JP2636926B2 - Method for removing zinc chloride from flue gas - Google Patents

Method for removing zinc chloride from flue gas

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Publication number
JP2636926B2
JP2636926B2 JP1033181A JP3318189A JP2636926B2 JP 2636926 B2 JP2636926 B2 JP 2636926B2 JP 1033181 A JP1033181 A JP 1033181A JP 3318189 A JP3318189 A JP 3318189A JP 2636926 B2 JP2636926 B2 JP 2636926B2
Authority
JP
Japan
Prior art keywords
zinc chloride
gas
flue gas
exhaust gas
combustion exhaust
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 - Fee Related
Application number
JP1033181A
Other languages
Japanese (ja)
Other versions
JPH02211221A (en
Inventor
淳史 鳥井
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.)
NIPPON GAISHI KK
Original Assignee
NIPPON GAISHI KK
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 NIPPON GAISHI KK filed Critical NIPPON GAISHI KK
Priority to JP1033181A priority Critical patent/JP2636926B2/en
Publication of JPH02211221A publication Critical patent/JPH02211221A/en
Application granted granted Critical
Publication of JP2636926B2 publication Critical patent/JP2636926B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は亜鉛化合物を含有する、各種産業廃棄物等を
焼却する際に生ずる燃焼排ガス中の塩化亜鉛除去方法に
関するものである。
Description: TECHNICAL FIELD The present invention relates to a method for removing zinc chloride from combustion exhaust gas generated when incinerating various industrial wastes containing a zinc compound.

(従来の技術) 焼却炉の燃焼排ガス中に含まれる塩化亜鉛を乾式によ
り除去するには、活性炭等の吸着剤で吸着除去する方法
が考えられるが、約150℃以上の排ガス中の塩化亜鉛を
効果的に吸着できる吸着剤は開発されていない。また、
燃焼排ガスを冷却して塩化亜鉛を凝縮させ、発生したダ
ストをフィルタで除去する方法が考えられるが、塩化亜
鉛は固体でも蒸気圧を持ちその飽和蒸気圧以下にするこ
とは困難であるため、一部が気体のままフィルタを通過
して大気中に放出されて環境を汚染することになる。特
に焼却炉の燃焼排ガスのように冷却すると酸が結露して
配管が腐食するおそれのある場合には燃焼排ガスを150
℃以下にまで冷却することができないため、多量の塩化
亜鉛が大気中に放出され環境を汚染することとなる。更
に、大気中に放出された際には塩化亜鉛が冷却されてダ
スト化し、ダスト化した塩化亜鉛やそれを核として凝縮
した水分が白煙として観測され、問題となるおそれもあ
る。また排ガス中の酸の結露が考えられない場合でも過
度のガス冷却は設備費用を大きくする原因となり、好ま
しいことではない。
(Prior art) In order to remove zinc chloride contained in the combustion exhaust gas of an incinerator by dry method, a method of adsorbing and removing it with an adsorbent such as activated carbon may be considered. Adsorbents that can be effectively adsorbed have not been developed. Also,
A method of cooling the combustion exhaust gas to condense the zinc chloride and remove the generated dust with a filter can be considered. The part passes through the filter as a gas and is released into the atmosphere, polluting the environment. In particular, when cooling such as the flue gas of an incinerator may cause condensation of the acid and cause corrosion of the piping, the flue gas is
Since it cannot be cooled down to below ℃, a large amount of zinc chloride is released into the atmosphere and pollutes the environment. Furthermore, when released into the atmosphere, zinc chloride is cooled and turned into dust, and dusted zinc chloride and water condensed by using it as nuclei are observed as white smoke, which may cause a problem. Excessive gas cooling also increases equipment costs, even when condensation of the acid in the exhaust gas cannot be considered, which is not preferable.

(発明が解決しようとする課題) 本発明は上記のような従来の問題を解決して、燃焼排
ガス中に含まれる塩化亜鉛を乾式法により従来の1/10程
度の濃度となるまで効率良く除去することができるとと
もに、配管中に酸の結露を生ずるおそれもない燃焼排ガ
ス中の塩化亜鉛除去方法を目的として完成されたもので
ある。
(Problems to be Solved by the Invention) The present invention solves the above-mentioned conventional problems, and efficiently removes zinc chloride contained in flue gas by a dry method until the concentration becomes about 1/10 of the conventional concentration. The present invention has been completed for the purpose of a method for removing zinc chloride from flue gas which does not cause dew condensation of acid in piping.

(課題を解決するための手段) 本発明は、塩化亜鉛を含有する燃焼排ガス中にSOx
スを添加し、燃焼排ガス温度を400℃以下に保持して硫
酸亜鉛を形成させたうえでフィルタにより捕集すること
を特徴とするものである。
(SUMMARY for a) the invention, the filter in terms of the addition of SO x gas in the combustion exhaust gas containing zinc chloride, to form a zinc sulfate to hold the flue gas temperature to 400 ° C. or less It is characterized by collecting.

以下に本発明を第1図を参照しつつ更に詳細に説明す
ると、(1)は焼却炉、(2)は冷却器、(3)は電気
集塵器、バグフィルタ、HEPAフィルタ等の集塵器であ
る。燃焼排ガス中には集塵器(3)の前段に設けられた
導入口(4)からSOxガスが導入される。SOxガスはガス
ボンベから導入しても、発煙硫酸の加熱、硫酸の加熱等
の手段によって発生させてもよいが、SOxガスの添加は
集塵器(3)の前段であればどの位置において行われて
もよいので、例えば焼却炉中で硫黄分を含有する可燃物
を燃焼させてSOxガスを発生させてもよい。このように
して燃焼排ガス中にSOxガスが添加されると硫酸亜鉛が
形成される。
Hereinafter, the present invention will be described in more detail with reference to FIG. 1. (1) is an incinerator, (2) is a cooler, (3) is a dust collector such as an electric dust collector, a bag filter, and a HEPA filter. It is a vessel. SO x gas is introduced from the introduction port provided in front of the dust collector is in the combustion exhaust gas (3) (4). The SO x gas may be introduced from a gas cylinder or may be generated by heating fuming sulfuric acid, heating sulfuric acid, or the like, but the SO x gas may be added at any position before the dust collector (3). since may be performed, for example, combustible materials containing sulfur in incinerator by burning may generate sO x gases. Thus when SO x gas is added zinc sulfate is formed and in the combustion exhaust gas to.

SOxガスの添加量は反応当量以上とする必要があり、
塩化亜鉛1.0mgに対してSO2は0.47mg以上、SO3は0.59mg
以上とすればよい。しかしSOx濃度があまり高すぎると
配管等の腐食やSOxの放出による環境汚染のおそれがあ
るため、通常は集塵器(3)の入口のSOx濃度が集塵器
(3)によって塩化亜鉛を除去することができる100〜1
000ppmに保たれるようにSOxを供給すればよい。なお燃
焼排ガス中に必要に応じてH2OやO2を供給してもよい。
このようにして塩化亜鉛とSOxが反応すると0.1〜1.0秒
程度のごく短時間で硫酸亜鉛が形成されるが、硫酸亜鉛
は740℃で分解するために740℃以下とする必要があるう
えに、400℃以上の高温では塩化亜鉛の飽和蒸気圧が高
く、一部の塩化亜鉛が未反応のまま残留するため、燃焼
排ガス温度を400℃以下に保持するものとする。このよ
うにして形成された硫酸亜鉛は集塵器によってダストと
して除去される。
The amount of SO x gas added must be equal to or higher than the reaction equivalent,
SO 2 is 0.47mg or more with respect to zinc chloride 1.0 mg, SO 3 is 0.59mg
That is all. However, since the SO x concentration is a risk of environmental pollution due to the release of corrosion and SO x such as piping and excessively high, usually chloride SO x concentration at the inlet of the dust collector (3) is precipitator by (3) 100-1 which can remove zinc
It may be supplied SO x so as to maintain the 000 ppm. Note that H 2 O or O 2 may be supplied to the combustion exhaust gas as needed.
When zinc chloride reacts with SO x in this way, zinc sulfate is formed in a very short time of about 0.1 to 1.0 seconds, but zinc sulfate must be kept at 740 ° C. or lower to decompose at 740 ° C. At a high temperature of 400 ° C. or higher, the saturated vapor pressure of zinc chloride is high, and some of the zinc chloride remains unreacted. Therefore, the temperature of the combustion exhaust gas is maintained at 400 ° C. or lower. The zinc sulfate thus formed is removed as dust by the dust collector.

(実施例) 第1図に示される装置として、排ガス冷却器(2)を
空気混合器、集塵器(3)をHEPAフィルタとしたものを
用い、導入口(4)から種々の濃度のSO2ガスを吹込ん
で集塵器(3)の出口における塩化亜鉛の濃度を測定し
た。集塵器(3)入口の塩化亜鉛の濃度10-2mg/Nl程度
の時、SO2ガスを添加しない場合の集塵器(3)の出口
における塩化亜鉛の濃度は10-4mg/Nl程度であったが、S
O2ガス濃度を100ppmとした場合には集塵器(3)の出口
における塩化亜鉛の濃度は10-5mg/Nl、SO2ガス濃度を25
0ppm以上とすると10-5mg/Nl未満(計器の測定限界以下
のため測定不能)のレベルまで低下した。これを第2図
にグラフとして示す。このように本発明によれば、SOx
を添加しない従来法による場合の1/10以下のレベルまで
燃焼排ガス中から塩化亜鉛を除去することが可能とな
る。また本発明によれば燃焼排ガス温度を400℃以下と
すればよく、酸の結露が生じるおそれのない150〜400℃
の温度範囲内に保つことができるので、配管等を腐食さ
せることもない。
(Example) As an apparatus shown in Fig. 1, an exhaust gas cooler (2) having an air mixer and a dust collector (3) having a HEPA filter was used, and SO2 of various concentrations was introduced from an inlet (4). Two gases were blown, and the concentration of zinc chloride at the outlet of the dust collector (3) was measured. When the concentration of zinc chloride at the inlet of the dust collector (3) is about 10 -2 mg / Nl, the concentration of zinc chloride at the outlet of the dust collector (3) when SO 2 gas is not added is 10 -4 mg / N. N l, but S
O 2 dust collector in the case of the gas concentration of 100 ppm (3) the concentration of zinc chloride at the outlet of 10 -5 mg / N l, the SO 2 gas concentration 25
When more than 0ppm less than 10 -5 mg / N l (instrument measurement limit or less for non-measurable) was reduced to the level of. This is shown graphically in FIG. Thus, according to the present invention, SO x
It is possible to remove zinc chloride from the combustion exhaust gas to a level of 1/10 or less of the case of the conventional method in which no is added. Further, according to the present invention, the temperature of the combustion exhaust gas may be set to 400 ° C. or lower, and 150 to 400 ° C. where there is no possibility that dew condensation of the acid occurs.
Temperature range, so that the pipes and the like are not corroded.

(発明の効果) 以上の説明から明らかなように、本発明は燃焼排ガス
中の塩化亜鉛を乾式法によって従来の1/10以下のレベル
となるまで効率良く除去することができ、しかも配管中
に酸の結露を生じるおそれもないのであるから、各種の
焼却炉から塩化亜鉛が大気中に発散することを防止する
うえで有効なものである。よって本発明は従来の問題点
を一掃した燃焼排ガス中の塩化亜鉛除去方法として、産
業の発展に寄与するところは極めて大である。
(Effects of the Invention) As is clear from the above description, the present invention can efficiently remove zinc chloride in combustion exhaust gas to a level of 1/10 or less of the conventional level by a dry method. It is effective in preventing zinc chloride from escaping into the atmosphere from various incinerators since there is no possibility of dew condensation of the acid. Therefore, the present invention greatly contributes to industrial development as a method for removing zinc chloride from combustion exhaust gas that has eliminated the conventional problems.

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

第1図は本発明に用いられる装置の一例を示すブロック
図、第2図は実施例におけるSO2濃度と塩化亜鉛濃度と
の関係を示すグラフである。 (1):焼却炉、(2):冷却器、(3):集塵器、 (4):導入口。
FIG. 1 is a block diagram showing an example of an apparatus used in the present invention, and FIG. 2 is a graph showing the relationship between the concentration of SO 2 and the concentration of zinc chloride in Examples. (1): incinerator, (2): cooler, (3): dust collector, (4): inlet.

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】塩化亜鉛を含有する燃焼排ガス中にSOx
スを添加し、燃焼排ガス温度を400℃以下に保持して硫
酸亜鉛を形成させたうえでフィルタにより捕集すること
を特徴とする燃焼排ガス中の塩化亜鉛除去方法。
[Claim 1] was added SO x gas in the combustion exhaust gas containing zinc chloride, it holds the flue gas temperature to 400 ° C. or less, characterized in that collected by the filter in terms of to form a zinc sulfate A method for removing zinc chloride from flue gas.
JP1033181A 1989-02-13 1989-02-13 Method for removing zinc chloride from flue gas Expired - Fee Related JP2636926B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1033181A JP2636926B2 (en) 1989-02-13 1989-02-13 Method for removing zinc chloride from flue gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1033181A JP2636926B2 (en) 1989-02-13 1989-02-13 Method for removing zinc chloride from flue gas

Publications (2)

Publication Number Publication Date
JPH02211221A JPH02211221A (en) 1990-08-22
JP2636926B2 true JP2636926B2 (en) 1997-08-06

Family

ID=12379336

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1033181A Expired - Fee Related JP2636926B2 (en) 1989-02-13 1989-02-13 Method for removing zinc chloride from flue gas

Country Status (1)

Country Link
JP (1) JP2636926B2 (en)

Also Published As

Publication number Publication date
JPH02211221A (en) 1990-08-22

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