause Practice for Pesticide Residue in Agricultural Products exceeded, injury and environmental pollution to non-target organism etc. many negative
Face problem.The utilization efficiency and Targeting delivery function for how effectively improving pesticide are urgently to be resolved main of current pesticide field
One of problem.
Slow controlled-release technology is that one kind can be such that pesticide activity component slowly releases within given time by physically or chemically means
It is put in target site, and drug concentration is made to maintain the novel medicine feeding technology of effective concentration or more in a long time.Biology is more
Hole charcoal is that have one of the material preferably adsorbed, main waste silkworm excrement of the silkworm excrement base charcoal in silkworm industry,
Often arbitrarily abandoning in rural area leads to environmental pollution, silkworm excrement known to from Electron microscope from natural three-dimensional drape structure and
Phosphorus content is high, can obtain high-ratio surface multiporous biological charcoal, and its surface N (O) also rich in through high temperature cabonization and activation
Group can promote its slow controlled release ability by modification.
Summary of the invention
The object of the present invention is to provide a kind of O doping vario-property silkworm excrement base multi-stage porous Carbon Materials and the preparation method and application thereof.
The present invention first carries out swelling expanding treatment to silkworm excrement, is activated at high temperature using protection gas bar part to silkworm excrement, then lead to
The mode for crossing plasma modification carries out the modification of O doping surfaces, obtained Carbon Materials specific surface with higher to the material
Long-pending and controllable polar group containing O, can there is higher adsorption capacity and preferable slow-releasing and controlled-releasing action to pesticide.
The purpose of the present invention is achieved through the following technical solutions:
O doping vario-property silkworm excrement base multi-stage porous Carbon Materials of the invention are three dimensional pore structures, Langmuir specific surface area
For 950~1300m2/ g, total pore volume is in 0.4-0.60cm3/ g, wherein micropore specific area and Kong Rong account for total specific surface area and hole
50~70% held.
The preparation method of O doping vario-property silkworm excrement base multi-stage porous Carbon Materials of the invention, includes the following steps:
(1) by Faeces bombycis and ZnCl2It is freeze-dried after solution mixing swelling；Silkworm excrement is in N after being lyophilized2, the protectiveness such as Ar gas
Reaming reaction is activated in gas, is then cleaned after being rinsed 3 times using dilute hydrochloric acid and deionized water again and is dried to obtain silkworm excrement base multi-stage porous
Carbon Materials；
(2) by silkworm excrement base multi-stage porous Carbon Materials and in O2It is modified that plasma reactor progress surface is put under atmosphere, it is defeated
Enter 20~50V of voltage, 1~30min of modification time, modification temperature is not higher than 200 DEG C；It is modified to be obtained with deionized water cleaning, drying
To O doping vario-property silkworm excrement base multi-stage porous Carbon Materials.
As the further preferred of scheme, the ZnCl of step (1) Faeces bombycis and mass concentration 0.25g/mL2Solution mixes matter
Body ratio is 1:100~200, and mixing temperature is 30~50 DEG C, and incorporation time is 0.5~3h.Freezing dry process is first at -25 °
DEG C~-20C under 2~4h of precooling, be then cooled to -60 DEG C~-40 DEG C 24~72h of freeze-drying.
As the further preferred of scheme, plasma reactor 30~40V of input voltage, 5~20min of modification time.
As the further preferred of scheme, silkworm excrement reaming reaction temperature is 300~700 DEG C after the freeze-drying, the reaction time
For 0.5~5h.Optimum reaction condition is that reaming reaction temperature is 400~600 DEG C, and the reaction time is 2~3h.
In terms of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials of the invention can be applicable to medicine sustained and controlled release, especially
In terms of pesticide delays controlled release.
Product of the present invention, which is applied, delays controlled release field in pesticide, adsorbs anabasine pesticide Diacloden, absorption using the material
Load capacity can reach 500mg/g or more, and can prepare and delay controlled release farm chemical carrier within the scope of 15~60 days effective time of sustained release (to release
90% Diacloden of total amount is put as endpoint calculation).
The principle of the invention: limited swelling work can occur in aqueous solution for the special macromolecular structure as possessed by silkworm excrement
With volume will increase 1~20 times after swelling, silkworm excrement after swelling is freeze-dried by substep, freezing pretreatment can make silkworm excrement
Fluffy macromolecular structure when keeping being swollen, then freeze-drying ensure that the abundant drying of silkworm excrement, and further consolidate its structure, can prolong
Long silkworm excrement carbon skeleton improves the specific surface area and porosity of silkworm excrement base Carbon Materials after carbonization-activation.It is added in swelling process simultaneously
ZnCl2Solution can make activator ZnCl2It is sufficiently mixed with silkworm excrement, more conducively next step obtains better activated material.
The present invention carries out O doping surfaces to the material under the conditions of oxygen-enriched atmosphere by way of plasma modification and repairs
Decorations, can make the C atom of material surface in conjunction with the O atom under plasmoid, and the material surface formation-COOH ,-
The oxygen-containing groups such as OH and-CHO.In conventional pesticide molecule mostly containing polar group (carboxyl, carbonyl, sulfur-bearing and contain cl radical
Deng), and this segment polarity group is also the dominant reactive part in pesticide, these polar groups can with it is oxygen-containing in silkworm excrement
Group combines.The oxygen-containing group quantity of silkworm excrement base charcoal material surface can be adjusted by controlling plasma modification condition, into
And the adsorption capacity of pesticide and Carbon Materials can be regulated and controled, reach the slow-releasing and controlled-releasing action to pesticide.
Plasma just refers to ionized gas, it is the molecular collection of the grains such as electronics, ion, atom, molecule or free radical
Zoarium, these are all as lively as a cricket reactive species.Particle combines bond energy between capable of destroying original material molecule in plasma, and
Molecule and plasma intermediate ion is set in material to be combined into new chemical bond, and since its energy is penetrated far below high-energy radioactive
Line, thus plasma pertains only to the surface of material, does not influence the bulk properties of material, and plasma modification has efficient, ring
The advantages that protecting, be easily controllable, easy to operate.
Compared with prior art, the present invention is advantageous in that:
1. the raw materials used in the present invention silkworm excrement has native three dimensional pleated structure and contains a large amount of carboxyls, hydroxyl and amino group
And cellulose components, ZnCl2Activating mechanism be dissolution cellulose removing hydrone, use ZnCl2Expanding treatment silkworm excrement is activated,
High-ratio surface microcellular structure can be formed on activation silkworm excrement surface, be obtained by the microcellular structure of high-ratio surface to the higher of pesticide
Adsorption capacity.
2. by silkworm excrement swelling action can in the case where not changing silkworm excrement polymer configuration by silkworm excrement volume increase 1~
20 times, its internal structure is fixed by silkworm excrement after swelling by way of freeze-drying, silkworm excrement base raw material of wood-charcoal after activation can be improved
The porosity and specific surface area of material.
3. by ZnCl in swelling process2Solution is adsorbed onto silkworm excrement, by being freeze-dried ZnCl2It is fixed in silkworm excrement
Portion and surface, the method increase activator ZnCl2With the dispersion degree of silkworm excrement, more conducively activate in next step.
4. being modified by plasma mode to silkworm excrement base Carbon Materials, in O2Under atmosphere by plasma O atom with
Material surface C atom combines, the oxygen-containing groups such as formation-COOH ,-OH and-CHO.The reaction and tradition O doping way (carbohydrate, fibre
Dimension element etc. hydration methods) compared to having a clear superiority: (1) without containing other oxygenatedchemicals only use O2Doping, reduces other elements
Influence to reaction system；(2) reaction time short (within 30min), be added without other reaction dissolvents reduce reaction after centrifugation,
Filtering and etc..
5. the reaction process duration short (within 30min), plasma modification temperature are low (200 DEG C or less), with tradition
High-temperature calcination method ratio (2~6h, 400~600 DEG C), has a clear superiority, and the method reduce high temperature O2To C in material
The consumption of atom had not only improved product yield but also had guaranteed material surface pattern and specific surface area.
6. by the quantity of factor controllings silkworm excrement surface groups containing O such as plasma modification condition, since group containing O can be to agriculture
Adsorption capacity between medicine and material has an important influence on, therefore passes through the controllable silkworm excrement base Carbon Materials of plasma modification condition and agriculture
Adsorption capacity between medicine molecule achievees the purpose that delay controlled release to pesticide.
7. material prepared by the present invention is for adsorbing anabasine pesticide Diacloden, adsorbance can reach 500mg/g
More than, sustained-release pesticides carrier of the slow-release time within the scope of 15~60 days can be prepared (to discharge always by regulating and controlling carburizing temperature
90% Diacloden is measured as endpoint calculation).
Detailed description of the invention
Fig. 1 is that Faeces bombycis is sliced electron-microscope scanning figure.
Fig. 2 is silkworm excrement slice electron-microscope scanning figure after swelling freeze-drying.
Fig. 3 is silkworm excrement inner surface electron-microscope scanning figure after swelling freeze-drying.
Fig. 4 is that embodiment 1O doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials electron-microscope scanning figure.
Fig. 5 difference slow-release material load capacity curve.
Fig. 6 difference slow-release material is sustained release profiles.
Specific embodiment
The present invention will be further described with reference to the accompanying drawings and examples, but the scope of protection of present invention is not
It is confined to the range of embodiment statement.
Embodiment 1
A kind of preparation method of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials, includes the following steps,
(1) by the ZnCl of Faeces bombycis and mass concentration 0.25g/mL2Solution is 1:100 progress according to plastid ratio at 30 DEG C
Silkworm excrement is pulled out after mixing swelling 3.0h, freeze-drying process is carried out to silkworm excrement, first the freezing pretreatment 4h at -20 DEG C, then is cooled down
For 24 hours to -60 DEG C of freeze-dryings, silkworm excrement after being lyophilized.
(2) silkworm excrement is in N after being lyophilized2300 DEG C are raised to the heating rate of 5 DEG C/min in atmosphere, and is protected at 300 DEG C
It holds 5.0h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 20V, modification time 2min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O and mix
Miscellaneous surface modification silkworm excrement base multi-stage porous Carbon Materials.
Embodiment 2
(1) by the ZnCl of Faeces bombycis and mass concentration 0.25g/mL2Solution is 1:120 progress according to plastid ratio at 35 DEG C
Silkworm excrement is pulled out after mixing swelling 2.5h, freeze-drying process is carried out to silkworm excrement, first the freezing pretreatment 3h at -20 DEG C, then is cooled down
To -55 DEG C of freeze-drying 36h, silkworm excrement after being lyophilized.
(2) silkworm excrement after freeze-drying is raised to 350 DEG C in an ar atmosphere with the heating rate of 5 DEG C/min, and is protected at 350 DEG C
It holds 4.0h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 30V, modification time 6min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O and mix
Miscellaneous surface modification silkworm excrement base multi-stage porous Carbon Materials.
Embodiment 3
(1) by the ZnCl of Faeces bombycis and mass concentration 0.30g/mL2Solution is 1:140 progress according to plastid ratio at 40 DEG C
Silkworm excrement is pulled out after mixing swelling 2.0h, freeze-drying process is carried out to silkworm excrement, first the freezing pretreatment 2h at -25 DEG C, then is cooled down
To -50 DEG C of freeze-drying 48h, silkworm excrement after being lyophilized.
(2) silkworm excrement is in N after being lyophilized2400 DEG C are raised to the heating rate of 5 DEG C/min in atmosphere, and is protected at 400 DEG C
It holds 3.0h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 35V, modification time 10min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O
Doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials.
Embodiment 4
(1) by the ZnCl of Faeces bombycis and mass concentration 0.25g/mL2Solution is 1:160 progress according to plastid ratio at 40 DEG C
Silkworm excrement is pulled out after mixing swelling 1.5h, freeze-drying process is carried out to silkworm excrement, first the freezing pretreatment 2.5h at -25 DEG C, then is dropped
Temperature is to -40 DEG C of freeze-drying 72h, silkworm excrement after being lyophilized.
(2) silkworm excrement is in N after being lyophilized2450 DEG C are raised to the heating rate of 5 DEG C/min in atmosphere, and is protected at 450 DEG C
It holds 2.0h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 40V, modification time 15min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O
Doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials.
Embodiment 5
(1) by the ZnCl of Faeces bombycis and mass concentration 0.30g/mL2Solution is 1:180 progress according to plastid ratio at 45 DEG C
Silkworm excrement is pulled out after mixing swelling 1.0h, freeze-drying process is carried out to silkworm excrement, first the freezing pretreatment 4h at -20 DEG C, then is cooled down
To -45 DEG C of freeze-drying 60h, silkworm excrement after being lyophilized.
(2) silkworm excrement is in N after being lyophilized2550 DEG C are raised to the heating rate of 5 DEG C/min in atmosphere, and is protected at 550 DEG C
It holds 1.0h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 45V, modification time 20min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O
Doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials.
Embodiment 6
(1) by the ZnCl of Faeces bombycis and mass concentration 0.25g/mL2Solution according to plastid ratio is 1:200, temperature is 50 DEG C
Be 0.5h mixing with the time, first -20 DEG C of freezings pre-process 4h after mixing, are carrying out freeze-drying process, be freeze-dried temperature for -
40 DEG C, time 72h.
(2) silkworm excrement is in N after being lyophilized2700 DEG C are raised to the heating rate of 5 DEG C/min in atmosphere, and is protected at 700 DEG C
It holds 0.5h and carries out reaming reaction, to be cooled to room temperature naturally, obtained solid is dissolved in cleaning dissolution ZnCl in the HCl of 1mol/L2,
It reuses after deionized water is cleaned to pH ≈ 7 and is centrifuged, be placed in baking oven and be dried overnight, silkworm excrement base multi-stage porous raw material of wood-charcoal is obtained after drying
Material.
(3) 1.0g silkworm excrement base multi-stage porous Carbon Materials are put into plasma reactor, are passed through O2As modified gas, etc.
Plasma reactor input voltage 50V, modification time 30min, it is modified cleared up 3 times with deionized water after low temperature drying obtain O
Doping surfaces modify silkworm excrement base multi-stage porous Carbon Materials.
(1) electron microscope of silkworm excrement base multi-stage porous Carbon Materials
Using Japanese Hitachi S-3400N type low power scanning electron microscope to silkworm after Faeces bombycis slice, swelling freeze-drying
O doping surfaces obtained by silkworm excrement inner surface and the embodiment of the present invention 1 modify silkworm excrement base multi-stage porous charcoal after sand slice, swelling freeze-drying
Material carries out the characterization of material surface pattern, as shown in Figure 1, Figure 2, Figure 3, Figure 4.
By Fig. 1 and Fig. 2 comparison it is found that silkworm excrement volume becomes larger after swelling and internal layer generates a large amount of pore structures.Fig. 3
It is silkworm excrement inner surface electron-microscope scanning figure after being swollen, embodies silkworm excrement tridimensional network.Fig. 4 is O doping surfaces modification silkworm excrement base
Multi-stage porous Carbon Materials electron-microscope scanning figure, it can be seen that the silkworm excrement base Carbon Materials after plasma modification can form porous knot
Structure.
(2) pore structure study of silkworm excrement base multi-stage porous Carbon Materials
The 3-Flex specific surface pore-size distribution instrument for using Micro company, the U.S. to produce is to non-swelling treatment silkworm excrement and swelling
Silkworm excrement is that raw material prepares O doping table prepared by silkworm excrement porous carbon material (according to 5 activation condition of embodiment), the present invention after processing
Face modification silkworm excrement base multi-stage porous Carbon Materials pore structure is measured, and the results are shown in Table 1.
The specific surface area and pore-size distribution of 1. silkworm excrement base multi-stage porous Carbon Materials of table.
Smicro, VtAnd VmicroRespectively indicate specific surface area provided by micropore, Kong Rong provided by total pore volume and micropore.
According to 1 column data of table it is found that silkworm excrement base multi-stage porous Carbon Materials Langmuir prepared by six kinds of embodiments compares table
Area is in 950~1300m2/ g, total pore volume is about in 0.4-0.60cm3/ g, wherein micropore specific area and Kong Rong account for total specific surface
Long-pending and Kong Rong 50~70% or so.Silkworm excrement porous carbon is prepared with silkworm excrement after non-swelling treatment silkworm excrement and swelling treatment respectively
Material, specific surface area and porosity have significant difference, and the specific surface area and porosity for not being swollen silkworm excrement base Carbon Materials is only to be swollen
60% or so of silkworm excrement base Carbon Materials afterwards.By the silkworm excrement base multi-stage porous charcoal for the O doping surfaces modification that plasma modification obtains
The data such as the specific surface area of material and hole appearance illustrate plasma modification with to there is slightly decline (about 10% or so) before modified
Can closely there be a small amount of influence to silkworm excrement base multi-stage porous carbon surface pore structure.This explanation, in the embodiment of the present invention coverage area,
Preparing obtained silkworm excrement base multi-stage porous Carbon Materials is a kind of multi-stage porous Carbon Materials with high specific surface area.
(3) different silkworm excrement base Carbon Materials and Faeces bombycis constituent content and product yield analysis
Using Japanese Hitachi S-3400N type low power scanning electron microscope energy spectrum analysis, to Faeces bombycis, unmodified silkworm
Silkworm excrement base multi-stage porous Carbon Materials obtained by the husky, embodiment of the present invention 1~6 carry out the analysis of C, N, O elemental composition and product yield
Compare as shown in table 2.
The different silkworm excrement base Carbon Materials of table 2 and Faeces bombycis constituent content and product yield analysis
| Sample | C element (%) | N element (%) | O element (%) | Product yield (%) |
| Silkworm feculae | 71.82 | 3.03 | 21.86 | - |
| Unmodified silkworm excrement base Carbon Materials | 88.18 | 6.23 | 4.78 | 37.46 |
| 1 material of case study on implementation | 86.56 | 7.27 | 5.36 | 37.89 |
| 2 material of case study on implementation | 84.41 | 7.01 | 6.98 | 38.56 |
| 3 material of case study on implementation | 84.79 | 6.87 | 7.63 | 39.72 |
| 4 material of case study on implementation | 84.74 | 6.11 | 8.47 | 40.15 |
| 5 material of case study on implementation | 84.05 | 5.59 | 9.81 | 40.63 |
| 6 material of case study on implementation | 83.49 | 5.27 | 10.64 | 40.89 |
From 2 data of table it is found that with 1~6 plasma modified condition voltage of case and action time increase O element
Content is continuously increased (i.e. oxygen-containing group quantity is continuously increased) and product yield is continuously improved.
(4) silkworm excrement base multi-stage porous Carbon Materials sustained release performance is analyzed
Pesticide Diacloden absorption carriage amount and sustained release are carried out to silkworm excrement base multi-stage porous Carbon Materials prepared by case study on implementation 1,3,5
Tracing analysis, wherein the adsorption conditions of Carbon Materials are that 50mg slow-release material is put into oscillation suction in 50mL 0.8g/L Diacloden solution
It is attached, 30 DEG C of bath temperature, vibrate 200 revs/min of revolving speed；The sustained release condition of Carbon Materials is that slow-release material is put into after 50mg is adsorbed
In 120mL deionized water, water 100mL being changed daily, 30 DEG C of bath temperature, vibrating 200 revs/min of revolving speed, experimental result is respectively such as
Shown in Fig. 5, Fig. 6.From figure 5 it can be seen that 3 kinds of slow-release materials all reach 500 in absorption 48 hours back loading amounts of Diacloden~
Between 560mg/g, and there is no difference between three kinds of materials, illustrates such material with the same of different slow release effects
When be able to maintain similar adsorption effect.From fig. 6, it can be seen that respectively 15 days, 30 days and 60 days or so completion release processes (with
90% Diacloden of total volume is as endpoint calculation), it is able to satisfy the requirement of different times pesticide slow-release.
The above embodiment of the present invention is only intended to clearly illustrate examples made by the present invention, and is not to of the invention
The restriction of embodiment.For those of ordinary skill in the art, other can also be made on the basis of the above description
Various forms of variations or variation.There is no necessity and possibility to exhaust all the enbodiments.It is all in spirit of the invention
With any modifications, equivalent replacements, and improvements made within principle etc., the protection scope of the claims in the present invention should be included in
Within.
Claims (5)
1. a kind of application of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials, it is characterised in that: it is in terms of pesticide delays controlled release
Utilization；The material is three dimensional pore structures, and Langmuir specific surface area is 950 ~ 1300 m2/ g, total pore volume 0.4 ~
0.60 cm3/ g, wherein micropore specific area and Kong Rong account for the 50 ~ 70% of total specific surface area and Kong Rong；Preparation method includes
Following steps,
(1) by Faeces bombycis and ZnCl2It is freeze-dried after solution mixing swelling, then silkworm excrement after freeze-drying is lived in protective gas
Change reaming reaction, silkworm excrement base porous carbon material is obtained after then cleaning, be centrifuged and drying again；The freezing dry process is first
2 ~ 4h of precooling at -25 oC of oC ~ -20 is then cooled to -60 oC of oC ~ -40 and 24 ~ 72h is lyophilized；
(2) by silkworm excrement base multi-stage porous Carbon Materials in O2It is modified that plasma reactor progress surface is put under atmosphere, input voltage 20
~ 50 V, 1 ~ 30 min of modification time；Modified to be cleaned with deionized water, O doping surfaces modification silkworm excrement Quito can be obtained in drying
Grade hole Carbon Materials.
2. the application of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials according to claim 1, it is characterised in that: institute
State the ZnCl of silkworm excrement and 0.25 ~ 0.30 g/mL of mass concentration in step (1)2Solution mixing plastid ratio is 1:100 ~ 200, is mixed
Conjunction temperature is 30 ~ 50 o C, and incorporation time is 0.5 ~ 3 h.
3. the application of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials according to claim 1, it is characterised in that: institute
State 30 ~ 40 V of plasma reactor input voltage, 5 ~ 20 min of modification time.
4. the application of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials according to claim 1, it is characterised in that: institute
Silkworm excrement activation reaming reaction temperature is 300 ~ 700 oC after stating step (1) freeze-drying, and the reaction time is 0.5 ~ 5 h.
5. the application of O doping surfaces modification silkworm excrement base multi-stage porous Carbon Materials according to claim 1, it is characterised in that: freeze
Silkworm excrement reaming reaction temperature is 400 ~ 600 oC after dry, and the reaction time is 2 ~ 3 h.
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| CN103537262A (en) * | 2013-10-31 | 2014-01-29 | 陕西师范大学 | Preparation method of nitrogen-doped hierarchical pore carbon materials |
| CN104140100A (en) * | 2014-08-18 | 2014-11-12 | 福建师范大学 | Method for preparing micro-porous activated carbon for gas adsorption by virtue of vacuum freeze drying |
| CN105060293A (en) * | 2015-07-17 | 2015-11-18 | 安徽中烟工业有限责任公司 | Method for preparing tobacco activated carbon based on low temperature plasma modification |
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| CN103537262A (en) * | 2013-10-31 | 2014-01-29 | 陕西师范大学 | Preparation method of nitrogen-doped hierarchical pore carbon materials |
| CN104140100A (en) * | 2014-08-18 | 2014-11-12 | 福建师范大学 | Method for preparing micro-porous activated carbon for gas adsorption by virtue of vacuum freeze drying |
| CN105060293A (en) * | 2015-07-17 | 2015-11-18 | 安徽中烟工业有限责任公司 | Method for preparing tobacco activated carbon based on low temperature plasma modification |
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