JPH0157617B2 - - Google Patents
Info
- Publication number
- JPH0157617B2 JPH0157617B2 JP57013893A JP1389382A JPH0157617B2 JP H0157617 B2 JPH0157617 B2 JP H0157617B2 JP 57013893 A JP57013893 A JP 57013893A JP 1389382 A JP1389382 A JP 1389382A JP H0157617 B2 JPH0157617 B2 JP H0157617B2
- Authority
- JP
- Japan
- Prior art keywords
- ammonium
- mercury vapor
- activated carbon
- gas
- acid
- 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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- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 36
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 claims description 29
- 239000003463 adsorbent Substances 0.000 claims description 21
- 239000002253 acid Substances 0.000 claims description 11
- GEHMBYLTCISYNY-UHFFFAOYSA-N Ammonium sulfamate Chemical compound [NH4+].NS([O-])(=O)=O GEHMBYLTCISYNY-UHFFFAOYSA-N 0.000 claims description 4
- UYJXRRSPUVSSMN-UHFFFAOYSA-P ammonium sulfide Chemical compound [NH4+].[NH4+].[S-2] UYJXRRSPUVSSMN-UHFFFAOYSA-P 0.000 claims description 4
- SOIFLUNRINLCBN-UHFFFAOYSA-N ammonium thiocyanate Chemical compound [NH4+].[S-]C#N SOIFLUNRINLCBN-UHFFFAOYSA-N 0.000 claims description 4
- XYXNTHIYBIDHGM-UHFFFAOYSA-N ammonium thiosulfate Chemical compound [NH4+].[NH4+].[O-]S([O-])(=O)=S XYXNTHIYBIDHGM-UHFFFAOYSA-N 0.000 claims description 4
- 238000000034 method Methods 0.000 description 14
- 239000007789 gas Substances 0.000 description 13
- 150000003863 ammonium salts Chemical class 0.000 description 12
- 238000001179 sorption measurement Methods 0.000 description 9
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 6
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 6
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 6
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 4
- 239000011521 glass Substances 0.000 description 4
- 229910052753 mercury Inorganic materials 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- QGJOPFRUJISHPQ-UHFFFAOYSA-N Carbon disulfide Chemical compound S=C=S QGJOPFRUJISHPQ-UHFFFAOYSA-N 0.000 description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 229910001873 dinitrogen Inorganic materials 0.000 description 2
- 239000003345 natural gas Substances 0.000 description 2
- 235000006408 oxalic acid Nutrition 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 239000011593 sulfur Substances 0.000 description 2
- 235000013162 Cocos nucifera Nutrition 0.000 description 1
- 244000060011 Cocos nucifera Species 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 239000003456 ion exchange resin Substances 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000002574 poison Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 159000000000 sodium salts Chemical class 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Hydrogen, Water And Hydrids (AREA)
Description
本発明は、ガス中の水銀蒸気吸着剤に関する。
電解水素ガス、天然ガス、焼却炉排ガス、水銀を
取扱う工場の排ガス中には、水銀蒸気が含まれて
いることが多い。すなわち、電解水素は医薬品、
食品、その他の製品を製造するプロセスに使用さ
れ、微量の水銀蒸気が触媒を被毒したり製品に混
入したりするので問題となることがある。天然ガ
ス中の水銀蒸気は、ガスの液化プロセスにおける
アルミニウム製の熱交換器などを腐食し、大きな
事故の原因となる。また焼却炉排ガスおよび水銀
蒸気を取扱う工場の排ガス中の水銀蒸気は、大気
汚染上または作業環境上、問題となる。
したがつてこれらガス中の水銀蒸気は、何らの
処理によつて除去しなければならない。これま
で、ガス中の水銀を除去する方法として、薬液洗
浄法、活性炭やイオン交換樹脂などの吸着剤を使
用する乾式吸着法などが知られているが、前者の
薬液洗浄法は、水銀蒸気の除去効率が不充分でか
つ廃液を生じるなどの欠点がある。後者の乾式吸
着法では、水銀蒸気の吸着容量が小さく充分満足
し得るものではない。
本発明者らは、このような点に鑑み種研究した
結果、チオシアン酸アンモニウム、チオ硫酸アン
モニウム、硫化アンモニウム、スルフアミン酸ア
ンモニウムを担持した活性炭は、ガス中の水銀蒸
気を効率よく吸着し、かつその吸着容量が著しく
大きいことを見出し、本発明を完成した。
すなわち、本発明は、活性炭にチオシアン酸ア
ンモニウム、チオ硫酸アンモニウム、硫化アンモ
ニウム、スルフアミン酸アンモニウム(以下アン
モニウム塩という)の少なくとも一つを担持して
なる水銀蒸気吸着剤である。
本発明において使用される活性炭は木炭、コー
クス、ヤシガラ、樹脂などを原料として公知方法
により製造されたもので、その比表面積が200〜
2000m2/gのものであれば、いかなるものでもよ
い。
活性炭に対するアンモニウム塩の担持量は、活
性炭1g当り5〜800mg、好ましくは10〜550mgで
ある。
活性炭にアンモニウム塩を担持するには、たと
えば、アンモニウム塩を水に溶解し、これを活性
炭に含浸または散布し、必要に応じて乾燥する方
法などが挙げられる。
本発明の水銀蒸気吸着剤はアンモニウム塩の他
さらに不揮発性酸を担持していてもよく、不揮発
性酸を担持せしめることにより、吸着剤の水銀吸
着能力を高めることができる。ここにいう不揮発
性酸は、100℃における蒸気圧が50mmHg以下の
酸をいい、たとえば硫酸、リン酸、シユウ酸、ク
エン酸などがあげられる。不揮発性酸の担持量
は、活性炭1g当り5〜500mg、好ましくは10〜
400mgである。不揮発性酸を担持せしめる方法は、
アンモニウム塩の活性炭への担持方法と同様にし
て行なわれ、アンモニウム塩と不揮発性酸の活性
炭に担持せしめる順序は、いずれでもよい。たと
えば、アンモニウム塩と不揮発性酸を含有する水
溶液を活性炭に含浸または散布する方法、アンモ
ニウム塩を担持した後、不揮発性酸を担持する方
法、または、不揮発性酸を担持した後アンモニウ
ム塩を担持する方法などがあげられる。
本発明の水銀蒸気吸着剤を用いてガス中の水銀
蒸気を除去するには、水銀蒸気を含有するガスと
本発明の吸着剤とを接触させればよい。接触温度
は、150℃以下、好ましくは−10〜120℃で、接触
圧力は50Kg/cm2以下、好ましくは0.1〜35Kg/cm2
で、接触時間は25℃1Kg/cm2換算で1/10〜30秒、
好ましくは1/5〜20秒である。また、本吸着剤と
水銀蒸気含有ガスとの接触は、たとえば固定層、
移動層、流動層などを用いて行なうことができ
る。
以下に実施例を示して本発明をより具体的に説
明する。
実施例 1
BET比表面積1150m2/gの4〜6mesh粒状活
性炭を16〜24meshに破砕整粒した。この活性炭
AにNH4SCN、(NH4)2S2O3、(NH4)2Sおよび
NH4OSO2NH2を溶解した水溶液を均一に散布
し、NH4SCN、(NH4)2S2O3、(NH4)2S、およ
びNH4OSO2NH2をそれぞれ100mg/g担持し、
110℃で乾燥した(吸着剤B〜E)。
なお対照としてこれらアンモニウム塩の代りナ
トリウム塩を前記と同様にそれぞれ100mg/g担
持し、110℃で乾燥した(吸着剤b〜e)。また活
性炭Aにイオウを溶解した二硫化炭素溶液を散布
し、120℃で乾燥してイオウ100mg/g担持活性炭
(吸着剤f)を調整した。
このようにして得られた吸着剤A〜Eおよびb
〜fの各6mlを1.6cmφのガラス製カラムに充填
して、水銀蒸気9mg/m3含有の30℃ガス(N2−
84.8vol%、O2−14.5vol%、H2O−0.7vol%)を線流
速40cm/secで流通し、水銀蒸気の破過吸着テス
トを行なつた。結果は第1表のとおりである。
The present invention relates to mercury vapor adsorbents in gases.
Mercury vapor is often contained in electrolyzed hydrogen gas, natural gas, incinerator exhaust gas, and exhaust gas from factories that handle mercury. In other words, electrolytic hydrogen is used for pharmaceuticals,
It is used in the process of manufacturing food and other products, and trace amounts of mercury vapor can cause problems as it can poison catalysts or mix into products. Mercury vapor in natural gas corrodes aluminum heat exchangers during the gas liquefaction process, causing major accidents. Furthermore, mercury vapor in incinerator exhaust gas and exhaust gas from factories that handle mercury vapor poses problems in terms of air pollution and the working environment. Therefore, mercury vapor in these gases must be removed by some kind of treatment. Until now, known methods for removing mercury from gas include chemical cleaning methods and dry adsorption methods using adsorbents such as activated carbon and ion exchange resins. There are disadvantages such as insufficient removal efficiency and generation of waste liquid. The latter dry adsorption method has a small adsorption capacity for mercury vapor and is not fully satisfactory. In view of these points, the present inventors conducted research and found that activated carbon supporting ammonium thiocyanate, ammonium thiosulfate, ammonium sulfide, and ammonium sulfamate efficiently adsorbs mercury vapor in gas and has a high adsorption capacity. They discovered that the capacity was significantly large and completed the present invention. That is, the present invention is a mercury vapor adsorbent comprising activated carbon supporting at least one of ammonium thiocyanate, ammonium thiosulfate, ammonium sulfide, and ammonium sulfamate (hereinafter referred to as ammonium salt). The activated carbon used in the present invention is produced by a known method using charcoal, coke, coconut shell, resin, etc. as raw materials, and has a specific surface area of 200 to 200.
Any material may be used as long as it has an area of 2000m 2 /g. The amount of ammonium salt supported on activated carbon is 5 to 800 mg, preferably 10 to 550 mg per gram of activated carbon. In order to support the ammonium salt on the activated carbon, for example, a method of dissolving the ammonium salt in water, impregnating or spraying the ammonium salt on the activated carbon, and drying as necessary can be mentioned. The mercury vapor adsorbent of the present invention may carry a nonvolatile acid in addition to the ammonium salt, and by supporting the nonvolatile acid, the mercury adsorption ability of the adsorbent can be increased. The non-volatile acid referred to herein refers to an acid with a vapor pressure of 50 mmHg or less at 100°C, such as sulfuric acid, phosphoric acid, oxalic acid, and citric acid. The amount of nonvolatile acid supported is 5 to 500 mg, preferably 10 to 500 mg per gram of activated carbon.
It is 400mg. The method for supporting non-volatile acids is as follows:
This is carried out in the same manner as the method for supporting ammonium salts on activated carbon, and the order in which ammonium salts and nonvolatile acids are supported on activated carbon may be arbitrary. For example, a method of impregnating or spraying activated carbon with an aqueous solution containing an ammonium salt and a non-volatile acid, a method of supporting an ammonium salt and then supporting a non-volatile acid, or a method of supporting a non-volatile acid and then supporting an ammonium salt. Examples include methods. In order to remove mercury vapor from a gas using the mercury vapor adsorbent of the present invention, it is sufficient to bring the gas containing mercury vapor into contact with the adsorbent of the present invention. The contact temperature is 150°C or less, preferably -10 to 120°C, and the contact pressure is 50Kg/ cm2 or less, preferably 0.1 to 35Kg/ cm2.
The contact time is 1/10 to 30 seconds at 25°C in terms of 1 kg/ cm2 .
Preferably it is 1/5 to 20 seconds. In addition, the contact between the present adsorbent and the mercury vapor-containing gas can be carried out, for example, by using a fixed layer,
This can be carried out using a moving bed, fluidized bed, etc. EXAMPLES The present invention will be explained in more detail with reference to Examples below. Example 1 Granular activated carbon of 4 to 6 mesh with a BET specific surface area of 1150 m 2 /g was crushed and sized to 16 to 24 mesh. NH 4 SCN, (NH 4 ) 2 S 2 O 3 , (NH 4 ) 2 S and
Spread an aqueous solution containing NH 4 OSO 2 NH 2 uniformly to support 100 mg/g of each of NH 4 SCN, (NH 4 ) 2 S 2 O 3 , (NH 4 ) 2 S, and NH 4 OSO 2 NH 2 death,
Dry at 110°C (adsorbents BE). As a control, 100 mg/g of each sodium salt was supported in place of these ammonium salts in the same manner as above and dried at 110°C (adsorbents b to e). Further, a carbon disulfide solution containing sulfur dissolved in activated carbon A was sprayed and dried at 120° C. to prepare activated carbon supporting 100 mg/g of sulfur (adsorbent f). Adsorbents A to E and b thus obtained
6 ml of each of ~
84.8 vol %, O 2 -14.5 vol %, H 2 O - 0.7 vol %) were passed at a linear flow rate of 40 cm/sec to conduct a breakthrough adsorption test for mercury vapor. The results are shown in Table 1.
【表】【table】
【表】
実施例 2
実施例1の吸着剤B〜Eおよびb〜eにさらに
硫酸を100mg/g担持し、110℃で乾燥した(吸着
剤B1〜E1およびb1〜e1)。
このようにして得られた吸着剤A〜E、B1〜
E1、b〜eおよびb1〜e1の各6mlを1.6cmφのガ
ラス製カラムに充填して、水銀蒸気9mg/m3含有
の30℃の窒素ガスを線流速40cm/secで流通し、
水銀蒸気の破過吸着テストを行なつた。結果は第
2表の通りである。
実施例 3
実施例1の活性炭A(16〜24mesh)に
NH4SCNを5、10、50、100、200、400、500お
よび550mg/g担持し110℃で乾燥した。
このようにして得られた吸着剤の各6mlを1.5
cmφのガラス製カラムに充填して、水銀蒸気9
mg/m3の30℃のガス(N2−84.8vol%、O2−14.5vol
%、H2O−0.7vol%)を線流速40cm/secで300時
間流通した後、各吸着剤に吸着された水銀吸着量
を測定しその結果を第3表に示した。[Table] Example 2 Adsorbents B to E and b to e of Example 1 were further loaded with 100 mg/g of sulfuric acid and dried at 110°C (adsorbents B 1 to E 1 and b 1 to e 1 ). The thus obtained adsorbents A to E, B 1 to
6 ml each of E 1 , b to e, and b 1 to e 1 was packed into a 1.6 cmφ glass column, and nitrogen gas at 30°C containing 9 mg/m 3 of mercury vapor was passed through at a linear flow rate of 40 cm/sec.
A breakthrough adsorption test for mercury vapor was conducted. The results are shown in Table 2. Example 3 Activated carbon A (16-24mesh) of Example 1
5, 10, 50, 100, 200, 400, 500 and 550 mg/g of NH 4 SCN were supported and dried at 110°C. 1.5 ml of each 6 ml of the adsorbent thus obtained
Packed into a cmφ glass column, mercury vapor 9
mg/m 3 of gas at 30 °C (N 2 −84.8 vol %, O 2 −14.5 vol
%, H 2 O-0.7 vol %) at a linear flow rate of 40 cm/sec for 300 hours, the amount of mercury adsorbed on each adsorbent was measured, and the results are shown in Table 3.
【表】【table】
【表】
実施例 4
実施例1の活性炭A(16〜24mesh)に
NH4SCNを125mg/g担持し、110℃で乾燥した。
これにさらに、硫酸、リン酸、シユウ酸、クエン
酸をそれぞれ50mg/g担持し、110℃で乾燥した。
このようにして調製された吸着剤の各6mlを
1.6cmφのガラス製カラムに充填し、水銀蒸気9
mg/m3含有の30℃窒素ガスを線流速40cm/secで
流通し、水銀蒸気の破過吸着テストを行なつた。
結果は、第4表の通りである。[Table] Example 4 Activated carbon A (16-24mesh) of Example 1
125 mg/g of NH 4 SCN was supported and dried at 110°C.
Furthermore, 50 mg/g of each of sulfuric acid, phosphoric acid, oxalic acid, and citric acid were supported and dried at 110°C. Each 6 ml of the adsorbent thus prepared was
Packed into a 1.6 cmφ glass column, mercury vapor 9
A breakthrough adsorption test for mercury vapor was conducted by flowing nitrogen gas containing mg/m 3 at 30°C at a linear flow rate of 40 cm/sec.
The results are shown in Table 4.
【表】
実施例 5
実施例2の吸着剤B〜EおよびB1〜E1の各6
mlを1.6cmφのガラス製カラムに充填して、水銀
蒸気1mg/m3含有の30℃の水素ガスを線流速40
cm/secで流通し、水銀蒸気の破過吸着テストを
行なつた。その結果を第5表に示した。[Table] Example 5 Each 6 of adsorbents B to E and B 1 to E 1 of Example 2
ml was packed into a 1.6 cmφ glass column, and hydrogen gas at 30°C containing 1 mg/ m3 of mercury vapor was applied at a linear flow rate of 40°C.
cm/sec, and a breakthrough adsorption test for mercury vapor was conducted. The results are shown in Table 5.
Claims (1)
酸アンモニウム、硫化アンモニウム、スルフアミ
ン酸アンモニウムの少なくとも一つを担持してな
る水銀蒸気吸着剤。 2 チオシアン酸アンモニウム、チオ硫酸アンモ
ニウム、硫化アンモニウム、スルフアミン酸アン
モニウムの少なくとも一つと共に不揮発性酸を担
持してなる特許請求の範囲第1項記載の水銀蒸気
吸着剤。[Scope of Claims] 1. A mercury vapor adsorbent comprising activated carbon supporting at least one of ammonium thiocyanate, ammonium thiosulfate, ammonium sulfide, and ammonium sulfamate. 2. The mercury vapor adsorbent according to claim 1, which carries a nonvolatile acid together with at least one of ammonium thiocyanate, ammonium thiosulfate, ammonium sulfide, and ammonium sulfamate.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57013893A JPS58131132A (en) | 1982-01-29 | 1982-01-29 | Adsorbent for mercury vapor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57013893A JPS58131132A (en) | 1982-01-29 | 1982-01-29 | Adsorbent for mercury vapor |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS58131132A JPS58131132A (en) | 1983-08-04 |
JPH0157617B2 true JPH0157617B2 (en) | 1989-12-06 |
Family
ID=11845856
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP57013893A Granted JPS58131132A (en) | 1982-01-29 | 1982-01-29 | Adsorbent for mercury vapor |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS58131132A (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007012836A (en) * | 2005-06-30 | 2007-01-18 | Rohm Co Ltd | Method of manufacturing solid-state electrolytic capacitor |
JP4491688B2 (en) * | 2005-09-08 | 2010-06-30 | 日立造船株式会社 | Production inhibitor and production inhibition method for chlorinated aromatic compounds |
EP2611533A1 (en) * | 2010-08-30 | 2013-07-10 | Albemarle Corporation | Improved sorbents for removing mercury from emissions produced during fuel combustion |
-
1982
- 1982-01-29 JP JP57013893A patent/JPS58131132A/en active Granted
Also Published As
Publication number | Publication date |
---|---|
JPS58131132A (en) | 1983-08-04 |
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