JPH0147217B2 - - Google Patents
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- Publication number
- JPH0147217B2 JPH0147217B2 JP57003876A JP387682A JPH0147217B2 JP H0147217 B2 JPH0147217 B2 JP H0147217B2 JP 57003876 A JP57003876 A JP 57003876A JP 387682 A JP387682 A JP 387682A JP H0147217 B2 JPH0147217 B2 JP H0147217B2
- Authority
- JP
- Japan
- Prior art keywords
- arsenic
- oxidizing agent
- titanic acid
- gas
- adsorbed
- 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
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- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【発明の詳細な説明】
本発明は耐熱性、耐薬品性を優れかつ、取り扱
いの容易で反復使用可能な新規な排気ガス中ヒ素
化合物の吸着除去方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a novel method for adsorption and removal of arsenic compounds in exhaust gas, which has excellent heat resistance and chemical resistance, is easy to handle, and can be used repeatedly.
従来ヒ素を含有する混合ガスの処理方法とし
て、硫酸銅の液体中に混合ガスを通じヒ化銅とし
て沈澱させる方法、あるいは高熱を加えた石英管
内に混合ガスを通じた後、冷却して金属ヒ素とし
て固化させる方法、さらに、また、混合ガスを加
熱された銅、鉄、ニツケルまたはコバルト上に導
き、ヒ素をこれらの金属と反応させるとともに反
応生成物とその金属内部に拡散させる方法等が知
られているが、これらの方法はいずれもヒ素の除
去方法としては不完全なものであり、処理ガス中
のヒ素濃度を十分低下させるためには複雑かつ大
型の装置が必要になるばかりでなく、数百度もの
高熱下での反応であり、処理操作上も危険かつ多
大のエネルギーを消費する方法である。また、ヒ
素との反応生成物からはヒ素との再分離が困難で
あるから反応生成物のまま処理系から除去し、廃
棄せねばならず、言うまでもなく再使用が不可能
であつた。 Conventional methods for treating mixed gases containing arsenic include passing the mixed gas into liquid copper sulfate to precipitate it as copper arsenide, or passing the mixed gas through a quartz tube heated to high temperatures, then cooling it and solidifying it as metallic arsenic. Additionally, methods are known in which a gas mixture is introduced onto heated copper, iron, nickel, or cobalt to cause arsenic to react with these metals and to diffuse the reaction products into the interior of the metal. However, all of these methods are incomplete as methods for removing arsenic, and in order to sufficiently reduce the arsenic concentration in the processing gas, they not only require complicated and large equipment, but also require heating at hundreds of degrees Celsius. The reaction is carried out under high heat, and the process is dangerous and consumes a large amount of energy. Furthermore, since it is difficult to re-separate arsenic from the reaction product with arsenic, the reaction product must be removed from the treatment system and disposed of, and needless to say, it cannot be reused.
本発明者らは、かかる従来法によつては不可能
であつた耐熱性・耐薬品性に優れかつ取り扱いが
容易で反復使用可能な新規な排気ガス中ヒ素化合
物の吸着除去方法を得るべく鋭意検討した結果粉
末チタン酸(二酸化チタン水和物)に水および硫
酸を添加して得られらる混和物を微小粒子に造
粒・成形、焼成して得られる粒状物は、これに酸
化剤水溶液を含浸、吸着保持させると、ガス状ヒ
素化合物の吸着・除去に好適な性能を有する事実
を見い出した。本発明は酸化剤水溶液を吸着・保
持させたチタン酸粒状物とヒ素成分・含有ガスと
を接触させることよりなるガス中のヒ素成分の除
去方法である。 The present inventors have worked diligently to develop a new method for adsorption and removal of arsenic compounds in exhaust gas that has excellent heat resistance and chemical resistance, is easy to handle, and can be used repeatedly, which was not possible using conventional methods. As a result of the study, the mixture obtained by adding water and sulfuric acid to powdered titanic acid (titanium dioxide hydrate) is granulated into fine particles, molded, and fired. It has been discovered that when impregnated, adsorbed and retained, it has properties suitable for adsorbing and removing gaseous arsenic compounds. The present invention is a method for removing arsenic components in a gas, which comprises bringing titanic acid particles adsorbed and retained an oxidizing agent aqueous solution into contact with an arsenic component/containing gas.
以下本発明の除去法を詳細に説明する。 The removal method of the present invention will be explained in detail below.
本発明で用いられるチタン酸とは化学式
TiO2・nH2O(n=0.5〜2.0)で示される二酸化チ
タン水和物であればよいが硫酸チタニル
(TiOSO4)、チタンテトライソブロポキシド(Ti
〔OCH(CH3)2〕4)、四塩化チタン(TiCl4)等の
加水分解によつて製造されたものであれば比表面
積が大きく保持量の大きな吸着剤を得る目的のた
めには好都合である。 The chemical formula of titanic acid used in the present invention is
Any titanium dioxide hydrate represented by TiO 2 .nH 2 O (n = 0.5 to 2.0) may be used, but titanyl sulfate (TiOSO 4 ), titanium tetraisopropoxide (Ti
[OCH (CH 3 ) 2 ] 4 ), titanium tetrachloride (TiCl 4 ), etc. manufactured by hydrolysis have a large specific surface area and are convenient for the purpose of obtaining an adsorbent with a large retention capacity. It is.
粉末チタン酸を造粒成形するには水および硫酸
を添加して特開昭55−8844に示された方法により
混練、押し出し造粒、焼成する方法によれば吸着
剤として十分な強度と比表面積(約200m2/g)
を有する粒状物が得られるが、これをさらに粉
砕、篩分したものであるならば粒経が十数ミリメ
ートル以下任意の大きさが得られる。また混練物
の成形法として通常用いられる圧縮造粒法によつ
て球状に成形するならば比表面積の低下を招くこ
となく粒径が数センチメートルまでの任意の大き
さが得られる。 Powdered titanic acid can be granulated and molded by adding water and sulfuric acid, kneading, extruding, granulating, and firing according to the method disclosed in JP-A-55-8844, which has sufficient strength and specific surface area as an adsorbent. (approx. 200m 2 /g)
However, if this is further crushed and sieved, any grain size of less than ten millimeters can be obtained. Further, if the kneaded product is formed into a spherical shape by compression granulation, which is commonly used as a method for forming the kneaded product, any particle size up to several centimeters can be obtained without causing a decrease in the specific surface area.
ヒ素吸着の高度の処理効果を望むらなば粒径の
小さいものを篩分して得ればよいが、通常粒径
0.1mm〜1cm、より好ましくは0.5〜5mmにすれば
好適である。吸着剤の充填による通気抵抗の増大
を避けるには粒径の大きな吸着剤を用いればよ
い。 If you want a high level of arsenic adsorption treatment effect, you can obtain it by sieving small particles, but usually
A suitable range is 0.1 mm to 1 cm, more preferably 0.5 to 5 mm. In order to avoid an increase in ventilation resistance due to adsorbent filling, an adsorbent with a large particle size may be used.
本発明のチタン酸はチタン酸単独系で充填式吸
着剤として十分な造粒強度を有するがさらにアル
ミナもしくはシリカまたは両者を合計30重量%ま
で含有した混和物から造粒成形、焼成した場合も
なお十分な強度を維持する。さらに含有率を増大
させると強度は低下していく。強度を優先させる
ならばこれらの無機物の含有率は低下させればよ
いが。これらの含有による充填剤の特性の変化を
優先するならばこれらの2者あるいはさらに他の
無機物または有機物を混有する成形体として吸着
剤とすることができる。また別個に造粒・成形、
篩分したチタン酸、アルミナあるいはシリカ充填
剤を混合して混合充填式吸着剤として用いること
も可能である。 The titanic acid of the present invention has sufficient granulation strength as a titanic acid alone system as a packed adsorbent, but it also has sufficient granulation strength when it is granulated and calcined from a mixture containing alumina or silica, or a total of 30% by weight of both. Maintain sufficient strength. When the content is further increased, the strength decreases. If priority is given to strength, the content of these inorganic substances may be reduced. If priority is given to changes in the properties of the filler due to the inclusion of these substances, the adsorbent may be prepared as a molded body containing these two or other inorganic or organic substances. In addition, granulation and molding are carried out separately.
It is also possible to mix sieved titanic acid, alumina or silica filler and use it as a mixed packing type adsorbent.
また本発明で前記チタン酸粒状物に吸着、保持
させるために用いられる酸化剤は過マンガン酸あ
るいはその塩類、クロム酸およびその塩類、硝酸
およびその塩酸、過酸化物、硫酸等通常の酸化剤
で水溶性のものであるならば何でもよい。酸化剤
の水溶液中濃度は0.1%程度以上であれば有効で
あるが好ましくは3%であれば十分である。酸化
剤水溶液の必要量は吸着剤表面を湿潤させる目的
に要する量であり、吸着剤1gにつき0.1〜2.0ml
であればよいが好ましくは0.5〜1.0mlであればよ
い。2.0ml以上の酸化剤水溶液を吸着・保持させ
ると吸着剤粒子間の微少空間が該小溶液により満
たされて、ガス状物質の進入が困難となり通気低
抗の増大を招くので低通気抵抗を望む場合には不
都合である。このようにして得られた酸化剤水溶
液を担持したチタン酸粒状物をガス状のヒ素化合
物を含有するガスと接触させるとヒ素化合物が効
率良く粒状物に吸着され、除去される。除去の対
象となるヒ素成分としてはヒ素単体(AS4、
AS2)、アルシン(AsH3)、五フツ化ヒ素
(AsF5)あるいはこれらの有機化合物誘導体など
のヒ素化合物が挙げられる。更に本発明にあつて
はヒ素成分の他に酸化剤によつて酸化され酸化酸
陰イオンを生成する物質も吸着除去されるためホ
スフイン(PH3)やスチビン(SbH3)などを共
存含有する混合ガスに適用するとヒ素成分と同時
にこれらも除去され極めて好都合である。粒状物
とガスの接触は形状任意の充填塔式でたて型、横
型いずれでも行うことができる。接触温度はガス
の温度のまゝで吸着除去が可能で特別の冷却或は
加熱を行わなくても良いが必要に応じてガスの前
処理をしても良い。 Further, in the present invention, the oxidizing agent used for adsorption and retention on the titanic acid granules is a common oxidizing agent such as permanganic acid or its salts, chromic acid and its salts, nitric acid and its hydrochloric acid, peroxide, sulfuric acid, etc. Any water-soluble material may be used. It is effective if the concentration of the oxidizing agent in the aqueous solution is about 0.1% or more, but preferably 3% is sufficient. The required amount of oxidizing agent aqueous solution is the amount required for the purpose of moistening the adsorbent surface, and is 0.1 to 2.0 ml per 1 g of adsorbent.
It may be any amount, but preferably 0.5 to 1.0 ml. If 2.0ml or more of an oxidizing agent aqueous solution is adsorbed and retained, the small spaces between the adsorbent particles will be filled with the small solution, making it difficult for gaseous substances to enter and causing an increase in ventilation resistance, so low ventilation resistance is desired. This is inconvenient in some cases. When the titanic acid granules carrying the oxidizing agent aqueous solution thus obtained are brought into contact with a gas containing a gaseous arsenic compound, the arsenic compound is efficiently adsorbed onto the granules and removed. Arsenic components targeted for removal include arsenic alone (AS 4 ,
Examples include arsenic compounds such as AS 2 ), arsine (AsH 3 ), arsenic pentafluoride (AsF 5 ), and organic compound derivatives thereof. Furthermore, in the present invention, in addition to the arsenic component, substances that are oxidized by the oxidizing agent to produce oxidized acid anions are also adsorbed and removed, so the mixture containing phosphine (PH 3 ), stibine (SbH 3 ), etc. When applied to gases, these are removed at the same time as arsenic components, which is extremely convenient. The contact between the granules and the gas can be carried out in a packed column of any shape, either vertically or horizontally. Adsorption and removal is possible at the contact temperature of the gas, and no special cooling or heating is required, but the gas may be pretreated if necessary.
ヒ素ガスを吸着した粒状チタン酸からヒ素を回
収するには該粒状チタン酸を充填塔より取り出し
アルカリ水溶液中に投入し、スラリー状態として
撹拌、チタン酸をロ過することにより水溶液中に
転溶・回収することができる。液性はアルカリ性
であればよいが、転溶速度を重視するならば強ア
ルカリ性(PH10以上)が有利であり、この場合1
時間以内に吸着ヒ素の90%以上を回収することが
できる。アルカリの種類は水酸化ナトリウム、水
酸化カリウム等通常のアルカリであれば全く問題
はないので、効果および経済性の観点から水酸化
ナトリウムを用いるのが有利である。必要なアル
カリ水溶液量はチタン酸とスラリー状態を維持で
きれば十分であるから、極めて濃厚な少量のヒ素
溶液としてヒ素を回収することができる。 To recover arsenic from granular titanic acid that has adsorbed arsenic gas, the granular titanic acid is taken out of the packed tower and put into an alkaline aqueous solution, stirred as a slurry, and the titanic acid is transferred and dissolved into the aqueous solution by filtration. It can be recovered. The liquid property should be alkaline, but if the speed of dissolution is important, strong alkalinity (PH10 or higher) is advantageous, and in this case, 1
More than 90% of adsorbed arsenic can be recovered within hours. As long as the type of alkali is a common alkali such as sodium hydroxide or potassium hydroxide, there will be no problem, so it is advantageous to use sodium hydroxide from the viewpoint of effectiveness and economy. Since the required amount of alkaline aqueous solution is sufficient to maintain a slurry state with titanic acid, arsenic can be recovered as a small amount of extremely concentrated arsenic solution.
またこの脱ヒ素化されたチタン酸粒状物は、反
復使用することが可能である。 Further, the dearsenated titanic acid granules can be used repeatedly.
さらに、本チタン酸粒状物は耐熱性に優れるの
で、高温の混合ガスを対象としても300℃までは
何ら形状をそこなうことなく使用することができ
るが酸化剤水溶液が蒸発して行くので、性能はや
や低下する。 Furthermore, this titanic acid granule has excellent heat resistance, so it can be used in high-temperature mixed gases up to 300℃ without losing its shape, but the oxidant aqueous solution will evaporate, resulting in poor performance. It decreases slightly.
次に本発明を実施例により説明するが本発明は
その要旨を越えない限り以下の実施例に限定され
るものではない。 Next, the present invention will be explained using Examples, but the present invention is not limited to the following Examples unless the gist of the invention is exceeded.
実施例
特開昭55−8844に示された方法によつて造粒・
成形されたチタン酸粒状物(0.5mmφ×7mmL)
2.0gの表面に酸化剤水溶液1.6mlを吸着保持させ
る。酸化剤水溶液は過マンガン酸カリウム0.3g
に濃硝酸3.0mlを添加し水で合計100mlになるよう
に調製した。この酸化剤吸着チタン酸をJIS
K0101−1979に示されたAs分析法における導管
内に充填し両端を図1に示すようにグラスウール
で封じた。ガス導入側のグラスウールには酢酸鉛
を含浸させたものを用いた。該JIS分析法に従つ
てヒ酸によう化カリウム、塩化すず()及び亜
鉛を加えてアルシンを発生させ該ガスを酸化剤吸
着チタン酸粒状物を充填した導管中を通過させた
後ジエチルジチオカルバミン酸銀溶液中に吸収さ
せ、生成する赤紫色の吸光度を測定して、吸着除
去されなかつたヒ素量を測定した。発生アルシン
量を種々変えて、未吸着ヒ素量を測定したとこ
ろ、ヒ素原子(As)換算で発生量100μgまでは
ヒ素は完全に吸着除去されていた。Example: Granulation and
Molded titanic acid granules (0.5mmφ×7mmL)
1.6 ml of oxidizing agent aqueous solution is adsorbed and retained on the surface of 2.0 g. Oxidizing agent aqueous solution is potassium permanganate 0.3g
3.0 ml of concentrated nitric acid was added to the solution, and water was added to make a total of 100 ml. This oxidant adsorbed titanic acid is
It was filled into a conduit in the As analysis method shown in K0101-1979, and both ends were sealed with glass wool as shown in FIG. The glass wool on the gas introduction side was impregnated with lead acetate. According to the JIS analysis method, potassium iodide, tin chloride () and zinc are added to arsenic acid to generate arsine, and the gas is passed through a conduit filled with oxidizing agent-adsorbing titanic acid particles, followed by diethyldithiocarbamic acid. The amount of arsenic that was not adsorbed and removed was determined by absorbing it into a silver solution and measuring the absorbance of the reddish-purple color produced. When the amount of unadsorbed arsenic was measured by varying the amount of arsine generated, it was found that arsenic was completely adsorbed and removed up to the amount of 100 μg generated in terms of arsenic atoms (As).
極小量の酸化剤と粒状チタン酸の組み合わせに
よりアルシンが効果的に除去されていることが知
見される。 It is found that arsine is effectively removed by the combination of a minimal amount of oxidizing agent and particulate titanic acid.
比較例
図2に示すように実施例と同様のアルシン発生
液に粒状チタン酸の封入されていないガラス導管
の一端を接続し他端を実施例と同様の酸化剤100
ml中に導き、酸化剤中を通過したアルシンをさら
にガラス管によりアルシン吸収管中に導入した。
実施例と同様の条件でアルシンを発出させ、同様
の分析条件で未吸着ヒ素量を測定した。発生アル
シン量を種々変えて未吸着量ヒ素量を測定したと
ころヒ素原子換算で10μgの発生ヒ素に対してす
でに0.45μgが未吸着となり、100μgの発生量に
対しては4.55μgが未吸着であつた。吸着効果は
酸化剤液量を増加しても酸化剤濃度を高めても殆
んど向上が見られなかつた。実施例に比較して著
しく多量の酸化剤を使用しても酸化剤吸着保持チ
タン酸の効果に遠く及ばないことが知見される。Comparative Example As shown in Figure 2, one end of a glass conduit in which granular titanic acid was not sealed was connected to the same arsine generating liquid as in the example, and the other end was connected to the same oxidizing agent as in the example.
The arsine that had passed through the oxidizing agent was further introduced into an arsine absorption tube through a glass tube.
Arsine was emitted under the same conditions as in the example, and the amount of unadsorbed arsenic was measured under the same analytical conditions. When the amount of unadsorbed arsenic was measured by varying the amount of arsine generated, 0.45 μg was already unadsorbed for 10 μg of generated arsenic in terms of arsenic atoms, and 4.55 μg was unadsorbed for 100 μg of generated arsenic. Ta. The adsorption effect hardly improved even when the amount of oxidizing agent was increased or the oxidizing agent concentration was increased. It is found that even if a significantly larger amount of oxidizing agent is used than in the examples, the effect of adsorbing and retaining the oxidizing agent is not far superior to that of titanic acid.
第1図は本発明の方法を実施するために用いる
ガス状ヒ素の除去装置の1例を示したものであ
る。第2図は、比較のための除去装置の例であ
る。
1……アルシン発生液、2……グラスウール、
3……酸化剤吸着チタン酸粒状物、4……ガラス
導管、5……アルシン吸収液、6……酸化剤水溶
液。
FIG. 1 shows an example of a gaseous arsenic removal apparatus used to carry out the method of the present invention. FIG. 2 is an example of a removal device for comparison. 1...Arsine generating liquid, 2...Glass wool,
3... Oxidizing agent adsorbed titanic acid granules, 4... Glass conduit, 5... Arsine absorption liquid, 6... Oxidizing agent aqueous solution.
Claims (1)
着保持させたチタン酸粒状物と接触させることを
特徴とするガス中ヒ素成分の除去法。1. A method for removing arsenic components in a gas, which comprises bringing a gas containing an arsenic component into contact with titanic acid particles that have adsorbed and retained an oxidizing agent aqueous solution.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57003876A JPS58122026A (en) | 1982-01-13 | 1982-01-13 | Removal of arsenic component in gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57003876A JPS58122026A (en) | 1982-01-13 | 1982-01-13 | Removal of arsenic component in gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS58122026A JPS58122026A (en) | 1983-07-20 |
| JPH0147217B2 true JPH0147217B2 (en) | 1989-10-12 |
Family
ID=11569382
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57003876A Granted JPS58122026A (en) | 1982-01-13 | 1982-01-13 | Removal of arsenic component in gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS58122026A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60114328A (en) * | 1983-11-24 | 1985-06-20 | Showa Eng Kk | Processing method for gas containing hydrogen arsenide |
| KR100456185B1 (en) * | 2001-07-25 | 2004-11-10 | 주식회사 얼라이브텍 | Eliminator For Removing Harmful Gases In Flue Gases And Method For Removing The Sames Thereby |
-
1982
- 1982-01-13 JP JP57003876A patent/JPS58122026A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS58122026A (en) | 1983-07-20 |
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