CN102120134A - Electrochemical treatment device and method for removing hydrogen sulfide in methane - Google Patents
Electrochemical treatment device and method for removing hydrogen sulfide in methane Download PDFInfo
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- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 title claims abstract description 34
- 229910000037 hydrogen sulfide Inorganic materials 0.000 title claims abstract description 34
- 238000000034 method Methods 0.000 title claims abstract description 15
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title description 4
- 238000006477 desulfuration reaction Methods 0.000 claims abstract description 76
- 230000023556 desulfurization Effects 0.000 claims abstract description 76
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims abstract description 38
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims abstract description 38
- 239000007788 liquid Substances 0.000 claims abstract description 29
- 238000010521 absorption reaction Methods 0.000 claims abstract description 23
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 claims abstract description 13
- 230000008929 regeneration Effects 0.000 claims abstract description 13
- 238000011069 regeneration method Methods 0.000 claims abstract description 13
- 239000001257 hydrogen Substances 0.000 claims abstract description 12
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 12
- 230000001172 regenerating effect Effects 0.000 claims description 20
- 238000006243 chemical reaction Methods 0.000 claims description 19
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 18
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 11
- 229910052717 sulfur Inorganic materials 0.000 claims description 11
- 239000011593 sulfur Substances 0.000 claims description 11
- 239000010802 sludge Substances 0.000 claims description 6
- 239000007921 spray Substances 0.000 claims description 4
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 2
- 229910002804 graphite Inorganic materials 0.000 claims description 2
- 239000010439 graphite Substances 0.000 claims description 2
- 238000000926 separation method Methods 0.000 claims description 2
- 125000004122 cyclic group Chemical group 0.000 claims 1
- 238000004062 sedimentation Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 7
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 abstract description 4
- DHCDFWKWKRSZHF-UHFFFAOYSA-N sulfurothioic S-acid Chemical compound OS(O)(=O)=S DHCDFWKWKRSZHF-UHFFFAOYSA-N 0.000 abstract description 4
- 238000003912 environmental pollution Methods 0.000 abstract description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- HYHCSLBZRBJJCH-UHFFFAOYSA-M sodium hydrosulfide Chemical compound [Na+].[SH-] HYHCSLBZRBJJCH-UHFFFAOYSA-M 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 230000002745 absorbent Effects 0.000 description 2
- 239000002250 absorbent Substances 0.000 description 2
- 238000005868 electrolysis reaction Methods 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- VDQVEACBQKUUSU-UHFFFAOYSA-M disodium;sulfanide Chemical compound [Na+].[Na+].[SH-] VDQVEACBQKUUSU-UHFFFAOYSA-M 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 239000002737 fuel gas Substances 0.000 description 1
- XLYOFNOQVPJJNP-ZSJDYOACSA-N heavy water Substances [2H]O[2H] XLYOFNOQVPJJNP-ZSJDYOACSA-N 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000010687 lubricating oil Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000003595 mist Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 229910052979 sodium sulfide Inorganic materials 0.000 description 1
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
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Abstract
去除沼气中硫化氢的电化学处理装置及处理方法,它涉及一种去除沼气中硫化氢的处理装置及处理方法。本发明为了解决现有的湿式脱硫装置需要解收剂且再生效果差以及现有的湿式脱硫方法脱硫时生成硫酸盐和硫代硫酸盐,导致溶液的吸收能力降低,从而带来二次环境污染的问题。沉降槽通过第二导管与再生电解槽连通,出氢管的上端与再生电解槽的底端面连通,再生电解槽上端通过回流管与脱硫塔的上部连通,所述回流管插装在脱硫塔内,脱硫塔内的回流管上装有多个喷嘴。方法采用三氯化铁溶液作为吸收液进行脱硫。本发明的电化学处理装置适用于大中型的沼气脱硫工程中;本发明的电化学处理方法采用三氯化铁溶液作为吸收液,吸收液的吸收能力保持不变。
The invention discloses an electrochemical treatment device and a treatment method for removing hydrogen sulfide in biogas, and relates to a treatment device and a treatment method for removing hydrogen sulfide in biogas. The present invention solves the problem that the existing wet desulfurization device needs desorbent and has poor regeneration effect, and that sulfate and thiosulfate are generated during desulfurization by the existing wet desulfurization method, which leads to a decrease in the absorption capacity of the solution, thereby causing secondary environmental pollution The problem. The settling tank communicates with the regeneration electrolyzer through the second conduit, the upper end of the hydrogen outlet pipe communicates with the bottom end of the regeneration electrolyzer, and the upper end of the regeneration electrolyzer communicates with the upper part of the desulfurization tower through a return pipe, and the return pipe is inserted into the desulfurization tower , the return pipe in the desulfurization tower is equipped with multiple nozzles. Methods Ferric chloride solution was used as the absorbing liquid for desulfurization. The electrochemical treatment device of the present invention is suitable for large and medium-sized biogas desulfurization projects; the electrochemical treatment method of the present invention uses ferric chloride solution as the absorption liquid, and the absorption capacity of the absorption liquid remains unchanged.
Description
技术领域technical field
本发明涉及一种去除沼气中硫化氢的电化学处理装置及利用该装置去除沼气中硫化氢的电化学方法。The invention relates to an electrochemical treatment device for removing hydrogen sulfide in biogas and an electrochemical method for removing hydrogen sulfide in biogas by using the device.
背景技术Background technique
随着工农业废弃物厌氧生物处理技术的广泛应用,沼气作为一种可再生的生物质能源,在石化能源日益匮乏的今天,越来越受到人们的关注和重视。正常状态下,沼气的主要成分为甲烷和二氧化碳,并含有少量的一氧化碳、氢气、硫化氢、氧气和氮气等。沼气中的硫化氢产生于蛋白质和其他含硫化合物的降解过程.因此硫化氢浓度取决于沼气发生器的进料情况,并在0.1%~2%之间变化。硫化氢浓度过高是沼气作为燃气使用最大的限制因素之一,因为硫化氢对燃烧动力设备和金属管道具有很强的腐蚀作用,并且还会引发润滑油的变质从而加速发动机的磨损;此外,沼气在经过燃烧后,硫化氢会转化为硫的氧化物(SOX)并释放到空气中,造成大气污染。因此,在沼气燃烧利用之前,必须去除其中的硫化氢。With the wide application of anaerobic biological treatment technology for industrial and agricultural waste, biogas, as a renewable biomass energy, has attracted more and more attention and attention in today's increasingly scarce petrochemical energy. Under normal conditions, the main components of biogas are methane and carbon dioxide, and contain a small amount of carbon monoxide, hydrogen, hydrogen sulfide, oxygen and nitrogen. Hydrogen sulfide in biogas is produced from the degradation process of protein and other sulfur-containing compounds. Therefore, the concentration of hydrogen sulfide depends on the feed of the biogas generator and varies between 0.1% and 2%. Excessive concentration of hydrogen sulfide is one of the biggest limiting factors for the use of biogas as fuel gas, because hydrogen sulfide has a strong corrosive effect on combustion power equipment and metal pipes, and it will also cause deterioration of lubricating oil and accelerate engine wear; in addition, After the biogas is burned, hydrogen sulfide will be converted into sulfur oxides (SO X ) and released into the air, causing air pollution. Therefore, the hydrogen sulfide in the biogas must be removed before it can be burned and utilized.
大多数污水处理厂设计的脱硫装置分为干式脱硫和湿式脱硫两种。在干式脱硫中使用干式脱硫塔,塔内装填多层脱硫剂,使用时往往脱硫剂更换频繁,并且脱硫效果较差,干式脱硫不适合污水处理厂消化池沼气中高浓度H2S的去除。湿式脱硫采用的脱硫装置为湿式脱硫塔,消化的沼气从底部进入塔中,与吸收剂逆流接触反应,然后从塔顶部排除。目前采用较多的是用NaOH作为吸收剂,反应如下:The desulfurization devices designed by most sewage treatment plants are divided into two types: dry desulfurization and wet desulfurization. In dry desulfurization, a dry desulfurization tower is used. The tower is filled with multiple layers of desulfurizers. The desulfurizers are often replaced during use, and the desulfurization effect is poor. Dry desulfurization is not suitable for the high concentration of H 2 S in the digester biogas of sewage treatment plants. remove. The desulfurization device used in wet desulfurization is a wet desulfurization tower. The digested biogas enters the tower from the bottom, contacts and reacts with the absorbent in countercurrent, and then is discharged from the top of the tower. At present, NaOH is used more as absorbent, and the reaction is as follows:
2NaOH+H2S→Na2S+2H2O2NaOH+ H2S → Na2S + 2H2O
NaOH+H2S→NaHS+H2ONaOH+ H2S →NaHS+ H2O
现有的湿式脱硫装置脱硫和再生没有分开设置,需要解收剂且再生效果差;现有的湿式脱硫方法的脱硫碱液的吸收受到流速、流量、温度等因素的影响,H2S的溶解度达不到100%,脱硫时易形成NaHS,NaHS再生时会与O2反应生成硫酸盐和硫代硫酸盐,有害物质在吸收液中富集,导致溶液的吸收能力降低,从而带来二次环境污染。The desulfurization and regeneration of existing wet desulfurization devices are not separately set up, desorbent is needed and the regeneration effect is poor; the absorption of desulfurization alkali liquor in the existing wet desulfurization method is affected by factors such as flow rate, flow rate, temperature, etc., and the solubility of H 2 S If it does not reach 100%, it is easy to form NaHS during desulfurization. When NaHS is regenerated, it will react with O2 to generate sulfate and thiosulfate. environmental pollution.
发明内容Contents of the invention
本发明的目的是为解决现有的湿式脱硫装置需要解收剂且再生效果差以及现有的湿式脱硫方法脱硫时生成硫酸盐和硫代硫酸盐,导致溶液的吸收能力降低,从而带来二次环境污染的问题,进而提供了一种去除沼气中硫化氢的电化学处理装置及处理方法。The purpose of the present invention is to solve the problem that the existing wet desulfurization device needs a desorbent and the regeneration effect is poor, and that sulfate and thiosulfate are generated during desulfurization in the existing wet desulfurization method, which leads to a decrease in the absorption capacity of the solution, thereby causing two In order to solve the problem of secondary environmental pollution, an electrochemical treatment device and treatment method for removing hydrogen sulfide in biogas are provided.
本发明的去除沼气中硫化氢的电化学处理装置包括脱硫塔、多个喷嘴、第一导管、第一水泵、第二水泵、沉降槽、再生电解槽、第二导管、排泥管、出氢管和回流管,所述脱硫塔的底端面上开有出液口,所述脱硫塔的外侧壁上开有沼气进口,所述脱硫塔的顶端开有沼气出口,所述脱硫塔的出液口通过第一导管与沉降槽连通,所述沉降槽的下部设有排泥管,排泥管与沉降槽连通,第一导管上装有第一水泵、沉降槽通过第二导管与再生电解槽连通,出氢管的上端与再生电解槽的底端面连通,再生电解槽上端通过回流管与脱硫塔的上部连通,回流管上装有第二水泵,所述回流管插装在脱硫塔内,脱硫塔内的回流管上装有多个喷嘴。The electrochemical treatment device for removing hydrogen sulfide in biogas of the present invention includes a desulfurization tower, a plurality of nozzles, a first conduit, a first water pump, a second water pump, a settling tank, a regenerative electrolyzer, a second conduit, a sludge discharge pipe, and a hydrogen outlet There is a liquid outlet on the bottom end surface of the desulfurization tower, a biogas inlet is opened on the outer wall of the desulfurization tower, a biogas outlet is opened on the top of the desulfurization tower, and the liquid outlet of the desulfurization tower is The port is connected with the settling tank through the first conduit, and the lower part of the settling tank is provided with a mud discharge pipe, which is connected with the settling tank, and the first water pump is installed on the first conduit, and the settling tank is connected with the regenerative electrolyzer through the second conduit , the upper end of the hydrogen outlet pipe communicates with the bottom end of the regenerative electrolyzer, the upper end of the regenerative electrolyzer communicates with the upper part of the desulfurization tower through a return pipe, the second water pump is installed on the return pipe, and the return pipe is inserted into the desulfurization tower, and the desulfurization tower The inner return pipe is equipped with multiple nozzles.
本发明的去除沼气中硫化氢的电化学处理方法是按照以下步骤实现的:The electrochemical treatment method for removing hydrogen sulfide in biogas of the present invention is realized according to the following steps:
步骤一、将沼气从沼气进口充入脱硫塔内,沼气的停留时间为5~10分钟,采用三氯化铁溶液作为吸收液,三氯化铁溶液的浓度为0.5~0.7mol/L,开启第二水泵,将再生电解槽内的三氯化铁溶液通过回流管进入脱硫塔内,并从喷嘴喷出,充入脱硫塔内的沼气上升,沼气中的硫化氢与喷嘴喷出三氯化铁吸收液逆向接触发生反应,去除沼气中的硫化氢;
步骤二、与吸收液反应后的已脱硫沼气继续向脱硫塔的上方流动,然后从沼气出口流出;Step 2: The desulfurized biogas after reacting with the absorption liquid continues to flow to the top of the desulfurization tower, and then flows out from the biogas outlet;
步骤三、三氯化铁吸收液与沼气中的硫化氢反应后大部分变为二氯化铁溶液,二氯化铁溶液和反应生成的硫单质从脱硫塔8底端的第一导管流出,开启第一水泵,使二氯化铁溶液和反应生成的硫单质进入沉降槽内,硫单质在沉降槽中经沉降分离后从排泥管排出;Step 3: After the ferric chloride absorbing liquid reacts with the hydrogen sulfide in the biogas, most of it turns into a ferric chloride solution, and the ferric chloride solution and the sulfur element generated by the reaction flow out from the first conduit at the bottom of the
步骤四、沉降槽内的二氯化铁溶液经第二导管进入再生电解槽内进行再生反应,
反应生成的氢气从出氢管排出,经过再生的二氯化铁溶液反应生成三氯化铁吸收液,生成的三氯化铁吸收液通过回流管进入脱硫塔进行循环反应。The hydrogen gas generated by the reaction is discharged from the hydrogen outlet pipe, and the regenerated ferric chloride solution reacts to generate ferric chloride absorption liquid, and the generated ferric chloride absorption liquid enters the desulfurization tower through the return pipe for circular reaction.
本发明的有益效果是:本发明的电化学处理装置的脱硫和再生分开设置,不需要解收剂且再生效果好,本发明的电化学处理装置设置有沉降槽,使得硫单质在沉降槽中分离,脱硫效果好,硫化氢的去除率达到99%;本发明的电化学处理装置适用于大中型的沼气脱硫工程中;本发明的电化学处理方法采用三氯化铁溶液作为吸收液,脱硫时没有硫酸盐和硫代硫酸盐生成,吸收液的吸收能力保持不变。The beneficial effects of the present invention are: the desulfurization and regeneration of the electrochemical treatment device of the present invention are set separately, no desorbent is needed and the regeneration effect is good, the electrochemical treatment device of the present invention is provided with a settling tank, so that the sulfur element is in the settling tank Separation, good desulfurization effect, the removal rate of hydrogen sulfide reaches 99%; the electrochemical treatment device of the present invention is suitable for large and medium-sized biogas desulfurization projects; the electrochemical treatment method of the present invention uses ferric chloride solution as the absorption liquid, desulfurization When no sulfate and thiosulfate are formed, the absorption capacity of the absorption liquid remains unchanged.
附图说明Description of drawings
图1本发明的电化学处理装置的整体结构主视图,图2是本发明的再生电解槽的剖视图。Fig. 1 is a front view of the overall structure of the electrochemical treatment device of the present invention, and Fig. 2 is a sectional view of the regenerative electrolyzer of the present invention.
具体实施方式Detailed ways
具体实施方式一:如图1~2所示,本实施方式的去除沼气中硫化氢的电化学处理装置包括脱硫塔8、多个喷嘴4、第一导管5、第一水泵6、第二水泵7、沉降槽9、再生电解槽10、第二导管14、排泥管12、出氢管13和回流管11,所述脱硫塔8的底端面上开有出液口8-1,所述脱硫塔8的外侧壁上开有沼气进口1,所述脱硫塔8的顶端开有沼气出口8-2,所述脱硫塔8的出液口8-1通过第一导管5与沉降槽9连通,所述沉降槽9的下部设有排泥管12,排泥管12与沉降槽9连通,第一导管5上装有第一水泵6、沉降槽9通过第二导管14与再生电解槽10连通,出氢管13的上端与再生电解槽10的底端面连通,再生电解槽10上端通过回流管11与脱硫塔8的上部连通,回流管11上装有第二水泵7,所述回流管11插装在脱硫塔8内,脱硫塔8内的回流管11上装有多个喷嘴4。Specific Embodiment 1: As shown in Figures 1-2, the electrochemical treatment device for removing hydrogen sulfide in biogas in this embodiment includes a
具体实施方式二:如图2所示,本实施方式所述再生电解槽10的阴极10-1和阳极10-2均由石墨制成。其它组成及连接关系与具体实施方式一相同。Embodiment 2: As shown in FIG. 2, the cathode 10-1 and the anode 10-2 of the regenerative
具体实施方式三:如图1所示,本实施方式所述处理装置还包括除沫器3,所述除沫器3位于脱硫塔8内且位于喷嘴4的上方。如此设计,可以去除脱硫塔8内反应产生的雾沫。其它组成及连接关系与具体实施方式一或二相同。Embodiment 3: As shown in FIG. 1 , the processing device in this embodiment further includes a
具体实施方式四:如图1~2所示,本实施方式的去除沼气中硫化氢的电化学处理方法步骤如下:Specific embodiment four: as shown in Figures 1-2, the steps of the electrochemical treatment method for removing hydrogen sulfide in biogas in this embodiment are as follows:
步骤一、将沼气从沼气进口8-1充入脱硫塔8内,沼气的停留时间为5~10分钟,采用三氯化铁溶液作为吸收液,三氯化铁溶液的浓度为0.5~0.7mol/L,开启第二水泵7,将再生电解槽10内的三氯化铁溶液通过回流管11进入脱硫塔8内,并从喷嘴4喷出,充入脱硫塔8内的沼气上升,沼气中的硫化氢与喷嘴4喷出三氯化铁吸收液逆向接触发生反应,去除沼气中的硫化氢;
反应方程式如下:The reaction equation is as follows:
H2S+2FeCl3→2FeCl2+2HCl+S(S)↓H 2 S+2FeCl 3 →2FeCl 2 +2HCl+S(S)↓
或表示为:or expressed as:
H2S+2Fe3+→2Fe2++2H++S(S)↓H 2 S+2Fe 3+ →2Fe 2+ +2H + +S(S)↓
步骤二、与吸收液反应后的已脱硫沼气继续向脱硫塔8的上方流动,然后从沼气出口8-2流出;Step 2, the desulfurized biogas after reacting with the absorption liquid continues to flow to the top of the
步骤三、三氯化铁吸收液与沼气中的硫化氢反应后大部分变为二氯化铁溶液,二氯化铁溶液和反应生成的硫单质从脱硫塔8底端的第一导管5流出,开启第一水泵6,使二氯化铁溶液和反应生成的硫单质进入沉降槽9内,硫单质在沉降槽9中经沉降分离后从排泥管12排出;
步骤四、沉降槽9内的二氯化铁溶液经第二导管14进入再生电解槽10内进行再生反应,
反应方程式如下:The reaction equation is as follows:
2H++2e-→H2(电解)2H + +2e - →H 2 (electrolysis)
Fe2+-e-→Fe3+(电解)Fe 2+ -e - →Fe 3+ (electrolysis)
反应生成的氢气从出氢管13排出,经过再生的二氯化铁溶液反应生成三氯化铁吸收液,生成的三氯化铁吸收液通过回流管11进入脱硫塔8进行循环反应。The hydrogen gas generated by the reaction is discharged from the
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