JPH0975717A - Method for removing arsenate ion - Google Patents

Method for removing arsenate ion

Info

Publication number
JPH0975717A
JPH0975717A JP22937195A JP22937195A JPH0975717A JP H0975717 A JPH0975717 A JP H0975717A JP 22937195 A JP22937195 A JP 22937195A JP 22937195 A JP22937195 A JP 22937195A JP H0975717 A JPH0975717 A JP H0975717A
Authority
JP
Japan
Prior art keywords
water
activated alumina
adsorbent
alumina
arsenate ions
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.)
Granted
Application number
JP22937195A
Other languages
Japanese (ja)
Other versions
JP3291994B2 (en
Inventor
Seiichi Hamano
誠一 浜野
Osamu Yamanishi
修 山西
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sumitomo Chemical Co Ltd
Original Assignee
Sumitomo Chemical Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Sumitomo Chemical Co Ltd filed Critical Sumitomo Chemical Co Ltd
Priority to JP22937195A priority Critical patent/JP3291994B2/en
Publication of JPH0975717A publication Critical patent/JPH0975717A/en
Application granted granted Critical
Publication of JP3291994B2 publication Critical patent/JP3291994B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Removal Of Specific Substances (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To allow spherical activated alumina having a specified Na2 O content and a specified wear rate to satisfy all of cost, handleability and treating effect as an adsorbent by bringing an adsorbent made of the alumina into contact with water contg. arsenate ions and removing the arsenate ions from the water. SOLUTION: Aluminum hydroxide such as gibbsite is calcined for 0.1sec to several min in a flow of hot air at 500-1,200 deg.C, the calcined body is separated and cooled and the resultant activated alumina powder having rehydratability is pulverized and compacted in a sphere shape to obtain spherical activated alumina having <=0.3wt.% Na2 O content and <=1% wear rate. An adsorbent made of the alumina is brought into contact with water contg. arsenate ions and the arsenate ions are removed from the water. The alumina can satisfy all of cost, handleability and treating effect as an adsorbent.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、水中からのヒ酸イ
オン除去方法に関する。より詳細にはヒ酸イオンを含有
する工場排水、家庭排水、工業用水、水道用水等よりヒ
酸イオンを吸着除去する方法に関するものである。
TECHNICAL FIELD The present invention relates to a method for removing arsenate ions from water. More specifically, the present invention relates to a method for adsorbing and removing arsenate ions from factory wastewater, domestic wastewater, industrial water, tap water, etc., containing arsenate ions.

【0002】[0002]

【従来の技術】近年、各種の化学形態のヒ酸イオンを含
有する浄水中、あるいは排水中よりヒ素濃度を高度に低
減すべく、凝集沈殿法、石灰軟化法、吸着法、生物濃縮
法、逆浸透法などの種々の方法が検討されている。この
うち吸着法は、広い処理場面積を要しないこと、廃泥等
を発生せず、面倒な濾過操作がないことから、特に中小
規模の施設においては有利であると考えられる。該吸着
法に用いる吸着剤としては活性炭、活性アルミナ、マグ
ネシア、マグネシア修飾スラグ、チタニア修飾活性炭、
陰イオン交換樹脂、赤泥粒等が知られているが、就中、
活性アルミナが安価で安全な吸着剤として適用されてい
る。
2. Description of the Related Art In recent years, in order to reduce the arsenic concentration to a higher degree than in purified water containing various chemical forms of arsenate ions or in waste water, a flocculation-precipitation method, a lime softening method, an adsorption method, a bio-concentration method, a reverse method. Various methods such as the penetration method have been studied. Of these, the adsorption method is considered to be particularly advantageous in small and medium-scale facilities because it does not require a large treatment plant area, does not generate waste sludge, and does not require a troublesome filtration operation. As the adsorbent used in the adsorption method, activated carbon, activated alumina, magnesia, magnesia modified slag, titania modified activated carbon,
Anion exchange resin, red mud particles, etc. are known, but above all,
Activated alumina is applied as an inexpensive and safe adsorbent.

【0003】ヒ酸の吸着に活性アルミナを用いた例とし
ては Environmental Progress 誌第6巻第3号第150
頁に記載の M.M.Ghosh氏およびJ.R.Yuan氏の論文があ
る。該論文においては、Na2 O含有量が0.9重量
%、BET表面積が218m2 /gで粒径が28〜48
メッシュの破砕状活性アルミナ塊状物をカラムに充填
し、これに低濃度のヒ酸イオンを含有した水を通水し、
ヒ酸を吸着除去する方法が開示されている。
As an example of using activated alumina for adsorbing arsenic acid, Environmental Progress magazine Vol. 6, No. 3, 150
There is a paper by MMGhosh and JRYuan on the page. In this paper, the Na 2 O content is 0.9% by weight, the BET surface area is 218 m 2 / g, and the particle size is 28 to 48.
The crushed activated alumina lumps of mesh were packed in a column, and water containing low concentration of arsenate ions was passed through the column,
A method for adsorbing and removing arsenic acid is disclosed.

【0004】[0004]

【発明が解決しようとする課題】しかし吸着剤として破
砕状活性アルミナをそのままカラムに充填し用いる場合
には、通水後の水が白濁するため、充填前に該活性アル
ミナを懸濁洗浄しダストを除去しなければならず、作業
が煩雑となるばかりか、白濁洗浄水の処理が必要とな
る。また吸着剤として活性アルミナ単独で吸着能力が不
足する場合に被処理水のpHを制御する併用方法が教示
されているがこの場合には水処理コストが高くなる。他
方、活性アルミナ以外の吸着剤の適用も紹介されてはい
るが、高価であったり、吸着剤自身から好ましくない成
分が漏出する等、吸着剤として価格、取扱性、処理効果
を全て満足し得るものは未だ見られない。かかる状況下
に鑑み,本発明者らは簡便かつ廉価で効率的な水中から
のヒ酸イオン除去方法を見いだすことを目的として鋭意
研究を重ねた結果,本発明を完成するに到った.
However, when crushed activated alumina as an adsorbent is directly packed in a column and used, since water after passing water becomes cloudy, the activated alumina is suspended and washed before packing. Must be removed, which not only complicates the work, but also requires treatment of the cloudy cleaning water. Further, a combined method of controlling the pH of the water to be treated has been taught when activated alumina alone as an adsorbent is insufficient in adsorption capacity, but in this case, the cost of water treatment becomes high. On the other hand, although the application of adsorbents other than activated alumina has been introduced, it is possible to satisfy all of the price, handleability, and treatment effects as an adsorbent, such as being expensive and leaking undesired components from the adsorbent itself. I haven't seen anything yet. In view of such circumstances, the present inventors have conducted intensive studies to find a simple, inexpensive, and efficient method for removing arsenate ions from water, and as a result, completed the present invention.

【0005】[0005]

【課題を解決するための手段】本発明の第1は、Na2
O含有量が0.3%以下で、かつ磨耗率が1%以下の球
状活性アルミナよりなる吸着剤を、ヒ酸イオンを含む水
と接触させ該水中よりヒ酸イオンを吸着除去することを
特徴とする水中のヒ酸イオンの除去方法を提供するにあ
る。また本発明の第2は、酸成分を被着させて成る、8
0℃の水に浸積したときの水のpHが3ないし6の値を
呈する請求項1の活性アルミナを、ヒ酸イオンを含む水
と接触させ該水中よりヒ酸イオンを吸着除去することを
特徴とする水中のヒ酸イオン除去方法を提供するにあ
る。
The first aspect of the present invention relates to Na 2
An adsorbent made of spherical activated alumina having an O content of 0.3% or less and a wear rate of 1% or less is brought into contact with water containing arsenate ions to adsorb and remove arsenate ions from the water. The present invention provides a method for removing arsenate ions in water. A second aspect of the present invention comprises depositing an acid component, 8
The activated alumina of claim 1 having a pH value of 3 to 6 when immersed in water at 0 ° C. is brought into contact with water containing arsenate ions to adsorb and remove arsenate ions from the water. It is to provide a characteristic method for removing arsenate ion in water.

【0006】[0006]

【発明の実施の形態】以下、本発明を詳細に説明する。
本発明方法の実施に際し、ヒ酸イオンの吸着に使用する
吸着剤は、Na2 O含有量が約0.3重量%以下、好ま
しくは約0.2重量%以下、より好ましくは約0.1重
量%以下で、かつ耐粉化性の指標である磨耗率が約1%
以下、好ましくは約0.8%以下の球状活性アルミナで
あることを必須とする。磨耗率が約1%を越える場合、
またその形状が粉状や破砕により得た塊状品は、吸着処
理後の水に濁りが発生し、フィルターつまりや粉発生が
しやすいので好ましくない。また、活性アルミナ中のN
2 O(全ソーダ)量が約0.3重量%を越えると活性
アルミナ周囲の水中のpHが上昇し、ヒ酸イオンの吸着
が阻害される。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below.
In carrying out the method of the present invention, the adsorbent used for adsorbing arsenate ions has a Na 2 O content of about 0.3% by weight or less, preferably about 0.2% by weight or less, more preferably about 0.1% by weight or less. Abrasion rate of less than 1% by weight, which is an index of dust resistance, is about 1%
In the following, it is essential that the spherical activated alumina is preferably 0.8% or less. If the wear rate exceeds about 1%,
In addition, a powdery product or a lump product obtained by crushing is not preferable because turbidity occurs in water after the adsorption treatment and a filter is easily clogged or powder is generated. In addition, N in activated alumina
If the amount of a 2 O (total soda) exceeds about 0.3% by weight, the pH of the water around the activated alumina rises and the adsorption of arsenate ions is hindered.

【0007】水中に含有されるヒ酸イオンの吸着剤とし
ては上記低Na2 O含量、耐粉化性に優れる球状活性ア
ルミナを用ることにより、かなり優れた効果を挙げるこ
とができるが、より優れたヒ酸イオンの吸着効果を付与
せしめる方法として、上記物性を有する球状活性アルミ
ナに特定量の酸成分、即ち「80℃の水100mlに酸
処理後の吸着剤10gを30分保持し、その後該水中よ
り吸着剤を濾過・分離した場合、該水のpHが3〜6の
値を呈する量」を被着・含浸させて成る球状活性アルミ
ナを吸着剤として用いる除去法が推奨される。該方法に
おいて酸成分の被着・含浸量が多く、上記処理による処
理水のpHが3未満となる場合にはヒ酸の吸着効果が低
下すると伴に、処理後の水の中和処理剤が多量必要とな
るので好ましくない。他方pHが6を越える場合には、
酸性分被着処理を行わない場合に較べてヒ酸の吸着向上
が殆ど見られない。
As the adsorbent for arsenate ions contained in water, the use of spherical activated alumina having a low Na 2 O content and an excellent resistance to pulverization gives a considerably excellent effect. As a method of imparting an excellent arsenate ion adsorption effect, a spherical activated alumina having the above-mentioned physical properties is added with a specific amount of an acid component, that is, "10 g of the adsorbent after acid treatment is retained in 100 ml of water at 80 ° C for 30 minutes, and When the adsorbent is filtered and separated from the water, a removal method using a spherical activated alumina as an adsorbent, which is formed by depositing and impregnating "amount in which the pH of the water exhibits a value of 3 to 6" is recommended. In this method, when the amount of the acid component deposited / impregnated is large and the pH of the treated water by the above treatment is less than 3, the effect of adsorbing arsenic acid decreases, and at the same time, a neutralizing agent for the treated water is added. A large amount is required, which is not preferable. On the other hand, if the pH exceeds 6,
There is almost no improvement in the adsorption of arsenic acid as compared with the case where the acid component deposition treatment is not performed.

【0008】本発明でいう活性アルミナとは、当該分野
で通常呼称される公知のものであればよく、所謂αアル
ミナ以外のアルミニウム酸化物(遷移アルミナ)をい
う。本発明方法において、磨耗率が1%以下の球状活性
アルミナの製法は、とくに限定されないが、再水和性ア
ルミナを経由する方法が大きいBET表面積と強度を持
つ吸着剤が得易いことから推奨される。すなわち、ギブ
サイト等の水酸化アルミニウムを500〜1200℃の
熱風気流中で0.1秒〜数分瞬間仮焼し、次いで分離・
冷却することで再水和性を有する活性アルミナ粉末(以
下、再水和性アルミナと呼ぶ)が得られる。この再水和
性アルミナをそのままで、或いは粉砕後、球状に成形す
る。 得られた成形体は次いで成形体自体の機械的強度
を高めるために再水和に足る時間、室温〜120℃、好
ましくは50〜90℃の水、水蒸気または水蒸気含有ガ
ス中で保持・熟成され再水和される。再水和は一般に1
分ないし1週間行われる。再水和された成形体は続いて
焼成し、成形体中の付着水分及び結晶水を除く。焼成温
度は通常300〜900℃、好ましくは300〜500
℃であり、焼成時間は約10分〜約100時間である。
球状活性アルミナに含有される全Na2 Oを0.3重量
%にするには、公知の方法であればよく、特に制限され
ないが簡単には原料である水酸化アルミニウムとして全
Na2 O含量が0.3重量%以下のもの、より好ましく
は0.1重量%のものを用いればよい。但し、球状活性
アルミナに酸成分を被着・含浸せしめる処理を行う場合
には、原料である水酸化アルミニウム中の全Na2 O含
量は高くてもよく、酸処理後の球状活性アルミナ中に含
有される全Na2 O含量が0.3重量%以下であればよ
い。
The activated alumina referred to in the present invention may be any known one commonly referred to in the art, and is an aluminum oxide (transition alumina) other than so-called α-alumina. In the method of the present invention, the method for producing the spherical activated alumina having a wear rate of 1% or less is not particularly limited, but it is recommended that the method via rehydratable alumina is easy to obtain an adsorbent having a large BET surface area and strength. It That is, aluminum hydroxide such as gibbsite is instantaneously calcined in a hot air stream at 500 to 1200 ° C. for 0.1 seconds to several minutes, and then separated and separated.
By cooling, activated alumina powder having rehydration properties (hereinafter referred to as rehydration alumina) is obtained. This rehydratable alumina is formed into a spherical shape as it is or after pulverization. The obtained molded product is then held and aged in water, steam or a steam-containing gas at room temperature to 120 ° C., preferably 50 to 90 ° C. for a time sufficient for rehydration in order to increase the mechanical strength of the molded product itself. Rehydrated. Rehydration is generally 1
Minutes to a week. The rehydrated molded body is subsequently fired to remove the attached water and crystal water in the molded body. The firing temperature is usually 300 to 900 ° C., preferably 300 to 500.
C. and the firing time is about 10 minutes to about 100 hours.
A known method may be used to set the total Na 2 O contained in the spherical activated alumina to 0.3% by weight, and there is no particular limitation, but it is easy to obtain the total Na 2 O content as aluminum hydroxide as a raw material. It may be 0.3 wt% or less, more preferably 0.1 wt%. However, when the spherical activated alumina is subjected to a treatment for depositing / impregnating it with an acid component, the total content of Na 2 O in the starting aluminum hydroxide may be high, and it may be contained in the spherical activated alumina after the acid treatment. The total Na 2 O content may be 0.3% by weight or less.

【0009】活性アルミナへの酸成分の被着は、酸成分
被着後の活性アルミナを、80℃の水100mlに吸着
剤10gを30分保持した後、該水中より吸着剤を濾過
・分離した後の水のpHが3ないし6の値を呈する量で
被着せしめればよく、その被着方法としてはとくに制限
されないが、例えば(1)磨耗率が1%以下の球状活性
アルミナを酸成分を含有する水溶液と接触して得る。
(2)再水和性アルミナ粉末を水溶液と接触、成形し、
熟成して成形体強度を付与した後、該成形体に酸成分を
含有する水溶液を接触させ次いで焼成して得る、等の方
法が採用できる。
To deposit the acid component on the activated alumina, 10 g of the adsorbent was held in 100 ml of water at 80 ° C. for 30 minutes, and the adsorbent was filtered and separated from the water. The subsequent water may be applied in such an amount that the pH of the water exhibits a value of 3 to 6, and the application method is not particularly limited. For example, (1) spherical activated alumina having an abrasion rate of 1% or less is used as an acid component. It is obtained by contact with an aqueous solution containing.
(2) Rehydrated alumina powder is contacted with an aqueous solution and molded,
After aging to impart strength to the molded body, the molded body may be brought into contact with an aqueous solution containing an acid component and then baked to obtain a method.

【0010】活性アルミナと酸性分含有水溶液の接触法
としては、活性アルミナを水溶液に含浸する、活性アル
ミナの吸水率分の水溶液を供給吸液させる等の方法があ
る。酸成分と接触後、水洗、濾過、乾燥あるいは焼成を
行っても良い。水洗、濾過を行うと活性アルミナ中のN
2 Oが減少するので好都合である。製法(1)の場
合、湿潤状態のまま吸着装置に充填して使用してもよ
い。
As a method for contacting the activated alumina with the acidic component-containing aqueous solution, there are a method of impregnating the activated alumina with the aqueous solution, a method of supplying and absorbing an aqueous solution having a water absorption rate of the activated alumina, and the like. After contact with the acid component, it may be washed with water, filtered, dried or calcined. After washing with water and filtration, N in activated alumina
It is advantageous because it reduces a 2 O. In the case of the production method (1), the adsorbing device may be filled in the wet state and used.

【0011】酸成分としては塩酸、フッ酸,硝酸、硫
酸、酢酸の少なくとも1種が適当である。酸成分を含有
する水溶液の酸成分の濃度は、通常、0.001N〜
0.5Nであるが、厳密には酸の種類、酸成分と活性ア
ルミナの重量比によって異なるので、80℃の水100
mlに吸着剤10gを30分保持した後、該水中より吸
着剤を濾過・分離した後の水のpHが3ないし6にする
ための条件を予備実験により決める必要がある。水溶液
の温度は約0〜100℃、接触時間は約1分以上、好ま
しくは常温〜80℃、接触時間は約10分〜24時間で
あればよい。
As the acid component, at least one of hydrochloric acid, hydrofluoric acid, nitric acid, sulfuric acid and acetic acid is suitable. The concentration of the acid component of the aqueous solution containing the acid component is usually 0.001N to
Although it is 0.5 N, strictly speaking, it depends on the type of acid and the weight ratio of the acid component and activated alumina.
After holding 10 g of the adsorbent in 30 ml for 30 minutes, the conditions for adjusting the pH of the water after filtering and separating the adsorbent from the water to 3 to 6 need to be determined by a preliminary experiment. The temperature of the aqueous solution may be about 0 to 100 ° C., the contact time may be about 1 minute or longer, preferably room temperature to 80 ° C., and the contact time may be about 10 minutes to 24 hours.

【0012】活性アルミナのBET表面積は、100m
2 /g以上、好ましくは200m2/g以上が好まし
い。吸着剤の形状は、粒径が小さい方が吸着速度は速い
が、通液抵抗が増加するので、粒径は約0.5〜約10
mmが適当である。
The BET surface area of activated alumina is 100 m
2 / g or more, preferably 200 m 2 / g or more. As for the shape of the adsorbent, the smaller the particle size, the faster the adsorption rate, but the liquid resistance increases, so the particle size is about 0.5 to about 10.
mm is suitable.

【0013】本発明の吸着剤のヒ酸イオンの平衡吸着量
は、平衡濃度0.1mg/lで約2mg−As/g以
上、好ましくは約5mg−As/g以上である。充填密
度は0.4〜1.0kg/l、耐圧強度は通常2kg以
上、細孔容積は0.3〜1.0cm3 /gである.本発
明の吸着剤に、ヒ酸浄化性能が低減しない範囲で他の機
能を持つ吸着剤や濾過剤を添加することができる。
The equilibrium adsorption amount of arsenate ion of the adsorbent of the present invention is about 2 mg-As / g or more, preferably about 5 mg-As / g or more at an equilibrium concentration of 0.1 mg / l. The packing density is 0.4 to 1.0 kg / l, the compressive strength is usually 2 kg or more, and the pore volume is 0.3 to 1.0 cm 3 / g. To the adsorbent of the present invention, an adsorbent or a filtering agent having another function can be added as long as the arsenic acid purification performance is not reduced.

【0014】本発明で得られた吸着剤は河川、湖あるい
は井戸水等の原料水浄化、各種産業排水等に適用でき
る。使用にあたっては、固定床、移動床、流動床、バッ
チ式等の形で被処理水の吸着浄化が行われる。通液速度
はSV値で約1〜100hr-1が適当である。バッチ式
の場合、1〜100時間の接触時間が適当である。被処
理水が亜ヒ酸イオンを含有する場合には、該被処理水
を、予め酸化処理しヒ酸イオンの形態にした後、吸着処
理を行えば良い。
The adsorbent obtained by the present invention can be applied to purification of raw water such as river, lake or well water and various industrial wastewater. Upon use, the treated water is adsorbed and purified in a fixed bed, moving bed, fluidized bed, batch type or the like. An appropriate SV value for the liquid passage rate is about 1 to 100 hr −1 . In the case of a batch method, a contact time of 1 to 100 hours is suitable. When the water to be treated contains arsenite ions, the water to be treated may be previously subjected to an oxidation treatment to be in the form of arsenate ions and then subjected to an adsorption treatment.

【0015】[0015]

【発明の効果】以上詳述したように、本発明は、Na2
O含有量が0.3重量%以下で、かつ磨耗率が1%以下
の球状活性アルミナよりなる吸着剤を、ヒ酸イオンを含
む水と接触させ該水中よりヒ酸イオンを吸着除去するこ
とを特徴とする水中のヒ酸イオンの除去方法、とくには
酸成分を被着させて成る、80℃の水に浸積したときの
水のpHが3ないし6の値を呈する活性アルミナを、ヒ
酸イオンを含む水と接触させ該水中よりヒ酸イオンを吸
着除去することを特徴とする請求項1記載の水中のヒ酸
イオンの除去方法を提供するものであり、かかる方法に
より従来法に比較し廉価かつ簡便な方法で高度なヒ酸イ
オン吸着除去効果を可能としたもので、その産業的価値
は頗る大である。
As described above in detail, according to the present invention, Na 2
The adsorbent made of spherical activated alumina having an O content of 0.3% by weight or less and a wear rate of 1% or less is brought into contact with water containing arsenate ions to adsorb and remove arsenate ions from the water. A method for removing arsenate ions in water, which is characterized in that activated alumina having a pH value of 3 to 6 when immersed in water at 80 ° C. formed by applying an acid component is treated with arsenic acid. A method for removing arsenate ions in water according to claim 1, which comprises contacting with water containing ions to adsorb and remove arsenate ions from the water. It is an inexpensive and simple method that enables a high degree of arsenate ion adsorption removal effect, and its industrial value is enormous.

【0016】[0016]

【実施例】以下、本発明を実施例を用いて、さらに詳細
に説明するが、本発明はかかる実施例によりその範囲を
制限されるものではない。なお、本発明に於いて、pH
値の測定、Asの分析、磨耗率の測定は下記の方法によ
った。
EXAMPLES Hereinafter, the present invention will be described in more detail with reference to examples, but the scope of the present invention is not limited by these examples. Incidentally, in the present invention, the pH
The following methods were used to measure values, analyze As, and measure wear rate.

【0017】pH値:測定試料10gを80℃の水10
0ml中に30分保持し、濾過し、冷却後の濾液のpH
を堀場製作所F8型、pHメーターにより測定した。 As分析:JIS−K0102により測定した。 磨耗率:JIS−K1464に準じて測定した。
PH value: 10 g of a measurement sample was added to 10 g of water at 80 ° C.
Hold in 0 ml for 30 minutes, filter, pH of filtrate after cooling
Was measured with a Horiba Mfg. Model F8, pH meter. As analysis: Measured according to JIS-K0102. Abrasion rate: Measured according to JIS-K1464.

【0018】実施例1 〔浄化剤の製法〕バイヤー工程から得られたギブサイト
(アルミナ三水和物)を約700℃の熱ガス中に投入し
瞬間仮焼し、灼熱原料は5%,平均粒子径15μの主と
してχおよびρの結晶形態よりなる再水和性アルミナを
得た。このようにして得られた再水和性アルミナ1kg
に対し水約0.5kgを加え、皿型造粒機で直径1〜2
mmの球状に成形した後,該成形体を蓋付容器に入れ密
閉して80℃の温度で16時間保持して再水和せしめ
た.この成形体を電気炉に入れ1時間で380℃まで昇
温し3時間保持し,活性アルミナAを得た.活性アルミ
ナ成形体AのNa2 O含有量は0.25%、充填密度は
0.75kg/l、磨耗率は0.1%、耐圧強度は6k
g、BET表面積は303m2 /g、細孔容積は0.4
2cm3 /g、pHは9.8であった.
Example 1 [Manufacturing Method of Purifying Agent] Gibbsite (alumina trihydrate) obtained from the Bayer process was put into a hot gas at about 700 ° C. and instantaneously calcined, and 5% of the caustic raw material had an average particle size. A rehydratable alumina consisting mainly of crystalline forms of χ and ρ with a diameter of 15μ was obtained. 1 kg of rehydratable alumina thus obtained
About 0.5 kg of water is added to the above, and the diameter is 1-2 with a plate type granulator.
After being molded into a spherical shape of mm, the molded body was placed in a container with a lid, sealed, and kept at a temperature of 80 ° C. for 16 hours for rehydration. This molded body was placed in an electric furnace, heated to 380 ° C. for 1 hour and held for 3 hours to obtain activated alumina A. The activated alumina compact A has a Na 2 O content of 0.25%, a packing density of 0.75 kg / l, an abrasion rate of 0.1%, and a pressure resistance of 6 k.
g, BET surface area is 303 m 2 / g, pore volume is 0.4
2 cm 3 / g, pH was 9.8.

【0019】ついで活性アルミナAの成形体1.2kg
を0.3%塩酸溶液4.3リットル中に16時間含浸
し、水洗・濾過した後、電気炉に入れ250℃で4時間
保持し活性アルミナBを得た。 活性アルミナ成形体B
のNa2 O含有量は0.06%、充填密度は0.76k
g/l、磨耗率は0.1%、 耐圧強度は4kg、BE
T表面積は312m2 /g、細孔容積は0.38cm3
/g、pHは4.0であった。
Next, 1.2 kg of a molded body of activated alumina A
Was impregnated in 4.3 liters of a 0.3% hydrochloric acid solution for 16 hours, washed with water, filtered, placed in an electric furnace and kept at 250 ° C. for 4 hours to obtain activated alumina B. Activated alumina compact B
Content of Na 2 O is 0.06%, the packing density is 0.76k
g / l, wear rate 0.1%, compressive strength 4 kg, BE
T surface area is 312 m 2 / g, pore volume is 0.38 cm 3
/ G, pH was 4.0.

【0020】〔除去テスト〕As換算2.4mg/lの
Na2 HAsO4 水溶液を作成し、被処理液サンプルと
した。この液0.5リットルを三角フラスコに入れ、上
記実施例で得られた成形体約0.2gを吸着剤として添
加し、シェーカーにより7日間、30℃で撹拌し吸着処
理を行った。処理後の液中のAs濃度を調べた結果活性
アルミナA、Bとも検出下限(0.005mg/l)以
下であった。
[Removal test] A 2.4 mg / l As 2 Na 2 HAsO 4 aqueous solution was prepared and used as a sample to be treated. 0.5 liter of this solution was placed in an Erlenmeyer flask, and about 0.2 g of the molded body obtained in the above Example was added as an adsorbent, and the mixture was stirred by a shaker at 30 ° C. for 7 days for adsorption treatment. As a result of examining the As concentration in the liquid after the treatment, the activated aluminas A and B were both below the detection limit (0.005 mg / l).

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 Na2 O含有量が0.3重量%以下で、
かつ磨耗率が1%以下の球状活性アルミナよりなる吸着
剤を、ヒ酸イオンを含む水と接触させ該水中よりヒ酸イ
オンを除去することを特徴とするヒ酸イオンの除去方
法。
1. A Na 2 O content of 0.3% by weight or less,
A method for removing arsenate ions, which comprises contacting an adsorbent made of spherical activated alumina having a wear rate of 1% or less with water containing arsenate ions to remove the arsenate ions from the water.
【請求項2】 吸着剤が、Na2 O含有量が0.3重量
%以下でかつ磨耗率が1%以下の球状活性アルミナに、
80℃の水に浸漬したときの水のpHが3〜6の値を呈
する酸成分を被着させたものであることを特徴とする請
求項1記載のヒ酸イオンの除去方法。
2. The adsorbent is spherical activated alumina having a Na 2 O content of 0.3% by weight or less and a wear rate of 1% or less,
The method for removing arsenate ions according to claim 1, wherein an acid component having a pH of water of 3 to 6 when immersed in water at 80 ° C. is deposited.
【請求項3】 酸成分が塩酸、フッ化水素酸、硝酸、硫
酸および酢酸の少なくとも1種であることを特徴とする
請求項2記載のヒ酸イオンの除去方法。
3. The method for removing arsenate ions according to claim 2, wherein the acid component is at least one of hydrochloric acid, hydrofluoric acid, nitric acid, sulfuric acid and acetic acid.
JP22937195A 1995-09-06 1995-09-06 How to remove arsenate ions Expired - Fee Related JP3291994B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP22937195A JP3291994B2 (en) 1995-09-06 1995-09-06 How to remove arsenate ions

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP22937195A JP3291994B2 (en) 1995-09-06 1995-09-06 How to remove arsenate ions

Publications (2)

Publication Number Publication Date
JPH0975717A true JPH0975717A (en) 1997-03-25
JP3291994B2 JP3291994B2 (en) 2002-06-17

Family

ID=16891131

Family Applications (1)

Application Number Title Priority Date Filing Date
JP22937195A Expired - Fee Related JP3291994B2 (en) 1995-09-06 1995-09-06 How to remove arsenate ions

Country Status (1)

Country Link
JP (1) JP3291994B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002509801A (en) * 1998-04-01 2002-04-02 アルキャン・インターナショナル・リミテッド Product for water treatment and its production
JP2002234724A (en) * 2001-02-01 2002-08-23 Sumitomo Chem Co Ltd Active alumina particle for removing harmful ion in water and producing method thereof
JP2002263636A (en) * 2001-03-13 2002-09-17 Sumitomo Chem Co Ltd Method for removing phosphoric acid ion in water
KR101337984B1 (en) * 2011-03-23 2013-12-06 (주)선진환경 Filter Medium and Method of Preparing the Same from Recycled Alumium Oxide

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002509801A (en) * 1998-04-01 2002-04-02 アルキャン・インターナショナル・リミテッド Product for water treatment and its production
JP2002234724A (en) * 2001-02-01 2002-08-23 Sumitomo Chem Co Ltd Active alumina particle for removing harmful ion in water and producing method thereof
JP2002263636A (en) * 2001-03-13 2002-09-17 Sumitomo Chem Co Ltd Method for removing phosphoric acid ion in water
KR101337984B1 (en) * 2011-03-23 2013-12-06 (주)선진환경 Filter Medium and Method of Preparing the Same from Recycled Alumium Oxide

Also Published As

Publication number Publication date
JP3291994B2 (en) 2002-06-17

Similar Documents

Publication Publication Date Title
EP0191893B1 (en) Process for adsorption treatment of dissolved fluorine
KR100951492B1 (en) Mixtures of Adsorber Materials
CA2327087C (en) Water treatment product &amp; method
JP4423645B2 (en) Hydroxyapatite silica composite porous material adsorbent and method for producing the same
CA2507571A1 (en) Improved arsenic removal media
WO1992010292A1 (en) The removal of heavy metals, especially lead, from aqueous systems containing competing ions utilizing amorphous tin and titanium silicates
CA2598074A1 (en) Products and methods for removing substances from aqueous solution
WO1994004271A1 (en) Composite ion-exchange material, preparation and use thereof
US20030089665A1 (en) Arsenic removal media
US5536415A (en) Removal of sulfate ions from saline solutions comprised thereof
JP7177703B2 (en) Water purification device and water purification method using layered double hydroxide
JPH022612B2 (en)
JPH0975717A (en) Method for removing arsenate ion
JP2004066161A (en) Water treatment method
JPS6259973B2 (en)
Vinayagam et al. Equilibrium and kinetics of adsorption of cationic dyes by STISHOVITE clay-TiO2 nanocomposite
JPS61192385A (en) Treatment of fluorine-containing waste solution
JPS61192340A (en) Fluorine complex ion adsorbent
JP2000033387A (en) Method for removing arsenic in water
JP3709612B2 (en) How to remove arsenate ions
JP3412455B2 (en) Activated alumina for arsenate ion adsorption and method for adsorbing arsenate ions from aqueous solution using the same
JPH01127094A (en) Removal of arsenic
KR101699349B1 (en) Absorbing medium using water-treatment sludge and method for fabricating the same
JPS6136973B2 (en)
JP7419952B2 (en) Novel silicotitanate composition and method for producing the same

Legal Events

Date Code Title Description
S531 Written request for registration of change of domicile

Free format text: JAPANESE INTERMEDIATE CODE: R313531

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090329

Year of fee payment: 7

RD05 Notification of revocation of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: R3D05

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090329

Year of fee payment: 7

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100329

Year of fee payment: 8

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110329

Year of fee payment: 9

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120329

Year of fee payment: 10

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130329

Year of fee payment: 11

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130329

Year of fee payment: 11

FPAY Renewal fee payment (prs date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140329

Year of fee payment: 12

LAPS Cancellation because of no payment of annual fees