TWI838069B - Desulfurization method for sulfur-containing tail gas - Google Patents

Desulfurization method for sulfur-containing tail gas Download PDF

Info

Publication number
TWI838069B
TWI838069B TW112100717A TW112100717A TWI838069B TW I838069 B TWI838069 B TW I838069B TW 112100717 A TW112100717 A TW 112100717A TW 112100717 A TW112100717 A TW 112100717A TW I838069 B TWI838069 B TW I838069B
Authority
TW
Taiwan
Prior art keywords
sulfur
gas
hydrogen sulfide
tail gas
alkaline
Prior art date
Application number
TW112100717A
Other languages
Chinese (zh)
Other versions
TW202428885A (en
Inventor
林勳佑
王俊修
游承修
陳永富
Original Assignee
中國鋼鐵股份有限公司
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 中國鋼鐵股份有限公司 filed Critical 中國鋼鐵股份有限公司
Priority to TW112100717A priority Critical patent/TWI838069B/en
Application granted granted Critical
Publication of TWI838069B publication Critical patent/TWI838069B/en
Publication of TW202428885A publication Critical patent/TW202428885A/en

Links

Images

Landscapes

  • Gas Separation By Absorption (AREA)
  • Industrial Gases (AREA)
  • Treating Waste Gases (AREA)

Abstract

一種含硫尾氣的脫硫方法,適用於處理包含硫化氫及二氧化硫的含硫尾氣,且包含步驟(a)將含硫尾氣進行冷卻處理以減少含硫尾氣中的硫化氫及二氧化硫,獲得包含硫化氫及濃度為20ppm以下的二氧化硫的氣體混合物;步驟(b)提供鹼性處理液,且鹼性處理液包含自用於洗滌焦爐氣的脫硫裝置回收得到的經使用的鹼性溶液;步驟(c)使氣體混合物與鹼性處理液在溼式洗滌裝置中接觸,並使氣體混合物中的硫化氫被鹼性處理液吸收,獲得經處理氣體。本發明透過步驟(a)至(c)的搭配,能去除含硫尾氣中的硫化氫並具有節省後續處理成本的優點。A method for desulfurizing sulfur-containing tail gas is applicable to treating the sulfur-containing tail gas containing hydrogen sulfide and sulfur dioxide, and comprises the following steps: (a) cooling the sulfur-containing tail gas to reduce hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas, thereby obtaining a gas mixture containing hydrogen sulfide and sulfur dioxide with a concentration of less than 20 ppm; (b) providing an alkaline treatment liquid, wherein the alkaline treatment liquid comprises a used alkaline solution recovered from a desulfurization device used for scrubbing coke furnace gas; and (c) contacting the gas mixture with the alkaline treatment liquid in a wet scrubbing device, and allowing the hydrogen sulfide in the gas mixture to be absorbed by the alkaline treatment liquid, thereby obtaining treated gas. The present invention can remove hydrogen sulfide in sulfur-containing tail gas through the combination of steps (a) to (c) and has the advantage of saving subsequent treatment costs.

Description

含硫尾氣的脫硫方法Desulfurization method for sulfur-containing tail gas

本發明是有關於一種氣體的分離方法,特別是指一種含硫尾氣的脫硫方法。The present invention relates to a gas separation method, in particular to a desulfurization method for sulfur-containing tail gas.

現有的煉焦製程中往往會伴隨著包含例如硫化氫、氰化氫、二氧化碳等酸性物質及氨氣的粗焦爐氣(crude coke oven gas)產生,即未純化的焦爐氣。焦爐氣(coke oven gas,簡稱COG)是一種可燃性氣體,因此,焦爐氣能夠進一步被作為燃料使用。而為了有效地利用焦爐氣,通常會對該粗焦爐氣進行洗滌以去除該粗焦爐氣中的酸性物質及氨氣,以獲得純度高的焦爐氣。The existing coking process often produces crude coke oven gas containing acidic substances such as hydrogen sulfide, hydrogen cyanide, carbon dioxide and ammonia, i.e., unpurified coke oven gas. Coke oven gas (COG) is a combustible gas, so it can be used as a fuel. In order to effectively utilize the coke oven gas, the crude coke oven gas is usually scrubbed to remove the acidic substances and ammonia in the crude coke oven gas to obtain coke oven gas with high purity.

參閱圖1,對該粗焦爐氣進行洗滌以去除酸性物質的方式例如在一個脫硫裝置91中使用鹼性溶液去除該粗焦爐氣中的酸性物質而產生包含酸性物質的經使用的鹼性溶液,且使該經使用的鹼性溶液經過回收再製處理後產生再製的鹼性溶液及含硫廢氣。該再製的鹼性溶液能夠被輸送回該脫硫裝置91中作為鹼性溶液使用。該含硫廢氣會被導入一個硫磺回收裝置92進行硫磺回收處理獲得硫磺,且同時伴隨產生包含硫化氫及二氧化硫的含硫尾氣。為了避免該含硫尾氣被直接排放至大氣中,通常會將該含硫尾氣與下一批次的粗焦爐氣混合獲得混合物,再將該混合物通入該脫硫裝置91進行處理。但,由於該含硫尾氣中的硫化氫濃度及二氧化硫濃度高,以至於在該鹼性溶液的使用量不變的情況下使用該鹼性溶液對該混合物進行洗滌時,反而會因為洗滌過程中存在的酸性成分的總含量增加,即粗焦爐氣中原有的酸性物質加上含硫尾氣中的硫化氫及二氧化硫,而增加了該脫硫裝置91的洗滌負荷,進而無法於下一批次的處理有效地獲得純度高的焦爐氣。Referring to FIG. 1 , the crude coke furnace gas is scrubbed to remove acidic substances by, for example, using an alkaline solution in a desulfurization device 91 to remove acidic substances in the crude coke furnace gas to produce a used alkaline solution containing acidic substances, and the used alkaline solution is recycled and processed to produce a recycled alkaline solution and sulfur-containing exhaust gas. The recycled alkaline solution can be transported back to the desulfurization device 91 for use as an alkaline solution. The sulfur-containing exhaust gas is introduced into a sulfur recovery device 92 for sulfur recovery processing to obtain sulfur, and at the same time, sulfur-containing tail gas containing hydrogen sulfide and sulfur dioxide is produced. In order to prevent the sulfur-containing tail gas from being directly discharged into the atmosphere, the sulfur-containing tail gas is usually mixed with the next batch of crude coke gas to obtain a mixture, and then the mixture is passed into the desulfurization device 91 for treatment. However, due to the high concentration of hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas, when the alkaline solution is used to wash the mixture without changing the amount of the alkaline solution, the total content of the acidic components present in the washing process will increase, that is, the original acidic substances in the crude coke gas plus the hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas, which increases the washing load of the desulfurization device 91, and thus it is impossible to effectively obtain high-purity coke gas in the next batch of treatment.

基於上述,為了能夠於下一批次的處理獲得純度高的焦爐氣,雖然可以透過大量提升鹼性溶液的使用量來改善上述問題,但,鹼性溶液的使用量提高反而會造成處理成本的增加。Based on the above, in order to obtain high-purity coke furnace gas for the next batch of processing, although the above problem can be improved by greatly increasing the amount of alkaline solution used, the increase in the amount of alkaline solution used will instead increase the processing cost.

因此,本發明的目的,即在提供一種能夠降低成本的含硫尾氣的脫硫方法。Therefore, the purpose of the present invention is to provide a method for desulfurizing sulfur-containing tail gas which can reduce costs.

於是,本發明含硫尾氣的脫硫方法,適用於處理一包含硫化氫及二氧化硫的含硫尾氣,該含硫尾氣的脫硫方法包含一步驟(a)、一步驟(b)及一步驟(c)。Therefore, the desulfurization method of sulfur-containing tail gas of the present invention is applicable to treating a sulfur-containing tail gas containing hydrogen sulfide and sulfur dioxide. The desulfurization method of sulfur-containing tail gas comprises step (a), step (b) and step (c).

該步驟(a)是將該含硫尾氣進行冷卻處理以減少該含硫尾氣中的硫化氫含量及二氧化硫含量,獲得包含硫化氫及濃度為20ppm以下的二氧化硫的氣體混合物,其中,該氣體混合物中的硫化氫含量小於該含硫尾氣中的硫化氫含量。The step (a) is to cool the sulfur-containing tail gas to reduce the hydrogen sulfide content and sulfur dioxide content in the sulfur-containing tail gas, thereby obtaining a gas mixture containing hydrogen sulfide and sulfur dioxide with a concentration of less than 20 ppm, wherein the hydrogen sulfide content in the gas mixture is less than the hydrogen sulfide content in the sulfur-containing tail gas.

該步驟(b)是提供一鹼性處理液,該鹼性處理液包含自脫硫裝置中回收得到的經使用的鹼性溶液,且該脫硫裝置是用於利用含有氫氧化鈉的鹼性溶液對包含焦爐氣的混合物進行洗滌,該經使用的鹼性溶液包括氫氧化鈉。The step (b) is to provide an alkaline treatment solution, wherein the alkaline treatment solution comprises a used alkaline solution recovered from a desulfurization device, and the desulfurization device is used to scrub a mixture containing coke furnace gas with an alkaline solution containing sodium hydroxide, and the used alkaline solution comprises sodium hydroxide.

該步驟(c)是使該氣體混合物與該鹼性處理液在一溼式洗滌裝置中接觸,並使該氣體混合物中的硫化氫被該鹼性處理液吸收,獲得經處理氣體。The step (c) is to make the gas mixture contact with the alkaline treatment liquid in a wet scrubber, and make the hydrogen sulfide in the gas mixture be absorbed by the alkaline treatment liquid to obtain treated gas.

本發明的功效在於:透過該步驟(a)至(c)的搭配,本發明能夠有效地去除含硫尾氣中的硫化氫,因此,該經處理氣體中的硫化氫含量小於該含硫尾氣中的硫化氫含量。The effect of the present invention is that: through the combination of the steps (a) to (c), the present invention can effectively remove hydrogen sulfide in the sulfur-containing tail gas, so that the hydrogen sulfide content in the treated gas is less than the hydrogen sulfide content in the sulfur-containing tail gas.

另一方面,當後續為了不讓該經處理氣體被直接排放至大氣中而將該經處理氣體與下一批次的粗焦爐氣混合時,由於該經處理氣體中的硫化氫含量低,所以能避免該經處理氣體與粗焦爐氣混合得到的混合物中的酸性成分過高的問題,因此,透過本發明含硫尾氣的脫硫方法,能夠使後續對包含粗焦爐氣及經處理氣體的混合物進行洗滌時,在鹼性溶液的使用量維持不變的情況下獲得純度更高的焦爐氣,抑或是在訴求的焦爐氣的純度不變的情況下以更少的鹼性溶液的使用量來獲得該焦爐氣,所以本發明具有能夠節省後續處理成本的優點。On the other hand, when the treated gas is subsequently mixed with the next batch of crude coke furnace gas in order to prevent the treated gas from being directly discharged into the atmosphere, the low content of hydrogen sulfide in the treated gas can avoid the problem of excessive acidic components in the mixture obtained by mixing the treated gas and the crude coke furnace gas. Therefore, through the desulfurization method of sulfur-containing tail gas of the present invention, when the mixture containing crude coke furnace gas and treated gas is subsequently washed, coke furnace gas with higher purity can be obtained while the amount of alkaline solution used remains unchanged, or the coke furnace gas can be obtained with a smaller amount of alkaline solution used while the required purity of the coke furnace gas remains unchanged. Therefore, the present invention has the advantage of being able to save subsequent processing costs.

參閱圖2,本發明含硫尾氣的脫硫方法,適用於處理一包含硫化氫及二氧化硫的含硫尾氣。該含硫尾氣的來源例如但不限於自一個硫磺回收裝置2所排放出的含硫尾氣。該硫磺回收裝置2是用以接收含硫廢氣,並對該含硫廢氣進行回收處理,從而自該含硫廢氣中回收得到硫磺,同時排放出該含硫尾氣。Referring to FIG. 2 , the desulfurization method of sulfur-containing tail gas of the present invention is applicable to treating a sulfur-containing tail gas containing hydrogen sulfide and sulfur dioxide. The source of the sulfur-containing tail gas is, for example but not limited to, the sulfur-containing tail gas discharged from a sulfur recovery device 2. The sulfur recovery device 2 is used to receive the sulfur-containing waste gas and recover the sulfur-containing waste gas, thereby recovering sulfur from the sulfur-containing waste gas and discharging the sulfur-containing tail gas.

該含硫尾氣的脫硫方法包含一步驟(a)、一步驟(b)及一步驟(c)。The desulfurization method of sulfur-containing tail gas comprises a step (a), a step (b) and a step (c).

該步驟(a)是將該含硫尾氣進行冷卻處理以減少該含硫尾氣中的硫化氫含量及二氧化硫含量,獲得包含硫化氫及濃度為20ppm以下的二氧化硫的氣體混合物,其中,該氣體混合物中的硫化氫含量小於該含硫尾氣中的硫化氫含量。The step (a) is to cool the sulfur-containing tail gas to reduce the hydrogen sulfide content and sulfur dioxide content in the sulfur-containing tail gas, thereby obtaining a gas mixture containing hydrogen sulfide and sulfur dioxide with a concentration of less than 20 ppm, wherein the hydrogen sulfide content in the gas mixture is less than the hydrogen sulfide content in the sulfur-containing tail gas.

該步驟(b)是提供一鹼性處理液,該鹼性處理液包含自脫硫裝置1中回收得到的經使用的鹼性溶液,且該脫硫裝置1是用於利用含有氫氧化鈉的鹼性溶液對包含焦爐氣的混合物進行洗滌,該經使用的鹼性溶液包括氫氧化鈉。The step (b) is to provide an alkaline treatment liquid, wherein the alkaline treatment liquid comprises a used alkaline solution recovered from a desulfurization device 1, and the desulfurization device 1 is used to scrub a mixture containing coke furnace gas with an alkaline solution containing sodium hydroxide, and the used alkaline solution comprises sodium hydroxide.

該步驟(c)是使該氣體混合物與該鹼性處理液在一溼式洗滌裝置3中接觸,並使該氣體混合物中的硫化氫被該鹼性處理液吸收,獲得經處理氣體。The step (c) is to make the gas mixture contact with the alkaline treatment liquid in a wet scrubber 3, and make the hydrogen sulfide in the gas mixture be absorbed by the alkaline treatment liquid to obtain treated gas.

以下對本發明進行詳細說明。The present invention is described in detail below.

《步驟(a)》《Step (a)》

該含硫尾氣除了包含硫化氫及二氧化硫外,通常還包含水蒸氣。該冷卻處理是用以降低該含硫尾氣的溫度,以使該含硫尾氣在降溫的過程中,該含硫尾氣中的水蒸氣冷凝為水,同時,使部分的硫化氫及部分的二氧化硫溶解於該水中,從而減少該含硫尾氣中的硫化氫含量及二氧化硫含量,進而獲得該氣體混合物及包含亞硫酸及硫酸的酸性冷凝液。The sulfur-containing tail gas generally contains water vapor in addition to hydrogen sulfide and sulfur dioxide. The cooling treatment is used to reduce the temperature of the sulfur-containing tail gas so that the water vapor in the sulfur-containing tail gas condenses into water during the cooling process of the sulfur-containing tail gas, and at the same time, part of the hydrogen sulfide and part of the sulfur dioxide are dissolved in the water, thereby reducing the hydrogen sulfide content and sulfur dioxide content in the sulfur-containing tail gas, and then obtaining the gas mixture and the acidic condensate containing sulfurous acid and sulfuric acid.

進行該冷卻處理的方式沒有特別限制,只要能夠使該含硫尾氣的溫度下降,同時還能夠減少該含硫尾氣中的硫化氫含量及二氧化硫含量的方法均適用於本發明。在本發明的一些實施態樣中,該冷卻處理是利用溫度為室溫(25℃)的冷卻水對該含硫尾氣進行降溫,以使該含硫尾氣的溫度降至室溫(25℃)。There is no particular limitation on the method of cooling treatment, as long as the temperature of the sulfur-containing tail gas can be reduced and the content of hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas can be reduced, the present invention is applicable. In some embodiments of the present invention, the cooling treatment is to cool the sulfur-containing tail gas using cooling water at room temperature (25° C.) to reduce the temperature of the sulfur-containing tail gas to room temperature (25° C.).

要說明的是,由於在該步驟(a)中透過該冷卻處理降低該含硫尾氣的溫度,以使該含硫尾氣中的水蒸氣冷凝成水,進而讓部分的硫化氫及部分的二氧化硫溶解於該水中而成為酸性冷凝液,而能減少該含硫尾氣中的硫化氫及二氧化硫的含量,並獲得該氣體混合物,因此,在該步驟(c)中能夠在使用少量的該鹼性處理液的情況下,有效地自該氣體混合物中吸收硫化氫,從而具有好的硫化氫吸收效果。It should be noted that, since the temperature of the sulfur-containing tail gas is lowered by the cooling treatment in the step (a), the water vapor in the sulfur-containing tail gas is condensed into water, and then part of the hydrogen sulfide and part of the sulfur dioxide are dissolved in the water to form an acidic condensate, thereby reducing the content of hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas and obtaining the gas mixture. Therefore, in the step (c), hydrogen sulfide can be effectively absorbed from the gas mixture while using a small amount of the alkaline treatment liquid, thereby having a good hydrogen sulfide absorption effect.

《步驟(b)》《Step (b)》

該脫硫裝置1是用以接收包含酸性物質及氨氣的粗焦爐氣,並利用該鹼性溶液對該粗焦爐氣進行洗滌以降低該粗焦爐氣中例如硫化氫、氰化氫、二氧化碳等酸性物質的含量,藉此獲得純度高的焦爐氣而有利於後續將焦爐氣作為燃料的應用。The desulfurization device 1 is used to receive the crude coke furnace gas containing acidic substances and ammonia, and use the alkaline solution to wash the crude coke furnace gas to reduce the content of acidic substances such as hydrogen sulfide, hydrogen cyanide, carbon dioxide, etc. in the crude coke furnace gas, thereby obtaining high-purity coke furnace gas, which is beneficial to the subsequent application of the coke furnace gas as fuel.

另外,以該鹼性溶液對該粗焦爐氣進行洗滌的過程中,該鹼性溶液會吸收例如硫化氫、氰化氫、二氧化碳等酸性物質,因此,自該脫硫裝置1中回收得到的該經使用的鹼性溶液中除了包括氫氧化鈉外,還包括例如硫化氫、氰化氫、二氧化碳等酸性物質或是上述酸性物質與氫氧化鈉反應後的產物。In addition, during the process of washing the crude coke furnace gas with the alkaline solution, the alkaline solution absorbs acidic substances such as hydrogen sulfide, hydrogen cyanide, carbon dioxide, etc. Therefore, the used alkaline solution recovered from the desulfurization device 1 includes, in addition to sodium hydroxide, acidic substances such as hydrogen sulfide, hydrogen cyanide, carbon dioxide, etc. or products of the reaction between the above acidic substances and sodium hydroxide.

要說明的是,該脫硫裝置1除了能夠排放出該經使用的鹼性溶液,部分的該經使用的鹼性溶液在該脫硫裝置1中會再經過回收再製處理而產生再製的鹼性溶液及含硫廢氣,因此,該脫硫裝置1還會排放出包含硫化氫的含硫廢氣。該含硫廢氣後續可進一步被輸送至如上所述的該硫磺回收裝置2中進行回收處理,從而轉變為硫磺及含硫尾氣。It should be noted that, in addition to being able to discharge the used alkaline solution, part of the used alkaline solution will be recycled and processed in the desulfurization device 1 to produce recycled alkaline solution and sulfur-containing exhaust gas. Therefore, the desulfurization device 1 will also discharge sulfur-containing exhaust gas containing hydrogen sulfide. The sulfur-containing exhaust gas can be further transported to the sulfur recovery device 2 as described above for recycling and processing, thereby being converted into sulfur and sulfur-containing tail gas.

在本發明的一些實施態樣中,為使該氣體混合物中的硫化氫能夠更有效地被該鹼性處理液吸收,以達到更好的硫化氫去除效果,該鹼性處理液還包含一鹼性調整劑。該鹼性調整劑是用以調整該鹼性處理液的pH值,從而使該鹼性處理液對硫化氫具有更好的吸收效果。該鹼性調整劑的種類沒有特別限制,只要能夠賦予該鹼性處理液具有更好的硫化氫吸收效果的試劑均適用於本發明。在本發明的一些實施態樣中,該鹼性調整劑為包含濃度為0.5wt%的氫氧化鈉的氫氧化鈉水溶液。在本發明的一些實施態樣中,該經使用的鹼性溶液與該鹼性調整劑的體積比值範圍為0.1至9。In some embodiments of the present invention, in order to make the hydrogen sulfide in the gas mixture be more effectively absorbed by the alkaline treatment liquid to achieve a better hydrogen sulfide removal effect, the alkaline treatment liquid further comprises an alkaline adjusting agent. The alkaline adjusting agent is used to adjust the pH value of the alkaline treatment liquid, so that the alkaline treatment liquid has a better absorption effect on hydrogen sulfide. The type of the alkaline adjusting agent is not particularly limited, as long as the reagent can give the alkaline treatment liquid a better hydrogen sulfide absorption effect, it is applicable to the present invention. In some embodiments of the present invention, the alkaline adjusting agent is a sodium hydroxide aqueous solution containing sodium hydroxide at a concentration of 0.5wt%. In some embodiments of the present invention, the volume ratio of the alkaline solution to the alkaline adjuster is in the range of 0.1 to 9.

《步驟(c)》《Step (c)》

該溼式洗滌裝置3包含一用以供該氣體混合物通過的第一注入口、一與該第一注入口上下相對設置且用以供該鹼性處理液通過的第二注入口,及一設置於該第一注入口與該第二注入口間的填充床,該填充床是用以使該氣體混合物與該鹼性處理液間能夠有效地相互接觸,從而有效地藉由該鹼性處理液去除該氣體混合物中的硫化氫。在本發明的一些實施態樣中,該第一注入口是形成於該溼式洗滌裝置3的下部,以使該氣體混合物通過該第一注入口進入該溼式洗滌裝置3後是由下至上地流動;而該第二注入口是形成於該溼式洗滌裝置3的上部,以使該鹼性處理液通過該第二注入口進入該溼式洗滌裝置3後是由上至下地澆淋在該氣體混合物上。The wet scrubbing device 3 includes a first injection port for allowing the gas mixture to pass through, a second injection port arranged vertically opposite to the first injection port and used for allowing the alkaline treatment liquid to pass through, and a packed bed arranged between the first injection port and the second injection port. The packed bed is used to enable the gas mixture and the alkaline treatment liquid to effectively contact each other, thereby effectively removing hydrogen sulfide in the gas mixture through the alkaline treatment liquid. In some embodiments of the present invention, the first injection port is formed at the lower part of the wet scrubber 3 so that the gas mixture flows from bottom to top after entering the wet scrubber 3 through the first injection port; and the second injection port is formed at the upper part of the wet scrubber 3 so that the alkaline treatment solution flows from top to bottom on the gas mixture after entering the wet scrubber 3 through the second injection port.

在本發明的一些實施態樣中,在具有好的硫化氫去除效果的情況下,為了進一步兼顧去除該氣體混合物中的硫化氫時的操作成本,該氣體混合物與該鹼性處理液的流量比值範圍為33至100。In some embodiments of the present invention, under the condition of having a good hydrogen sulfide removal effect, in order to further take into account the operating cost when removing hydrogen sulfide from the gas mixture, the flow ratio of the gas mixture to the alkaline treatment liquid ranges from 33 to 100.

該填充床的數量不以一個為限,也可以是多個,可依據使用需求任意地調整填充床的數量。在本發明的一些實施態樣中,為了進一步提高硫化氫的去除效果,該填充床的高度範圍為37cm至148cm。The number of the packed beds is not limited to one, but may be multiple, and the number of packed beds can be adjusted arbitrarily according to the use requirements. In some embodiments of the present invention, in order to further improve the removal effect of hydrogen sulfide, the height of the packed bed ranges from 37 cm to 148 cm.

在本發明的一些實施態樣中,在該步驟(c)中,該氣體混合物與該鹼性處理液接觸後,該氣體混合物中部分的硫化氫被該鹼性處理液吸收,所以在該步驟(c)中所獲得的該經處理氣體中包含硫化氫,且該經處理氣體中的硫化氫是來自於該氣體混合物中未被該鹼性處理液吸收的硫化氫。由於該經處理氣體中的硫化氫是來自於該氣體混合物中未被該鹼性處理液吸收的硫化氫,因此,該經處理氣體中的硫化氫濃度低於該氣體混合物中的硫化氫濃度。In some embodiments of the present invention, in step (c), after the gas mixture contacts the alkaline treatment liquid, part of the hydrogen sulfide in the gas mixture is absorbed by the alkaline treatment liquid, so the treated gas obtained in step (c) contains hydrogen sulfide, and the hydrogen sulfide in the treated gas comes from the hydrogen sulfide in the gas mixture that is not absorbed by the alkaline treatment liquid. Since the hydrogen sulfide in the treated gas comes from the hydrogen sulfide in the gas mixture that is not absorbed by the alkaline treatment liquid, the concentration of hydrogen sulfide in the treated gas is lower than the concentration of hydrogen sulfide in the gas mixture.

本發明將就以下實施例來作進一步說明,但應瞭解的是,所述實施例僅為例示說明之用,而不應被解釋為本發明實施之限制。The present invention will be further described with respect to the following embodiments, but it should be understood that the embodiments are only for illustrative purposes and should not be interpreted as limitations on the implementation of the present invention.

[實施例1][Example 1]

(a)將來自一硫磺回收裝置2所排放出且溫度為140℃且包含硫化氫、二氧化硫及水蒸氣的含硫尾氣進行冷卻處理,以使該含硫尾氣的溫度下降至室溫(25℃),從而讓該水蒸氣冷凝成水,並使部分的硫化氫及部分的二氧化硫溶解於該水中,獲得包含濃度為13222ppm的硫化氫及濃度為6ppm的二氧化硫的氣體混合物及包含亞硫酸及硫酸的酸性冷凝液。其中,該含硫尾氣包含濃度為4000ppm至6000ppm的硫化氫及濃度為500ppm至1200ppm的二氧化硫。該含硫尾氣中的硫化氫濃度及二氧化硫濃度是在140℃下量測得到,該氣體混合物中的硫化氫濃度及二氧化硫濃度是在25℃下量測得到。(a) Cooling sulfur-containing tail gas discharged from a sulfur recovery device 2 and containing hydrogen sulfide, sulfur dioxide and water vapor at a temperature of 140° C. to reduce the temperature of the sulfur-containing tail gas to room temperature (25° C.), thereby condensing the water vapor into water, and dissolving part of the hydrogen sulfide and part of the sulfur dioxide in the water, to obtain a gas mixture containing hydrogen sulfide at a concentration of 13222 ppm and sulfur dioxide at a concentration of 6 ppm and an acidic condensate containing sulfurous acid and sulfuric acid. The sulfur-containing tail gas contains hydrogen sulfide at a concentration of 4000 ppm to 6000 ppm and sulfur dioxide at a concentration of 500 ppm to 1200 ppm. The concentrations of hydrogen sulfide and sulfur dioxide in the sulfur-containing tail gas were measured at 140° C., and the concentrations of hydrogen sulfide and sulfur dioxide in the gas mixture were measured at 25° C.

(b)自一利用含有氫氧化鈉的鹼性溶液對包含焦爐氣的混合物進行洗滌的脫硫裝置1中回收得到經使用的鹼性溶液,並將該經使用的鹼性溶液作為鹼性處理液使用,其中,該經使用的鹼性溶液包括氫氧化鈉。(b) recovering a used alkaline solution from a desulfurization device 1 for scrubbing a mixture containing coke furnace gas with an alkaline solution containing sodium hydroxide, and using the used alkaline solution as an alkaline treatment solution, wherein the used alkaline solution includes sodium hydroxide.

(c)將該氣體混合物自形成於一溼式洗滌裝置3下部的一第一注入口通入該溼式洗滌裝置3內,及將該鹼性處理液自形成於該溼式洗滌裝置3上部的一第二注入口通入該溼式洗滌裝置3內,以使位於該溼式洗滌裝置3內的該氣體混合物由下至上地流動,並與由上至下淋洗的該鹼性處理液接觸,從而使該氣體混合物中的硫化氫被該鹼性處理液吸收,獲得包含濃度為5468ppm的硫化氫的經處理氣體。其中,該氣體混合物是以40L/min的流量通入該溼式洗滌裝置3,該鹼性處理液是以0.4L/min的流量通入該溼式洗滌裝置3,該氣體混合物與該鹼性處理液的流量比值為100,該填充床的高度為37cm。此外,由該經處理氣體中的硫化氫濃度可知,該氣體混合物中的硫化氫的去除率為58.6%。(c) the gas mixture is introduced into the wet scrubber 3 through a first injection port formed at the lower portion of the wet scrubber 3, and the alkaline treatment liquid is introduced into the wet scrubber 3 through a second injection port formed at the upper portion of the wet scrubber 3, so that the gas mixture in the wet scrubber 3 flows from bottom to top and contacts the alkaline treatment liquid eluted from top to bottom, so that hydrogen sulfide in the gas mixture is absorbed by the alkaline treatment liquid, and a treated gas containing hydrogen sulfide at a concentration of 5468 ppm is obtained. The gas mixture is passed into the wet scrubber 3 at a flow rate of 40 L/min, the alkaline treatment liquid is passed into the wet scrubber 3 at a flow rate of 0.4 L/min, the flow ratio of the gas mixture to the alkaline treatment liquid is 100, and the height of the packed bed is 37 cm. In addition, according to the concentration of hydrogen sulfide in the treated gas, the removal rate of hydrogen sulfide in the gas mixture is 58.6%.

[實施例2至9][Examples 2 to 9]

實施例2至9是以與實施例1類似的方式對含硫尾氣進行處理,差別在於:改變填充床的高度及改變鹼性處理液的流量,結果如表1所示。Examples 2 to 9 treat sulfur-containing tail gas in a manner similar to Example 1, except that the height of the packed bed and the flow rate of the alkaline treatment solution are changed. The results are shown in Table 1.

[實施例10至13][Examples 10 to 13]

實施例10至13是以與實施例1類似的方式對含硫尾氣進行處理,差別在於:在步驟(a)中,該氣體混合物包含濃度為14000ppm的硫化氫及濃度為6ppm的二氧化硫;在步驟(c)中,該鹼性處理液的流量為1.2L/min,該氣體混合物與該鹼性處理液的流量比值為33.3,其中,實施例10至13的填充床的高度為依序為37cm、74cm、111cm及148cm。Examples 10 to 13 treat sulfur-containing tail gas in a manner similar to Example 1, except that: in step (a), the gas mixture contains hydrogen sulfide with a concentration of 14000 ppm and sulfur dioxide with a concentration of 6 ppm; in step (c), the flow rate of the alkaline treatment liquid is 1.2 L/min, and the flow rate ratio of the gas mixture to the alkaline treatment liquid is 33.3, wherein the heights of the packed beds of Examples 10 to 13 are 37 cm, 74 cm, 111 cm and 148 cm, respectively.

[實施例14至25][Examples 14 to 25]

實施例14至25是以與實施例1類似的方式對含硫尾氣進行處理,差別在於:在步驟(a)中,該氣體混合物包含濃度為14000ppm的硫化氫及濃度為6ppm的二氧化硫;在步驟(b)中,是將該經使用的鹼性溶液與包含濃度為0.5wt%的氫氧化鈉的氫氧化鈉水溶液(作為鹼性調整劑)進行混合,獲得鹼性處理液;在步驟(c)中,該鹼性處理液的流量為1.2L/min,該氣體混合物與該鹼性處理液的流量比值為33.3,其中,在實施例14至17中,經使用的鹼性溶液與鹼性調整劑的體積比值為9,填充床的高度為依序為37cm、74cm、111cm及148cm;在實施例18至21中,經使用的鹼性溶液與鹼性調整劑的體積比值為1,填充床的高度為依序為37cm、74cm、111cm及148cm;在實施例22至25中,經使用的鹼性溶液與鹼性調整劑的體積比值為0.11,填充床的高度為依序為37cm、74cm、111cm及148cm。Examples 14 to 25 treat sulfur-containing tail gas in a manner similar to Example 1, except that: in step (a), the gas mixture contains hydrogen sulfide at a concentration of 14000 ppm and sulfur dioxide at a concentration of 6 ppm; in step (b), the used alkaline solution is mixed with an aqueous sodium hydroxide solution containing 0.5 wt % sodium hydroxide (as an alkaline adjuster) to obtain an alkaline treatment solution; in step (c), the flow rate of the alkaline treatment solution is 1.2 L/min, and the flow rate ratio of the gas mixture to the alkaline treatment solution is 33.3, wherein In Examples 14 to 17, the volume ratio of the alkaline solution to the alkaline adjuster was 9, and the heights of the packed beds were 37 cm, 74 cm, 111 cm and 148 cm, respectively; in Examples 18 to 21, the volume ratio of the alkaline solution to the alkaline adjuster was 1, and the heights of the packed beds were 37 cm, 74 cm, 111 cm and 148 cm, respectively; in Examples 22 to 25, the volume ratio of the alkaline solution to the alkaline adjuster was 0.11, and the heights of the packed beds were 37 cm, 74 cm, 111 cm and 148 cm, respectively.

[實施例26][Example 26]

實施例26是以與實施例1類似的方式對含硫尾氣進行處理,差別在於:在步驟(a)中,該氣體混合物包含濃度為13800ppm的硫化氫及濃度為6ppm的二氧化硫;在步驟(c)中,該鹼性處理液的流量為1.2L/min,該氣體混合物與該鹼性處理液的流量比值為33.3,經使用的鹼性溶液與鹼性調整劑的體積比值為0.11,填充床為111cm。Example 26 treats sulfur-containing tail gas in a manner similar to Example 1, except that: in step (a), the gas mixture contains hydrogen sulfide with a concentration of 13800 ppm and sulfur dioxide with a concentration of 6 ppm; in step (c), the flow rate of the alkaline treatment liquid is 1.2 L/min, the flow rate ratio of the gas mixture to the alkaline treatment liquid is 33.3, the volume ratio of the alkaline solution used to the alkaline adjuster is 0.11, and the packed bed is 111 cm.

[評價項目][Evaluation Items]

以下以實施例1為例說明,其餘實施例是以相同的方式進行。The following is explained using Example 1 as an example, and the remaining examples are carried out in the same manner.

硫化氫去除率:利用一台雷射氣體分析儀(廠牌:SERVOMEX)對該氣體混合物及該經處理氣體進行量測,獲得該氣體混合物中的硫化氫的濃度及該經處理氣體中的硫化氫的濃度,並依據該氣體混合物與該經處理氣體中的硫化氫的濃度計算得到該氣體混合物中的硫化氫的去除率。 硫化氫的去除率(單位:%)=(氣體混合物中的硫化氫的濃度-經處理氣體中的硫化氫的濃度)/氣體混合物中的硫化氫的濃度×100%。 Hydrogen sulfide removal rate: The gas mixture and the treated gas are measured using a laser gas analyzer (brand: SERVOMEX) to obtain the concentration of hydrogen sulfide in the gas mixture and the concentration of hydrogen sulfide in the treated gas, and the removal rate of hydrogen sulfide in the gas mixture is calculated based on the concentration of hydrogen sulfide in the gas mixture and the treated gas. Hydrogen sulfide removal rate (unit: %) = (hydrogen sulfide concentration in the gas mixture - hydrogen sulfide concentration in the treated gas) / hydrogen sulfide concentration in the gas mixture × 100%.

表1 實施例 1 2 3 4 5 6 7 8 9 氣體混合物中的硫化氫濃度(ppm) 13222 13222 13222 13222 13222 13222 13222 13222 13222 氣體混合物的流量(L/min) 40 40 40 40 40 40 40 40 40 鹼性處理液的流量(L/min) 0.4 0.4 0.4 0.8 0.8 0.8 1.2 1.2 1.2 氣體混合物與鹼性處理液的流量比值 100 100 100 50 50 50 33.3 33.3 33.3 填充床的高度(cm) 37 74 111 37 74 111 37 74 111 經處理氣體中的硫化氫濃度(ppm) 5468 5062 3387 5325 4506 2862 4981 3931 2093 硫化氫去除率(%) 58.6 61.7 74.4 59.7 65.9 78.4 62.3 70.3 84.2 Table 1 Embodiment 1 2 3 4 5 6 7 8 9 Hydrogen sulfide concentration in gas mixture (ppm) 13222 13222 13222 13222 13222 13222 13222 13222 13222 Flow rate of gas mixture (L/min) 40 40 40 40 40 40 40 40 40 Alkaline treatment liquid flow rate (L/min) 0.4 0.4 0.4 0.8 0.8 0.8 1.2 1.2 1.2 Flow ratio of gas mixture to alkaline treatment liquid 100 100 100 50 50 50 33.3 33.3 33.3 Height of packed bed (cm) 37 74 111 37 74 111 37 74 111 Hydrogen sulfide concentration in treated gas (ppm) 5468 5062 3387 5325 4506 2862 4981 3931 2093 Hydrogen sulfide removal rate (%) 58.6 61.7 74.4 59.7 65.9 78.4 62.3 70.3 84.2

表2 實施例 10 11 12 13 14 15 16 17 氣體混合物中的硫化氫濃度(ppm) 14000 14000 14000 14000 14000 14000 14000 14000 氣體混合物的流量(L/min) 40 40 40 40 40 40 40 40 鹼性處理液 經使用的鹼性溶液 O O O O O O O O 鹼性調整劑 X X X X O O O O 經使用的鹼性溶液與鹼性調整劑的體積比值 -- -- -- -- 9 9 9 9 流量(L/min) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 氣體混合物與鹼性處理液的流量比值 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 填充床的高度(cm) 37 74 111 148 37 74 111 148 經處理氣體中的硫化氫濃度(ppm) 4806 3289 2900 2812 4556 2991 2630 2578 硫化氫去除率(%) 65.7 76.5 79.3 79.9 67.5 78.6 81.2 81.6 註:「O」表示有使用;「X」表示未使用。 Table 2 Embodiment 10 11 12 13 14 15 16 17 Hydrogen sulfide concentration in gas mixture (ppm) 14000 14000 14000 14000 14000 14000 14000 14000 Flow rate of gas mixture (L/min) 40 40 40 40 40 40 40 40 Alkaline treatment solution Alkaline solution used O O O O O O O O Alkaline regulator X X X X O O O O Volume ratio of alkaline solution to alkaline regulator used -- -- -- -- 9 9 9 9 Flow rate (L/min) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 Flow ratio of gas mixture to alkaline treatment liquid 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 Height of packed bed (cm) 37 74 111 148 37 74 111 148 Hydrogen sulfide concentration in treated gas (ppm) 4806 3289 2900 2812 4556 2991 2630 2578 Hydrogen sulfide removal rate (%) 65.7 76.5 79.3 79.9 67.5 78.6 81.2 81.6 Note: “O” indicates used; “X” indicates not used.

表3 實施例 18 19 20 21 22 23 24 25 26 氣體混合物中的硫化氫濃度(ppm) 14000 14000 14000 14000 14000 14000 14000 14000 13800 氣體混合物的流量(L/min) 40 40 40 40 40 40 40 40 40 鹼性處理液 經使用的鹼性溶液 O O O O O O O O O 鹼性調整劑 O O O O O O O O O 經使用的鹼性溶液與鹼性調整劑的體積比值 1 1 1 1 0.11 0.11 0.11 0.11 0.11 流量(L/min) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 氣體混合物與鹼性處理液的流量比值 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 填充床的高度(cm) 37 74 111 148 37 74 111 148 111 經處理氣體中的硫化氫濃度(ppm) 3304 1487 1036 930 2792 860 351 176 83 硫化氫的去除率(%) 76.4 89.4 92.6 93.4 80.1 93.9 97.5 98.7 99.4 註:「O」表示有使用。 table 3 Embodiment 18 19 20 twenty one twenty two twenty three twenty four 25 26 Hydrogen sulfide concentration in gas mixture (ppm) 14000 14000 14000 14000 14000 14000 14000 14000 13800 Flow rate of gas mixture (L/min) 40 40 40 40 40 40 40 40 40 Alkaline treatment solution Alkaline solution used O O O O O O O O O Alkaline regulator O O O O O O O O O Volume ratio of alkaline solution to alkaline regulator used 1 1 1 1 0.11 0.11 0.11 0.11 0.11 Flow rate (L/min) 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 1.2 Flow ratio of gas mixture to alkaline treatment liquid 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 33.3 Height of packed bed (cm) 37 74 111 148 37 74 111 148 111 Hydrogen sulfide concentration in treated gas (ppm) 3304 1487 1036 930 2792 860 351 176 83 Removal rate of hydrogen sulfide (%) 76.4 89.4 92.6 93.4 80.1 93.9 97.5 98.7 99.4 Note: “O” means in use.

參閱表1,實施例1至9的含硫尾氣的脫硫方法具有58.6%至84.2%的硫化氫去除率,此表示實施例1至9確實能夠有效地去除含硫尾氣中的硫化氫。Referring to Table 1, the desulfurization methods of sulfur-containing tail gas of Examples 1 to 9 have hydrogen sulfide removal rates of 58.6% to 84.2%, which indicates that Examples 1 to 9 can indeed effectively remove hydrogen sulfide from the sulfur-containing tail gas.

參閱表2至表3,由實施例10至26的硫化氫去除率的結果可知,不論該鹼性處理液中是否有添加鹼性調整劑,實施例10至26均能夠有效地去除含硫尾氣中的硫化氫,而具有65.7%至99.4%的硫化氫去除率。此外,在填充床高度相同的情況下,當該鹼性處理液中該經使用的鹼性溶液與該鹼性調整劑的體積比值越小,也就是說,該鹼性調整劑的用量越多,硫化氫的去除效果越佳,此表示面對不同的硫化氫去除率需求,在該鹼性處理液中包含經使用的鹼性溶液下,本發明確實可依據不同的需求選擇是否添加鹼性調整劑。Referring to Tables 2 to 3, it can be seen from the results of the hydrogen sulfide removal rate of Examples 10 to 26 that, regardless of whether an alkaline regulator is added to the alkaline treatment solution, Examples 10 to 26 can effectively remove hydrogen sulfide from the sulfur-containing tail gas and have a hydrogen sulfide removal rate of 65.7% to 99.4%. In addition, under the same packed bed height, when the volume ratio of the used alkaline solution to the alkaline regulator in the alkaline treatment solution is smaller, that is, the more the alkaline regulator is used, the better the hydrogen sulfide removal effect is. This means that in the face of different hydrogen sulfide removal rate requirements, when the alkaline treatment solution contains the used alkaline solution, the present invention can indeed choose whether to add an alkaline regulator according to different requirements.

綜上所述,本發明含硫尾氣的脫硫方法透過該步驟(a)至(c)的搭配,本發明能夠有效地去除含硫尾氣中的硫化氫,因此,該經處理氣體中的硫化氫含量小於該含硫尾氣中的硫化氫含量。In summary, the desulfurization method of sulfur-containing tail gas of the present invention can effectively remove hydrogen sulfide in the sulfur-containing tail gas through the combination of steps (a) to (c). Therefore, the hydrogen sulfide content in the treated gas is less than the hydrogen sulfide content in the sulfur-containing tail gas.

另一方面,當後續為了不讓該經處理氣體被直接排放至大氣中而將該經處理氣體與下一批次的粗焦爐氣混合時,由於該經處理氣體中的硫化氫含量低,因此,在通入該脫硫裝置1的粗焦爐氣中的酸性物質的含量不變的情況下,由該經處理氣體與該粗焦爐氣混合得到的混合物中的酸性成分的總含量相對小於包含含硫尾氣及粗焦爐氣的混合物中的酸性成分的總含量,所以能避免由該經處理氣體與粗焦爐氣混合得到的混合物中的酸性成分過高,因此,透過本發明含硫尾氣的脫硫方法,能夠使後續對包含粗焦爐氣及經處理氣體的混合物進行洗滌時,在鹼性溶液的使用量維持不變的情況下獲得純度更高的焦爐氣,抑或是在訴求的焦爐氣的純度不變的情況下以更少的鹼性溶液的使用量來獲得該焦爐氣,所以本發明具有能夠節省後續處理成本的優點,故確實能達成本發明的目的。On the other hand, when the treated gas is subsequently mixed with the next batch of crude coke furnace gas in order to prevent the treated gas from being directly discharged into the atmosphere, since the hydrogen sulfide content in the treated gas is low, under the condition that the content of acidic substances in the crude coke furnace gas introduced into the desulfurization device 1 remains unchanged, the total content of acidic components in the mixture obtained by mixing the treated gas and the crude coke furnace gas is relatively smaller than the total content of acidic components in the mixture containing sulfur-containing tail gas and crude coke furnace gas, so the amount of hydrogen sulfide in the treated gas can be avoided. The acidic components in the mixture obtained by mixing the gas with the crude coke furnace gas are too high. Therefore, through the desulfurization method of sulfur-containing tail gas of the present invention, when the mixture containing the crude coke furnace gas and the treated gas is subsequently washed, coke furnace gas with higher purity can be obtained while the amount of alkaline solution used remains unchanged, or the coke furnace gas can be obtained with a smaller amount of alkaline solution used while the required purity of the coke furnace gas remains unchanged. Therefore, the present invention has the advantage of being able to save subsequent processing costs, and can indeed achieve the purpose of the present invention.

惟以上所述者,僅為本發明的實施例而已,當不能以此限定本發明實施的範圍,凡是依本發明申請專利範圍及專利說明書內容所作的簡單的等效變化與修飾,皆仍屬本發明專利涵蓋的範圍內。However, the above is only an embodiment of the present invention and should not be used to limit the scope of implementation of the present invention. All simple equivalent changes and modifications made according to the scope of the patent application of the present invention and the content of the patent specification are still within the scope of the present patent.

1:脫硫裝置1: Desulfurization device

2:硫磺回收裝置2: Sulfur recovery device

3:溼式洗滌裝置3: Wet washing device

本發明的其他的特徵及功效,將於參照圖式的實施方式中清楚地呈現,其中: 圖1是一流程圖,說明現有的粗焦爐氣、含硫廢氣及含硫尾氣的處理方法;及 圖2是一流程圖,說明本發明含硫尾氣的脫硫方法的一實施例。 Other features and effects of the present invention will be clearly presented in the embodiments with reference to the drawings, wherein: FIG. 1 is a flow chart illustrating the existing treatment method of crude coke furnace gas, sulfur-containing waste gas and sulfur-containing tail gas; and FIG. 2 is a flow chart illustrating an embodiment of the desulfurization method of sulfur-containing tail gas of the present invention.

1:脫硫裝置 1: Desulfurization device

2:硫磺回收裝置 2: Sulfur recovery device

3:溼式洗滌裝置 3: Wet washing device

Claims (6)

一種含硫尾氣的脫硫方法,適用於處理一包含硫化氫及二氧化硫的含硫尾氣,該含硫尾氣的脫硫方法包含以下步驟:(a)將該含硫尾氣進行冷卻處理以減少該含硫尾氣中的硫化氫含量及二氧化硫含量,獲得包含硫化氫及濃度為20ppm以下的二氧化硫的氣體混合物,其中,該氣體混合物中的硫化氫含量小於該含硫尾氣中的硫化氫含量;(b)提供一鹼性處理液,該鹼性處理液包含自脫硫裝置中回收得到的經使用的鹼性溶液,且該脫硫裝置是用於利用含有氫氧化鈉的鹼性溶液對包含焦爐氣的混合物進行洗滌,該經使用的鹼性溶液包括氫氧化鈉;及(c)使該氣體混合物與該鹼性處理液在一溼式洗滌裝置中接觸,並使該氣體混合物中的硫化氫被該鹼性處理液吸收,獲得經處理氣體,其中,該氣體混合物與該鹼性處理液的流量比值範圍為33至100。 A method for desulfurizing sulfur-containing tail gas is applicable to treating a sulfur-containing tail gas containing hydrogen sulfide and sulfur dioxide. The method for desulfurizing sulfur-containing tail gas comprises the following steps: (a) cooling the sulfur-containing tail gas to reduce the hydrogen sulfide content and sulfur dioxide content in the sulfur-containing tail gas, thereby obtaining a gas mixture containing hydrogen sulfide and sulfur dioxide with a concentration of less than 20 ppm, wherein the hydrogen sulfide content in the gas mixture is less than the hydrogen sulfide content in the sulfur-containing tail gas; (b) providing an alkaline treatment solution, wherein the alkaline treatment solution The method comprises: (a) recovering a used alkaline solution from a desulfurization device, wherein the desulfurization device is used to scrub a mixture containing coke furnace gas with an alkaline solution containing sodium hydroxide, wherein the used alkaline solution includes sodium hydroxide; and (c) contacting the gas mixture with the alkaline treatment liquid in a wet scrubbing device, and allowing the hydrogen sulfide in the gas mixture to be absorbed by the alkaline treatment liquid to obtain treated gas, wherein the flow ratio of the gas mixture to the alkaline treatment liquid ranges from 33 to 100. 如請求項1所述的含硫尾氣的脫硫方法,其中,該溼式洗滌裝置包含一用以供該氣體混合物通過的第一注入口、一與該第一注入口上下相對設置且用以供該鹼性處理液通過的第二注入口,及至少一設置於該第一注入口與該第二注入口間的填充床,且該至少一填充床的高度範圍為37cm至148cm。 The desulfurization method of sulfur-containing tail gas as described in claim 1, wherein the wet scrubber comprises a first injection port for the gas mixture to pass through, a second injection port disposed vertically opposite to the first injection port and for the alkaline treatment liquid to pass through, and at least one packed bed disposed between the first injection port and the second injection port, and the height of the at least one packed bed ranges from 37 cm to 148 cm. 如請求項1所述的含硫尾氣的脫硫方法,其中,在該溼式洗滌裝置中,該氣體混合物是由下至上地流動,該鹼性處 理液是由上至下地澆淋在該氣體混合物上。 The desulfurization method of sulfur-containing tail gas as described in claim 1, wherein, in the wet scrubbing device, the gas mixture flows from bottom to top, and the alkaline treatment liquid is poured on the gas mixture from top to bottom. 如請求項1所述的含硫尾氣的脫硫方法,其中,該鹼性處理液還包含一鹼性調整劑。 The desulfurization method of sulfur-containing tail gas as described in claim 1, wherein the alkaline treatment liquid also contains an alkaline regulator. 如請求項4所述的含硫尾氣的脫硫方法,其中,該鹼性調整劑為氫氧化鈉水溶液。 The desulfurization method of sulfur-containing tail gas as described in claim 4, wherein the alkaline regulator is an aqueous solution of sodium hydroxide. 如請求項4所述的含硫尾氣的脫硫方法,其中,該經使用的鹼性溶液與該鹼性調整劑的體積比值範圍為0.1至9。A method for desulfurizing sulfur-containing tail gas as described in claim 4, wherein the volume ratio of the used alkaline solution to the alkaline regulator ranges from 0.1 to 9.
TW112100717A 2023-01-07 2023-01-07 Desulfurization method for sulfur-containing tail gas TWI838069B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
TW112100717A TWI838069B (en) 2023-01-07 2023-01-07 Desulfurization method for sulfur-containing tail gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
TW112100717A TWI838069B (en) 2023-01-07 2023-01-07 Desulfurization method for sulfur-containing tail gas

Publications (2)

Publication Number Publication Date
TWI838069B true TWI838069B (en) 2024-04-01
TW202428885A TW202428885A (en) 2024-07-16

Family

ID=91618933

Family Applications (1)

Application Number Title Priority Date Filing Date
TW112100717A TWI838069B (en) 2023-01-07 2023-01-07 Desulfurization method for sulfur-containing tail gas

Country Status (1)

Country Link
TW (1) TWI838069B (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013024766A1 (en) * 2011-08-12 2013-02-21 Jfeスチール株式会社 Molten steel desulfurization method, molten steel secondary refining method, and molten steel manufacturing method
CN104561428A (en) * 2014-12-11 2015-04-29 新疆八一钢铁股份有限公司 Desulfurization recovery method of slag iron of blowing-process desulfurizing slag
US20180057901A1 (en) * 2015-03-13 2018-03-01 Radmat Ag Method and device for granulating molten material
CN107955855A (en) * 2016-10-16 2018-04-24 铁东区强东冶金技术咨询服务中心 The method of no slag gasification removing Sulfur Content in Hot Iron phosphorus silicon

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2013024766A1 (en) * 2011-08-12 2013-02-21 Jfeスチール株式会社 Molten steel desulfurization method, molten steel secondary refining method, and molten steel manufacturing method
CN104561428A (en) * 2014-12-11 2015-04-29 新疆八一钢铁股份有限公司 Desulfurization recovery method of slag iron of blowing-process desulfurizing slag
US20180057901A1 (en) * 2015-03-13 2018-03-01 Radmat Ag Method and device for granulating molten material
CN107955855A (en) * 2016-10-16 2018-04-24 铁东区强东冶金技术咨询服务中心 The method of no slag gasification removing Sulfur Content in Hot Iron phosphorus silicon

Also Published As

Publication number Publication date
TW202428885A (en) 2024-07-16

Similar Documents

Publication Publication Date Title
EP3401004A1 (en) Method for controlling aerosol production during sulfur dioxide absorption with ammonium salts in flue gas desulfurization
CN104555940B (en) Reduce the recovery technology of sulfur of sulfur dioxide (SO2) emissions
JP4427234B2 (en) Wet gas purification method and system
JP7062509B2 (en) Carbon capture
CN102160960A (en) Soda wet desulphurization process and system for sintering flue gas
CN106642165B (en) Method for treating volatile organic compounds in refinery
TWI838069B (en) Desulfurization method for sulfur-containing tail gas
CN106823745A (en) A kind of reaction end gas regeneration technology
KR101696048B1 (en) Method for separating gas components from desulfurization waste gas
CN110252090B (en) Method for improving absorption capacity and utilization rate of sodium sulfite desulfurization process by using triethanolamine
JP2016210855A (en) Method for refining coke-oven gas
CN109517630B (en) Process and system for deamination production of ammonium sulfate by coke oven gas ammonium sulfite method
CN209702677U (en) Coke-stove gas sulfurous acid ammonium salt process deamination produces sulphur ammonium system
CN112675669B (en) Device and method for removing sulfur oxides in high-humidity flue gas
CN105016309A (en) SWSR-2 sulfur recovery device and process
KR101155929B1 (en) Scrubbing water composition for removing hydrogen sulfide in coke oven gas and the method thereof
RU2349544C1 (en) Method of production of sulphuric acid
KR20160077393A (en) Apparatus of coke oven gas purification and method coke oven gas purification
CN111111413B (en) Desulfurization system and process for ultralow emission of waste gas in carbon black industry
JPS60139319A (en) Method of removing sulfur dioxide from flue gas of combustion apparatus by washing by liquid having oxidation action
KR100906563B1 (en) Method for absorption of hydrogen sulfide from coke oven gas
TW201240716A (en) Method for cleaning coke oven gas
KR102484968B1 (en) Method and apparatus for treating cokes oven gas
CN107150999A (en) A kind of technique of oxygen deprivation method Sulphuric acid
CN115924858A (en) Method for treating tail gas in sulfur dioxide production by sodium citrate method