JPS598175B2 - Manufacturing method of heavy metal ion adsorbent - Google Patents
Manufacturing method of heavy metal ion adsorbentInfo
- Publication number
- JPS598175B2 JPS598175B2 JP51074803A JP7480376A JPS598175B2 JP S598175 B2 JPS598175 B2 JP S598175B2 JP 51074803 A JP51074803 A JP 51074803A JP 7480376 A JP7480376 A JP 7480376A JP S598175 B2 JPS598175 B2 JP S598175B2
- Authority
- JP
- Japan
- Prior art keywords
- titanic acid
- adsorbent
- heavy metal
- metal ion
- uranium
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000003463 adsorbent Substances 0.000 title claims description 39
- 229910001385 heavy metal Inorganic materials 0.000 title claims description 14
- 238000004519 manufacturing process Methods 0.000 title claims description 8
- LLZRNZOLAXHGLL-UHFFFAOYSA-J titanic acid Chemical compound O[Ti](O)(O)O LLZRNZOLAXHGLL-UHFFFAOYSA-J 0.000 claims description 42
- 229920002554 vinyl polymer Polymers 0.000 claims description 12
- DHKHKXVYLBGOIT-UHFFFAOYSA-N acetaldehyde Diethyl Acetal Natural products CCOC(C)OCC DHKHKXVYLBGOIT-UHFFFAOYSA-N 0.000 claims description 11
- 125000002777 acetyl group Chemical class [H]C([H])([H])C(*)=O 0.000 claims description 11
- 239000000463 material Substances 0.000 claims description 8
- 238000001035 drying Methods 0.000 claims description 7
- 239000000057 synthetic resin Substances 0.000 claims description 4
- 229920003002 synthetic resin Polymers 0.000 claims description 4
- 229910052770 Uranium Inorganic materials 0.000 description 20
- JFALSRSLKYAFGM-UHFFFAOYSA-N uranium(0) Chemical compound [U] JFALSRSLKYAFGM-UHFFFAOYSA-N 0.000 description 20
- 239000013535 sea water Substances 0.000 description 14
- 238000000034 method Methods 0.000 description 12
- 239000011148 porous material Substances 0.000 description 11
- 150000002500 ions Chemical class 0.000 description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 9
- 238000001179 sorption measurement Methods 0.000 description 8
- 239000007864 aqueous solution Substances 0.000 description 7
- 238000005470 impregnation Methods 0.000 description 7
- 239000000243 solution Substances 0.000 description 5
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 4
- 229910021645 metal ion Inorganic materials 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- XJDNKRIXUMDJCW-UHFFFAOYSA-J titanium tetrachloride Chemical compound Cl[Ti](Cl)(Cl)Cl XJDNKRIXUMDJCW-UHFFFAOYSA-J 0.000 description 3
- -1 uranium Chemical class 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 208000005156 Dehydration Diseases 0.000 description 2
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 2
- ORTQZVOHEJQUHG-UHFFFAOYSA-L copper(II) chloride Chemical compound Cl[Cu]Cl ORTQZVOHEJQUHG-UHFFFAOYSA-L 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 238000007598 dipping method Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 235000013162 Cocos nucifera Nutrition 0.000 description 1
- 244000060011 Cocos nucifera Species 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 1
- 239000004952 Polyamide Substances 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- 239000004793 Polystyrene Substances 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000013522 chelant Substances 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 239000002826 coolant Substances 0.000 description 1
- 229960003280 cupric chloride Drugs 0.000 description 1
- 239000010408 film Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000003456 ion exchange resin Substances 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 1
- HWSZZLVAJGOAAY-UHFFFAOYSA-L lead(II) chloride Chemical compound Cl[Pb]Cl HWSZZLVAJGOAAY-UHFFFAOYSA-L 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 229920002647 polyamide Polymers 0.000 description 1
- 229920000768 polyamine Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 229920002635 polyurethane Polymers 0.000 description 1
- 239000004814 polyurethane Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
- 150000003608 titanium Chemical class 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- 229910002007 uranyl nitrate Inorganic materials 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
【発明の詳細な説明】
本発明は水中に溶存する重金属イオン特にウランに対し
て高吸着能ならびに耐久性を有する重金属イオン吸着材
の製造方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a heavy metal ion adsorbent having high adsorption capacity and durability for heavy metal ions, particularly uranium, dissolved in water.
従来廃水中に溶存する重金属イオンの吸着材としてイオ
ン交換樹脂或はポリアミン系キレート樹脂等の如き有機
系吸着材が使用されているが該吸着材は天然水特に海水
中に溶存する膨大なウラン資源を採取する吸着能を全《
有していない。Conventionally, organic adsorbents such as ion exchange resins or polyamine chelate resins have been used as adsorbents for heavy metal ions dissolved in wastewater, but these adsorbents are used to absorb the vast uranium resources dissolved in natural water, especially seawater. The total adsorption capacity for collecting
I don't have it.
近時該ウランに対して吸着能を有する無機系吸着材とし
てチタン酸が提案されている。Recently, titanic acid has been proposed as an inorganic adsorbent having the ability to adsorb uranium.
該吸着材は特にウラン吸着能に秀れているが粉末状であ
るチタン酸は海水との接触或は回収処理時に流出して、
実用には供し難く、該吸着材の改良方法として活性炭或
はガラスクールにチタン酸或はチタン塩を均一に溶解し
た水溶液を附着せしめてそのまま或はアンモニア水中で
中和処理した後乾燥を行ないチタン酸を薄膜状に担持せ
しめる方法が提案されているが、チタン酸の担体との接
着力が弱く、又細紛化して脱落し易《、実用上満足しう
るものではない。This adsorbent has a particularly excellent ability to adsorb uranium, but powdered titanic acid leaks out when it comes into contact with seawater or during the recovery process.
It is difficult to put it to practical use, and as a method to improve the adsorbent, titanium can be obtained by applying an aqueous solution of titanic acid or titanium salt uniformly dissolved on activated carbon or glass coolant, and drying it as it is or after neutralizing it in aqueous ammonia. A method has been proposed in which acid is supported in the form of a thin film, but the adhesion to the titanic acid carrier is weak, and the film tends to become fine and fall off, making it unsatisfactory in practice.
本発明者等は斯様な問題点を解消すべく鋭意研究の結果
本発明を完成したものである。The present inventors completed the present invention as a result of intensive research to solve such problems.
本発明の目的は水中に溶存する重金属イオン特に海水中
のウランに対して優れた吸着能を有し、海水中へ脱落及
び流出が極めて少ない耐久性のある重金属イオン吸着材
の製造方法を提供するにある。An object of the present invention is to provide a method for producing a durable heavy metal ion adsorbent that has excellent adsorption ability for heavy metal ions dissolved in water, especially uranium in seawater, and has extremely low dropout and leakage into seawater. It is in.
即ち、本発明はチタン酸のヒドロゾルを、微細空隙を有
する物質に含浸せしめて乾燥を行ないチタン酸を少《と
も10多重量%担持せしめることを特徴とする重金属イ
オン吸着材の製造方法である。That is, the present invention is a method for producing a heavy metal ion adsorbent, which is characterized by impregnating a hydrosol of titanic acid into a substance having fine voids and drying the material to support at least 10% by weight of titanic acid.
本発明に示すチタン酸のヒドロゾルとは粒径が1〜10
0mμ好まし《は10〜50mμのチタン酸を5〜70
重量係好ましくは10〜50重量係含有するヒドロゾル
である。The titanic acid hydrosol shown in the present invention has a particle size of 1 to 10
0 mμ preferably << is 10 to 50 mμ titanic acid 5 to 70
The hydrosol preferably contains 10 to 50% by weight.
粒径が1mμ未満のゾルは製造が困難であり、又100
mμを超えた場合、担体より脱落し易《なるので好まし
くない。It is difficult to produce a sol with a particle size of less than 1 mμ, and
If it exceeds mμ, it is not preferable because it tends to fall off from the carrier.
又ヒドロゾルのチタン酸濃度が5重量係未満の場合前記
担体に少くとも10重量%を担持せしめるには浸漬一乾
燥を繰り返す必要があり又70重量係を超えた場合ヒド
ロゾルの調製が困難となり又粘度も高《前記担体に含浸
した場合微細空隙を閉塞して海水との接触効率ならびに
吸着能を低下さすため前記範囲に従うのが望ましい。Furthermore, if the concentration of titanic acid in the hydrosol is less than 5% by weight, it is necessary to repeat dipping and drying to ensure that the carrier supports at least 10% by weight, and if it exceeds 70% by weight, it becomes difficult to prepare the hydrosol and the viscosity increases. It is desirable to follow the above range because when impregnated into the carrier, the micropores are blocked and the contact efficiency with seawater and adsorption capacity are reduced.
又、本発明に適する微細空隙を有する物質とはポリビニ
ルアセタール.ポリウレタン.ポリ酢eビニル.ポリア
ミド.ポリエチレン.ポリプロピレン.ポリスチレン等
の如き合成樹脂多孔体、特に空隙率が40〜95%を有
する該物質がチタン酸を担持せしめるのに好適である。Further, the material having microscopic voids suitable for the present invention is polyvinyl acetal. Polyurethane. Polyvinegar e-vinyl. polyamide. polyethylene. polypropylene. A porous synthetic resin material such as polystyrene, particularly a material having a porosity of 40 to 95%, is suitable for supporting titanic acid.
該微細空隙を有する物質の中でも特に平均孔径が10μ
〜1mmの連通孔を倚する合成樹脂多孔体は、海水との
接触効率が浸れるため担持せるチタン酸の重金属イオン
の吸着速度が著し《速《、特に海水中のウランを採取す
るための吸着材として好適である。Among the substances having microscopic voids, those having an average pore diameter of 10μ
The synthetic resin porous body with ~1 mm communicating pores has a high contact efficiency with seawater, so the adsorption speed of heavy metal ions of titanic acid that it can support is extremely fast, especially for collecting uranium from seawater. Suitable as an adsorbent.
中でもポリビニルアセタールの発泡体は、チタン酸を強
固に担持し、海水中に長期間浸漬しても脱落は極めて少
な《耐久性の優れた吸着材が得られる。Among these, polyvinyl acetal foam firmly supports titanic acid, and even when immersed in seawater for a long period of time, there is very little shedding (providing a highly durable adsorbent).
前記チタン酸のヒドロゾルの調製並びに微細空隙を有す
る前記担体にチタン酸を担持する方法はチタン酸を前記
範囲に従って酸性水溶液(PH:1.0〜2.5)に均
一に撹拌混合して解膠しヒドロゾルを調製して前記担体
に含浸せしめる。The method for preparing the hydrosol of titanic acid and supporting titanic acid on the carrier having microscopic voids is to uniformly stir and mix titanic acid into an acidic aqueous solution (PH: 1.0 to 2.5) according to the above range, and then peptize the titanic acid. A hydrosol is prepared and impregnated into the carrier.
含浸方法は浸漬のみでは前記担体の微細空隙内部まで含
浸することが困難であり、担体をチタン酸のヒドロゾル
に浸漬して減圧することにより微細空隙の脱気を行なっ
て含浸せしめる方法が有効である。As for the impregnation method, it is difficult to impregnate the inside of the fine pores of the carrier by dipping alone, and an effective method is to immerse the carrier in a hydrosol of titanic acid and depressurize it, thereby deaerating the fine pores and impregnating the carrier. .
担体の該ヒドロゾルの含浸率は、圧搾或は遠心脱水等適
宜な手段により調節することが好ましく、過剰のヒドロ
ゾルを除去すると同時に微細空隙の閉塞を防止するため
に含浸率は100〜1000重量係範囲が好適である。The impregnation rate of the hydrosol in the carrier is preferably adjusted by appropriate means such as compression or centrifugal dehydration, and the impregnation rate is in the range of 100 to 1000 by weight in order to remove excess hydrosol and at the same time prevent clogging of micropores. is suitable.
次にチタン酸のヒドロゾルを含浸した担体は風乾もし《
は100℃以下の温度で乾燥を行ないチタン酸を前記物
質の微細空隙の内部に強固に担持せしめる。Next, the carrier impregnated with titanic acid hydrosol is air-dried.
Drying is carried out at a temperature of 100° C. or less to firmly support titanic acid inside the fine pores of the material.
担持せるチタン酸は少くとも10重量係であり、該範囲
未満の場合、吸着材としての性能が不充分であり実用上
不適当である。The amount of titanic acid that can be supported is at least 10% by weight, and if it is less than this range, the performance as an adsorbent is insufficient and it is not suitable for practical use.
本発明の方法による吸着材は重金属イオン特にウランの
吸着能が浸れ、海水との接触によるチタン酸の流出或は
アルカリ水溶液により該吸着材からウランを回収する処
理工程に於てもチタン酸の脱落はな《、耐久性の優れた
吸着材である。The adsorbent produced by the method of the present invention has a high ability to adsorb heavy metal ions, especially uranium, and the titanic acid will not be removed during the process of recovering uranium from the adsorbent using an alkaline aqueous solution or outflow of titanic acid due to contact with seawater. It is an adsorbent with excellent durability.
又該吸着材は製造及び加工することが容易であり板状.
細片状.円筒状等如回なる形状にも加工することができ
る。In addition, the adsorbent is easy to manufacture and process, and is shaped like a plate.
Strip-like. It can be processed into any shape such as a cylindrical shape.
又該吸着材は工場廃水或は排気処理に適用して重金属イ
オンを除去する等公害防止の面からその利用価1直は極
めて大きいものである。Moreover, the adsorbent has an extremely large utility value in terms of pollution prevention, such as when it is applied to factory wastewater or exhaust treatment to remove heavy metal ions.
以下本発明の方法をさらに詳細に実施例によって説明す
る。The method of the present invention will be explained in more detail below with reference to Examples.
実施例 1
四塩化チタンを含む塩酸溶液にアンモニア水を滴丁して
5〜20゜Cで中和を行ない析出するチタン酸の沈澱を
沢過及び水洗を行なって精製した後塩酸水溶液(PH:
1.5)によりチタン酸を40重量%含有するヒドロゾ
ルを調製した。Example 1 Aqueous ammonia is added dropwise to a hydrochloric acid solution containing titanium tetrachloride, neutralized at 5 to 20°C, and the precipitated titanic acid is purified by filtering and washing with water, followed by an aqueous hydrochloric acid solution (PH:
1.5) A hydrosol containing 40% by weight of titanic acid was prepared.
次に連通孔を有した空隙率90%.平均孔径50μから
なる外径75m+++内径25M.高さ250糎の円筒
状ポリビニルアセタール多孔体を上記ヒドロゾル中に浸
漬して、減圧処理( 8 mmH gL)にまり脱気を
行ない空隙内部まで含浸せしめた後遠心脱水処理を行な
い更に60℃に保温せる通風乾燥器内で乾燥してチタン
酸を70重量係担持した吸着坂Aを得た。Next, the porosity is 90% with communicating holes. Outer diameter 75m+++inner diameter 25M. with average pore diameter 50μ. A cylindrical porous polyvinyl acetal material with a height of 250 mm was immersed in the above hydrosol and degassed under reduced pressure treatment (8 mmH gL) to impregnate the inside of the voids, followed by centrifugal dehydration treatment and further heat retention at 60 ° C. The mixture was dried in a ventilation dryer to obtain an adsorption slope A carrying 70% titanic acid by weight.
又比較対照として上記せる未処理の円筒状ポリビニルア
セタール多孔体をチタン酸重量に換算して40重量係き
有する四塩化チタンを均一に溶解した塩酸水溶液に浸漬
後前記と同様の方法で脱気して含浸せしめた後アンモニ
ア水中に浸漬して中和を行ない次に遠心脱水して更に前
記同様乾燥処理を行なってチタン酸を75重量%担持し
た吸着材Bを得た。As a comparison, the untreated cylindrical polyvinyl acetal porous body described above was immersed in an aqueous hydrochloric acid solution in which titanium tetrachloride, which has a weight of 40% in terms of titanic acid weight, was uniformly dissolved, and then degassed in the same manner as above. After impregnation, the material was immersed in aqueous ammonia for neutralization, then centrifugally dehydrated, and then dried in the same manner as described above to obtain adsorbent B carrying 75% by weight of titanic acid.
該吸着材A,Bは、それぞれ500tに150・確のウ
ランを含有せしめる様、硝酸ウラニルを添加調製した海
水を円筒形吸着材を通過循環しながら20時間海水を接
触させた後吸着材を炭酸ナトリウム水溶液中に浸漬して
ウランを回収した。Adsorbents A and B are made by contacting seawater with uranyl nitrate for 20 hours while circulating it through a cylindrical adsorbent, and then carbonating the adsorbent. Uranium was recovered by immersing it in an aqueous sodium solution.
海水との接触による吸着材からのチタン酸の脱落率及び
吸着材によるウランの回収量を螢光X線分析法により定
量として第1表に示す結果を得た。The drop-off rate of titanic acid from the adsorbent due to contact with seawater and the amount of uranium recovered by the adsorbent were quantitatively determined by fluorescent X-ray analysis, and the results shown in Table 1 were obtained.
上表に示す如《比較例の吸着材Bはチタン酸の脱落は著
し《、又ウランの回収量も少なく本発明方法による吸着
剤Aはチタン酸を強固に担持して脱落は極めて微量であ
り又ウランの吸着能も非常に優れている。As shown in the table above, the adsorbent B of the comparative example shows a significant amount of titanic acid falling off, and the amount of uranium recovered is small. It also has an excellent ability to adsorb uranium.
実施例 2
実施例1に示すチタン酸のヒドロゾルを使用して平均孔
径100μの連通孔を有する空隙率92%巾1 0 0
mm,長さ200問、厚さ2tranのシート状ポリビ
ニールアセタール多孔体を使用して同様に含浸処理を行
ない絞りロールにより含浸率を種種に変化せしめて常温
乾燥を行ないチタン酸の担−持量を種々変化せしめた吸
着材を得た。Example 2 The titanic acid hydrosol shown in Example 1 was used to create a porosity of 92% width 100 having communicating pores with an average pore diameter of 100μ.
Using a sheet-like polyvinyl acetal porous material with a length of 200 mm and a thickness of 2 tran, impregnation treatment was performed in the same manner, the impregnation rate was varied in various ways using a squeezing roll, and the amount of titanic acid carried was determined by drying at room temperature. Adsorbents with various changes were obtained.
又、比較対照として上記未処理のシート状ポリビニルア
セタールを実施例1に示す四塩化チタンの塩酸水溶液を
使用して同様に含浸せしめた後アンモニア水中に浸漬し
て中和を行ない上記と同様の方法で含浸率を変化せしめ
て乾燥を行ないチタン酸の担持量を変化せしめた吸着材
を得た。In addition, as a comparison, the untreated sheet-like polyvinyl acetal was similarly impregnated using the hydrochloric acid aqueous solution of titanium tetrachloride shown in Example 1, and then neutralized by immersing it in aqueous ammonia in the same manner as above. By changing the impregnation rate and drying, adsorbents with varying amounts of titanic acid supported were obtained.
該吸着材は夫々ウラン1.2■を含む海水4t中で1日
間攪拌浸漬することによりウランを吸着せしめて実施例
1と同様に定計を行ない又吸着材から脱落するチタン酸
を定量して第2表に示す結果を得た。Each of the adsorbents was stirred and immersed in 4 tons of seawater containing 1.2 cm of uranium for one day to adsorb uranium, and measurements were carried out in the same manner as in Example 1. Also, titanic acid falling off from the adsorbents was determined. The results shown in Table 2 were obtained.
上表より明らかな如くチタン酸の担持量は少な《とも1
0重量係が必要であり、又本発明方法により吸着材から
のチタン酸の脱落率は非常に小さいものである。As is clear from the table above, the amount of titanic acid supported is small (at least 1
0 weight coefficient is required, and the rate of dropping of titanic acid from the adsorbent by the method of the present invention is extremely small.
実施例 3
実施例2に示すチタン酸を150重量係担持せるシ一ト
状ポリビニルアセタール多孔体の吸着材を塩化第2銅.
塩化第2鉄.二塩化鉛.無水クロム酸を各々金属イオン
として10ppm含有する3tの水溶液中に浸漬して5
時間撹拌を行なった後、該吸着材をIN−塩酸水溶液中
に60℃の温度で30分間浸漬して吸着した金属イオン
を脱着して溶出せしめ水溶液中の金属イオンの定量を行
なって第3表に示す結果を得た。Example 3 The sheet-shaped porous polyvinyl acetal adsorbent that can support 150% titanic acid by weight as shown in Example 2 was used as an adsorbent with cupric chloride.
Ferric chloride. Lead dichloride. Chromic anhydride was immersed in 3 tons of aqueous solution containing 10 ppm of each metal ion.
After stirring for a period of time, the adsorbent was immersed in an IN-hydrochloric acid aqueous solution at a temperature of 60°C for 30 minutes to desorb and elute the adsorbed metal ions, and the metal ions in the aqueous solution were quantified. The results shown are obtained.
上表に示す如《本発明方法による吸着材は重金属イオン
に対して優れた吸着能を示し、廃水処理に好適である。As shown in the above table, the adsorbent produced by the method of the present invention exhibits excellent adsorption ability for heavy metal ions and is suitable for wastewater treatment.
実施例 4
実施例1に準じた方法にて、チタン酸を70重量%担持
した乎均孔径50μを有するポリビニルアセタール多孔
体( 1 0 0mmX 2 0 0mmX 2rrr
m )A及びチタン酸を50重量係担持したヤシガラ活
性炭8f(20〜35メッシュ)Bを調製した。Example 4 A polyvinyl acetal porous body (100 mm x 200 mm x 2rr
m) Coconut shell activated carbon 8f (20 to 35 mesh) B carrying 50 weight of A and titanic acid was prepared.
該吸着材をウラン15TII!を含有する海水500t
中に浸漬し、実施列2に同様に1日間撹拌してウランを
吸着せしめた後実施例1に示す方法に従ってウランの定
量及び脱落チタン酸の分析を行ない第4表に示す結果を
得た。The adsorbent is uranium 15TII! 500 tons of seawater containing
After stirring for 1 day in the same manner as in Example 2 to adsorb uranium, uranium was quantified and titanic acid was analyzed according to the method shown in Example 1, and the results shown in Table 4 were obtained.
上表に示す如《、平均50μの比較的マクロな孔径を有
するポリビニルアセタール多孔体は、チタン酸の担持が
強固で脱落が少なく、耐久性に優れており、又ミクロな
孔径を有するヤシガラ活性炭と比較して、希薄なウラン
溶液中からのウラン吸着速度が著るし《速い。As shown in the table above, the polyvinyl acetal porous material, which has a relatively macroscopic pore size of 50μ on average, has strong titanic acid support, less shedding, and excellent durability. In comparison, the rate of uranium adsorption from a dilute uranium solution is remarkable and fast.
該結果より天然海水中に極めて希薄な濃度で溶存してい
るウランを採取する吸着材として特にポリビニルアセタ
ールが優れていることがわかる。These results show that polyvinyl acetal is particularly excellent as an adsorbent for collecting uranium dissolved in extremely dilute concentrations in natural seawater.
Claims (1)
多孔体に含浸せしめて乾燥を行ないチタン酸を少《とも
10重量係担持せしめることを特徴とする重金属イオン
吸着材の製造方法。 2 ヒドロゾルがチタン酸を5〜70重量係含有するも
のである特許請求の範囲第1項記載の重金属イオン吸着
材の製造方法。 3 合成樹脂多孔体がポリビニルアセタールである特許
請求の範囲第1項記載の重金属イオン吸着材の製造方法
。[Claims] 1. A method for producing a heavy metal ion adsorbent, which comprises impregnating a hydrosol of titanic acid into a synthetic resin porous body having fine voids and drying the resulting material so that at least 10% of titanic acid is supported by weight. . 2. The method for producing a heavy metal ion adsorbent according to claim 1, wherein the hydrosol contains titanic acid in an amount of 5 to 70% by weight. 3. The method for producing a heavy metal ion adsorbent according to claim 1, wherein the synthetic resin porous body is polyvinyl acetal.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51074803A JPS598175B2 (en) | 1976-06-23 | 1976-06-23 | Manufacturing method of heavy metal ion adsorbent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51074803A JPS598175B2 (en) | 1976-06-23 | 1976-06-23 | Manufacturing method of heavy metal ion adsorbent |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS52156793A JPS52156793A (en) | 1977-12-27 |
| JPS598175B2 true JPS598175B2 (en) | 1984-02-23 |
Family
ID=13557822
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51074803A Expired JPS598175B2 (en) | 1976-06-23 | 1976-06-23 | Manufacturing method of heavy metal ion adsorbent |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS598175B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110205490B (en) * | 2019-05-22 | 2020-10-02 | 浙江大学 | A method of separating uranium and iron |
-
1976
- 1976-06-23 JP JP51074803A patent/JPS598175B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS52156793A (en) | 1977-12-27 |
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