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JPS602896B2 - Method for removing mercury from smelting exhaust gas - Google Patents
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JPS602896B2 - Method for removing mercury from smelting exhaust gas - Google Patents

Method for removing mercury from smelting exhaust gas

Info

Publication number
JPS602896B2
JPS602896B2 JP55160744A JP16074480A JPS602896B2 JP S602896 B2 JPS602896 B2 JP S602896B2 JP 55160744 A JP55160744 A JP 55160744A JP 16074480 A JP16074480 A JP 16074480A JP S602896 B2 JPS602896 B2 JP S602896B2
Authority
JP
Japan
Prior art keywords
mercury
sulfur
exhaust gas
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
Application number
JP55160744A
Other languages
Japanese (ja)
Other versions
JPS5784722A (en
Inventor
秀来 阿部
洋 田中
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.)
Dowa Holdings Co Ltd
Original Assignee
Dowa Mining 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 Dowa Mining Co Ltd filed Critical Dowa Mining Co Ltd
Priority to JP55160744A priority Critical patent/JPS602896B2/en
Publication of JPS5784722A publication Critical patent/JPS5784722A/en
Publication of JPS602896B2 publication Critical patent/JPS602896B2/en
Expired legal-status Critical Current

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Description

【発明の詳細な説明】 本発明は製錬排ガス例えば亜鉛製錬所における硫化鉱の
焔焼の際に発生する水銀を含有する排ガスから水銀を効
率よくかつ経済的に除去する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for efficiently and economically removing mercury from smelting exhaust gases, such as mercury-containing exhaust gases generated during the incineration of sulfide ores in zinc smelters.

従来製錬排ガス中の水銀の除去法としては、ィ)セレン
と水銀の親和力の大きいことを利用した方法、ロ)金属
硫化物と水銀を反応させる方法、ハ)濃硫酸やニ)チオ
尿素、アミルザンセートカIJなどによるガスの洗浄法
などがあるが、これらには以下のような問題点がある。
Conventional methods for removing mercury from smelting exhaust gas include a) a method that takes advantage of the high affinity between selenium and mercury, b) a method of reacting metal sulfide with mercury, c) concentrated sulfuric acid, d) thiourea, There are gas cleaning methods such as Amilzansetka IJ, but these methods have the following problems.

ィ)のセレンと水銀の親和力を利用した方法例えば金属
セレンを詰めた充填塔に水銀を含有した排ガスを通す方
法においては、金属セレンが高価であるため吸着した水
銀をストリップし、セレンを活性化して再使用する工程
が必要となって繁雑さを伴なう。しかも、セレンは毒性
を有するさめ取り扱いに注意が必要となるずロ)の金属
硫化物を吸収剤とする方法では、金属硫化物をスラリー
としてこれを水銀含有ガスと接触させて水銀を吸収除去
する場合、排ガス中にSQ以外に含まれているS03が
スラリー液に吸収されて酸濃度が増加し、金属硫化物と
反応して日2Sガスが発生してしまう点が問題となる。
b) A method that utilizes the affinity between selenium and mercury. For example, in the method of passing mercury-containing exhaust gas through a packed tower filled with metallic selenium, since metallic selenium is expensive, adsorbed mercury is stripped off and the selenium is activated. This necessitates a process of reuse, which is complicated. In addition, selenium is toxic and must be handled with care.In the method using metal sulfide as an absorbent, the metal sulfide is made into a slurry and brought into contact with a mercury-containing gas to absorb and remove mercury. In this case, the problem is that S03, which is contained in the exhaust gas other than SQ, is absorbed by the slurry liquid, increasing the acid concentration and reacting with metal sulfides to generate 2S gas.

酸化を利用した水銀除去法がいくつあるが、酸化剤を使
用して金属水銀を水銀イオンに酸化して洗浄除去する方
法は大量のS02ガスを含む製錬排ガスには適当ではな
い。また、ハ)の硫酸による洗浄法は、次式の反応によ
ってHg十舷S04十1/202→H$04十比○水銀
をHgS04結晶として析出させ、シックナーによって
分離するものである。
Although there are several methods for removing mercury using oxidation, the method of oxidizing metallic mercury to mercury ions using an oxidizing agent and cleaning and removing it is not suitable for smelting exhaust gas containing a large amount of S02 gas. Further, in the cleaning method using sulfuric acid (c), mercury is precipitated as HgSO4 crystals by the reaction of the following formula, and is separated by a thickener.

しかし、この場合の硫酸濃度は85〜90%であること
が必要であるが、排ガス中に含まれる水分が硫酸濃度を
下げる結果となるために硫酸濃度を維持するには液温を
140〜200℃に制御する必要があり、このように高
温高濃度の硫酸を使用するため装置の材質選定が困鱗と
なる欠点がある。また、ニ)のチオ尿素やアミルザンセ
ートカリのスラリーを吸収液とする方法は、チオ尿素や
アミルザンセートカリが分解して生ずる元素硫黄が水銀
と吸着反応し、HgSとなったものを除去するという原
理である。
However, the sulfuric acid concentration in this case needs to be 85-90%, but since the water contained in the exhaust gas lowers the sulfuric acid concentration, the liquid temperature must be lowered to 140-200% in order to maintain the sulfuric acid concentration. ℃, and the use of high-temperature, high-concentration sulfuric acid has the disadvantage that it is difficult to select the material for the equipment. In addition, in the method (d) using a slurry of thiourea and amylzanthate potash as the absorption liquid, the elemental sulfur produced by the decomposition of thiourea and amylzanthate potash adsorbs and reacts with mercury to remove HgS. The principle is that

ところが、これらの試薬が分解して生ずる元素硫黄量は
試薬量の極く一部に過ぎず、使用試薬量に比して吸着水
銀量は少量で試薬の価格が高いこととあいまって経済的
な方法とは言い難い。そこで、本発明者らは以上のよう
な諸点を改善しかつ高濃度の水銀を含む製錬排ガスを処
理する方法について種々の試験、検討を行なって来た結
果、元素状硫黄の懸濁した溶液が製錬排ガス中の水銀を
吸収・除去するのに極めて有効であることが明らかにな
った。
However, the amount of elemental sulfur produced when these reagents decompose is only a small portion of the amount of reagent, and the amount of mercury adsorbed is small compared to the amount of reagent used, making it difficult to use economically. It's hard to call it a method. Therefore, the present inventors have carried out various tests and studies on methods for improving the above points and treating smelting exhaust gas containing high concentrations of mercury.As a result, we have developed a solution in which elemental sulfur is suspended. was found to be extremely effective in absorbing and removing mercury from smelting exhaust gas.

そして、吸収剤として使用される元素硫黄は活性度の高
いものでなければ高能率の水銀の除去は望めないが、様
々な種類の硫黄について実験を行なったところ、クラウ
ス反応によって生ずるような非常に微細な活性度の高い
元素硫黄が最もこの目的に適していることが確認された
。本発明はクラゥス反応等により生成した極めて微細な
元素状硫黄を含有する溶液を吸収液として水銀を含む製
錬排ガスと接触させて該ガス中の水銀を硫黄に吸着せし
めて水銀を除去する方法において、該吸着反応により生
成する水銀を多量に吸着した高(大)比重の硫黄は湿式
分級により系外に抜出し、未反応硫黄と水銀を若干吸着
している小比重の硫黄は吸収液中に残留させるようにし
たことを特徴とする製錬排ガスからの水銀除去方法に関
するものである。
Elemental sulfur used as an absorbent must have a high degree of activity to remove mercury with high efficiency, but experiments with various types of sulfur have shown that highly active mercury, such as that produced by the Claus reaction, It has been determined that fine, highly active elemental sulfur is most suitable for this purpose. The present invention provides a method for removing mercury by contacting a solution containing extremely fine elemental sulfur produced by the Claus reaction or the like with mercury-containing smelting exhaust gas as an absorbing liquid, and causing the mercury in the gas to be adsorbed by sulfur. The high (large) specific gravity sulfur that adsorbs a large amount of mercury produced by the adsorption reaction is extracted from the system by wet classification, and the unreacted sulfur and the low specific gravity sulfur that has adsorbed some mercury remain in the absorption liquid. The present invention relates to a method for removing mercury from smelting exhaust gas, characterized by:

次に、本発明を工業的に実施するための工程の一例を説
明すると、水銀を含有した製錬排ガスは吸収塔に導かれ
吸収液中の硫黄によって排ガス中の水銀が吸着除去され
る。
Next, an example of a process for industrially implementing the present invention will be described. The mercury-containing smelting exhaust gas is led to an absorption tower, and the mercury in the exhaust gas is adsorbed and removed by the sulfur in the absorption liquid.

吸収塔としてはスプレー塔、充填塔、濡れ棚塔などの装
置が考えられる。水銀を吸着した硫黄を除去して新たな
硫黄と交換するためには、吸収塔を数基設けて水銀吸着
量が大きくなった塔から1風こ吸収塔中の硫黄の全量を
入れ替えるか、もしくは水銀を吸着した硫黄は比重が大
きくなっているのでこの比重の差を利用して湿式分級を
行ない、水銀を大量に吸着したものとそうでないものと
に分別して大量の水銀を吸着した硫黄のみを系外に取り
出す方法がある。後記実施例2において述べるが、この
後者の方法は若干の水銀を吸着した硫黄を吸収塔に残す
ことになるため、硫黄の全量を新しいものと交換する前
者の場合と比べて水銀吸着速度が早くなる。実施例 1
亜硫酸水に硫化水素を吹き込んで得たクラウス硫黄を使
って35夕/その水溶液を作り、これを吸収液として1
そのG−2フィルター付ガス洗浄ビンに流し、洗浄前後
のガス中の水銀濃度を分析したところ第1表の結果を得
た。
As the absorption tower, devices such as a spray tower, a packed tower, and a wet tray tower can be considered. In order to remove sulfur that has adsorbed mercury and replace it with new sulfur, it is necessary to install several absorption towers and replace the entire amount of sulfur in one wind absorption tower from the tower where the amount of mercury adsorption has increased, or Sulfur that has adsorbed mercury has a high specific gravity, so wet classification is performed using this difference in specific gravity to separate sulfur into those that have adsorbed a large amount of mercury and those that have not. There is a way to take it out of the system. As will be described in Example 2 below, this latter method leaves sulfur with some mercury adsorbed in the absorption tower, so the mercury adsorption rate is faster than in the former case where the entire amount of sulfur is replaced with fresh sulfur. Become. Example 1
Using Claus sulfur obtained by blowing hydrogen sulfide into sulfurous acid water, make an aqueous solution of it for 35 minutes and use this as an absorption liquid for 1 hour.
When the gas was poured into a gas cleaning bottle equipped with a G-2 filter and the mercury concentration in the gas was analyzed before and after cleaning, the results shown in Table 1 were obtained.

なお、試験条件は実際の製錬排ガスを想定し、空気量2
0そ/分に亜硫酸ガス1〆/分を添加したものを使用し
た。第1表実施例 2 硫黄製造工場において中間製品として得られるクラウス
硫黄を使って23夕/その溶液を作り、これを吸収液と
して1そのG−2フィルター付ガス洗浄ビンに0.8夕
探つたものを2本準備し、直列につないで水銀含有ガス
を流した。
The test conditions assume actual smelting exhaust gas, and the air amount is 2.
A mixture of 0 sulfur dioxide gas and 1 sulfur dioxide gas added per minute was used. Table 1 Example 2 Using Claus sulfur obtained as an intermediate product at a sulfur manufacturing plant, a solution was prepared for 23 days, and this was poured into a gas washing bottle with a G-2 filter as an absorbent for 0.8 days. Two tubes were prepared, connected in series, and mercury-containing gas was passed through them.

洗浄後のガス中の水銀濃度を分析したところ第1図のグ
ラフに示す結果を得た。なお、試験条件は実施例1と同
じである。第1図のグラフから明らかなように、ガス通
気直後は水銀除去率が低く、硫黄が若干の水銀を吸着し
た時点で水銀の除去率が最大になる。
When the mercury concentration in the gas after cleaning was analyzed, the results shown in the graph of FIG. 1 were obtained. Note that the test conditions are the same as in Example 1. As is clear from the graph in FIG. 1, the mercury removal rate is low immediately after gas ventilation, and the mercury removal rate reaches its maximum when sulfur adsorbs some mercury.

このことから、前記したように水銀を吸着した硫黄を湿
式分級で分別し、若干の水銀を吸着しているに過ぎない
ものは吸収液中に残留させることによって水銀吸着速度
を早くすることができる。実施例 3 実施例2の場合と同様の硫黄製造工場において得られた
クラゥス硫黄を使って60夕/その溶液を作り、これを
吸収液として1夕採り、小規模の充填塔へスプレーして
水銀含有ガスからの水銀除去を行なった。
Therefore, as mentioned above, the rate of mercury adsorption can be increased by separating the sulfur that has adsorbed mercury by wet classification and leaving the sulfur that has adsorbed only a small amount of mercury in the absorption liquid. . Example 3 Using Claus sulfur obtained at the same sulfur manufacturing plant as in Example 2, a solution was prepared for 60 minutes, and this was collected overnight as an absorption liquid, and then sprayed into a small-scale packed column to remove mercury. Mercury was removed from the contained gas.

吸収液の流量は0.3そ/分とし、その他の条件は実施
例1に同じである。充填塔は内法断面4×4仇、充填厚
さは8奴、圧力損失は50〜7仇舷水柱であった。この
ときの結果を第2図のグラフに示す。
The flow rate of the absorption liquid was 0.3 so/min, and the other conditions were the same as in Example 1. The packed tower had an internal cross section of 4 x 4 m, a packing thickness of 8 m, and a pressure loss of 50 to 7 m water columns. The results at this time are shown in the graph of FIG.

【図面の簡単な説明】[Brief explanation of drawings]

第1図及び第2図は硫黄含有吸収液により排ガス中の水
銀を除去した場合の水銀除去率の変化を示すグラフであ
る。 第1図 第2図
FIGS. 1 and 2 are graphs showing changes in mercury removal rate when mercury in exhaust gas is removed using a sulfur-containing absorption liquid. Figure 1 Figure 2

Claims (1)

【特許請求の範囲】[Claims] 1 クラウス反応等により生成した極めて微細な元素状
硫黄を含有する溶液を吸収液として水銀を含む製錬排ガ
スと接触させて該ガス中の水銀を硫黄に吸着せしめて水
銀を除去する方法において、該吸収反応により生成する
水銀を多量に吸着した高比重の硫黄は湿式分級により系
外に抜出し、末反応硫黄と水銀を若干吸着している小比
重の硫黄は吸収液中に残留させるようにしたことを特徴
とする製錬排ガスからの水銀除去方法。
1. A method of removing mercury by contacting a solution containing extremely fine elemental sulfur produced by Claus reaction etc. with mercury-containing smelting exhaust gas as an absorption liquid to cause the mercury in the gas to be adsorbed to sulfur. The high specific gravity sulfur that adsorbs a large amount of mercury produced by the absorption reaction is extracted from the system by wet classification, while the end-reacted sulfur and the low specific gravity sulfur that has adsorbed some mercury remain in the absorption liquid. A method for removing mercury from smelting exhaust gas, characterized by:
JP55160744A 1980-11-17 1980-11-17 Method for removing mercury from smelting exhaust gas Expired JPS602896B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP55160744A JPS602896B2 (en) 1980-11-17 1980-11-17 Method for removing mercury from smelting exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP55160744A JPS602896B2 (en) 1980-11-17 1980-11-17 Method for removing mercury from smelting exhaust gas

Publications (2)

Publication Number Publication Date
JPS5784722A JPS5784722A (en) 1982-05-27
JPS602896B2 true JPS602896B2 (en) 1985-01-24

Family

ID=15721510

Family Applications (1)

Application Number Title Priority Date Filing Date
JP55160744A Expired JPS602896B2 (en) 1980-11-17 1980-11-17 Method for removing mercury from smelting exhaust gas

Country Status (1)

Country Link
JP (1) JPS602896B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0221700A (en) * 1987-12-30 1990-01-24 Sooken:Kk Electronic equipment having function of preventing generation of static electricity and penetration of electromagnetic wave noise

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4764219A (en) * 1986-10-27 1988-08-16 Mobil Oil Corporation Clean up and passivation of mercury in gas liquefaction plants
US4897247A (en) * 1988-05-16 1990-01-30 B. Richard Sacks Treatment of exhaust gases to reduce multi-valent heavy metals
JPH10216476A (en) * 1997-01-31 1998-08-18 Kawasaki Heavy Ind Ltd Exhaust gas treatment method and apparatus

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0221700A (en) * 1987-12-30 1990-01-24 Sooken:Kk Electronic equipment having function of preventing generation of static electricity and penetration of electromagnetic wave noise

Also Published As

Publication number Publication date
JPS5784722A (en) 1982-05-27

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