CN104208992A - Method for desulfurizing acid gas containing hydrogen sulfide and recycling sulfur - Google Patents
Method for desulfurizing acid gas containing hydrogen sulfide and recycling sulfur Download PDFInfo
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- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 title claims abstract description 72
- 239000007789 gas Substances 0.000 title claims abstract description 66
- 239000011593 sulfur Substances 0.000 title claims abstract description 61
- 229910052717 sulfur Inorganic materials 0.000 title claims abstract description 61
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 title claims abstract description 49
- 229910000037 hydrogen sulfide Inorganic materials 0.000 title claims abstract description 49
- 238000000034 method Methods 0.000 title claims abstract description 29
- 230000003009 desulfurizing effect Effects 0.000 title claims abstract description 7
- 239000002253 acid Substances 0.000 title claims description 13
- 238000004064 recycling Methods 0.000 title 1
- 239000003054 catalyst Substances 0.000 claims abstract description 48
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims abstract description 46
- 238000002485 combustion reaction Methods 0.000 claims abstract description 38
- 239000007788 liquid Substances 0.000 claims abstract description 22
- 238000005984 hydrogenation reaction Methods 0.000 claims abstract description 16
- 238000010521 absorption reaction Methods 0.000 claims abstract description 15
- 239000012670 alkaline solution Substances 0.000 claims abstract description 9
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 230000009471 action Effects 0.000 claims abstract description 8
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 8
- 239000001257 hydrogen Substances 0.000 claims abstract description 8
- 238000001816 cooling Methods 0.000 claims abstract description 7
- 230000008569 process Effects 0.000 claims abstract description 7
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 4
- 238000006243 chemical reaction Methods 0.000 claims description 28
- 239000000243 solution Substances 0.000 claims description 13
- 238000011084 recovery Methods 0.000 claims description 8
- 238000006477 desulfuration reaction Methods 0.000 claims description 7
- 230000023556 desulfurization Effects 0.000 claims description 7
- 230000035484 reaction time Effects 0.000 claims description 6
- 229910018072 Al 2 O 3 Inorganic materials 0.000 claims description 3
- 239000000203 mixture Substances 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 3
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims 1
- 239000003638 chemical reducing agent Substances 0.000 claims 1
- 238000005265 energy consumption Methods 0.000 abstract description 2
- 230000002378 acidificating effect Effects 0.000 abstract 2
- 230000007613 environmental effect Effects 0.000 abstract 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 10
- 230000006872 improvement Effects 0.000 description 9
- 239000002585 base Substances 0.000 description 4
- 230000003197 catalytic effect Effects 0.000 description 4
- 230000018109 developmental process Effects 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 230000008929 regeneration Effects 0.000 description 3
- 238000011069 regeneration method Methods 0.000 description 3
- 230000008676 import Effects 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000003345 natural gas Substances 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 1
- 239000013543 active substance Substances 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 239000013538 functional additive Substances 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 235000000396 iron Nutrition 0.000 description 1
- 230000004807 localization Effects 0.000 description 1
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- 239000003921 oil Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 150000003464 sulfur compounds Chemical class 0.000 description 1
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Abstract
一种对含有硫化氢的酸性气体进行脱硫并回收硫的方法,依次包括如下步骤:将酸性气体通入燃烧炉中,与从另一管道通入的空气混合进行燃烧反应;在燃烧炉中反应后的气体进入到降温器中降温至230~250℃,降温后液态硫从液体出口分离,而在燃烧炉中的混合气体进入催化剂反应器,在催化剂反应器中使硫化氢与二氧化硫之间反应生成硫与水,生成的液态硫从催化剂反应器的液体出口分离;催化剂反应器中混合气体进入至加氢反应器中,在加氢反应器中的二氧化硫与氢反应;加氢反应器中的气体进入到硫化氢吸收装置中,将硫化氢在碱性溶液、络合物催化剂和通入空气的作用下生成单质硫。其优点在于:工艺路线短,产生硫品质好,能耗低。能完全去除SO2气体,绿色环保。
A method for desulfurizing acidic gas containing hydrogen sulfide and recovering sulfur, comprising the following steps in sequence: feeding the acidic gas into a combustion furnace, mixing it with air fed from another pipeline for combustion reaction; reacting in the combustion furnace The final gas enters the desuperheater and cools down to 230-250°C. After cooling, the liquid sulfur is separated from the liquid outlet, and the mixed gas in the combustion furnace enters the catalyst reactor, and the hydrogen sulfide and sulfur dioxide react in the catalyst reactor. Sulfur and water are generated, and the generated liquid sulfur is separated from the liquid outlet of the catalyst reactor; the mixed gas in the catalyst reactor enters the hydrogenation reactor, and the sulfur dioxide in the hydrogenation reactor reacts with hydrogen; The gas enters the hydrogen sulfide absorption device, and hydrogen sulfide is generated into elemental sulfur under the action of alkaline solution, complex catalyst and air. The advantages are: short process route, high quality sulfur and low energy consumption. Can completely remove SO 2 gas, green and environmental protection.
Description
技术领域technical field
本发明涉及工业废气处理技术领域,尤其指一种对含有硫化氢的酸性气体进行脱硫并回收硫的方法。The invention relates to the technical field of industrial waste gas treatment, in particular to a method for desulfurizing acid gas containing hydrogen sulfide and recovering sulfur.
背景技术Background technique
随着我国经济高速发展,对煤、石油、天然气等原材料需求量不断增加,由于我国石油和天然气量较小,大部分依赖于从国外进口。随着国家市场需求量加大,好品质原材料进口难度大、价格竞争激励,为降低成本,进口原材料大多含硫量较高。为达到后续客户及市场需求,必须对硫进行脱除。硫回收工艺在国内经过近40年引进和发展,呈现国内自由技术和国际技术平行发展趋势。1883年,英国科学家克劳斯首先提出从H2S气体回收硫磺工艺方法,经过100多年发展,技术得到很大改进。据统计,2000-2003年,中国硫回收装置从62套增至100多套,至2014年又有近50套大、中型装置投产。经济虽快速发展,但近几年环境污染严重,特别是雾霾天气对环境造成巨大危害,而SO2对雾霾天气“贡献”较大,国家为了治理环境,排放气中SO2含量将在2015年降低到50mg/m3以下。国内现在所有硫回收装置中SO2排放95%不达标。多年来,硫回收工艺虽经过多次变革和改进,并且增加了尾气处理措施,但工艺原理未变,现在使用的技术多在改良克劳斯基础上,在基础理论、工艺流程、催化剂研制、设备结构及材质、自控方案及连锁等多方面加以发展及改进,但最终没有彻底实现污染物零排放。现有一种申请号CN96102799.1名称为《一种含H2S的混合气体中提取单质硫的方法》的中国发明专利公开了一种从一种含H2S的混合气体中提取单质硫的方法,其中,该混合气体首先在一个克劳斯设备中被脱硫并同时产生单质硫,其次,在克劳斯废气中仍含有的硫化合物通过氢化被转变成H2S,接下来,氢化了的克劳斯废气进行H2S的直接催化氧化并生成单质硫。然而,该发明不能完全去除SO2,气体的排放,而且H2S的吸收处理能耗较大,因此,有必要对该方法作进一步地改进。With the rapid development of my country's economy, the demand for raw materials such as coal, oil, and natural gas continues to increase. Due to the small amount of oil and natural gas in my country, most of them rely on imports from abroad. With the increasing demand in the national market, it is difficult to import high-quality raw materials, and price competition is incentivized. In order to reduce costs, most of the imported raw materials contain high sulfur content. In order to meet subsequent customer and market demands, sulfur must be removed. The sulfur recovery process has been introduced and developed in China for nearly 40 years, showing a parallel development trend of domestic free technology and international technology. In 1883, the British scientist Claus first proposed the process of recovering sulfur from H 2 S gas. After more than 100 years of development, the technology has been greatly improved. According to statistics, from 2000 to 2003, the number of sulfur recovery devices in China increased from 62 to more than 100, and by 2014, nearly 50 large and medium-sized devices were put into operation. Although the economy is developing rapidly, the environmental pollution has been serious in recent years, especially the smog weather has caused great harm to the environment, and SO 2 has made a great contribution to the smog weather. In order to control the environment, the SO 2 content in the exhaust gas will In 2015, it was reduced to below 50mg/m 3 . 95% of SO 2 emissions from all domestic sulfur recovery units are not up to standard. Over the years, although the sulfur recovery process has been reformed and improved many times, and tail gas treatment measures have been added, the process principle has not changed. Most of the technologies used now are based on improved Claus, based on basic theory, process flow, catalyst development, The equipment structure and material, automatic control scheme and interlocking have been developed and improved in many aspects, but in the end the zero discharge of pollutants has not been completely realized. An existing Chinese invention patent with the application number CN96102799.1 titled "A Method for Extracting Elemental Sulfur from a Mixed Gas Containing H 2 S" discloses a method for extracting elemental sulfur from a mixed gas containing H 2 S method, wherein the mixed gas is firstly desulfurized in a Claus plant with simultaneous production of elemental sulfur, and secondly, the sulfur compounds still contained in the Claus off-gas are converted into H 2 S by hydrogenation, followed by hydrogenation The Claus exhaust gas undergoes direct catalytic oxidation of H 2 S and generates elemental sulfur. However, this invention cannot completely remove SO 2 , gas emissions, and the absorption and treatment of H 2 S consumes a lot of energy. Therefore, it is necessary to further improve the method.
发明内容Contents of the invention
本发明所要解决的技术问题是针对上述现有技术现状而提供一种既能脱硫又能回收硫且酸性气体中的硫化氢能完全被去除的脱硫并回收硫的方法。The technical problem to be solved by the present invention is to provide a desulfurization and sulfur recovery method that can not only desulfurize but also recover sulfur, and hydrogen sulfide in acid gas can be completely removed in view of the above-mentioned prior art.
本发明解决上述技术问题所采用的技术方案为:本对含有硫化氢的酸性气体进行脱硫并回收硫的方法,其特征在于:依次包括如下步骤:The technical solution adopted by the present invention to solve the above-mentioned technical problems is: the method for desulfurizing acid gas containing hydrogen sulfide and recovering sulfur, which is characterized in that it includes the following steps in sequence:
步骤一、将含有硫化氢的酸性气体通入燃烧炉中,与从另一管道通入燃烧炉的空气混合进行燃烧反应,所述燃烧炉中通入的酸性气体的进气压力保持为20~100KPa;反应式方程为:2H2S+O2→2S↓+2H2O;2H2S+3O2→2SO2+2H2O;Step 1. Pass the acid gas containing hydrogen sulfide into the combustion furnace, and mix it with the air passing into the combustion furnace from another pipeline to carry out the combustion reaction. The inlet pressure of the acid gas passed into the combustion furnace is maintained at 20- 100KPa; the reaction equation is: 2H 2 S+O 2 →2S↓+2H 2 O; 2H 2 S+3O 2 →2SO 2 +2H 2 O;
步骤二、在燃烧炉中反应后的气体进入到降温器中降温至230~250℃,降温后液态硫从液体出口分离出,而在燃烧炉中未完全燃尽的硫化氢气体与燃烧后生成的二氧化硫气体的混合气体进入催化剂反应器,在催化剂反应器中基触媒的作用下使硫化氢与二氧化硫之间反应生成硫与水,生成的液态硫从催化剂反应器的液体出口分离,反应方程式为:2H2S+SO2→3S↓+2H2O;Step 2. The reacted gas in the combustion furnace enters the cooling device to cool down to 230-250°C. After cooling, the liquid sulfur is separated from the liquid outlet, and the incompletely burnt hydrogen sulfide gas in the combustion furnace is formed after combustion. The mixed gas of sulfur dioxide gas enters the catalyst reactor, and under the action of the base catalyst in the catalyst reactor, the hydrogen sulfide and sulfur dioxide react to form sulfur and water, and the generated liquid sulfur is separated from the liquid outlet of the catalyst reactor. The reaction equation is : 2H 2 S+SO 2 →3S↓+2H 2 O;
步骤三、将催化剂反应器中未反应完全的硫化氢与二氧化硫混合气体进入至压力保持在20~100KPa的加氢反应器中,在加氢反应器中混合气体的二氧化硫与氢反应而将二氧化硫还原成硫化氢,反应方程式为:SO2+3H2→H2S+2H2O;Step 3. Put the unreacted hydrogen sulfide and sulfur dioxide mixed gas in the catalyst reactor into the hydrogenation reactor whose pressure is kept at 20-100KPa, and the sulfur dioxide in the mixed gas reacts with hydrogen in the hydrogenation reactor to reduce the sulfur dioxide into hydrogen sulfide, the reaction equation is: SO 2 +3H 2 →H 2 S+2H 2 O;
步骤四、将加氢反应器中的硫化氢与二氧化硫被氢还原成硫化氢的气体进入到其内置有碱性溶液和络合物催化剂的硫化氢吸收装置中,将硫化氢在碱性溶液、络合物催化剂和通入空气的作用下生成单质硫,反应方程式为:Step 4, the hydrogen sulfide and sulfur dioxide in the hydrogenation reactor are reduced to hydrogen sulfide by hydrogen into the hydrogen sulfide absorption device with a built-in alkaline solution and complex catalyst, and the hydrogen sulfide is dissolved in the alkaline solution, Elemental sulfur is generated under the action of the complex catalyst and air, and the reaction equation is:
·CO3 2-+CO2+H2O→2HCO3 - ·CO 3 2- +CO 2 +H 2 O→2HCO 3 -
·H2S+OH-→HS-+H2O·H 2 S+OH - →HS - +H 2 O
·Fe3+(络合态)+HS-→Fe2+(络合态)+S+H+ ·Fe 3+ (complexed state)+HS - →Fe 2+ (complexed state)+S+H +
·总反应式为:Fe3+(络合态)+H2S+OH-→Fe2+(络合态)+S↓+H2OThe overall reaction formula is: Fe 3+ (complexed state)+H 2 S+OH - →Fe 2+ (complexed state)+S↓+H 2 O
即完成脱硫和回收硫步骤。That is, the steps of desulfurization and sulfur recovery are completed.
作为改进,在步骤四中的硫化氢吸收装置有间隔地通入空气,直至不再产生沉淀。As an improvement, the hydrogen sulfide absorption device in step 4 is fed with air at intervals until no more precipitation occurs.
作为进一步改进,每次通入空气的时间为0.2~3秒。As a further improvement, the time for feeding air each time is 0.2-3 seconds.
作为改进,在步骤一的燃烧炉中反应后的气体进入到压力为20~100KPa的降温器中降温至230~250℃。As an improvement, the reacted gas in the combustion furnace in step 1 enters a desuperheater with a pressure of 20-100KPa to cool down to 230-250°C.
作为改进,在步骤三中,将催化剂反应器中未反应完全的硫化氢与二氧化硫混合气体进入至压力保持在20~100KPa的加氢反应器中。As an improvement, in step 3, the mixed gas of hydrogen sulfide and sulfur dioxide not completely reacted in the catalyst reactor enters into the hydrogenation reactor whose pressure is kept at 20-100KPa.
作为改进,所述步骤四中的硫化氢吸收装置内反应温度保持在50~60℃。As an improvement, the reaction temperature in the hydrogen sulfide absorption device in the step 4 is kept at 50-60°C.
作为改进,所述燃烧炉中气体燃烧的反应温度保持在980~1370℃,反应时间为0.5~3秒。As an improvement, the reaction temperature of gas combustion in the combustion furnace is kept at 980-1370° C., and the reaction time is 0.5-3 seconds.
作为改进,所述催化剂反应器中反应温度保持为265~275℃,反应时间为3~10秒。As an improvement, the reaction temperature in the catalyst reactor is kept at 265-275° C., and the reaction time is 3-10 seconds.
作为改进,所述燃烧炉和催化剂反应器反应生成的液态硫分别通过管道统一收集到硫磺池中,所述硫磺池中的液态硫由硫磺泵输送至硫磺造粒机生产固体硫磺。As an improvement, the liquid sulfur generated by the reaction of the combustion furnace and the catalyst reactor is collected uniformly through pipelines into the sulfur pool, and the liquid sulfur in the sulfur pool is transported by a sulfur pump to a sulfur granulator to produce solid sulfur.
作为改进,所述催化剂为络合物催化剂,所述基触媒为Al2O3,所述碱性溶液为Na2CO3溶液。As an improvement, the catalyst is a complex catalyst, the base catalyst is Al 2 O 3 , and the alkaline solution is Na 2 CO 3 solution.
与现有技术相比,本发明的对含有硫化氢的酸性气体进行脱硫并回收硫的方法具有如下优点:工艺路线短,所用设备制造加工简单,能完全实现国产化,催化剂活性好,产生硫品质好,能耗低,控制方便。经过本工艺脱硫操作后,气体中95%以上H2S转化为单质硫,剩余气体中SO2完全转化为H2S,出第三反应器的气体含有少量H2S,通过硫化氢吸收装置,吸收几乎全部的H2S,使H2S气体在O2和催化剂作用下转化为单质硫,气体达到脱除H2S目的,最终气体中H2S含量小于1ppM,SO2含量为零。催化剂采用变价金属铁的络合物,为两种金属铁的复配络合体系,用于含硫溶液时性能稳定,脱硫效率高,再生能力强,有效硫容可达0.60g/L(以H2S含量≤1500mg/Nm3计算)以上,脱硫后H2S含量可达5mg/Nm3以下,并且催化剂中配有多种功能性助剂,能提高催化剂的稳定性,减少降解率,提高硫粒子的表面性能,使硫粒子长大,经中科院材料所激光粒度测定仪测定大部分硫颗粒粒径为11μm,硫泡沫丰富稳定,易于清除;再生反应完全,形成二元催化剂氧化体系,加快再生反应速度,提高吸收后溶液中HS-氧化速度,使离开硫化氢吸收装置的溶液中HS-浓度降到最低;溶液中含有离子型表面活性物质,可以降低溶液的表面张力,使单质硫磺相对富集,非常容易从硫液中析出,悬浮硫含量低,不易堆积堵塞。硫化氢吸收装置温度保持在50~60℃,温度为50-60℃时,溶液对CO2的吸收量小,有利于H2S的脱除。高温吸收可加速HCO3-的解吸,生成CO32-,稳定溶液酸碱度,降低碱耗。Compared with the prior art, the method for desulfurizing acid gas containing hydrogen sulfide and recovering sulfur of the present invention has the following advantages: the process route is short, the manufacturing and processing of the equipment used is simple, the localization can be fully realized, the catalyst activity is good, and the production of sulfur Good quality, low energy consumption and convenient control. After the desulfurization operation of this process, more than 95% of the H 2 S in the gas is converted into elemental sulfur, and the SO 2 in the remaining gas is completely converted into H 2 S, and the gas leaving the third reactor contains a small amount of H 2 S, which passes through the hydrogen sulfide absorption device , absorb almost all of the H 2 S, so that the H 2 S gas is converted into elemental sulfur under the action of O 2 and the catalyst, and the gas achieves the purpose of removing H 2 S, and the H 2 S content in the final gas is less than 1ppM, and the SO 2 content is zero . The catalyst adopts complexes of variable-valence metal iron, which is a compound complex system of two metal irons. It has stable performance when used in sulfur-containing solutions, high desulfurization efficiency, strong regeneration ability, and effective sulfur capacity can reach 0.60g/L (within H 2 S content ≤ 1500mg/Nm 3 (calculated), the H 2 S content after desulfurization can reach below 5mg/Nm 3 , and the catalyst is equipped with a variety of functional additives, which can improve the stability of the catalyst and reduce the degradation rate. Improve the surface properties of sulfur particles and make them grow up. The particle size of most of the sulfur particles measured by the laser particle size analyzer of the Institute of Materials, Chinese Academy of Sciences is 11 μm. The sulfur foam is rich and stable and easy to remove; the regeneration reaction is complete, forming a binary catalyst oxidation system. Accelerate the regeneration reaction speed, increase the HS-oxidation rate in the solution after absorption, and minimize the HS - concentration in the solution leaving the hydrogen sulfide absorption device; the solution contains ionic surface active substances, which can reduce the surface tension of the solution and make the elemental sulfur Relatively enriched, it is very easy to precipitate from the sulfur solution, the content of suspended sulfur is low, and it is not easy to accumulate and block. The temperature of the hydrogen sulfide absorption device is kept at 50-60°C. When the temperature is 50-60°C, the absorption of CO 2 by the solution is small, which is beneficial to the removal of H 2 S. High-temperature absorption can accelerate the desorption of HCO3 - , generate CO3 2- , stabilize the pH of the solution, and reduce the alkali consumption.
附图说明Description of drawings
图1为应用本发明的装置的结构示意图。Fig. 1 is a schematic structural diagram of a device applying the present invention.
具体实施方式Detailed ways
以下结合附图实施例对本发明作进一步详细描述。The present invention will be further described in detail below in conjunction with the accompanying drawings and embodiments.
如图1所示,本发明的对含有硫化氢的酸性气体进行脱硫并回收硫的方法,依次包括如下步骤:As shown in Figure 1, the method for desulfurizing acid gas containing hydrogen sulfide and reclaiming sulfur of the present invention comprises the following steps successively:
步骤一、将含有硫化氢的酸性气体通入燃烧炉1中,与从另一管道通入燃烧炉1的空气混合进行燃烧反应,所述燃烧炉1中通入的酸性气体的进气压力保持为20~100KPa;反应式方程为:2H2S+O2→2S↓+2H2O;2H2S+3O2→2SO2+2H2O;Step 1, the acid gas containing hydrogen sulfide is passed into the combustion furnace 1, mixed with the air passing into the combustion furnace 1 from another pipeline to carry out the combustion reaction, the intake pressure of the acid gas passed into the combustion furnace 1 is kept 20~100KPa; the reaction equation is: 2H 2 S+O 2 →2S↓+2H 2 O; 2H 2 S+3O 2 →2SO 2 +2H 2 O;
步骤二、在燃烧炉1中反应后的气体进入到降温器2中降温至230~250℃,降温后液态硫从液体出口分离出,而在燃烧炉1中未完全燃尽的硫化氢气体与燃烧后生成的二氧化硫气体的混合气体进入催化剂反应器3,在催化剂反应器3中基触媒的作用下使硫化氢与二氧化硫之间反应生成硫与水,生成的液态硫从催化剂反应器3的液体出口分离,反应方程式为:2H2S+SO2→3S↓+2H2O;Step 2: The gas reacted in the combustion furnace 1 enters the cooling device 2 to cool down to 230-250°C, and the liquid sulfur is separated from the liquid outlet after cooling, while the incompletely burned hydrogen sulfide gas in the combustion furnace 1 and The mixed gas of sulfur dioxide gas generated after combustion enters the catalytic reactor 3, and under the action of the base catalyst in the catalytic reactor 3, hydrogen sulfide and sulfur dioxide are reacted to generate sulfur and water, and the liquid sulfur generated is released from the liquid in the catalytic reactor 3. The outlet is separated, and the reaction equation is: 2H 2 S+SO 2 →3S↓+2H 2 O;
步骤三、将催化剂反应器3中未反应完全的硫化氢与二氧化硫混合气体进入至压力保持在20~100KPa的加氢反应器4中,在加氢反应器4中混合气体的二氧化硫与氢反应而将二氧化硫还原成硫化氢,反应方程式为:SO2+3H2→H2S+2H2O;Step 3, enter the mixed gas of unreacted hydrogen sulfide and sulfur dioxide in the catalyst reactor 3 into the hydrogenation reactor 4 whose pressure is maintained at 20-100KPa, and react the sulfur dioxide and hydrogen of the mixed gas in the hydrogenation reactor 4 to form Reducing sulfur dioxide to hydrogen sulfide, the reaction equation is: SO 2 +3H 2 →H 2 S+2H 2 O;
步骤四、将加氢反应器4中的硫化氢与二氧化硫被氢还原成硫化氢的气体进入到其内置有碱性溶液和络合物催化剂的硫化氢吸收装置5中,将硫化氢在碱性溶液、络合物催化剂和通入空气的作用下生成单质硫,反应方程式为:Step 4, the hydrogen sulfide and sulfur dioxide in the hydrogenation reactor 4 are reduced to hydrogen sulfide gas by hydrogen into the hydrogen sulfide absorption device 5 which has a built-in alkaline solution and a complex catalyst, and the hydrogen sulfide in the alkaline Elemental sulfur is generated under the action of solution, complex catalyst and air, and the reaction equation is:
·CO3 2-+CO2+H2O→2HCO3 - ·CO 3 2- +CO 2 +H 2 O→2HCO 3 -
·H2S+OH-→HS-+H2O·H 2 S+OH - →HS - +H 2 O
·Fe3+络合态+HS-→Fe2+络合态+S+H+ ·Fe 3+ complex state+HS - →Fe 2+ complex state+S+H +
·总反应式为:Fe3+络合态+H2S+OH-→Fe2+络合态+S↓+H2OThe overall reaction formula is: Fe 3+ complex state + H 2 S + OH - → Fe 2+ complex state + S↓ + H 2 O
即完成脱硫和回收硫步骤。That is, the steps of desulfurization and sulfur recovery are completed.
在步骤四中的硫化氢吸收装置5有间隔地通入空气,直至不再产生沉淀。每次通入空气的时间为0.2~3秒。在步骤一的燃烧炉1中反应后的气体进入到压力为20~100KPa的降温器2中降温至230~250℃。在步骤三中,将催化剂反应器3中未反应完全的硫化氢与二氧化硫混合气体进入至压力保持在20~100KPa的加氢反应器4中。所述步骤四中的硫化氢吸收装置5内反应温度保持在50~60℃。所述燃烧炉1中气体燃烧的反应温度保持在980~1370℃,反应时间为0.5~3秒。所述催化剂反应器3中反应温度保持为265~275℃,反应时间为3~10秒。所述燃烧炉1和催化剂反应器3反应生成的液态硫分别通过管道统一收集到硫磺池6中,所述硫磺池6中的液态硫由硫磺泵输送至硫磺造粒机生产固体硫磺。所述催化剂为络合物催化剂,所述基触媒为Al2O3,所述碱性溶液为Na2CO3溶液。The hydrogen sulfide absorbing device 5 in the step 4 is fed with air at intervals until no more precipitation occurs. The time for feeding air each time is 0.2 to 3 seconds. The gas reacted in the combustion furnace 1 in step 1 enters the desuperheater 2 with a pressure of 20-100KPa and cools down to 230-250°C. In Step 3, the unreacted hydrogen sulfide and sulfur dioxide mixed gas in the catalyst reactor 3 enters into the hydrogenation reactor 4 whose pressure is maintained at 20-100KPa. The reaction temperature in the hydrogen sulfide absorption device 5 in the step 4 is kept at 50-60°C. The reaction temperature of gas combustion in the combustion furnace 1 is kept at 980-1370° C., and the reaction time is 0.5-3 seconds. The reaction temperature in the catalyst reactor 3 is kept at 265-275° C., and the reaction time is 3-10 seconds. The liquid sulfur generated by the reaction of the combustion furnace 1 and the catalyst reactor 3 is respectively collected into the sulfur pool 6 through pipelines, and the liquid sulfur in the sulfur pool 6 is transported by a sulfur pump to a sulfur granulator to produce solid sulfur. The catalyst is a complex catalyst, the base catalyst is Al 2 O 3 , and the alkaline solution is Na 2 CO 3 solution.
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