CN1890027B - Anion adsorptive carbon material and its production method and device - Google Patents
Anion adsorptive carbon material and its production method and device Download PDFInfo
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- CN1890027B CN1890027B CN2004800361714A CN200480036171A CN1890027B CN 1890027 B CN1890027 B CN 1890027B CN 2004800361714 A CN2004800361714 A CN 2004800361714A CN 200480036171 A CN200480036171 A CN 200480036171A CN 1890027 B CN1890027 B CN 1890027B
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Abstract
Disclosed is a low-cost, environmentally friendly anion-adsorbing carbon material which is excellent in anion absorption. Also disclosed are a method and apparatus for producing such an anion-adsorbing carbon material. The present invention is characterized in that a raw material of plant origin is carbonized after being brought into contact with a solution containing calcium ions and then the resulting is brought into contact with an acid solution.
Description
Technical field
The present invention relates to adsorb anionic anion-adsorbing carbon material and manufacture method and manufacturing installations such as nitrate ion, fluorine ion.
Background technology
The pollution of heavy metal, agricultural chemicals, the caused water quality of organic chloride and soil can destroy environment, and this is becoming problem.These harmful substances can be removed with sorbing materials such as active carbon, zeolite absorption, are difficult to utilize sorbing material to be handled but present situation is the nitric acid type nitrogen that exists with anionic form or nitrite type nitrogen, fluorine, arsenic, cyano group etc.
That is, nitric acid type nitrogen and nitrite type nitrogen are included in the fertilizer that uses in tea field and the golf course lawn etc., have constituted one of reason of the underground water pollution that becomes serious problems now.This be because, nitrate ion and nitrite ion have negative electrical charge, do not combine with other chemical substances and can form indissoluble salt, thereby the easiest soil from negative electrical charge molten from.So, must take the countermeasure at the problems referred to above, but for example utilize denitrifier etc. removing the microbiological treatment of nitrate ion and nitrite ion, existence must be the restriction of anaerobic condition etc., additive method also is same, and does not find effective countermeasure.And, begin recently to suspect that nitric acid type nitrogen and nitrite type nitrogen are environmental hormones.
In addition, fluorine is included in the waste water of semiconductor, glass, plating factory etc., the method of removing that calcium compound forms calcirm-fluoride is added in fluorine employing in the plant chimney stalk, but because the adsorption tower that utilizes activated alumina or fluorine to use anion exchange resin also must be set, so cost increases.And, reach the environmental standard 0.8mg/L of Japan or below the 0.8mg/L, then need expensive special-purpose anion exchange resin.Other processing that are included in arsenic in plant chimney stalk or the underground water, cyano group etc. also need expensive anion exchange resin in addition.
As mentioned above, also be not used in the above-mentioned anionic cheap material that absorption is representative with the nitrate ion now, in a single day therefore the pollution that is caused by these anion has the tendency of expansion, and is polluted by above-mentioned anion, and its reparation needs great amount of cost.
Patent documentation 1: the spy opens flat 10-165824 communique
Summary of the invention
Therefore, seeking cheapness, be of value to the material of the adsorpting anion of environment.The charcoal that is all the representative of porous material with active carbon is extensively popularized and is humidity adjusting material or river purification, soil improvement material, for example be used to remove chlorine-containing gas in the waste gas and sulfur oxide etc., but charcoal and active carbon are same, only utilize the characterization of adsorption that micropore produced of porous carbon material inside, and can adsorb the nitric acid type nitrogen that exists with anionic form or nitrite type nitrogen, fluorine, arsenic, cyano group etc. hardly.
The present invention In view of the foregoing finishes, so its purpose is to provide anion-adsorbing carbon material and manufacture method and manufacturing installation cheap, that be of value to environment, anion adsorptivity excellence.
The inventor at following investigation of materials anionic absorption property, to such an extent as to found that excellent anion absorption property.Described material is following to be obtained: before with the plant material charing, for example the solution of calcium hydroxide (limewash) or suspension (milk of lime) contact this raw material to make the solution (preferably mainly containing calcium ion as cation) that contains calcium ion in advance, in this raw material, import Ca (calcium), subsequently this has been imported the raw material charing of Ca, charcoal contact HCl, the H of Ca that made the importing that obtains again
2SO
4Deng acid.And the wastewater treatment of this situation only is neutralizing acid, and is useful to environment.
As the solution that contains calcium ion, except limewash, milk of lime, can enumerate calcium acetate solution, calcium chloride solution etc.Preferably contain 0.03~30 weight % as calcium, more preferably contain 0.1~7.0 weight %.
Contact the method for above-mentioned plant material as the solution that makes calcium ions, can be drip, solution or other modes of coating, spraying, spraying calcium ions, but the most effectively above-mentioned raw materials is immersed in the solution that contains calcium ion.In addition, the method as making acid solution contact carbonated material can be dropping, coating, spraying, spray acid solution or other modes, but the most effectively carbide is immersed in the acid solution.
Like this, the manufacture method of the described anion-adsorbing carbon material of claim 1 is characterised in that, carries out charing after making the solution contact plant material of calcium ions, and acid solution is contacted with it.
In addition, consider that the described the moon of claim 2 is characterised in that from the manufacture method in adsorbing carbon material, the plant material of the solution of contacted calcium ions is carried out charing, make acid solution contact its carbide again from other angle.
And then, consider that from other angle the manufacture method of the described anion-adsorbing carbon material of claim 3 is characterised in that, make the acid solution contact carry out carbide after the charing to the plant material of the solution of contacted calcium ions.
As the plant material among the present invention, so long as plant just can be suitable for, preferably by in natural fiber, the wood materials constitute more than a kind or a kind and the carbide of above-mentioned raw materials has the raw material of micropore, can enumerate for example natural fiber such as all wood materials such as thinnings, felled tree, culled wood or fiber crops.Contain hardly and can carry out under the situation of solution (for example limewash with milk of lime etc.) as the solution that contacts this raw material of calcium ions of anion (for example chlorion etc.) of ion-exchange using with absorption object anion, as above-mentioned raw materials, form the such raw material of a large amount of particle diameters in the micropore at its carbide when preferably after importing calcium, carrying out charing smaller or equal to the calcium compound of 100nm.Preferably specifically use coniferous trees such as the Japan cypress that water imbibition is high, China fir to be sliced into the wooden bits that size for example obtains smaller or equal to 10mm.
In addition, contain simultaneously and can carry out under the situation of the anion (for example chlorion etc.) of ion-exchange and the solution of calcium ion (for example calcium chloride solution etc.) using with absorption object anion, as above-mentioned raw materials, such raw material that solution infiltrates easily when preferably flooding in solution.Specifically, preferably use coniferous trees such as the Japan cypress that water imbibition is high, China fir to be sliced into the wooden bits that size for example obtains smaller or equal to 50mm.And then for the situation of using any one solution, bamboo, sawdust, husk, coconut, betelnut tree, jute, rice straw can be used as plant material.In addition, as above-mentioned plant material, can also enumerate agricultural wastes such as skin citrus or apple and press for extracting juice back dregs.In addition, in plant, has the part of channel organization (conduit, tracheid or screen casing) especially preferably as plant material.
In the present invention, for example limewash or milk of lime etc. contact plant material to make the solution that contains calcium ion.When being impregnated into above-mentioned raw materials in the solution that contains calcium ion, solution penetrates in the raw material, thereby can obtain having imported the sheet bits of Ca.Particularly use under the situation of alkaline solution (for example limewash etc.) as the solution that contains calcium ion, shown in Fig. 7 (A), to be immersed among the limewash C and contact as for example wooden of plant material bits 2, obtain importing sheet bits 30 (with reference to Fig. 7 (C)) of Ca.Shown in Fig. 7 (B), think this be since the organic matter of wooden bits in 2 because of the alkali stripping, calcium ion is considered 2 composition to be worth doing and is reacted with wooden.In addition, the solution that contains calcium ion preferably contains the calcium of 0.03~30 weight %, more preferably contains 0.1~7.0 weight %.
Then, in the present invention, by above-mentioned sheet bits 30 (with reference to Fig. 8 (A)) that imported Ca that obtain are carried out charing, obtained importing the charcoal (being designated hereinafter simply as the Ca charcoal) 31 (with reference to Fig. 8 (C)) of Ca, wherein think, the organic matter that has imported during above-mentioned charing among sheet bits 30 (with reference to Fig. 8 (B)) of Ca decomposes because of heat, and calcium ion is separated out (with reference to Fig. 8 (C)) on the micro-pore wall surface of the sheet bits 30 that imported Ca simultaneously.Can think that calcium ion is owing to separate out (with reference to Fig. 8 (B)) on the micro-pore wall surface of the sheet bits 30 that imported Ca in this case, thus fine, high dispersion state formed, thus draw a large amount of functional groups everywhere from micro-pore wall.
In the present invention, after the contacted plant material that contains the solution of calcium ion is carried out charing, make acid solution contact its carbide, can be combined in from the functional group that the micro-pore wall of carbide is drawn with the anion that absorption object anion carries out ion-exchange thereby can make.What the inventor studied with keen determination found that, by control temperature and time in carbonization process, can generate the functional group of carbide more.
That is to say, shown in the invention of claim 1 record, when making calcium contact above-mentioned raw materials in advance, inventor's affirmation for example continues 1 hour situation about cooling off naturally behind 650~750 ℃ the carbonization temperature, compare with the situation that continues to cool off naturally behind about 600 ℃ and the about 800 ℃ carbonization temperature in 1 hour, can form more functional group.Particularly under the situation of the contacted calcium of raw material, when observing, can observe, for the carbide that carries out charing as mentioned above at 650~750 ℃ carbonization temperature with electron microscope, the particulate of its calcium compound is separated out on above-mentioned micro-pore wall surface midway, and evenly disperses.
On the other hand, for the carbonization temperature of about 600C, observe the particulate of calcium compound and do not separate out to above-mentioned micro-pore wall surface fully.In addition, for the carbonization temperature of about 800C, separate out to above-mentioned micro-pore wall surface though see the particulate of calcium compound, it is many to observe blank.Like this, draw functional group as much as possible from the above-mentioned micro-pore wall surface of carbide, can enumerate 650~750C as essential carbonization temperature in order to make calcium.
In the present invention, after making the solution contact plant material that contains calcium ion, carry out charing, make acid solution contact its carbonated material again.Can think, for example above-mentioned Ca charcoal 31 is immersed in when for example HCl Solution H (with reference to Fig. 9 (A)) is middle, with the calcium ion and above-mentioned functional group of the functional groups on the micro-pore wall surface of Ca charcoal 31 on (with reference to Fig. 9 (B)) combined chloride ion (with reference to Fig. 9 (C)), thereby obtain chlorion through calcium ion or directly be combined in acid treatment Ca charcoal 32 (with reference to Fig. 9 (D)) in this functional group.
As acid solution of the present invention, can enumerate HCl, H
2SO
4Deng no problem acid solution in wastewater treatment during fabrication.The concentration of acid solution is more than or equal to 0.01mol/L, and promptly 0.01mol/L~20mol/L is preferably 0.1mol/L~10mol/L.When concentration is lower than 0.01mol/L, can produce the unfavorable condition that can not get abundant effect.In addition, as acid solution, preferably contain the anion that can carry out ion-exchange with absorption object anion, but before charing in the solution of contact vegetable material, restriction does not contain the anion that can carry out ion-exchange with absorption object anion.
In addition, above-mentioned acid treatment adopts that to impregnated in when handling in the acid solution efficient good, preferably under reduced pressure carries out, and preferably carries out in the pressure limit of 1330Pa~13.3Pa.
In addition, the inventor found that through research with keen determination, before to the plant material charing, makes in advance and contains solution of metal chloride and for example contain CaCl
2Solution contact this raw material, in raw material, import CaCl
2, subsequently this has been imported CaCl
2Raw material carry out charing, the carbonated material that obtains thus has excellent anion absorption property.
Like this, the manufacture method of the described anion-adsorbing carbon material of claim 4 is characterised in that, makes and contains solution of metal chloride contact plant material, carries out charing then, makes its carbide contain described metal chloride.Because the chlorion of the metal chloride that contains at carbide embodies anion exchange capacity, so carbide plays a role as anion-adsorbing carbon material.In addition, contain the method that solution of metal chloride contacts above-mentioned plant material as making, can be with above-mentioned solution drip, be coated with, spray, spraying etc., but the most effectively above-mentioned raw materials is immersed in the above-mentioned solution.
According to the manufacture method of above-mentioned anion-adsorbing carbon material, above-mentioned plant material is immersed in contains metal chloride CaCl
2Solution in, in raw material, import calcium ion and chlorion and handle, subsequently this has been imported CaCl
2Material carry out charing, the importing that obtains CaCl
2Charcoal show excellent anion adsorption capacity.
That is, for example shown in the image pattern 14 (A), will be immersed in CaCl as wooden bits 2 of raw material
2Among the solution M and make its contact CaCl
2During solution M, CaCl
2Calcium ion among the solution M and chlorion are imported in the wooden bits 2, shown in Figure 14 (C), obtain having imported CaCl
2Sheet bits 35.Shown in Figure 14 (B), this is because CaCl
2Solution M infiltrates organizing particularly in the channel organization in the wooden bits 2.In addition, as the above-mentioned CaCl that is used for raw material pre-treatment (contact is handled)
2The concentration of solution M, preferred CaCl
2Be 0.1 weight %~50 weight %, consider 1 weight %~20 weight % more preferably from the angle of cost.When being lower than 0.1 weight %, can not find high anion adsorption capacity; Even surpass 50 weight %, the anion adsorption capacity can not improve yet.
Then, shown in Figure 15 (A) to the above-mentioned CaCl that imported
2 Sheet bits 35 when carrying out charing, shown in Figure 15 (C), obtain raw material of wood-charcoal material 37.In above-mentioned carbonization process, importing tablet CaCl
2Bits 35 in the organic matter decomposes, simultaneously chlorion and calcium ion are importing CaCl
2The micro-pore wall surface of sheet bits 35 separate out.This moment, chlorion and calcium ion were at CaCl shown in Figure 15 (B)
2Separate out with fine, high dispersion state on the micro-pore wall surface of importing tablet bits 35, draw a large amount of functional groups everywhere from micro-pore wall.Consequently, shown in Figure 15 (C), can think that chlorion is in through metal ion (this moment for calcium ion) or directly is combined in the state of a large amount of functional groups of drawing on the micro-pore wall surface.
In addition, the manufacture method of the described anion-adsorbing carbon material of claim 5 is characterised in that, the contacted plant material that contains solution of metal chloride is carried out charing, makes its carbide contain described metal chloride.That is,, then only it is carried out charing and just can obtain the same anion-adsorbing carbon material of invention that relates to claim 4 if prepare the contacted plant material that contains solution of metal chloride in advance.
Here, as the content of above-mentioned metal chloride, preferably contain 2%~25% the metal chloride (claim 6) in the carbide of being combined in as ash content.The metal chloride that what is called is combined in the carbide is attached to the metal chloride the metal chloride in the carbide, so it is meant that carbide is interior not to be dissolved and the metal remained chloride owing to being combined in after water or acid flushing except only.Content is lower than at 2% o'clock, and the anion adsorption capacity is relatively poor; Even content surpasses 25%, the anion adsorption capacity often can not improve yet.
And then, in the invention that claim 4~6 relates to, preferably make water and/or acid contact above-mentioned carbide (claim 7).Here, as the method that makes water and/or the above-mentioned carbide of acid contact, can be that water and/or acid drip, are coated with, spray, spraying etc., but the most above-mentioned carbide is immersed in water and/or the acid.
At this, preferably make the reason of water and/or the above-mentioned carbide of acid contact be thought as follows described.That is, shown in Figure 16 (A), will be as Figure 14 and shown in Figure 15 and raw material of wood-charcoal material (CaCl that obtain
2When charcoal) 37 dippings (contact) are in acid such as hydrochloric acid H or sulfuric acid for example, be removed attached to the crystallization of the unnecessary metal chloride on the raw material of wood-charcoal material 37.And, when using hydrochloric acid H, can increase the chlorion in the functional group that is combined in above-mentioned raw material of wood-charcoal material 37 newly, become the state shown in Figure 16 (C) from Figure 16 (B) as acid, the anion adsorption capacity of the anion-adsorbing carbon material of Zhi Zaoing improves thus, so be preferred.In addition, even without acid such as hydrochloric acid H and water contacts under the situation of above-mentioned carbide, also can be removed attached to the crystallization of the unnecessary metal chloride on the raw material of wood-charcoal material 37, thereby can improve the anion adsorption capacity.
In addition, raw material in the invention that relates to as claim 4~7, so long as plant all can be suitable for, preferably by constituting more than a kind or a kind in natural fiber or the wood materials and carbide have the raw material of micropore, can enumerate for example natural fiber such as all wood materials such as thinnings, felled tree, culled wood and fiber crops.As above-mentioned raw materials, preferably especially use coniferous trees such as the Japan cypress that water imbibition is high, China fir to be sliced into the wooden bits that size for example obtains smaller or equal to 50mm.And then, except above-mentioned wooden bits, also can use agricultural waste such as dregs after bamboo, sawdust, husk, coconut, betelnut tree, jute, rice straw, skin citrus or apple, press for extracting juice citrus or apple.In addition, the part that in plant, especially preferably has channel organization (conduit, tracheid or screen casing).
Specifically, can enumerate CaCl as above-mentioned metal chloride
2Or BaCl
2(claim 8).
And in any one invention in aforesaid right requirement 1~8, the carbonization temperature of above-mentioned raw materials is preferably 400 ℃~1000 ℃.This is that micropore is undeveloped, as the poor-performing of sorbing material when being lower than 400 ℃ owing to the charing treatment temperature; When said temperature surpasses 1000 ℃, because excessively charing, and can not get characterization of adsorption.Here, more preferably 500 ℃~900 ℃ of charing treatment temperatures are most preferably 600 ℃~800 ℃.
The described anion-adsorbing carbon material of claim 9 is characterised in that it is to make by the manufacture method of any described anion-adsorbing carbon material in the claim 1~8.
In addition, anion-adsorbing carbon material of the present invention also can be formed by following approach: remove the anion of absorption from having adsorbed the described anion-adsorbing carbon material of anionic claim 9, simultaneously, substitute the above-mentioned anion of removing and in conjunction with the anion (claim 10) that can carry out ion-exchange with absorption object anion subsequently.At this, the adsorbable anion of anion-adsorbing carbon material of the present invention is the anion that can carry out ion-exchange with the anion on the micro-pore wall surface that is combined in the raw material of wood-charcoal material in advance, certainly, it is in advance through metal ion or directly be combined in anion beyond the anion in the functional group on micro-pore wall surface of above-mentioned raw material of wood-charcoal material.
The manufacturing installation of the described anion-adsorbing carbon material of claim 11 is characterised in that to have the carbonizing apparatus and the device that makes the carbide contact acid solution that generates in this carbonizing apparatus that plant material are carried out charing.
At this moment, as carbonizing apparatus, use can be set the retort of carbonization temperature.In addition, as the device that makes the carbide contact acid solution that in carbonizing apparatus, generates, use the known devices such as acid resistance jar that hold acid solution.
In addition, the manufacturing installation of the described anion-adsorbing carbon material of claim 12 is characterised in that to have the device that the device, the butt joint above-mentioned raw materials after touch that make plant material contact the solution of calcium ions carry out the carbonizing apparatus of charing and make the carbide contact acid solution that generates in this carbonizing apparatus.
At this moment, the device as the solution that makes plant material contact calcium ions uses known devices such as jar.As carbonizing apparatus, use can be set the retort of carbonization temperature.In addition, as the device that makes the carbide contact acid solution that in carbonizing apparatus, generates, use the known devices such as acid resistance jar that hold acid solution.
As making the solution that contains calcium ion contact the method (means) of above-mentioned plant material, can be that the solution with calcium ions drips, be coated with, spray, spraying etc., but the most effectively above-mentioned raw materials is immersed in the solution that contains calcium ion.In addition, as the method (means) that makes acid solution contact carbide, can be with acid solution drip, be coated with, spray, spraying etc., but the most effectively carbide is immersed in the acid solution.
Invention according to claim 11, after the plant material charing, by making its carbide contact acid solution, can be directly in the functional group that forms on the micro-pore wall of the carbide of plant or through calcium ion in conjunction with on can carry out ion-exchange with absorption object anion anion; Or, invention according to claim 12, after the plant material charing with the solution of contacted calcium ions, by making its carbide contact acid solution, can be directly in the functional group that forms drawing from the micro-pore wall of carbide or through calcium ion in conjunction with on can carry out ion-exchange with absorption object anion anion.
In the manufacturing installation of claim 11 or 12 described anion-adsorbing carbon materials, carbonizing apparatus can be to carry out the device that charing forms micropore with the carbide inside at plant material and form a large amount of functional groups on its micro-pore wall, simultaneously, the device of contact acid solution can be can in the above-mentioned functional group directly or through calcium ion in conjunction with on can carry out ion-exchange with absorption object anion anionic device (claim 13).
The inventor etc. found that through research with keen determination, by control temperature and time in carbonization process, can generate the functional group of carbide more.That is to say that as described in the invention of claim 11 record, when not importing calcium in above-mentioned raw materials, the difference of functional group's growing amount of the carbide that is caused by heating-up temperature during charing is few.On the other hand, as described in the invention of claim 12 record, when in above-mentioned raw materials, importing calcium in advance, the inventor confirms, with continue 1 hour about 600 ℃ and about 800 ℃ carbonization temperature after naturally the situation of cooling compare, for example situation about cooling off naturally behind about carbonization temperature of 650~750 ℃ in lasting 1 hour can form more functional group.
Particularly imported the situation of calcium, when observing with electron microscope, can observe for carrying out the carbide of charing at about 650 ℃~750 ℃ carbonization temperature as mentioned above, the particulate of its calcium compound is separated out to stop at the micro-pore wall surface of above-mentioned carbide, and evenly disperses.On the other hand, for about 600 ℃ carbonization temperature, observe the particulate of calcium compound and do not separate out to above-mentioned micro-pore wall surface fully.In addition, for about 800 ℃ carbonization temperature, separate out to above-mentioned micro-pore wall surface though see the particulate of calcium compound, it is many to observe blank.Like this, draw functional group as much as possible from the above-mentioned micro-pore wall surface of carbide, can enumerate about 650 ℃~750 ℃ as essential carbonization temperature in order to make calcium.
As acid solution of the present invention, can enumerate HCl, H
2SO
4Deng no problem acid solution in wastewater treatment during fabrication.The concentration of acid solution is more than or equal to 0.01mol/L, and promptly 0.01mol/L~20mol/L is preferably 0.1mol/L~10mol/L.Concentration is lower than 0.01mol/L, can produce the unfavorable condition that can not get abundant effect.In addition, as acid solution, preferably contain the anion that can carry out ion-exchange with absorption object anion, but contact in the solution of vegetable material before the charing, restriction does not contain the anion that can carry out ion-exchange with absorption object anion.
In the described invention of claim 11, by making the micro-pore wall of the carbide that acid solution contact such as HCl solution for example forms by carbonizing apparatus charing plant material, thereby in the functional group that forms on the micro-pore wall surface of the carbide of plant can in conjunction with can with absorption object anion such as nitric acid type nitrogen or the nitrite type nitrogen anion that carries out ion-exchange for example, for example chlorion etc.Think that this is when making carbide for example contact HCl solution, the chlorion in the HCl solution can be combined in the functional group on micro-pore wall surface of carbide, is combined in acid treatment charcoal S (with reference to Fig. 1) in this functional group and obtain chlorion.
And then, in the described invention of claim 12, by carrying out charing behind the solution that makes plant material contact calcium ions, make the micro-pore wall of the carbide that acid solution contact charing such as HCl solution for example forms, thereby can be directly in the functional group of drawing from above-mentioned micro-pore wall or through calcium ion in conjunction with can with absorption object anion such as nitric acid type nitrogen or the nitrite type nitrogen anion that carries out ion-exchange for example, for example chlorion etc.Think that this is for example above-mentioned Ca charcoal 31 to be immersed in when for example HCl Solution H (with reference to Fig. 9 (A)) is middle, (with reference to Fig. 9 (B)) combined chloride ion (with reference to Fig. 9 (C)) on the micro-pore wall surface and calcium ion functional groups and above-mentioned functional group of Ca charcoal 31, thus chlorion obtained through calcium ion or directly be combined in acid treatment Ca charcoal 32 (with reference to Fig. 9 (D)) in this functional group.
In addition, above-mentioned acid treatment adopts that to impregnated in when handling in the acid solution efficient good, preferably under reduced pressure carries out, and preferably carries out in the pressure limit of 1330Pa~13.3Pa.
The manufacturing installation of the described anion-adsorbing carbon material of claim 14 is characterised in that to have the carbonizing apparatus that the contacted plant material that contains solution of metal chloride is carried out charing.This moment, use can be set the retort of carbonization temperature as carbonizing apparatus.
The manufacturing installation of the described anion-adsorbing carbon material of claim 15 is characterised in that to have the device that makes the muriatic solution of plant material contact containing metal and dock the carbonizing apparatus that above-mentioned raw materials after touch carries out charing.This moment, use can be set the retort of carbonization temperature as carbonizing apparatus.In addition, as making the muriatic solution of containing metal contact the device of above-mentioned plant material, also can consider Dropping feeder, apparatus for coating, spray equipment, sprayer unit of above-mentioned solution etc., but the most effectively above-mentioned raw materials is immersed in the immersion system in the above-mentioned solution.
For the situation that makes the muriatic solution contact of containing metal above-mentioned raw materials in advance, shown in claim 14, in the manufacturing installation of anion-adsorbing carbon material, do not need to be used to make the device of the muriatic solution of raw material contact containing metal; Shown in claim 15, have the situation of the device that is used to make the muriatic solution of raw material contact containing metal for the manufacturing installation of anion-adsorbing carbon material, can use plant material arbitrarily.
In addition, the metal chloride that above-mentioned what is called is combined in the carbide is,, be combined in so it is meant in the carbide and after water or acid flushing, do not dissolve and the metal remained chloride attached to the metal chloride the metal chloride in the carbide except only.And the content of metal chloride is lower than at 2% o'clock, and the anion adsorption capacity is relatively poor; Even content surpasses 25%, the anion adsorption capacity often can not improve yet.Therefore, preferably contain as ash content 2%~25% be combined in metal chloride in the carbide.
Manufacturing installation can also have carbide contact water and/or the acid solution that generates in the above-mentioned carbonizing apparatus by making, and removes attached to the unnecessary metal chloride crystallization on the carbide, improves the device (claim 17) of anion adsorption capacity.Here, as the device that makes water and/or the above-mentioned carbide of acid contact, can be the Dropping feeder, apparatus for coating, spray equipment, sprayer unit etc. of water and/or acid, but the most above-mentioned carbide is immersed in the device in water and/or the acid.
Manufacturing installation can also following formation: have the arid region, be used to obtain the intermediate of anion-adsorbing carbon material with drying, and utilize the used heat of carbonizing apparatus to come dry above-mentioned intermediate (claim 18) in dry zone at this.
In any one invention of claim 11~18, the carbonization temperature of above-mentioned carbonizing apparatus can be 400 ℃~1000 ℃.In addition, this carbonization temperature is preferably 500 ℃~900 ℃, most preferably is 650 ℃~750 ℃.
Particularly use CaCl as metal chloride
2Situation, find when observing with electron microscope, particularly naturally during cooling, can form more functional group after carbonizing apparatus is continuing 1 hour about carbonization temperature of 650 ℃~750 ℃, the particulate of metal chloride is separated out in the micro-pore wall surface of carbide and evenly dispersion midway.
Invention for claim 1~3 relates to owing to carry out charing after making the solution contact plant material that contains calcium ion, then makes acid solution contact; Perhaps the contacted plant material that contains the solution of calcium ion is carried out charing, make acid solution contact its carbide again; Perhaps make acid solution contact that the plant material of the solution of contacted calcium ions is carried out carbide after the charing, so when suitable when setting carbonization temperature, can obtain having equal or than the anion-adsorbing carbon material of the anion characterization of adsorption of anion exchange resin excellence with anion exchange resin.In addition, the anion-adsorbing carbon material of the manufacture method manufacturing by above-mentioned anion-adsorbing carbon material is of value to environment based on plant material.
For the invention that claim 4~8 relates to, can obtain having equal or than the anion-adsorbing carbon material of its excellent anion characterization of adsorption with anion exchange resin.And this anion-adsorbing carbon material is of value to environment based on plant material.
For the invention that claim 9 relates to, can obtain the anion-adsorbing carbon material that can repeated regeneration uses.
Such as claim 10 record, by from above-mentioned anion-adsorbing carbon material, removing the anion of absorption, simultaneously, substitute the above-mentioned anion of removing and, can use above-mentioned anion-adsorbing carbon material by repeated regeneration in conjunction with the anion that can carry out ion-exchange with absorption object anion subsequently.
The invention that relates to for claim 11, owing to have the carbonizing apparatus and the device that makes the carbide contact acid solution that in this carbonizing apparatus, generates that plant material are carried out charing, therefore can make the micro-pore wall of acid solution contact carbide, can make in the functional group that is formed on the above-mentioned micro-pore wall in conjunction with the anion that can carry out ion-exchange with absorption object anion.
The invention that relates to for claim 12, owing to have the device that device, the butt joint above-mentioned raw materials after touch of the solution that makes plant material contact calcium ions carry out the carbonizing apparatus of charing and make the carbide contact acid solution that generates in this carbonizing apparatus, therefore can make the micro-pore wall of acid solution contact carbide, in the functional group that can form drawing from above-mentioned micro-pore wall directly or through calcium ion in conjunction with the anion that can carry out ion-exchange with absorption object anion.
Thereby, can as situation about after plant material is carried out charing, being immersed in the ferric chloride solution, not produce the problem of the wastewater treatment of Fe, the anion-adsorbing carbon material that can obtain having the anion adsorption capacity.
And, for this invention, make plant material contact contain the situation of carrying out charing behind the solution of calcium ion, the suitable carbonization temperature of setting can obtain having equal or than the anion-adsorbing carbon material of the anion characterization of adsorption of anion exchange resin excellence with anion exchange resin.
The invention that relates to for claim 13, because charing by plant material, portion forms micropore within it, on this micro-pore wall, form a large amount of functional groups, so can be directly in this functional group or through calcium ion in conjunction with the anion that can carry out ion-exchange with absorption object anion, thereby can improve the anion adsorption capacity of carbide effectively.
The anion-adsorbing carbon material that the manufacturing installation of the anion-adsorbing carbon material of the invention that relates to by claim 14 and 15 forms, because the chlorion of the metal chloride that contains at carbide has anion exchange capacity, so carbide can be brought into play the function of anion-adsorbing carbon material.
Above-mentioned carbonizing apparatus is by plant material is carried out charing, and portion forms micropore within it, draws a large amount of functional groups on its micro-pore wall surface, simultaneously in this functional group through metal ion or directly in conjunction with can with absorption object anion (NO for example
3 -) anion (Cl for example that carries out ion-exchange
-) the situation (claim 16) of device, the charing by to the plant material of contacted metal chloride can improve anionic adsorption capacity effectively.
Have the carbide contact water and/or the acid solution that generate in the above-mentioned carbonizing apparatus by making, remove attached to the unnecessary metal chloride crystallization on the carbide, improve the situation (claim 17) of the device of anion adsorption capacity, owing to can further improve the anion adsorption capacity of anion-adsorbing carbon material, so be preferred.
Have the situation (claim 18) that the used heat that comes drying to be used to obtain the intermediate of anion-adsorbing carbon material and utilize carbonizing apparatus in this arid region in the arid region comes the such formation of dry above-mentioned intermediate, when this intermediate of charing, can shorten necessary heat time heating time.And, make the carbide intermediate contact the situation of water and/or acid solution, by making the intermediate drying, can also obtain light weight, easy to handle anion-adsorbing carbon material.In addition, utilize used heat to carry out drying in the arid region, therefore can effectively utilize energy.
Description of drawings
Fig. 1 is that the integral body of expression the 1st embodiment constitutes key diagram.
Fig. 2 is the figure of the whole manufacturing process in the above-mentioned embodiment of expression.
Fig. 3 is that the integral body of expression the 2nd embodiment constitutes key diagram.
Fig. 4 is the figure of the whole manufacturing process in expression the 2nd embodiment.
Fig. 5 is the figure of each adsorbance of anion-adsorbing carbon material in the adsorption test of nitric acid type nitrogen and nitrite type nitrogen that obtain by the 1st, 2 embodiments of expression.
Fig. 6 is the figure of each adsorbance of anion-adsorbing carbon material in the adsorption test of fluorine ion that obtain by the 1st, 2 embodiments of expression.
Fig. 7 is the figure that is illustrated in the operation of the solution that makes plant material contact calcium ions in the 2nd embodiment.
Fig. 8 is illustrated in the figure that the above-mentioned raw materials that docks in the 2nd embodiment after touch carries out the operation of charing.
Fig. 9 is the figure that is illustrated in the operation that makes the carbide contact acid solution that generates in the 2nd embodiment in carbonizing apparatus.
Figure 10 is that the anion-adsorbing carbon material that expression the 2nd embodiment obtains adsorbs the figure of the mechanism of nitrate ion.
Figure 11 is the key diagram of formation of the device of the manufacturing anion-adsorbing carbon material that relates to of schematic representation the 3rd embodiment of the present invention.
Figure 12 (A) is the figure of an example of expression anion-adsorbing carbon material, and Figure 12 (B) is the figure of the processing example of the above-mentioned anion-adsorbing carbon material of expression.
Figure 13 is that expression uses above-mentioned manufacturing installation to make the figure of an example of the technology of above-mentioned raw material of wood-charcoal material.
Figure 14 (A)~(C) is the figure of the detailed process of the step S2 among expression Figure 13.
Figure 15 (A)~(C) is the figure of the detailed process of the step S4 among expression Figure 13.
Figure 16 (A)~(C) is the figure of the detailed process of the step S5 among expression Figure 13.
Figure 17 (A)~(D) is the figure of the details of absorption nitrate ion in the above-mentioned embodiment of expression, (E) is the figure of the raw material of wood-charcoal material after the expression regeneration.
Figure 18 is expression above-mentioned raw material of wood-charcoal material and the comparative material chart to the comparative result of the adsorbance of nitric acid type nitrogen, nitrite type nitrogen.
Figure 19 is that expression changes the CaCl among the step S2
2The concentration of solution and raw material of wood-charcoal material that the raw material of wood-charcoal material made and HCl obtain after handling are to the chart of each adsorbance of nitric acid type nitrogen.
Figure 20 is expression above-mentioned raw material of wood-charcoal material and the comparative material chart to the comparative result of the adsorbance of fluorine ion.
Symbol description
1 carbonizing apparatus
2 plant materials
3 make the device of carbide contact acid solution
10 contacts contain the device of solution of metal chloride
12,24 arid regions
22 improve the device of anion adsorption capacity
A, 31,36 carbides (intermediate)
C contains the solution of calcium ion
The H acid solution
M contains solution of metal chloride
S, 30,32,35,37 intermediates
The specific embodiment
Following with reference to accompanying drawing, embodiments of the present invention are described.But the present invention is not limited to this.
Fig. 1, Fig. 2 represent the 1st embodiment of the present invention.
In Fig. 1, Fig. 2, the 1st, vegetalitas wood materials (example of plant material) 2 such as natural fibers such as fiber crops or timber are not activated and the retort (plant material being carried out an example of the carbonizing apparatus of charing) of charing.Use a for example wooden bits as above-mentioned raw materials 2.These wooden bits is that coniferous trees such as Japan cypress that for example water imbibition is high, China fir are sliced into the wooden bits that size for example obtains smaller or equal to 10mm.
The 3rd, be used for making acid treatment device at the carbide contact acid solution of carbonizing apparatus 1 generation, accommodating HCl, H
2SO
4Container 4 inside Deng acid solution H have stirrer paddle 5.The concentration of this acid solution H for example is 5mol/L.Acid treatment device 3 is to be used for the sheet bits shape charcoal A that obtains at retort 1 is carried out acid-treated device.And the acid treatment charcoal that can use at once after (1) acid treatment (example of intermediate) S is directly used.In addition, (2) can be used in the alkali after acid treatment and above-mentioned charcoal S as required, and (3) also can be washed the acid treatment charcoal S after the neutralization as required at this moment.
The 6th, drier, acid treatment charcoal S after utilizing retort used heat to acid treatment or the acid treatment charcoal S after acid treatment, neutralization, washing carry out drying.Also can omit drying when using with moisture state here.6a (with reference to Fig. 2) be used to process drying acid treatment charcoal S add the Ministry of worker.The 7th, the acid treatment charcoal S that this drying was handled is by granular goods, and the 8th, the acid treatment charcoal S that drying was handled pulverizes and the goods that form.Carry out the processing of goods respectively according to purposes.In addition, as the goods beyond goods 7 and 8, can enumerate and for example on nonwoven, adhere to the acid treatment charcoal S that drying handled and the goods that form.
Fig. 3, Fig. 4 represent the 2nd embodiment of the present invention.
At Fig. 3, among Fig. 4, acid treatment Ca charcoal 32 following obtaining as an example of anion-adsorbing carbon material: after being immersed in vegetalitas wood materials (example of plant material) 2 such as natural fiber such as fiber crops or timber in the solution of preparing in the device (making an example of the device of the solution contact plant material that contains calcium ion) 9 that imports Ca that contains calcium ion (for example limewash C), utilize drier 12 to carry out drying, then do not activate and charing in retort (example of carbonizing apparatus) 1, the carbide that will generate in carbonizing apparatus 1 at the acid treatment device 3 that is used for contact acid solution is immersed in HCl subsequently, H
2SO
4In acid solution H, and then utilize drier 6 to carry out drying, process adding the 6a of the Ministry of worker.
In this embodiment, use wooden bits as above-mentioned plant material (hereinafter to be referred as raw material) 2.These wooden bits is that coniferous trees such as Japan cypress that for example water imbibition is high, China fir are sliced into the wooden bits that size for example obtains smaller or equal to 10mm.The device 9 of above-mentioned importing Ca is the devices that are used for importing to wooden bits 2 Ca, has the container 10 of the solution that contains calcium ion that holds wooden bits 2 of dipping.In this embodiment, wooden bits 2 of dipping in limewash C, be immersed in wooden bits 2 among the limewash C of normal concentration (for example 5 weight %) after, from container 10, take out, thereby obtained importing sheet bits (example of intermediate) 30 of Ca.At this moment, fully infiltrate in the wooden bits 2, the composition of calcium ion and wooden bits 2 is fully reacted, preferably in wooden bits dipping process, drive the stirrer paddle 10a that is arranged on container 10 inside in order to make solution.
The sheet bits 30 of Ca that utilized importing that above-mentioned drier 12 dryings obtain.Drier 12 utilizes retort used heat to make the sheet that has imported Ca consider 30 dryings to be worth doing in this embodiment.Treatment effeciency is good when using milk of lime here.In addition, also can replace lime water C and milk of lime, use calcium chloride solution or calcium acetate solution.
Dry importing of crossing the sheet bits 30 of Ca in retort 1 by charing, obtain the Ca charcoal (example of carbide intermediate) 31 of sheet bits shape.In this embodiment, for carbonization condition, carbonization temperature is 650 ℃~750 ℃.
Above-mentioned acid treatment device 3 has the HCl of holding, H
2SO
4In acid solution H container 4, has stirrer paddle 5 in these container 4 inside.The concentration of this acid solution H for example is 5mol/L.Above-mentioned acid treatment device 3 is to be used for the sheet that obtains at retort 1 bits shape Ca charcoal 31 is carried out acid treatment and obtains the device of acid treatment Ca charcoal 32.In order to promote the calcium carbonate (CaCO on Ca charcoal 31 surfaces
3) dissolve because of acid, the functional group on chlorion and calcium ion and above-mentioned Ca charcoal 31 surfaces is fully reacted, the preferred stirrer paddle 5 that is arranged on container 4 inside that drives.The acid treatment Ca charcoal (example of carbide intermediate) 32 that utilizes above-mentioned drier 6 dryings to obtain.In this embodiment, drier 6 utilizes retort used heat to come dry acid treatment Ca charcoal 32.
And the acid treatment Ca charcoal 32 that can use at once after (1) acid treatment and the drying directly is processed into goods as anion-adsorbing carbon material.In addition, (2) can handle Ca charcoal 32 with the alkali neutralizing acid as required after acid treatment, and (3) also can be washed the acid treatment Ca charcoal after the neutralization as required at this moment.Here, situation about using with moisture state also can be omitted drying.
7 ' be acid treatment Ca charcoal 32 by granular goods, 8 ' is to pulverize acid treatment Ca charcoal 32 and the goods that form.As follows, carry out the processing of goods respectively according to purposes.In addition, as goods 7 ' and 8 ' goods in addition, for example can enumerate and load with acid treatment Ca charcoal 32 and the goods of formation to nonwoven.Here, also there are the situation of each comfortable different produce in factory in the sheet bits 30 that imported Ca and Ca charcoal 31, and can make acid treatment Ca charcoal 32 by the operation midway of above-mentioned embodiment this moment respectively.In addition, acid treatment Ca charcoal 32 also can unreally apply the worker and use with original shape.
" adsorption test of nitric acid type nitrogen, nitrite type nitrogen "
[test method]
The concentration of preparing 5 nitric acid type nitrogen and nitrite type nitrogen respectively is 50ml salpeter solution and the nitrous acid solution (titer) of 50mg/L (50ppm).Following 5 samples are put into corresponding titer respectively, and for example vibration was measured the concentration of the nitric acid type nitrogen in above-mentioned salpeter solution and the nitrous acid solution and the concentration of nitrite type nitrogen respectively after 10 hours under 200rpm, 20 ℃ condition, calculated adsorbance.
Described sample is:
(1) 700 ℃ make 2 charings of wooden bits and the charcoal 200mg (hereinafter to be referred as charcoal) that are used for comparative example that obtain,
(2) will be immersed in the FeCl of 1mol/L at 700 ℃ of charcoals that make 2 charings of wooden bits and obtain
3The iron chloride charcoal 200mg that is used for comparative example that washes after in the solution and obtain,
(3) will 700 ℃ make 2 charings of above-mentioned wooden bits and the charcoals that obtain are washed after being immersed in the HCl solution of 5mol/L and the acid treatment charcoal 200mg that obtains,
(4) after being immersed in wooden bits 2 in the limewash of 5 weight %, carry out charing at 700 ℃, again the charcoal that obtains is immersed in the HCl solution of 5mol/L and acid treatment Ca charcoal 32 (anion-adsorbing carbon material) 200mg that obtains,
(5) be used for the anion exchange resin 200mg of comparative example.
[result]
Fig. 5 represents the nitric acid type nitrogen of above-mentioned each sample and the comparison of nitrite type nitrogen adsorption capacity.
The charcoal of 700 ℃ of charings (1) adsorbs nitric acid type nitrogen and nitrite type nitrogen hardly, and the iron chloride charcoal of opposite (2) adsorbs the nitric acid type nitrogen of 2.75mg/g and the nitrite type nitrogen of 2.35mg/g respectively.In addition, the acid treatment charcoal S of (3) adsorbs the nitric acid type nitrogen of 2.50mg/g and the nitrite type nitrogen of 2.20mg/g respectively.(5) anion exchange resin adsorbs the nitric acid type nitrogen of 10.80mg/g and the nitrite type nitrogen of 10.00mg/g respectively.
On the other hand, carry out charing after being immersed in wooden bits 2 among the limewash C, the acid treatment Ca charcoal 32 of (4) that then are immersed in the HCl solution and form adsorbs the nitric acid type nitrogen of 10.75mg/g and the nitrite type nitrogen of 9.80mg/g respectively, demonstrates the equal or better adsorption capacity of anion exchange resin with (5).
Above-mentioned acid treatment Ca charcoal 32 for example adsorbs, and the mechanism of nitrate ion is thought as follows.Shown in Figure 10 (A), when for example being immersed in acid treatment Ca charcoal 32 (anion-adsorbing carbon material) among the salpeter solution L, on the micro-pore wall surface of acid treatment Ca charcoal 32 through calcium ion or directly exchange (with reference to Figure 10 (C)) with the chlorion (with reference to Figure 10 (B)) of functional groups and the nitrate ion among the salpeter solution L, nitrate ion is adsorbed (with reference to Figure 10 (D)) by acid treatment Ca charcoal 32.Variation when Figure 10 (E) expression is immersed in the acid treatment Ca charcoal 32 shown in Figure 10 (D) in KCl (perhaps NaCl) solution.That is, the acid treatment charcoal that has adsorbed nitrate ion carries out can regenerating after the exchange of chlorion and nitrate ion in KCl (perhaps NaCl) solution once more.Below describe at this regeneration test.
" regeneration test "
[test method]
With the acid treatment charcoal S of KCl (perhaps NaCl) solution washing after the adsorption test of above-mentioned nitric acid type nitrogen or the sample of acid treatment Ca charcoal 32 of 1mol/L, and then wash.Then, exchange standard liquid, preparing nitric acid type nitrogen concentration is 50ml (milliliter) salpeter solution of 50mg/L, and the 200mg said sample of washing is carried out the regeneration test first time.That is, said sample is put into salpeter solution, vibration was measured the nitric acid type nitrogen concentration in the above-mentioned salpeter solution after 10 hours under 200rpm for example, 20 ℃ condition, used said sample to carry out regeneration test calculating first time adsorbance.
Then, the said sample of in the regeneration test first time, having used with KCl (perhaps NaCl) solution washing of 1mol/L, and then washing.Then, exchange standard liquid, preparing nitric acid type nitrogen concentration is 50ml (milliliter) salpeter solution of 50mg/L, and the 200mg said sample of above-mentioned washing is carried out regeneration test.That is, said sample is put into 50ml (milliliter) salpeter solution, vibration was measured the nitric acid type nitrogen concentration in the above-mentioned salpeter solution after 10 hours under 200rpm for example, 20 ℃ condition, used said sample to carry out the regeneration test and calculated adsorbance.Repeat twice this processing subsequently.
[result]
Utilize the adsorbance of the nitric acid type nitrogen of acid treatment charcoal S
For the first time ... 2.5mg/g
Regeneration for the first time ... 2.5mg/g
Regeneration for the second time ... 2.4mg/g
Regeneration for the third time ... 2.5mg/g
Utilize the adsorbance of the nitric acid type nitrogen of acid treatment Ca charcoal 32
For the first time ... 10.8mg/g
Regeneration for the first time ... 10.6mg/g
Regeneration for the second time ... 10.9mg/g
Regeneration for the third time ... 10.7mg/g
As known from the above, by washing used above-mentioned acid treatment charcoal S and acid treatment Ca charcoal 32 respectively with dense KCl (or NaCl) solution, and then washing, can regenerate.Promptly, can know, by wash acid treatment charcoal S and the acid treatment Ca charcoal (anion-adsorbing carbon material) 32 that in the adsorption test of nitric acid type nitrogen, has adsorbed nitric acid type nitrogen (anion) respectively with KCl (or NaCl) solution, and then washing, the nitric acid type nitrogen (anion) that adsorbs in the adsorption test of nitric acid type nitrogen is removed, and by substituting the nitric acid type nitrogen (anion) be removed in conjunction with Cl
-, acid treatment charcoal S and acid treatment Ca charcoal 32 (anion-adsorbing carbon material) can be regenerated respectively.That is to say, can confirm, after each the use respectively to using once acid treatment charcoal S and acid treatment Ca charcoal 32 (anion-adsorbing carbon material) to wash and wash, thereby can use repeatedly.In addition, for the situation of having adsorbed nitrite type nitrogen, use acid treatment charcoal S and acid treatment Ca charcoal respectively as anion-adsorbing carbon material, regeneration principle is also identical.
" fluorine ion adsorption test "
[test method]
Preparing fluorinion concentration is the 50ml solution (titer) of 50mg/L, following 5 samples are put into corresponding titer respectively, for example measure the fluorinion concentration in the above-mentioned solution respectively after 10 hours, calculate adsorbance in vibration under 200rpm, 20 ℃ the condition.
Described sample is:
(1) 700 ℃ make 2 charings of wooden bits and the charcoal 100mg (hereinafter to be referred as charcoal) that are used for comparative example that obtain,
(2) will be immersed in the FeCl of 1mol/L at 700 ℃ of charcoals that make 2 charings of wooden bits and obtain
3The iron chloride charcoal 100mg that is used for comparative example that washes after in the solution and obtain,
(3) will 700 ℃ make 2 charings of above-mentioned wooden bits and the charcoals that obtain are washed after being immersed in the HCl solution of 5mol/L and the acid treatment charcoal 100mg that obtains,
(4) after being immersed in wooden bits 2 in the limewash of 5 weight %, carry out charing at 700 ℃, again the charcoal after the charing is immersed in the HCl solution of 5mol/L and anion-adsorbing carbon material (hereinafter to be referred as the acid treatment Ca charcoal 32) 100mg that obtains,
(5) be used for the anion exchange resin 100mg of comparative example.
[result]
Fig. 6 represents the comparison of the fluorine ion adsorption capacity of above-mentioned each sample.
The charcoal of 700 ℃ of charings (1) adsorbs fluorine ion hardly, the fluorine ion of the iron chloride charcoal absorption 7.50mg/g of opposite (2).In addition, the fluorine ion of the acid treatment charcoal S of (3) absorption 5.00mg/g.(5) fluorine ion of anion exchange resin absorption 8.50mg/g.
On the other hand, wooden bits 2 are carried out after being immersed in the limewash charing, then be immersed in the HCl solution and the fluorine ion of the acid treatment Ca charcoal 32 absorption 19.00mg/g of (4) that form demonstrates considerably beyond the adsorption capacity of the anion exchange resin of (5).
" regeneration test "
[test method]
Then, wash having carried out the acid treatment charcoal S after the above-mentioned fluorine adsorption test or the sample of acid treatment Ca charcoal 32 with the hydrochloric acid (perhaps sulfuric acid) of 1mol/L, and then wash.Then, exchange standard liquid, preparing fluorinion concentration is 50ml (milliliter) solution of 50mg/L, and the 200mg said sample of above-mentioned washing is carried out the regeneration test first time.That is, said sample is put into above-mentioned solution, vibration was measured the fluorinion concentration in the above-mentioned solution after 10 hours under 200rpm for example, 20 ℃ condition, used said sample to carry out regeneration test first time, the calculating adsorbance.Then, the said sample of in the regeneration test first time, having used with the hydrochloric acid (perhaps sulfuric acid) of 1mol/L washing, and then washing.Then, exchange standard liquid, preparing fluorinion concentration is the above-mentioned solution of 50ml (milliliter) of 50mg/L, and the 200mg said sample of above-mentioned washing is carried out regeneration test.That is, said sample is put into the above-mentioned solution of 50ml (milliliter), vibration was measured the fluorinion concentration in the above-mentioned solution after 10 hours under 200rpm for example, 20 ℃ condition, used said sample to carry out regeneration test calculating second time adsorbance.Repeat twice this processing subsequently.
[result]
Utilize the adsorbance of the fluorine ion of acid treatment charcoal S
For the first time ... 2.5mg/g
Regeneration for the first time ... 2.5mg/g
Regeneration for the second time ... 2.4mg/g
Regeneration for the third time ... 2.5mg/g
Utilize the adsorbance of the fluorine ion of acid treatment Ca charcoal 32
For the first time ... 18.7mg/g
Regeneration for the first time ... 18.2mg/g
Regeneration for the second time ... 18.9mg/g
Regeneration for the third time ... 18.6mg/g
As known from the above, by washing used above-mentioned acid treatment charcoal S and acid treatment Ca charcoal 32 respectively with dense hydrochloric acid (or sulfuric acid), and then washing, can regenerate.Promptly, can know, by wash acid treatment charcoal S and the acid treatment Ca charcoal 32 (anion-adsorbing carbon material) that in the fluorine adsorption test, has adsorbed fluorine ion (anion) respectively with hydrochloric acid (or sulfuric acid), and then washing, the fluorine ion that adsorbs in the fluorine ion adsorption test (anion) is removed, and by substituting the fluorine ion (anion) be removed in conjunction with Cl
-(or SO
4 2-), acid treatment charcoal S and acid treatment Ca charcoal 32 (anion-adsorbing carbon material) can be regenerated respectively.That is to say, can confirm, after each the use respectively to using once acid treatment charcoal S and acid treatment Ca charcoal 32 (anion-adsorbing carbon material) to wash and wash, thereby can use repeatedly.
Figure 11~Figure 20 represents the 3rd embodiment of the present invention.Figure 11 is an example of the manufacturing installation of the anion-adsorbing carbon material (hereinafter referred to as the raw material of wood-charcoal material) 37 that relates to of schematic representation the 3rd embodiment of the present invention, and in the figure, 2 is material plant, and 2 is wooden bits in this embodiment.This wooden bits 2 are that coniferous trees such as Japan cypress that for example water imbibition is high, China fir are sliced into wooden bits that obtain smaller or equal to the suitable size of 50mm.
Above-mentioned wooden bits 2 are sent to the metal chloride solutions that accommodates suitable concentration and (are CaCl in this embodiment
2Solution) in the treatment trough 20 of M (contact contains the device of solution of metal chloride), in this treatment trough 20, wooden bits 2 are carried out metal chloride and (be CaCl in this embodiment
2) importing handle, form metal chloride importing tablet bits (example of intermediate) 35.In addition, 20a is arranged on the stirring blade in the treatment trough 20, drives by motor (not shown) rotation, is used for the interior liquid of stir process groove 20 etc.Here, in metal chloride solutions, add a small amount of Ca (OH) in advance
2Be preferred aspect the raising anion adsorption capacity.
The metal chloride importing tablet that obtains as mentioned above bits 35 by drier 12 dry processing after, be sent to charing and handle stove 1 (carbonizing apparatus), do not activate and carry out charing and handle.Here, above-mentioned drier 12 is to the intermediate that can obtain raw material of wood-charcoal material 37, is the example that metal chloride importing tablet bits 35 carry out dry arid region that the used heat that the formation of drier 12 makes it possible to handle stove 1 discharge from charing is used in above-mentioned dry the processing.
Accommodate the retort body 1a of thermal source 21 heating that suited in the inside of above-mentioned charing processing stove 1.Metal chloride importing tablet bits 35 are in introduction part 1b is fed into above-mentioned retort body 1a, by heating with suitable temperature (aftermentioned) and suitable time (aftermentioned) by charing, form carbide, this carbide as the raw material of wood-charcoal material 36 of an example of intermediate outside discharge portion 1c is discharged to retort body 1a.
Subsequently, above-mentioned raw material of wood-charcoal material 36 is sent to the treatment trough 22 (improving the device of anion adsorption capacity) that accommodates water or HCl solution (hydrochloric acid) H, utilizes water or HCl Solution H to contact (dipping) to raw material of wood-charcoal material 36 in this treatment trough 22 and handles.Here, 23 are arranged on the stirring blade in the treatment trough 22, utilize motor (not shown) rotation to drive, and are used for the interior liquid of stir process groove 22 etc.Carried out and the processing of also carrying out sometimes after contacting of acid handled with water that contacts, and also can carry out according to reverse order.
Then, the raw material of wood-charcoal material (example of intermediate) 37 that flooded water or HCl Solution H is sent to drier 24, the dry plastochondria (particle) 7 of handling the suitable particle diameter of back formation " or pulverized thinner powder 8 ".Here, above-mentioned drier 24 is to be a granulated into particle 7 " or powder 8 " before the raw material of wood-charcoal material 37 as intermediate is carried out an example of dry arid region, the formation of drier 24 makes it possible to handle from charing the used heat that stove 1 discharges and is used in above-mentioned dry processing.
In addition, form the raw material of wood-charcoal material 37 of the sheet bits shape of the about 10mm of length shown in Figure 12 (A); Figure 12 (B) expression forms the raw material of wood-charcoal material 37 of above-mentioned bits shape the plastochondria (particle) 7 of suitable particle diameter " example.
Then, with reference to Figure 11 and Figure 13, explain an example of using device shown in Figure 11 to obtain the step of raw material of wood-charcoal material 37 by material plant 2.At first, prepare coniferous trees such as Japan cypress, China fir are sliced into wooden bits 2 (step S1) that obtain smaller or equal to the suitable size of 10mm.
Then, with the above-mentioned wooden CaCl that be adjusted into 1~20 weight % of bits 2 in treatment trough 20
2Dipping is for example at least 3 hours in the solution M.In the dipping process of this wooden bits 2, preferably make stirrer paddle 20a rotation.Thus, CaCl
2Solution M can infiltrate in the wooden bits 2, obtains metal chloride importing tablet bits 35 (the step S2) that calcium ion and chlorion are imported into wooden bits 2.
Subsequently, above-mentioned metal chloride importing tablet bits 35 are sent to drier 12 and carry out drying processing (step S3).
Then, above-mentioned wooden bits 2 are fed into the retort body 1a that stove 1 is handled in charing, about 1 hour of 400 ℃~1000 ℃ temperature ranges (in this embodiment being 700 ℃) heating, carry out charing and handle (step S4).Thus, obtain raw material of wood-charcoal material 37.
Above-mentioned raw material of wood-charcoal material 37 is fed into treatment trough 22, carries out impregnation process (step S5) in the HCl Solution H that is adjusted to 0.01mol/L~11mol/L (for example 5mol/L) in treatment trough 22.Preferably make stirrer paddle 23 rotations this moment, can remove the unnecessary metal chloride (CaCl that remains in the raw material of wood-charcoal material 37 thus
2) crystallization, simultaneously can further add chlorion, thus the raw material of wood-charcoal material 37 that obtains expecting.
Subsequently, the processing (step S6) that in drier 24, is dried usually of the raw material of wood-charcoal material 37 after the above-mentioned impregnation process.Can directly deliver to drier 24 this moment with raw material of wood-charcoal material 37, also can be in suitable alkaline solution impregnating and carry out neutralisation treatment, and then after neutralisation treatment, wash.Here, when using raw material of wood-charcoal material 37, do not carry out drying sometimes and handle with moisture state.
Raw material of wood-charcoal material 37 after above-mentioned dry the processing also can be considered shape to be worth doing with sheet and directly be used, and uses suitable processing machine to make it form the plastochondria (particle) 7 of suitable particle diameter in this embodiment " or thinner powder 8 " (step S7).In addition, above-mentioned raw material of wood-charcoal material 37 for example also can use with the state of loading with on nonwoven except using with simple substance form.
Above-mentioned raw material of wood-charcoal material 37 is not limited to above-mentioned steps S1~step S7 all to carry out in same factory and makes.For example proceed under the situation of a certain step among above-mentioned steps S1~step S7, from midway step, also can make raw material of wood-charcoal material 37 again in other factories etc.
The present invention can carry out various distortion and implement, and is not limited to above-mentioned embodiment.For example, in the above-described embodiment,, enumerated the CaCl that can obtain the anion-adsorbing carbon material of peak performance as metal chloride
2, but BaCl
2And MnCl
2Deng also being fine.
In addition, in the above-described embodiment, in treatment trough 22, carry out the processing that contacts of raw material of wood-charcoal material 37 and HCl Solution H, but also can substitute the HCl Solution H and make water.Do not carry out the additional of chlorion this moment, but only remove the crystallization that remains in the unnecessary metal chloride in the raw material of wood-charcoal material 37.
And then, in the above-described embodiment, handle in charing and in the stove 1 metal chloride importing tablet bits 35 to be carried out charing and handle, obtain raw material of wood-charcoal material 37 after, can be sent to treatment trough 22, but also can not be sent to treatment trough 22.This moment is not owing to needing above-mentioned raw material of wood-charcoal material 37 is delivered to drier 24, so can omit above-mentioned steps S5, S6 in the manufacture method of raw material of wood-charcoal material 37.At this moment,, can promptly stop, also can carry out step S7 subsequently with step S1~S4 as the manufacture method of raw material of wood-charcoal material 37.
Then, illustrate for the absorption property of the nitric acid type nitrogen of investigating above-mentioned raw material of wood-charcoal material 37 and nitrite type nitrogen and the test of carrying out.Described about being described as follows of the test method of the absorption property of nitric acid type nitrogen and nitrite type nitrogen and result of the test.
At first, prepare 2 groups of 7 samples (1)~(7) shown below, each sample is 200mg.Promptly prepare 2 groups of following 7 samples:
(1) 700 ℃ of heating made 2 charings of wooden bits in 1 hour and the charcoal that obtains,
(2) make 2 charings of wooden bits in 1 hour 700 ℃ of heating, be immersed in the FeCl of 1mol/L subsequently
3In the solution, and wash and the iron chloride charcoal that obtains,
(3) anion exchange resin,
(4) BaCl that wooden bits 2 are immersed in 10 weight %
2After in the solution, made its charing in 1 hour and the BaCl that obtains 700 ℃ of heating
2Charcoal,
(5) BaCl that wooden bits 2 are immersed in 10 weight %
2After in the solution, made its charing in 1 hour, subsequently impregnation process and the HCl treatments B aCl that obtains in the HCl of 5mol/L solution 700 ℃ of heating
2Charcoal,
(6) CaCl that wooden bits 2 are immersed in 10 weight %
2After in the solution, made its charing in 1 hour and the CaCl that obtains 700 ℃ of heating
2Charcoal,
(7) CaCl that wooden bits 2 are immersed in 10 weight %
2After in the solution, made its charing in 1 hour, subsequently impregnation process and the HCl that obtains handles CaCl in the HCl of 5mol/L solution 700 ℃ of heating
2Charcoal.Here, the sample of (4)~(7) is equivalent to above-mentioned raw material of wood-charcoal material 37, and the sample of (1)~(3) is to be used for the sample that compares with raw material of wood-charcoal material 37.
Subsequently, each sample of one group is dropped into respectively in the solution (the 1st titer) of 50mL nitric acid type nitrogen that nitric acid type nitrogen concentration is 50mg/L (50ppm), and each sample of another group is dropped into respectively in the solution (the 2nd titer) of 50mL nitrite type nitrogen that the nitrite type nitrogen concentration is 50mg/L (50ppm).Then, in vibration under 200rpm, 20 ℃ the condition after 10 hours, measure nitric acid type nitrogen concentration in the 1st titer and the nitrite type nitrogen concentration in the 2nd titer respectively, calculate the adsorbance of the nitric acid type nitrogen and the nitrite type nitrogen of each sample.
Figure 18 represents the nitric acid type nitrogen adsorption capacity of each sample of being obtained by above-mentioned test and the comparative result of nitrite type nitrogen adsorption capacity.Here, represent the adsorbance of the nitric acid type nitrogen and the nitrite type nitrogen of each sample in the figure with pair of columnar figure, the adsorbance of the histogram graph representation nitric acid type nitrogen in left side, the adsorbance of the histogram graph representation nitrite type nitrogen on right side.Can know that from the result shown in this figure sample of the present invention all has high nitric acid type nitrogen adsorption capacity and nitrite type nitrogen adsorption capacity.And then, by comparing the BaCl of (4)
2The HCl treatments B aCl of charcoal and (5)
2The nitric acid type nitrogen of charcoal and the adsorbance of nitrite type nitrogen, and compare the CaCl of (6)
2The HCl of charcoal and (7) handles CaCl
2The nitric acid type nitrogen of charcoal and the adsorbance of nitrite type nitrogen can be known and carry out raw material of wood-charcoal material 37 is immersed in the adsorption capacity that processing (HCl processing) in the HCl solution can further improve the nitric acid type nitrogen and the nitrite type nitrogen of raw material of wood-charcoal material 37.But, handle even do not carry out HCl, also can obtain having the raw material of wood-charcoal material 37 of the adsorption capacity of sufficiently high nitric acid type nitrogen and nitrite type nitrogen, only do not carry out the contact of HCl solution this moment and handle, can make raw material of wood-charcoal material 37 at low cost.
At this, shown in Figure 17 (A), above-mentioned raw material of wood-charcoal material 37 for example adsorb that nitrate ion is considered to because, with raw material of wood-charcoal material (CaCl
2Charcoal) 37 when being immersed among the salpeter solution L, exchanging (with reference to Figure 17 (C)) through the chlorion (with reference to Figure 17 (B)) of calcium ion combination or direct combination and the nitrate ion among the salpeter solution L in the functional group on raw material of wood-charcoal material 37 surfaces, thereby nitrate ion is by 37 absorption (with reference to Figure 17 (D)) of raw material of wood-charcoal material.
In addition, Figure 17 (E) expression will be adsorbed nitrate ion and the raw material of wood-charcoal material 37 that forms the state shown in Figure 17 (D) state after being immersed in the chloride solution (for example metal chloride solutions of KCl, NaCl or HCl Solution H) of high concentration.That is, exchanged with chlorion by chloride solution by the nitrate ion of raw material of wood-charcoal material 37 absorption, raw material of wood-charcoal material 37 is reproduced thus, presents anionic states such as adsorbable nitrate ion.Promptly, raw material of wood-charcoal material 37 of the present invention is not limited to always by the new raw material of wood-charcoal material that obtains of above-mentioned manufacture method, also can be from utilizing raw material of wood-charcoal material 37 that above-mentioned manufacture method obtains and that adsorbed anion (for example nitrate ion) to remove the anion (nitrate ion) of absorption, simultaneously, substitute the above-mentioned anion of removing (nitrate ion) and in conjunction with anion (being chlorion in this embodiment) the resulting raw material of wood-charcoal material (being the regenerated carbon material) that can carry out ion-exchange with absorption object anion (for example nitrate ion) subsequently.In addition, substitute above-mentioned chloride solution and when using sulfuric acid, nitrate ion does not carry out ion-exchange with above-mentioned chlorion with sulfate ion.
Then, the metal chloride solutions (CaCl that is used to flood wooden bits 2 in order to investigate in above-mentioned steps S2 is described
2Solution) the influence that the anion adsorption capacity of the raw material of wood-charcoal material 37 after making is produced of the concentration of M and the test carried out.Above-mentioned test is that wooden bits 2 are immersed in CaCl
2After among the solution M, by heating 1 hour and charing at 700 ℃, and wash and obtain raw material of wood-charcoal material 37, it is in the 50ml nitric acid type nitrogen solution (titer) of 50mg/L (50ppm) that this raw material of wood-charcoal material 37 is dropped into nitric acid type nitrogen concentration, investigate the test of the adsorption capacity of 37 pairs of nitric acid types of above-mentioned raw material of wood-charcoal material nitrogen, as above-mentioned CaCl
2Solution M working concentration is the solution of 1 weight %, 3 weight %, 5 weight %, 7 weight %, 10 weight %, 12 weight %, 14 weight %, 17 weight %, 20 weight %.Here, the addition of raw material of wood-charcoal material 37 is respectively 200mg.In addition, for relatively, use the following raw material of wood-charcoal material 37 of 200mg, also investigate at the adsorption capacity of its nitric acid type nitrogen, described raw material of wood-charcoal material 37 is by wooden bits 2 being immersed in the CaCl of 10 weight %
2After among the solution M, in 700 ℃ of heating charing in 1 hour, and then the HCl processing obtains.The results are shown among Figure 19 of above-mentioned test.
Can know from result shown in Figure 19, the anion adsorption capacity of raw material of wood-charcoal material 37 not with CaCl
2The concentration of solution improves pro rata, if from considerations such as cost aspects, then most preferable concentrations is about 10 weight %.In addition, can also know,, can carry out HCl to raw material of wood-charcoal material 37 and handle in order further to improve the anion adsorption capacity of raw material of wood-charcoal material 37 from result shown in Figure 19.
Then, regeneration test is described, the raw material of wood-charcoal material 37 that wherein adsorbs after the use of nitric acid type nitrogen is regenerated by KCl (or NaCl) solution, and the adsorption capacity of 37 pairs of nitric acid types of the raw material of wood-charcoal material nitrogen after the investigation regeneration.
At first, as raw material of wood-charcoal material 37, prepare the CaCl that 200mg is immersed in wooden bits 2 10 weight %
2The back made its charing in 1 hour and the CaCl that obtains 700 ℃ of heating in the solution
2Charcoal.Subsequently, with this CaCl
2It is in the 50ml nitric acid type nitrogen solution (titer) of 50mg/L (50ppm) that charcoal drops into nitric acid type nitrogen concentration, and vibration was measured the concentration of the nitric acid type nitrogen in the above-mentioned titer after 10 hours under 200rpm, 20 ℃ condition, calculated above-mentioned CaCl
2Charcoal is to the adsorbance (for the first time) of nitric acid type nitrogen.
Then, use the above-mentioned CaCl of KCl (or NaCl) solution washing of 1mol/L
2Charcoal, and then washing, thus regenerate.Subsequently, with the CaCl that regenerates
2In the new titer of preparing (concentration that is nitric acid type nitrogen is the 50ml nitric acid type nitrogen solution of 50mg/L) of charcoal input, vibration was measured the concentration of the nitric acid type nitrogen in the above-mentioned titer after 10 hours under 200rpm, 20 ℃ condition, calculated above-mentioned CaCl
2Charcoal is to the adsorbance of nitric acid type nitrogen.From this CaCl
23 times (regeneration for the first time~regeneration for the third time) is carried out in processing till the calculating of the adsorbance of the nitric acid type that the is regenerated to nitrogen of charcoal altogether.
The result of above-mentioned regeneration test is CaCl
2Charcoal to the adsorbance of nitric acid type nitrogen is:
For the first time ... 9.5mg/g
Regeneration for the first time ... 9.0mg/g
Regeneration for the second time ... 9.1mg/g
Regeneration for the third time ... 8.8mg/g.
Can confirm from above, be used for the raw material of wood-charcoal material 37 (CaCl of the absorption of nitric acid type nitrogen
2Charcoal) if, can regenerate with dense KCl (or NaCl) solution washing and washing.Think this be because, by adsorbed the CaCl of nitric acid type nitrogen with KCl (or NaCl) solution washing
2Charcoal, and then washing, nitric acid type nitrogen is from CaCl
2Be removed Cl on the charcoal
-Substitute this nitric acid type nitrogen that is removed and and functional groups.And, also can confirm from the result of above-mentioned regeneration test, if raw material of wood-charcoal material 37 (CaCl
2Charcoal) regenerates by carrying out KCl (or NaCl) solution washing and washing, can repeatedly be used to adsorb nitric acid type nitrogen so.In addition, with above-mentioned raw material of wood-charcoal material 37 (CaCl
2Charcoal) be used to adsorb the situation of nitrite type nitrogen, regeneration principle also is identical.
Then, use the CaCl that wooden bits 2 is immersed in 10 weight % as raw material of wood-charcoal material 37
2The back made its charing in 1 hour 700 ℃ of heating in the solution, carried out impregnation process subsequently in the HCl of 5mol/L solution and the HCl that obtains handles CaCl
2Charcoal is handled CaCl about this HCl
2Charcoal similarly carries out regeneration test and the result is shown with above-mentioned.
The result of above-mentioned regeneration test is that HCl handles CaCl
2Charcoal to the adsorbance of nitric acid type nitrogen is:
For the first time ... 11.0mg/g
Regeneration for the first time ... 11.0mg/g
Regeneration for the second time ... 10.8mg/g
Regeneration for the third time ... 10.8mg/g.
Can confirm that from above (HCl handles CaCl to the raw material of wood-charcoal material 37 that obtains for carrying out impregnation process after the charing in HCl solution
2Charcoal), after being used to adsorb nitric acid type nitrogen with dense KCl (or NaCl) solution washing, and then the washing, can regenerate.And also can confirm, make HCl handle CaCl repeatedly even carry out KCl (or NaCl) solution washing and wash
2Charcoal regeneration, the HCl that improves by the impregnation process in HCl solution handles CaCl
2The adsorption capacity of the nitric acid type nitrogen of charcoal also can continue (state of raising).
Then, the test of carrying out for the absorption property of investigating 37 pairs of fluorine ions of above-mentioned raw material of wood-charcoal material is described.At first, in order to carry out this test, prepare one group of above-mentioned 7 samples (1)~(7) of using in the absorption property test of nitric acid type nitrogen and nitrite type nitrogen, each sample is 50mg.Subsequently, each sample is dropped into respectively in the 50mL solution (titer) that fluorinion concentration is 50mg/L (50ppm), after 10 hours, the concentration of the fluorine ion in the bioassay standard liquid calculates the adsorbance of each sample to fluorine ion respectively in vibration under 200rpm, 20 ℃ the condition.
Figure 20 represents the comparative result of the fluorine ion adsorption capacity of each sample of being obtained by above-mentioned test.Can know that from the result shown in this figure sample of the present invention all has high fluorine ion adsorption capacity.And then, by comparing the BaCl of (4)
2The HCl treatments B aCl of charcoal and (5)
2The adsorbance of the fluorine ion of charcoal, and compare the CaCl of (6)
2The HCl of charcoal and (7) handles CaCl
2The adsorbance of the fluorine ion of charcoal can be known and carry out raw material of wood-charcoal material 37 is immersed in the fluorine ion adsorption capacity that processing (HCl processing) in the HCl solution can further improve raw material of wood-charcoal material 37.But, not handle even do not carry out HCl, the raw material of wood-charcoal material 37 that also can obtain having sufficiently high fluorine ion adsorption capacity does not only carry out the contact of HCl solution this moment and handles, and can make raw material of wood-charcoal material 37 at low cost.
Then, regeneration test is described, the raw material of wood-charcoal material 37 that wherein will be used to adsorb fluorine ion is by hydrochloric acid (or sulfuric acid) regeneration, and the fluorine ion adsorption capacity of the raw material of wood-charcoal material 37 after the investigation regeneration.
At first, as raw material of wood-charcoal material 37, prepare the CaCl that 200mg is immersed in wooden bits 2 10 weight %
2The back made its charing in 1 hour and the CaCl that obtains 700 ℃ of heating in the solution
2Charcoal.Subsequently, with this CaCl
2It is in the 50ml solution (titer) of 50mg/L (50ppm) that charcoal drops into fluorinion concentration, and vibration was measured the fluorinion concentration in the above-mentioned titer after 10 hours under 200rpm, 20 ℃ condition, calculated above-mentioned CaCl
2Charcoal is to the adsorbance (for the first time) of fluorine ion.
Then, the hydrochloric acid (or sulfuric acid) with 1mol/L washs above-mentioned CaCl
2Charcoal, and then washing, thus regenerate.Subsequently, with the CaCl that regenerates
2In the new titer of preparing (being that fluorinion concentration is the 50ml solution of 50mg/L) of charcoal input, vibration was measured the fluorinion concentration in the above-mentioned titer after 10 hours under 200rpm, 20 ℃ condition, calculated above-mentioned CaCl
2The fluorine ion adsorbance of charcoal.Carry out 3 times like this, altogether from this CaCl
2Processing till the calculating that is regenerated to the fluorine ion adsorbance of charcoal (regeneration for the first time~regeneration for the third time).
The result of above-mentioned regeneration test is CaCl
2Charcoal to the adsorbance of fluorine ion is:
For the first time ... 22.5mg/g
Regeneration for the first time ... 22.4mg/g
Regeneration for the second time ... 21.7mg/g
Regeneration for the third time ... 21.9mg/g.
Can confirm from above, be used for the raw material of wood-charcoal material 37 (CaCl of fluorine ion absorption
2Charcoal) if, can regenerate with dense hydrochloric acid (or sulfuric acid) washing and washing.Think this be because, by wash the CaCl adsorbed fluorine ion with hydrochloric acid (or sulfuric acid)
2Charcoal, and then washing, thus fluorine ion is from CaCl
2Be removed Cl on the charcoal
-(or SO
4 2-) substitute this fluorine ion that is removed and and functional groups.And, also can confirm raw material of wood-charcoal material 37 (CaCl from the result of above-mentioned regeneration test
2Charcoal) regenerates by carrying out hydrochloric acid (or sulfuric acid) washing and washing, can repeatedly be used to adsorb fluorine ion.
Then, as raw material of wood-charcoal material 37, use the CaCl that wooden bits 2 is immersed in 10 weight %
2The back made its charing in 1 hour 700 ℃ of heating in the solution, carried out impregnation process subsequently in the HCl of 5mol/L solution and the HCl that obtains handles CaCl
2Charcoal is handled CaCl about this HCl
2Charcoal similarly carries out regeneration test and the result is shown with above-mentioned.
The result of above-mentioned regeneration test is that HCl handles CaCl
2The adsorbance of the fluorine ion of charcoal is:
For the first time ... 32.0mg/g
Regeneration for the first time ... 31.5mg/g
Regeneration for the second time ... 31.4mg/g
Regeneration for the third time ... 31.2mg/g.
Can confirm that from above (HCl handles CaCl to the raw material of wood-charcoal material 37 that obtains for carrying out impregnation process after the charing in HCl solution
2Charcoal), after being used to adsorb fluorine ion with dense hydrochloric acid (or sulfuric acid) solution washing, and then the washing, can regenerate.And also can confirm, make HCl handle CaCl repeatedly even carry out hydrochloric acid (or sulfuric acid) to wash and wash
2Charcoal regeneration, the HCl that improves by the impregnation process in HCl solution handles CaCl
2The fluorine ion adsorption capacity of charcoal also can continue (state of raising).
The anion-adsorbing carbon material that the present invention relates to for example can mainly be used in following purposes owing to can adsorb the anion of nitric acid type nitrogen, nitrite type nitrogen, fluorine etc.
(1) sewage disposal with and the underground water scavenging material
For being present in nitric acid type nitrogen component and fluorine ions such as nitrite ion in sewage disposal water and the underground water, nitrate ion, present situation is that its major part is directly discharged under the state of being untreated.Anion-adsorbing carbon material of the present invention can as cheap and effectively sewage disposal with the underground water scavenging material.
In sewage treatment facility and ground water cleaning facility, for example sewage disposal scavenging material swimming in sewage by making suitable size, perhaps be contained in the cylinder mould or netted bag with suitable mesh, be arranged to can with the abundant state of contact of processed water, can positively adsorb anion such as the nitrite ion that is included in the processed water, nitrate ion, fluorine ion.In addition, when anion-adsorbing carbon material of the present invention is made powder shaped, it can be loaded on also that nonwoven is first-class to be used.
(2) use in waste water treatment scavenging material
Be used for adsorbing being included in and store factory, the spinning factory of fiber manufacturing industry, the waste water of bakery and confectionery from chemical plant, petroleum refinement factory, iron and steel and steel manufacturing works, paper mill, semiconductor factory, industrial waste, from the waste water of livestock products facility, also have nitrite ion and nitrate ion in the sanitary wastewater etc.; And be included in plant chimney stalk and in each family, merge the sanitary wastewater of purification tank, local unit, anionic cheap materials such as fluorine ion in the industrial wastewater of electronics industries such as glass, plating, refining of metal, Treatment of Metal Surface, ceramic industry, semiconductor, chemical industry etc., less at present.Anion-adsorbing carbon material of the present invention can be as cheap and effective use in waste water treatment scavenging material.
In the waste water stream that in each family, the waste water stream that merges the sanitary wastewater etc. of purification tank, local unit, waste water treatment tank or from the waste water of livestock products facility or various factories, flows through, the waste water treatment tank, for example sewage disposal scavenging material swimming in waste water by making suitable size, perhaps be contained in the cylinder mould or netted bag with suitable mesh, be arranged to can with the abundant state of contact of processed water, can positively adsorb anion such as the nitrite ion that is included in the processed water, nitrate ion, fluorine ion.In addition, when making powder shaped, it can be loaded on also that nonwoven is first-class to be used.
(3) running water scavenging material
Result from the waste water described in (2) in recent years, the fertilising of tea field, golf course lawn etc., a large amount of uses at the cattle waste in farmland, can see many serious zones of underground water pollution that cause because of nitrite ion, nitrate ion, also comprise rivers and creeks water, when being used as the water source of running water, need from the water of taking, remove nitric acid type nitrogen component.Anion-adsorbing carbon material of the present invention can be as cheap and effective running water scavenging material.
Running water cleaning equipment in the waterworks, rivers and creeks and phreaticly adopt in the wetting system or in the home-use water purifier, for example running water scavenging material swimming in running water by making suitable size, perhaps be contained in the cylinder mould or netted bag with suitable mesh, be arranged to can with the abundant state of contact of processed water, can positively adsorb anion such as the nitrite ion that is included in the processed water, nitrate ion.In addition, when making powder shaped, it can be loaded on also that nonwoven is first-class to be used.
(4) use to agriculture and animal husbandry scavenging material
Result from the fertilising in tea field, in a large amount of uses of the cattle waste of farmland, can see many serious zones of underground water pollution that cause because of nitrite ion, nitrate ion.Anion-adsorbing carbon material of the present invention can be used as cheap and effectively use to agriculture and animal husbandry scavenging material.
In agriculture and animal husbandry ground, for example sneak in the soil of farmland or grazing with scavenging material by the agriculture and animal husbandry ground of the size that will suit, perhaps be embedded in the deep layer in the soil, thereby can adsorb the nitrite ion, the nitrate ion that are derived from excessive fertilization or cattle waste, can reduce nitrite ion, nitrate ion flows into phreatic amount.And then this agriculture and animal husbandry ground also can be effectively as the physically improved material of soil with scavenging material, and the while is because nitrite ion, the nitrate ion of absorption can be by plant utilizations, so also have the function of controlled-release fertilizer.Therefore, the anion-adsorbing carbon material of the present invention that has adsorbed nitrite ion, nitrate ion can be used as soil improvement fertilizer.
(5) tank water and breed pond scavenging material
Raise in the breed pond with tank water, fish or the shrimp of tank (for example the tank in aquarium, industry with or home-use tank) raising biology that aquatic biology or amphibious organisms use, because their excreta, the residue of bait, can generate ammonia, further oxidation and form nitrite ion, nitrate ion, though toxicity can weaken lentamente, but under some concentration, raise biological meeting and produce poisoning symptom.Anion-adsorbing carbon material of the present invention can be as cheap and effective tank water scavenging material.
In tank, culture in the pond or in their water purification installation, for example by making tank water-breed pond scavenging material swimming in processed water of suitable size, perhaps be contained in the cylinder mould or netted bag with suitable mesh, be arranged to can with the abundant state of contact of processed water, can positively adsorb anion such as the nitrite ion that is included in the processed water, nitrate ion.In addition, when forming powder shaped, it is first-class and use also it can be loaded on nonwoven.
The possibility of utilizing on the industry
Therefore anion-adsorbing carbon material of the present invention goes for purification of water quality, prevents the caused pollution of livestock products, prevents that excessive fertilization pollutes in the agricultural use owing to can adsorb nitric acid type nitrogen, nitrite type nitrogen. In addition, because can Adsorption of fluoride, therefore can also be applicable to the final treatment facility of the semiconductor that utilizes hydrofluoric acid to wash, glass, plating factory etc.
Claims (6)
1. the manufacture method of anion-adsorbing carbon material, it is characterized in that, carry out charing after making the solution contact plant material that contains calcium ion, acid solution contacted, thus make carbide in conjunction with on can carry out ion-exchange with absorption object anion anion.
2. the manufacture method of anion-adsorbing carbon material, it is characterized in that, plant material to the solution of contacted calcium ions carries out charing and obtains carbide, makes acid solution contact this carbide again, thus make carbide in conjunction with on can carry out ion-exchange with absorption object anion anion.
3. the manufacture method of anion-adsorbing carbon material, it is characterized in that, make acid solution contact carry out carbide after the charing to the plant material of the solution of contacted calcium ions, thus make carbide in conjunction with on can carry out ion-exchange with absorption object anion anion.
4. anion-adsorbing carbon material, its manufacture method manufacturing by any described anion-adsorbing carbon material in the claim 1~3 forms.
5. anion-adsorbing carbon material, it is formed by following approach: remove the anion of absorption from having adsorbed the described anion-adsorbing carbon material of anionic claim 4, simultaneously, substitute the described absorption be removed anion and in conjunction with the anion that can carry out ion-exchange with absorption object anion subsequently.
6. the manufacturing installation of anion-adsorbing carbon material, this device is to make to make carbide combine the manufacturing installation that can carry out the anionic anion-adsorbing carbon material of ion-exchange with absorption object anion, it is characterized in that device, the butt joint described raw material after touch that this manufacturing installation has the solution that makes plant material contact calcium ions carries out the carbonizing apparatus that is formed by retort of charing and the device that makes the carbide contact acid solution that generates in this carbonizing apparatus.
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US4937223A (en) * | 1988-02-10 | 1990-06-26 | Mitsubishi Kasei Corporation | Process for preparing activated carbon |
US5162286A (en) * | 1989-10-20 | 1992-11-10 | Macdowall James D | Method of producing granular activated carbon |
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US4937223A (en) * | 1988-02-10 | 1990-06-26 | Mitsubishi Kasei Corporation | Process for preparing activated carbon |
CN1040185A (en) * | 1989-04-01 | 1990-03-07 | 张志强 | A kind of method of production of active carbon |
US5162286A (en) * | 1989-10-20 | 1992-11-10 | Macdowall James D | Method of producing granular activated carbon |
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JP昭56-160312A 1981.12.10 |
JP特开2002-88373A 2002.03.27 |
JP特开平6-127912A 1994.05.10 |
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