JPS5976537A - Adsorbent for mercury vapor - Google Patents
Adsorbent for mercury vaporInfo
- Publication number
- JPS5976537A JPS5976537A JP57186990A JP18699082A JPS5976537A JP S5976537 A JPS5976537 A JP S5976537A JP 57186990 A JP57186990 A JP 57186990A JP 18699082 A JP18699082 A JP 18699082A JP S5976537 A JPS5976537 A JP S5976537A
- Authority
- JP
- Japan
- Prior art keywords
- activated carbon
- mercury vapor
- oxide
- salt
- adsorbent
- 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
Links
Abstract
Description
【発明の詳細な説明】 本発明は、ガス中の水銀蒸気吸着剤に関する。[Detailed description of the invention] The present invention relates to mercury vapor adsorbents in gases.
111、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L)る
ことか多い
?i解水素は、医薬品9食品、その他の製品を製造する
プロセスに使用され、#’jk11.の水銀蒸気が触媒
毒となったシ、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。111. Does hydrogen gas, natural gas, incinerator exhaust gas, and exhaust gas from factories that handle mercury often contain mercury vapor? i Hydrogen is used in the process of manufacturing pharmaceuticals, 9 foods, and other products, and #'jk11. Mercury vapor can become a catalyst poison and contaminate products, causing problems. 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.
したがってこれらガス中の水銀蒸気は、何らかの処理に
よって除去しなけれはならない。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
らしているが、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との欠点がある。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。Therefore, mercury vapor in these gases must be removed by some kind of treatment. Until now, methods for removing mercury from gas have been known, such as the chemical cleaning method and the dry adsorption method using adsorbents such as activated carbon and ion exchange resin. The disadvantages are that the removal efficiency of mercury vapor is insufficient and that no waste liquid is produced. The latter dry adsorption method has a small adsorption capacity for mercury vapor and is not fully satisfactory.
本発明者らは、このような事情に鑑み、(1■(々研究
した結果、ヨウ素の酸化物またはそれに対応する酸素酸
あるいはその塩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
とを見出した。In view of these circumstances, the present inventors have conducted extensive research and found that activated carbon supporting iodine oxide or its corresponding oxygen acid or its salt efficiently adsorbs mercury vapor in gas. It was found that the adsorption capacity was extremely large.
すなわち本発明は、活性炭にヨウ素の酸化物またはそれ
に対応する酸素酸あるいはその塩(以Fヨウ素含有成分
ということもある)を担持せしめてなる水銀蒸気吸着剤
である。That is, the present invention is a mercury vapor adsorbent in which activated carbon supports an oxide of iodine, an oxygen acid corresponding thereto, or a salt thereof (hereinafter also referred to as F-iodine-containing component).
本発明において使用される活性炭は、木炭、コ−クス、
ヤシガラ樹脂などを原料とした公知の方法により製造さ
れたもので、その比表面積が200〜2000 nfl
yのものであれば、いかなるものでもよい。Activated carbon used in the present invention includes charcoal, coke,
It is manufactured by a known method using coconut husk resin as a raw material, and its specific surface area is 200 to 2000 nfl.
Any item may be used as long as it is y.
木フ【3明において用いられるヨウ素の酸化物としては
jことえ(li1205 、 102などが、ヨウ素の
酸化42rに対応する酸素酸としてはたとえばHIO2
゜D I 03などが、また該酸素酸の塩としてはたと
えば)訃すウム、カリウムなどのアルカリ金属との塩、
マグネシウム、カルシウム、ストロンチウムなどのアル
カリ土類金属との塩、アンモニウムとの塩、具体的には
N a I 02 、K I 02 + Na 103
! K 1035N114103.Mg(IO3)z
、 Ca(1(1+)z 、5r(IO3)2゜NFl
、IO4、Kio4. NI]4104などがあけられ
る。Examples of iodine oxides used in the oxidation process include li1205, 102, etc., and oxygen acids corresponding to the 42r oxidation of iodine include, for example, HIO2.
゜D I 03, etc., and the salts of the oxygen acids include, for example) salts with alkali metals such as aluminum and potassium;
Salts with alkaline earth metals such as magnesium, calcium, and strontium, salts with ammonium, specifically Na I 02 , K I 02 + Na 103
! K 1035N114103. Mg(IO3)z
, Ca(1(1+)z ,5r(IO3)2゜NFl
, IO4, Kio4. NI]4104 etc. can be opened.
本発明におけるヨウ素含有成分の活性炭への担4鍾1目
よ活性炭1f当シヨウ素として5〜500 my、好ま
しくは10〜400〜である。In the present invention, the loading of the iodine-containing component onto activated carbon is from 5 to 500 my, preferably from 10 to 400, as iodine per 1f of activated carbon.
本発明の水銀蒸気吸着剤は活性炭に上記ヨウ素含1成分
の他、■NH,,Na、i<、Mg、caまたはSrの
チオシアン酸塩、チオ硫酸塩、スルファミン酸塩または
硫化物あるいは単体イオウ(以下硫黄成分ということも
ある)、■硫酸、硝酸、リン酸。The mercury vapor adsorbent of the present invention contains activated carbon, in addition to the above-mentioned iodine-containing component, thiocyanate, thiosulfate, sulfamate or sulfide of NH, Na, i<, Mg, ca or Sr, or elemental sulfur. (hereinafter also referred to as sulfur components), ■ Sulfuric acid, nitric acid, phosphoric acid.
シュウ酸、クエン酸などの酸(以下酸成分ということも
ある)、■AI、V、Fe、Co、Ni、Cu、Znま
たはアンモニウムの硫酸塩オたは硝酸塩(以下無4シη
塩成分ということもある)および■K 、 Na 4た
はNH4の邸化物またはヨウ化物(以下ハロゲン化物成
分ということもある)から、iIdばれた成分の1種以
上を担持せしめたものでもよい。上記硫黄成分としては
、たとえば単体硫黄、たとえばト旧4SCN、Na5C
N、KSCN、Mg(SCN)2 、Ca(SCN)2
゜5r(SCN)2 などのチオシアン酸塩、たとえ
ば(NH4) 2520g 、 Na2S203t K
2SzO+ 、Mg5203. Ca 52031Sr
S203などのチオ硫酸塩、たとえばNH40S02N
H2゜Na05OzNHz 、 KO302NH2、
Mp:(O802NH2)2 。Acids such as oxalic acid and citric acid (hereinafter also referred to as acid components), ■AI, V, Fe, Co, Ni, Cu, Zn or ammonium sulfates or nitrates (hereinafter referred to as acid components)
It may be one in which one or more of the following components are supported: (also referred to as a salt component) and (ii) a compound or iodide of K, Na4, or NH4 (hereinafter also referred to as a halide component). The above-mentioned sulfur component includes, for example, elemental sulfur, such as old 4SCN, Na5C
N, KSCN, Mg(SCN)2, Ca(SCN)2
Thiocyanates such as ゜5r(SCN)2, e.g. (NH4) 2520g, Na2S203t K
2SzO+, Mg5203. Ca 52031Sr
Thiosulfates such as S203, e.g. NH40S02N
H2゜Na05OzNHz, KO302NH2,
Mp: (O802NH2)2.
Ca (O502NII2)2 、 S r (050
2NII2 )2 などのスルファミン酸塩、たとえ
は(NH4)2S 、 Na2S 、 K2S 、 i
N4g S 。Ca (O502NII2)2, S r (050
2NII2)2, such as (NH4)2S, Na2S, K2S, i
N4gS.
CaS 、 SrSなどの硫化物などがあげられる。上
記酸成分としてはたとえば硫酸、硝酸、リン酸、シュウ
酸、クエン酸などがあげられる。上記無機塩1ノ+−分
としては(NH4)2504 、A12(504)3
、 VO3O4。Examples include sulfides such as CaS and SrS. Examples of the acid components include sulfuric acid, nitric acid, phosphoric acid, oxalic acid, and citric acid. As for the above inorganic salt, (NH4)2504, A12(504)3
, VO3O4.
FeSO4,Fe2(804)3.CoSO4,NiS
O4,CuSO4゜7nSO+などの硫酸用、NH4N
O3、Al(NO3)3 。FeSO4, Fe2 (804)3. CoSO4, NiS
For sulfuric acid such as O4, CuSO4゜7nSO+, NH4N
O3, Al(NO3)3.
VOO103)2. Fe(N□+)2. Fe(NO
3)3.Co(NO3)21阻(NO3)2 、Cu(
NO3)2. Zn (NO3)2 などの硝酸J島が
あげられる。VOO103)2. Fe(N□+)2. Fe(NO
3)3. Co(NO3)21-(NO3)2, Cu(
NO3)2. Examples include nitric acid J islands such as Zn (NO3)2.
、これらの成分を担持するとき、その担持h1は活性炭
11当りいずれも500−以下、好ましくは10〜40
0町である。, when supporting these components, the supporting h1 is less than 500, preferably 10 to 40 per 11 activated carbons.
There are 0 towns.
本発明に係る水ρ1!蒸気II・冒A剤を片・す造する
に際し、活性炭にヨウ素3イ〕成分、また必要によシ硫
黄成分、酸成分、無1!r淵成分、ハロゲン化物成分を
担持させるには、たとえば、これら担持させようとする
成分を共に水または溶媒に溶解するか、または懸濁し、
これを活性炭に含浸または散布し、必建に応じて乾燥ま
たは焼成する方法などが挙げられる。Water ρ1 according to the present invention! When preparing steam II and Acid-containing agents, the activated carbon contains 3 iodine components, and also contains no sulfur components, no acid components, and 1! In order to support the r-fuchi component and the halide component, for example, these components to be supported are both dissolved or suspended in water or a solvent,
Examples include a method of impregnating or scattering activated carbon with this and drying or firing it as required.
且だ各成分は個別に担持せしめてもよく、この場合担持
せしめる順序は、いずれでもよい。In addition, each component may be supported individually, and in this case, the order in which they are supported may be arbitrary.
本発明の水銀蒸気吸着剤は活性炭にヨウ素含有成分のみ
を担持しているものでも高い水銀蒸気吸着効率および吸
着容量など良好な吸着効果を示すが、さらにこれに加え
て前記0)〜■の硫黄成分。The mercury vapor adsorbent of the present invention exhibits good adsorption effects such as high mercury vapor adsorption efficiency and adsorption capacity even when activated carbon supports only iodine-containing components, but in addition to this, the sulfur component.
酸成分、無機塩成分およびハロゲン化物成分の1種以上
を担持しているものの方がいっそう効果がよく、該■〜
■の成分のうち多種の成分を含むものほど効果がよい。Those that support one or more of acid components, inorganic salt components, and halide components are even more effective;
Among the ingredients in (2), those containing a greater variety of ingredients are more effective.
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
ましくは一10〜120℃で、接紳圧力は50〜以下、
好寸しくは01〜85 %Iで、接触時間は25’C1
%換弁′でV10〜30秒、好ましくは]/′15〜2
0秒である。また、木!it)若剤と水銀族気含有ガス
との接fφ1(は、たとえに1.固定Jffi 、移動
層、流動層などを用いて行なうことができる。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 50 to 120°C.
Preferably 01-85% I, contact time 25'C1
V10 to 30 seconds at % exchange valve', preferably ]/'15 to 2
It is 0 seconds. Also, trees! it) The contact fφ1 (of the young agent and the mercury group gas-containing gas) can be carried out using, for example, 1. a fixed Jffi, a moving bed, a fluidized bed, etc.
実施例1゜
BET表面積1280 rrl / f O) 16〜
24 meshの活性炭Aoに所定h(のヨウ素の酸化
物(第一成分)。Example 1゜BET surface area 1280 rrl/f O) 16~
24 mesh of activated carbon Ao with a predetermined amount of iodine oxide (first component).
所定風の硫酸塩または硝酸塩(第二成分)および所定量
のイオウ、チ副シアン酸塩、チオ硫酸塩。A specified amount of sulfate or nitrate (second component) and a specified amount of sulfur, thiocyanate, thiosulfate.
1+’1f115物、スルファミンrr;>、t= (
第三成分)を含有すイ、水j、′(散まtこはj、“褥
1脂代を均一に11(布し、担持しtこ彷120℃で乾
ヅ!5′81.た(吸着へIB〜S)。1+'1f115, sulfamine rr;>, t= (
Spread the amount of fat evenly on a cloth and dry at 120°C for 5'81. (IB to S to adsorption).
なお、対照として活性炭んに第二成分1.li独。In addition, as a control, the second component 1. Li alone.
hj(正、成分11.1.X、+5(およびヨウ化水を
前記と同様に所ンド111担持し、120°Cで乾燥し
た(吸着剤Al〜Al6)。hj (positive, component 11.1.
このようにしてf!#られだ吸着剤A、0−A、6 、
I3〜Sの各6 +++i!う腓G cm ’!’の
ガラス製カラムに充填し、zlc≦1Viヨ(1:(気
gmP/イ含’j’jcl) 25uの窒素ガスを線流
速40 tc奉’で流、ij+i L、水j?:4AI
’;気のIσ、7;l;f、lIノ、けiテストを行7
Jつだ結果は、第り表のji+1りでチ2る。In this way f! #Radar adsorbent A, 0-A, 6,
Each 6 from I3 to S +++i! G cm'! Packed into a glass column with zlc≦1Viyo (1: (air gmP/I included 'j'jcl) 25u of nitrogen gas was flowed at a linear flow rate of 40tc, ij + i L, water j?: 4AI
';Iσ, 7;l;f,lIノ,kei test line 7
The result is ji + 1 in the table below.
この結果から、)鵠性炭にfH’、45−成分を担持し
たものはすぐれた水ii1:I!順気吸t:ff17i
!lであることがわかる。From this result, it can be seen that) the charcoal carrying fH', 45-component is an excellent water ii1:I! Junki intake t:ff17i
! It turns out that it is l.
宜だ活性炭に2F二成分単独−または第三成分単独を4
川5しても水銀乞噸気を吸椙する能力が著しく悪く、こ
れらの成分と第一成分との複合成分を担稍ずろと、非常
にすぐれた水銀蒸気吸ね能力を発揮することがわかる。2F two components alone or the third component alone on Ida activated carbon
It can be seen that even in river 5, the ability to absorb mercury vapor is extremely poor, and when a composite component of these components and the first component is added, it exhibits an extremely excellent ability to absorb mercury vapor. .
実施例2゜
実施例1.の吸着剤A2+ A6 A6+ A91 A
I、+A14+ 13 +C,F、、I、J、八4.
Pおよび1への名6 mgを1.6σφのガラス製カラ
ムに充損し、水jliQX+、+1気1φl含11の2
肛の水素ガスを線流速40偲/蹴で流3mj1..、水
銀蒸気の破過吸着テストを行ない結果を第2表に示した
。Example 2゜Example 1. Adsorbent A2+ A6 A6+ A91 A
I, +A14+ 13 +C,F,,I,J,84.
Fill a 1.6σφ glass column with 6 mg of P and 1, and add 11 of 2 mg containing 1φl of water.
Flow hydrogen gas in the anus at a linear flow rate of 40 mj/kick to 3 mj1. .. A mercury vapor breakthrough adsorption test was conducted and the results are shown in Table 2.
実IJiii、例3゜
実77i1i、例1.の吸着剤へ、2* A41 A6
1 A91 A、+21 Al418 +C,I”、
I、 J、 M、 l)およびRの各6 rnfを1.
6(至)φのガラス製カラムに充損し、水銀蒸気に〜含
有の25’COガス(N2B4Bvo196゜02−1
4..5v01% 、H2O−0,7v01% ) を
線流速41)I′−nV/′srcて流通し、水銀蒸気
の破過吸佑テストを行なった。その結果は、第8表の通
りである。Real IJiii, Example 3゜ Real 77i1i, Example 1. to adsorbent, 2* A41 A6
1 A91 A, +21 Al418 +C, I”,
I, J, M, l) and R each 6 rnf to 1.
A glass column of 6 (up to) φ was filled with 25'CO gas (N2B4Bvo196°02-1) containing mercury vapor.
4. .. 5v01%, H2O-0.7v01%) was passed through the tube at a linear flow rate of 41) I'-nV/'src, and a breakthrough absorption test for mercury vapor was conducted. The results are shown in Table 8.
(以下金白) □I 第8表(hereinafter referred to as “Kinpaku”) □I Table 8
Claims (1)
:?、+′、酸あるいはその塩を担持せしめてなる水銀
蒸気吸着剤。Activated carbon with iodine oxide or its corresponding i”i:
:? , +', a mercury vapor adsorbent on which an acid or its salt is supported.
Priority Applications (5)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57186990A JPS5976537A (en) | 1982-10-25 | 1982-10-25 | Adsorbent for mercury vapor |
AU15801/83A AU559284B2 (en) | 1982-07-08 | 1983-06-15 | Adsorption of mercury vapour |
GB08316616A GB2122916B (en) | 1982-07-08 | 1983-06-17 | Mercury vapour separation |
US06/509,232 US4500327A (en) | 1982-07-08 | 1983-06-28 | Process for removal of mercury vapor and adsorbent therefor |
NLAANVRAGE8302430,A NL190104C (en) | 1982-07-08 | 1983-07-07 | METHOD FOR REMOVING MERCURY VAPOR FROM A GAS AND ADDRESSING PRINCIPLE THEREFOR. |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP57186990A JPS5976537A (en) | 1982-10-25 | 1982-10-25 | Adsorbent for mercury vapor |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5976537A true JPS5976537A (en) | 1984-05-01 |
JPH0159009B2 JPH0159009B2 (en) | 1989-12-14 |
Family
ID=16198268
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP57186990A Granted JPS5976537A (en) | 1982-07-08 | 1982-10-25 | Adsorbent for mercury vapor |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5976537A (en) |
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US6953494B2 (en) | 2002-05-06 | 2005-10-11 | Nelson Jr Sidney G | Sorbents and methods for the removal of mercury from combustion gases |
KR100760236B1 (en) | 2006-02-28 | 2007-10-04 | 한국과학기술연구원 | Mercury control process from flue gas by halogenated compounds-impregnated activated carbon |
JP2008238163A (en) * | 2007-03-01 | 2008-10-09 | Japan Enviro Chemicals Ltd | Removal method of mercury vapor in gas |
JP2010162520A (en) * | 2009-01-19 | 2010-07-29 | Babcock Hitachi Kk | Denitrification device |
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US9884286B2 (en) | 2010-02-04 | 2018-02-06 | ADA-ES, Inc. | Method and system for controlling mercury emissions from coal-fired thermal processes |
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-
1982
- 1982-10-25 JP JP57186990A patent/JPS5976537A/en active Granted
Cited By (23)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6953494B2 (en) | 2002-05-06 | 2005-10-11 | Nelson Jr Sidney G | Sorbents and methods for the removal of mercury from combustion gases |
KR100760236B1 (en) | 2006-02-28 | 2007-10-04 | 한국과학기술연구원 | Mercury control process from flue gas by halogenated compounds-impregnated activated carbon |
JP2008238163A (en) * | 2007-03-01 | 2008-10-09 | Japan Enviro Chemicals Ltd | Removal method of mercury vapor in gas |
JP2010162520A (en) * | 2009-01-19 | 2010-07-29 | Babcock Hitachi Kk | Denitrification device |
US10427096B2 (en) | 2010-02-04 | 2019-10-01 | ADA-ES, Inc. | Method and system for controlling mercury emissions from coal-fired thermal processes |
US10843130B2 (en) | 2010-02-04 | 2020-11-24 | ADA-ES, Inc. | Method and system for controlling mercury emissions from coal-fired thermal processes |
US11213787B2 (en) | 2010-02-04 | 2022-01-04 | ADA-ES, Inc. | Method and system for controlling mercury emissions from coal-fired thermal processes |
US9884286B2 (en) | 2010-02-04 | 2018-02-06 | ADA-ES, Inc. | Method and system for controlling mercury emissions from coal-fired thermal processes |
US11298657B2 (en) | 2010-10-25 | 2022-04-12 | ADA-ES, Inc. | Hot-side method and system |
US10124293B2 (en) | 2010-10-25 | 2018-11-13 | ADA-ES, Inc. | Hot-side method and system |
US9657942B2 (en) | 2010-10-25 | 2017-05-23 | ADA-ES, Inc. | Hot-side method and system |
US10730015B2 (en) | 2010-10-25 | 2020-08-04 | ADA-ES, Inc. | Hot-side method and system |
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