CN109550489A - The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water - Google Patents

The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water Download PDF

Info

Publication number
CN109550489A
CN109550489A CN201811467524.6A CN201811467524A CN109550489A CN 109550489 A CN109550489 A CN 109550489A CN 201811467524 A CN201811467524 A CN 201811467524A CN 109550489 A CN109550489 A CN 109550489A
Authority
CN
China
Prior art keywords
corncob
ion
solution
cob meal
preparation
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.)
Pending
Application number
CN201811467524.6A
Other languages
Chinese (zh)
Inventor
尹晓辉
陶镇
高伟荣
易玉龙
熊婕
骆兆宇
毛春奎
郑九林
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.)
Thiessens Environmental Ltd By Share Ltd
Original Assignee
Thiessens Environmental Ltd By Share 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 Thiessens Environmental Ltd By Share Ltd filed Critical Thiessens Environmental Ltd By Share Ltd
Priority to CN201811467524.6A priority Critical patent/CN109550489A/en
Publication of CN109550489A publication Critical patent/CN109550489A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/26Synthetic macromolecular compounds
    • B01J20/264Synthetic macromolecular compounds derived from different types of monomers, e.g. linear or branched copolymers, block copolymers, graft copolymers
    • 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
    • B01J20/28014Solid 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 form
    • B01J20/28023Fibres or filaments
    • 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
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • 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
    • B01J2220/4812Sorbents characterised by the starting material used for their preparation the starting material being of organic character
    • B01J2220/4825Polysaccharides or cellulose materials, e.g. starch, chitin, sawdust, wood, straw, cotton
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The present invention relates to a kind of preparation methods of the ion-exchange fibre of ammonia nitrogen in absorption waste water, include the following steps: that the plant Zea mays fruit after 1) normal growth is mature, by corn rod threshing, becomes corncob after natural air drying or drying.Corncob is put into baking oven to complete dehydration, the cylindric of 5cm or so is cut into, obtains the column corncob of uniform specification.2) the column corncob got ready is pre-processed with method in attached drawing;3) it activates;4) modified;5) it is grafted;6) cleaning, drying obtains ion-exchange fibre.Compared with the preparation approach of existing ion-exchange fibre, raw material are conveniently easy to get, and preparation process is simple and clear, and time-consuming short, energy consumption is few, and preparation cost is low, and product absorption property is good, are suitble to commercial introduction.

Description

The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water
Technical field
The present invention relates to a kind of preparation method of the ion-exchange fibre of ammonia nitrogen in absorption waste water, in particular to a kind of utilizations The method that agricultural by product corncob prepares natural plants ion-exchange fibre.
Background technique
Ion-exchange fibre (ion exchange fibers, IEF) is the adsorption and separation material of a fibre-like Material, the exchangeable ion and certain same sex ions dissociated mainly by the surface active groups of fiber or fibrous polymer into Row exchange, compared with traditional ion exchange resin, IEF has large specific surface area, and chemical stability is higher, mass transfer apart from short, Absorption and desorption rate are fast, and adsorptive selectivity is strong (to the absorption with higher such as metal ion, small organic molecule, pernicious gas Selectivity), thoroughly, elution and power of regeneration are strong for purification, many advantages, such as low energy consumption, and fluid resistance is small and bioactivity is high.It is existing It is widely used to water process, the isolation of purified of gas, the recycling of precious metal ion, the separation of drug and extraction and life The fields such as materialization work, are the rapid new high-tech industries of Developing, constantly bringing forth new ideas and improving with preparation method, IEF's Application prospect is more wide.
In addition, the special feature that ion-exchange fibre also has development and application various informative, can be made fiber, short fibre The forms such as dimension, fabric, non-woven cloth, felt, net, therefore can be applied to the ion exchange process of various different conditions.CN 1262706C reports a kind of preparation method of ion-exchange fibre and its fabric in closed reactor, and fabric product has The ability and power of regeneration of superpower absorption pernicious gas (sulfur dioxide, ammonia, hydrogen fluoride, hydrogen chloride), have good economy With social benefit.101736525 A of CN discloses a kind of method of non-woven cloth by ion-exchange fibre preparation, this is non-to knit Cotton material is made applied in the absorbent device of super absorbent polymer, the water absorbent rate of super absorbent polymer can be greatly improved, into And the usage amount of super absorbent polymer in absorbent device is reduced, economic benefit and actual benefit significantly improve.CN 101036897A is disclosed using crop waste fiber rice straw, corn stover, useless flax silk, waste cotton and is prepared anionite Method, preparation process is simple, low raw-material cost, be particularly suitable for be used to handle anion-containing waste water.
Research for ion-exchange fibre, in west, American-European countries, Japan, the former Soviet Union are research hotspots, have been possessed Many research reports and achievement.Wherein the research of the Japanese and former Soviet Union is relatively early and research is more, such as Japanese TIN and Russia VION, FIBAN etc. formd the product including seriations such as anion, cation, both sexes, chelatings.In RU1658444 In, be prepared for the Fibriform adsorbents containing carboxyl and diazanyl, in gas ammonia and ammonium nitrate have higher purification efficiency.In state Interior, the seventies begin to expand the development of ion exchange fiber material and using work, Zhongshan University, Beijing Institute of Technology, river The mechanisms such as southern fine chemistry industry key lab, Beijing Institute of Clothing Tech have successively developed a variety of different ion-exchange fibres Material, and have some products practical application in each different field.As CN 1112257C relates to a kind of use The method that sweller and free radical protective agent produce ion-exchange fibre, product exchange capacity are up to 3.0~5.0 mMs often Gram, at low cost, long service life and no pollution to the environment.CN 105688835A is disclosed a kind of to be gone using cotton stem as raw material Except the adsorbent material and preparation method thereof of ammonia nitrogen in solution, the biological carbon adsorbent of this method production, the suction to ammonia nitrogen in solution Attached amount is up to 209.4mg/g, and by the modified adsorbent of aqueous slkali, ammonia nitrogen absorption amount can achieve 518.9mg/g.But it should It is costly that method carries out anoxic firing to cotton stem, and easily pollutes the environment during the high temperature treatment process.CN 105561935A and CN 105561936A is proposed respectively using lotus leaf and sweet osmanthus leaf as cellulosic material, in isopropanol, NaOH solution Under the modification of citric acid solution, be prepared into plant cellulose modified absorbing material absorption waste water in heavy metal.The preparation work Skill is simple, high production efficiency, but it is mainly for the processing of heavy metal in waste water, aldehyde radical, hydroxyl and mercaptan etc. in the material There is also absorption and complexing, this method not to refer to the ammonia nitrogen in waste water for functional group.
The major processes of ion-exchange fibre are prepared currently with natural plants raw material or composite fibre materials Identical as above-mentioned process or compound use is further improved on the basis of these methods.Wherein utilize natural plants Raw material prepare the raw material of natural plants base ion-exchange fibre just like agricultural product, agricultural and sideline product, agricultural wastes, other plant Deng, such as stalk, rice husk, pericarp, linen-cotton etc..Their main component is cellulose, also contains hemicellulose, lignin and fruit Glue.
In practical applications, though preparation keeps the technique simplicity of the ion-exchange fibre of complete physical structure, it is handed over The utilization efficiency for changing capacity and product is lower than graininess ion-exchanger and powdered ion exchange material, and industrial applications are deposited Certain restricted, further decrease research and development preparation cost and further increase the service efficiency of product and service life be from The developing direction of sub- exchange fiber.
Corn (Classification system: Zea mays L.) is grass family Zea annual herb plant.Alias: maize, Ear of maize, maize, corn, corn, maize, maize, maize, luxuriant reed, big sorgo, belong to annual tall and big draft.
Corncob also known as corncob, to be commonly called as " ear of maize bone, " be core remained by corn threshing.It is processed into powder, is had There are stronger frictional property, nontoxicity, chemical stability, quality harder and high resilience, biodegradability, therefore can be used to The dry products such as metal or plastics are wiped, can be ground more bright;It can be used for feed industry;Be a kind of fabulous medicine, Chemical industry carrier;It can also be applied to rubber industry.Most importantly it has adsorptivity, is that one kind has expansionary active carbon very much Resource.
Summary of the invention
The purpose of the present invention is to provide a kind of preparation method of the ion-exchange fibre of ammonia nitrogen in absorption waste water, this method Have the characteristics that at low cost, absorption property is good.
To achieve the above object, the technical solution used in the present invention is: a kind of ion exchange for adsorbing ammonia nitrogen in waste water The preparation method of fiber, includes the following steps:
1) the plant Zea mays fruit after normal growth is mature, by corn rod threshing, makes it after natural air drying or drying As corncob;Corncob is put into baking oven to complete dehydration, is cut into the column corncob of uniform specification (preferably 5cm's or so is cylindric);
2) the cylindric corncob got ready is pre-processed with two methods of one of following methods:
A) by the cylindric corncob got ready crush crusher machine, obtain powdered corncobs, by corncob Powder, which is dipped into distilled water, stirs 45min, removes the sundries on corncob powder surface, then dries it in 50~70 DEG C of baking ovens Dry 3-6h, obtains the completely corncob powder without floating dust;
B) the cylinder corncob got ready is sawn into the fan-shaped cylinder that height is 2~3cm, obtains fan-shaped corncob Axis places it in 6~8h of immersion in distilled water;It is then placed into 60~80 DEG C of baking ovens and dries 12h, obtain the dry corn of fritter Cob;
3) it activates: weighing 10g corncob powder, place it in 50~75ml n,N-Dimethylformamide (DMF) and 20- In the mixed solution of 80ml epoxychloropropane, 0.5~1h is stirred under 40~90 DEG C of condition of water bath heating;
4) modified: 20~50ml pyridine solution is added and makees modifying agent, continues 40~90 DEG C of 0.5~1h of heating water bath;
5) it is grafted: 20~40ml glycidyl methacrylate (GMA) monomer (concentration 20vol.%) is added, continue 80~100 DEG C of 6~8h of heating water bath, the maize cob meal (preliminary product) after being grafted;
6) it cleans:
A) maize cob meal after grafting is cooling (being cooled to 20 DEG C or less), 2~3 are eluted with the liquid alkaline solution of 0.2mol/L It is secondary, then be placed in the liquid alkaline solution that 200ml concentration is 0.1mol/L, heating water bath 20min and strength under the conditions of 40~45 DEG C It stirs (removing removal of residue, part carbohydrate and protein);
B) by above-mentioned steps 6) a) obtained maize cob meal is eluted 2~3 times with 0.2mol/L hydrochloric acid solution, then is placed in In 200ml, 0.1mol/L hydrochloric acid solution, heating water bath 20min and strong stirring under the conditions of 40~45 DEG C adjust pH into Property;
C) by above-mentioned steps 6) b) obtained maize cob meal with concentration be 30wt% ethanol solution elute 2~3 times, then It is placed in 200ml, in the ethanol solution that concentration is 30wt%, simultaneously strong stirring 10min (is gone heating water bath under the conditions of 40~45 DEG C Except remaining organic reactant in preceding step);
D) by above-mentioned steps 6) c) obtained maize cob meal is eluted 2~3 times with 0.01mol/L sodium chloride solution, then is set Enter in 500ml, 0.01mol/L sodium chloride solution, heating water bath and 5~10min of strong stirring, obtain under the conditions of 40~45 DEG C Maize cob meal after cleaning;
7) by the maize cob meal after cleaning in drying 6~12h under the conditions of 65~75 DEG C, powdered/blocky ion is obtained Exchange fiber (final products are sealed in drier, spare).
The beneficial effects of the present invention are: in the plantation substantial amounts of China's corn, and corncob belongs in peasant's eye Discarded object, therefore ion-exchange fibre is prepared to develop for raw material using corncob, with existing ion-exchange fibre system Standby raw material has the characteristics of (waste utilization) at low cost, materials convenient and environmentally friendly (no pollution to the environment) compared with technology.
Natural plants ion-exchange fibre is prepared as raw material using the waste corncob of crops, has opened up natural plants Ion-exchange fibre prepares the type and preparation approach of raw material, compared with the preparation approach of existing ion-exchange fibre, prepares work Skill is simple and clear, and time-consuming short, energy consumption is few, and preparation cost is low, and absorption property is good, is suitble to commercial introduction.
Further, the strong stirring refers to that speed of agitator is 300~400r/min.
Product is cleaned in the way of the progress simultaneously of heating water bath electric stirring or heating water bath and magnetic agitation Decolourize de- slag.
Further, in lessivation, glass apparatus sand core funnel or filter funnel, preferred sand core leakage is utilized Bucket.
Detailed description of the invention
Fig. 1 is the preparation method process flow chart of the ion-exchange fibre of ammonia nitrogen in the absorption waste water of the embodiment of the present invention.
Specific embodiment
To explain the technical content, the achieved purpose and the effect of the present invention in detail, below in conjunction with embodiment and cooperate attached Figure is explained.
Embodiment 1:
As shown in Figure 1, a kind of preparation method for adsorbing the ion-exchange fibre of ammonia nitrogen in waste water, it includes the following steps:
1) the plant Zea mays fruit after normal growth is mature, by corn rod threshing, makes it after natural air drying or drying As corncob.Corncob is put into baking oven to complete dehydration, the cylindric of 5cm or so is cut into, obtains uniform specification Column corncob.
2) the cylindric corncob got ready is pre-processed: with crusher machine is crushed, obtains powdered corncobs, it will Corncob powder be dipped into distilled water and stir 45min, the sundries on corncob powder surface is removed, then by it in 50~70 3-6h is dried in DEG C baking oven, obtains the completely corncob powder without floating dust;
3) it activates: weighing the dry maize cob meal of 10g, be put into the tool plug flask with three necks,round bottom of 1L, two sides of three-necked flask Mouth is clogged with glass stopper and (note: only opens plug when needing to be added drug, continue beyond the Great Wall after adding drug, entirely react So operation in the process), electric mixer is protruded into from the main mouth of three-necked flask, is added from the small glass funnel of three-necked flask side port 50ml n,N-Dimethylformamide (DMF) solution, 30ml epoxychloropropane solution, unlatching electric stirring are persistently stirred molten Liquid (reacts, revolving speed stirs in 60~80r/min, entire reaction process not to be stopped) so that maize cob meal comes into full contact with reagent 0.5~1h of heating water bath under the conditions of 75 DEG C;
4) modified: 20ml pyridine solution is added and makees modifying agent, heating water bath 0.5h under the conditions of 80 DEG C;
5) it is grafted: 20ml glycidyl methacrylate (GMA) monomer (concentration 20vol.%) is added, continue 80 DEG C Heating water bath 6h, the maize cob meal (preliminary product) after being grafted;
6) it cleans:
A) by the maize cob meal after grafting it is cooling (it is pour out preliminary product from three-necked flask online to clean fine ga(u)ge screen, 20 DEG C are cooled to hereinafter, transferring in sand core funnel), it is eluted 2~3 times with the liquid alkaline solution of 0.5L, 0.2mol/L, then will It is transferred in 500ml large beaker, pours into the liquid alkaline solution of 200ml, 0.1mol/L, the heating water bath and strong under the conditions of 40 DEG C Power stirring 20min (removes removal of residue, par-tial polysaccharide substance and protein, the strong stirring refers to that speed of agitator is 300- 400r/min, same as below);
B) by above-mentioned steps 6) a) obtained maize cob meal 0.2mol/L hydrochloric acid solution elution 2~3 times, it then will be beautiful Rice core powder is transferred in 500ml large beaker, is poured into 200ml, 0.2mol/L hydrochloric acid solution, and heating water bath is simultaneously under the conditions of 40 DEG C Strong stirring 20min adjusts pH to neutrality;
C) by above-mentioned steps 6) b) obtained maize cob meal with concentration be 30wt% ethanol solution elute 2~3 times, so After transfer them in 500ml large beaker, pour into 200ml, concentration be 30wt% ethanol solution in, under the conditions of 40~45 DEG C Heating water bath and strong stirring 10min (removal residual organic reactant);
D) by above-mentioned steps 6) c) obtained maize cob meal 0.01mol/L sodium chloride solution elution 2~3 times, then Maize cob meal is transferred in 500ml large beaker, is poured into 500ml, 0.01mol/L sodium-chloride water solution, in 40~45 DEG C of items Heating water bath and 5~10min of strong stirring under part, the maize cob meal after being cleaned (purpose is thorough wash off product);
7) maize cob meal after cleaning is gone to below sieve and pads upper evaporating dish, dried 12h under the conditions of 60~65 DEG C, obtain To the ion-exchange fibre prepared by corncob (final products are sealed in drier, spare).
In order to preferably show the performance and effect of this ion-exchange fibre, absorption property is carried out to the ammonia nitrogen in water with it Test, specific experimental method is as follows:
More parts of 1 products obtained therefroms of 1g embodiment are weighed, is respectively put into the iodine flask of clean 250ml, pours into 50ml 30mg/L
The aqueous ammonium chloride solution of (referred to herein as ammonium ion concentration), covers lid, shakes under temperature (20 ± 1 DEG C) It swings, oscillation intensity 100r/min, vibrates 60min.Ammonia nitrogen concentration Two N-ammoniacal Measurements shown in HI535-2009 carry out Measurement, related experiment result such as table 1.
Influence of the 1 product dosage of table to removal rate
Product dosage (g/L) Ammonia nitrogen removal frank (%)
1 74.10
2 90.44
3 94.86
4 96.67
Embodiment 2:
The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water, it includes the following steps:
1) the plant Zea mays fruit after normal growth is mature, by corn rod threshing, makes it after natural air drying or drying As corncob.Corncob is put into baking oven to complete dehydration, the cylindric of 5cm or so is cut into, obtains uniform specification Column corncob.
2) the cylindric corncob got ready is pre-processed: with crusher machine is crushed, obtains powdered corncobs, it will Corncob powder be dipped into distilled water and stir 45min, the sundries on corncob powder surface is removed, then by it in 50~70 3-6h is dried in DEG C baking oven, obtains the completely corncob powder without floating dust;
3) it activates: weighing the dry maize cob meal of 10g, be put into the tool plug flask with three necks,round bottom of 1L, two sides of three-necked flask Mouth is clogged with glass stopper and (note: only opens plug when needing to be added drug, continue beyond the Great Wall after adding drug, entirely react So operation in the process), electric mixer is protruded into from the main mouth of three-necked flask, is added from the small glass funnel of three-necked flask side port 60ml n,N-Dimethylformamide (DMF) solution, 80ml epoxychloropropane solution, unlatching electric stirring are persistently stirred molten Liquid (reacts, revolving speed stirs in 60~80r/min, entire reaction process not to be stopped) so that maize cob meal comes into full contact with reagent 0.5~1h of heating water bath under the conditions of 75 DEG C;
4) modified: 20ml pyridine solution is added and makees modifying agent, heating water bath 0.5h under the conditions of 80 DEG C;
5) it is grafted: 20ml glycidyl methacrylate (GMA) monomer (concentration 20vol.%) is added, continue 80 DEG C Heating water bath 6h, the maize cob meal (preliminary product) after being grafted;
6) it cleans:
A) by the maize cob meal after grafting it is cooling (it is pour out preliminary product from three-necked flask online to clean fine ga(u)ge screen, 20 DEG C are cooled to hereinafter, transferring in sand core funnel), it is eluted 2~3 times with the liquid alkaline solution of 0.5L, 0.2mol/L, then will It is transferred in 500ml large beaker, pours into the liquid alkaline solution of 200ml, 0.1mol/L, the heating water bath and strong under the conditions of 40 DEG C Power stirring 20min (removes removal of residue, par-tial polysaccharide substance and protein, the strong stirring refers to that speed of agitator is 300- 400r/min, same as below);
B) by above-mentioned steps 6) a) obtained maize cob meal 0.2mol/L hydrochloric acid solution elution 2~3 times, it then will be beautiful Rice core powder is transferred in 500ml large beaker, is poured into 200ml, 0.2mol/L hydrochloric acid solution, and heating water bath is simultaneously under the conditions of 40 DEG C Strong stirring 20min adjusts pH to neutrality;
C) by above-mentioned steps 6) b) obtained maize cob meal with concentration be 30wt% ethanol solution elute 2~3 times, so After transfer them in 500ml large beaker, pour into 200ml, concentration be 30wt% ethanol solution in, under the conditions of 40~45 DEG C Heating water bath and strong stirring 10min (removal residual organic reactant);
D) by above-mentioned steps 6) c) obtained maize cob meal 0.01mol/L sodium chloride solution elution 2~3 times, then Maize cob meal is transferred in 500ml large beaker, is poured into 500ml, 0.01mol/L sodium-chloride water solution, in 40~45 DEG C of items Heating water bath and 5~10min of strong stirring under part, the maize cob meal after being cleaned (purpose is thorough wash off product);
7) maize cob meal after cleaning is gone to below sieve and pads upper evaporating dish, dried 12h under the conditions of 60~65 DEG C, obtain To the ion-exchange fibre prepared by corncob (final products are sealed in drier, spare).
Embodiment 2 exchanges effect (eliminating rate of absorption) such as table 2, and experimental method experiment condition is the same as embodiment 1.
Influence of the 2 product dosage of table to removal rate
Product dosage (g) Ammonia nitrogen removal frank (%)
1 76.40
2 90.31
3 93.76
4 95.84
Embodiment 3:
The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water, it includes the following steps:
1) the plant Zea mays fruit after normal growth is mature, by corn rod threshing, makes it after natural air drying or drying As corncob.Corncob is put into baking oven to complete dehydration, the cylindric of 5cm or so is cut into, obtains uniform specification Column corncob.
2) the cylindric corncob got ready is pre-processed: with crusher machine is crushed, obtains powdered corncobs, it will Corncob powder, which is dipped into distilled water, stirs 45min, the sundries on corncob powder surface is removed, then by it in 50~70 DEG C 3-6h is dried in baking oven, obtains the completely corncob powder without floating dust;
3) it activates: weighing 10g corncob powder, place it in 60ml n,N-Dimethylformamide (DMF) and 50ml epoxy In the mixed solution of chloropropane, 0.5~1h is stirred under 40~90 DEG C of condition of water bath heating;
4) modified: 20ml pyridine solution is added and makees modifying agent, heating water bath 0.5h under the conditions of 80 DEG C;
5) it is grafted: 20ml glycidyl methacrylate (GMA) monomer (concentration 20vol.%) is added, continue 80 DEG C Heating water bath 6h, the maize cob meal (preliminary product) after being grafted;
6) it cleans:
A) maize cob meal after grafting is cooling (being cooled to 20 DEG C or less), 2~3 are eluted with the liquid alkaline solution of 0.2mol/L It is secondary, then be placed in the liquid alkaline solution that 200ml concentration is 0.1mol/L, heating water bath 20min and strength under the conditions of 40~45 DEG C It stirs (removing removal of residue, part carbohydrate and protein);
B) by above-mentioned steps 6) a) obtained maize cob meal is eluted 2~3 times with 0.2mol/L hydrochloric acid solution, then is placed in In 200ml, 0.1mol/L hydrochloric acid solution, heating water bath 20min and strong stirring under the conditions of 40 DEG C adjust pH to neutrality;
C) by above-mentioned steps 6) b) obtained maize cob meal with concentration be 30wt% ethanol solution elute 2~3 times, then It is placed in 200ml, in the ethanol solution that concentration is 30wt%, simultaneously strong stirring 10min (is gone heating water bath under the conditions of 40~45 DEG C Except remaining organic reactant in preceding step);
D) by above-mentioned steps 6) c) obtained maize cob meal is eluted 2~3 times with 0.01mol/L sodium chloride solution, then is set Enter in 500ml, 0.01mol/L sodium chloride solution, heating water bath and 5~10min of strong stirring, are cleaned under the conditions of 40 DEG C Maize cob meal afterwards;
7) by the maize cob meal after cleaning in drying 6h under the conditions of 65~75 DEG C, powdered/blocky ion exchange is obtained Fiber (final products are sealed in drier, spare).
The experimental method experiment condition of 3 eliminating rate of absorption of embodiment is as a result same as Example 1 with embodiment 1.
Embodiment 4:
It is substantially the same manner as Example 2, the difference is that the bath temperature of three reaction steps is successively are as follows: 60 DEG C, 60 DEG C, 90℃。
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 5: it is substantially the same manner as Example 2, the difference is that finally clean the 0.01mol/L in product stage NaCl solution replaces with deionized water.
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 6: it is substantially the same manner as Example 2, the difference is that: 2) the cylinder corncob got ready is sawn into Height is the fan-shaped cylinder of 2~3cm, obtains fan-shaped corncob, places it in 6~8h of immersion in distilled water;Then it places 12h is dried into 60~80 DEG C of baking ovens, obtains the dry corncob of fritter;
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 7: it is substantially the same manner as Example 2, the difference is that: it is modified: 30ml pyridine solution is added and makees modifying agent, Continue 80 DEG C of heating water bath 0.5h.
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 8: it is substantially the same manner as Example 2, the difference is that: it is modified: 30ml pyridine solution is added and makees modifying agent, Continue 70 DEG C of heating water bath 1h.
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 9: it is substantially the same manner as Example 2, the difference is that: it is sweet that 40ml Glycidyl methacrylate grafting: is added Grease (GMA) monomer (concentration 20vol.%), continues 80 DEG C of heating water bath 6h, and the maize cob meal after being grafted is (preliminary to produce Product);
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
Embodiment 10: it is substantially the same manner as Example 2, the difference is that: it is sweet that 20ml Glycidyl methacrylate grafting: is added Grease (GMA) monomer (concentration 20vol.%), continues 80 DEG C of heating water bath 8h, and the maize cob meal after being grafted is (preliminary to produce Product);
The experimental method experiment condition of eliminating rate of absorption is as a result same as Example 2 with embodiment 2.
In order to preferably compare ammonia nitrogen removal effect of the invention, with other invention preparation material with it is prepared by the present invention Material comparison, specific ammonia nitrogen absorption Contrast on effect situation are as shown in table 3 below:
3 difference of table prepares material to ammonia nitrogen absorption Contrast on effect
It can be seen from the data in the table that the material of the embodiment of the present invention 1~10 prepared using corncob as raw material is to ammonia nitrogen Absorption property is preferable, is suitble to commercial introduction.
Specific embodiments of the present invention are described above.It is to be appreciated that the invention is not limited to above-mentioned Particular implementation, those skilled in the art can make various deformation or modification within the scope of the claims, have no effect on Substantive content of the invention.
The above description is only an embodiment of the present invention, is not intended to limit the scope of the invention, all to utilize this hair Equivalents made by bright specification and accompanying drawing content are applied directly or indirectly in relevant technical field, similarly include In scope of patent protection of the invention.

Claims (3)

1. the preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water, which comprises the steps of:
1) the plant Zea mays fruit after normal growth is mature, by corn rod threshing, becomes after natural air drying or drying Corncob;Corncob is put into baking oven to complete dehydration, is cut into the column corncob of uniform specification;
2) the cylindric corncob got ready is pre-processed with one of following two methods:
A) by the cylindric corncob got ready crush crusher machine, obtain powdered corncobs, by corncob powder soak It steeps and stirs 45min in distilled water, remove the sundries on corncob powder surface, it is then dried into 3- in 50~70 DEG C of baking ovens 6h obtains the completely corncob powder without floating dust;
B) the cylinder corncob got ready is sawn into the fan-shaped cylinder that height is 2~3cm, obtains fan-shaped corncob, Place it in 6~8h of immersion in distilled water;It is then placed into 60~80 DEG C of baking ovens and dries 12h, obtain the dry corncob of fritter Axis;
3) it activates: weighing 10g corncob powder, the mixing for placing it in 50~75ml DMF and 20-80ml epoxychloropropane is molten In liquid, 0.5~1h is stirred under 40~90 DEG C of condition of water bath heating;
4) modified: 20~50ml pyridine solution is added and makees modifying agent, continues 40~90 DEG C of 0.5~1h of heating water bath;
5) it is grafted: 20~40ml GMA monomer solution is added, the concentration of GMA is 20vol.% in the GMA monomer solution, is continued 6~8h, the maize cob meal after being grafted are heated in 80~100 DEG C of water-baths;
6) it cleans:
A) maize cob meal after grafting is cooling (being cooled to 20 DEG C or less), it is eluted 2~3 times with the liquid alkaline solution of 0.2mol/L, It is placed in the liquid alkaline solution that 200ml concentration is 0.1mol/L, heating water bath 20min and is strongly stirred under the conditions of 40~45 DEG C again It mixes;
B) by above-mentioned steps 6) a) obtained maize cob meal with 0.2mol/L hydrochloric acid solution elute 2~3 times, then be placed in 200ml, In 0.1mol/L hydrochloric acid solution, heating water bath 20min and strong stirring under the conditions of 30~40 DEG C adjust pH to neutrality;
C) by above-mentioned steps 6) b) obtained maize cob meal is eluted 2~3 times with the ethanol solution that concentration is 30wt%, then is placed in In 200ml, the ethanol solution that concentration is 30wt%, heating water bath and strong stirring 10min under the conditions of 40~50 DEG C;
D) by above-mentioned steps 6) c) obtained maize cob meal is eluted 2~3 times with 0.01mol/L sodium chloride solution, then is placed in In 500ml, 0.01mol/L sodium chloride solution, heating water bath and 5~10min of strong stirring, are washed under the conditions of 30~50 DEG C Maize cob meal after net;
7) by the maize cob meal after cleaning in drying 6~12h under the conditions of 65~75 DEG C, powdered/blocky ion exchange is obtained Fiber.
2. the preparation method of the ion-exchange fibre of ammonia nitrogen in absorption waste water according to claim 1, it is characterised in that: institute It states and is cut into the cylindric of 5cm or so in step 1).
3. the preparation method of the ion-exchange fibre of ammonia nitrogen in absorption waste water according to claim 1, it is characterised in that: institute It states strong stirring and refers to that speed of agitator is 300~400r/min.
CN201811467524.6A 2018-12-03 2018-12-03 The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water Pending CN109550489A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811467524.6A CN109550489A (en) 2018-12-03 2018-12-03 The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811467524.6A CN109550489A (en) 2018-12-03 2018-12-03 The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water

Publications (1)

Publication Number Publication Date
CN109550489A true CN109550489A (en) 2019-04-02

Family

ID=65868598

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811467524.6A Pending CN109550489A (en) 2018-12-03 2018-12-03 The preparation method of the ion-exchange fibre of ammonia nitrogen in a kind of absorption waste water

Country Status (1)

Country Link
CN (1) CN109550489A (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102614852A (en) * 2012-04-16 2012-08-01 武汉理工大学 Preparation method for spongy ion exchange fiber
CN103223354A (en) * 2013-03-29 2013-07-31 武汉理工大学 Preparation method of biomass-based anion exchange fiber

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102614852A (en) * 2012-04-16 2012-08-01 武汉理工大学 Preparation method for spongy ion exchange fiber
CN103223354A (en) * 2013-03-29 2013-07-31 武汉理工大学 Preparation method of biomass-based anion exchange fiber

Similar Documents

Publication Publication Date Title
CN102553538B (en) Modified peanut shell cationic adsorbent, preparation method and application
CN106010601A (en) Biochar prepared from banana peel, preparation method and application thereof
CN105148849B (en) It is a kind of that the application that solid absorbent handles waste water is prepared by wheat stalk
CN101239305A (en) Method for preparing modified plant fibrous sale price biological adsorption agent
CN103936930B (en) The preparation method of the netted quaternary ammonium salt cationic Mierocrystalline cellulose of sugarcane marrow thin-walled cell
CN102614852B (en) Preparation method for spongy ion exchange fiber
CN108325506A (en) A kind of preparation method of the modified cellulose aeroge of absorption heavy metal
CN104387478B (en) A kind of oil preparation method of Paeonia suffruticosa stem nano-cellulose
CN101829545A (en) Heavy metal biological adsorbent using eggshell membrane as matrix and preparation method thereof
CN110523389A (en) A kind of carboxylated banian aerial root fiber adsorbing substance and the preparation method and application thereof
CN102389777B (en) Preparation method and use of sulfydryl cotton stalk bark
CN107583609A (en) A kind of modified mangosteen shell charcoal and the method using vanadium in its reduction water body
CN106219657A (en) A kind of modified biomass adsorbent and its preparation method and application
CN106475065A (en) A kind of method for preparing adsorbent for heavy metal in ramie oxidation scouring processes
CN105964221B (en) A kind of composite carbon rod and preparation method thereof based on discarded hair granular activated carbon
CN107552027A (en) A kind of application that the method for carbon material and its carbon material of preparation are prepared using biomass dead meal
CN104326471A (en) Method for preparing active carbon from licorice waste residue
CN106000348A (en) Preparation method of adsorbent for treating zinc-containing wastewater
CN108295820A (en) A kind of preparation method and applications of plant fiber adsorbing material
CN108117168A (en) The purposes of water quality cleansing agent containing biological enzyme
CN103223354B (en) Preparation method of biomass-based anion exchange fiber
CN108033449A (en) A kind of preparation method of medicinal carbon
CN108949188A (en) A kind of preparation method of antibacterial passivator
CN108311118A (en) A kind of preparation method of modified synthesis zeolite heavy metal ion adsorbing material
CN104084143A (en) Preparation method of function material in biomass water treatment environment

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20190402