CN201648109U - A Biogas Production-Desulfurization Integrated Device - Google Patents

A Biogas Production-Desulfurization Integrated Device Download PDF

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CN201648109U
CN201648109U CN2010201095947U CN201020109594U CN201648109U CN 201648109 U CN201648109 U CN 201648109U CN 2010201095947 U CN2010201095947 U CN 2010201095947U CN 201020109594 U CN201020109594 U CN 201020109594U CN 201648109 U CN201648109 U CN 201648109U
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biogas
desulfurization
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spray liquid
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郑平
陆慧锋
陈小光
余一
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Zhejiang University ZJU
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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Abstract

本实用新型公开了一种沼气生产-脱硫一体化装置。其主体包括沼气生产区I、三相分离区II、单质硫分离区III和沼气脱硫区IV。沼气生产区底部设有排泥管,反应筒的壁上设有进水管、取样管和回流管;三相分离区内部设有污泥沉淀室、倒漏斗状三相分离器和第一气室,筒壁上设有溢流出水管和喷淋液回流管;单质硫分离区内部设有斜板式喷淋液贮槽,贮槽板面上纵向设有空气输入管、沼气输入管和锥形布气器,贮槽中心设有喷淋液液位管,筒壁外侧设有气体监测采样管和排硫管;沼气脱硫区的脱硫筒内部设有生物填料、盘型喷淋头和第三气室,筒壁上设有沼气输出管。本实用新型中厌氧反应器与生物脱硫装置融于一体,气相中脱除H2S,可促进液相中H2S释放。

Figure 201020109594

The utility model discloses a biogas production-desulfurization integrated device. Its main body includes biogas production zone I, three-phase separation zone II, elemental sulfur separation zone III and biogas desulfurization zone IV. There is a sludge discharge pipe at the bottom of the biogas production area, and a water inlet pipe, a sampling pipe and a return pipe on the wall of the reaction cylinder; a sludge settling chamber, an inverted funnel-shaped three-phase separator and a first air chamber are arranged inside the three-phase separation area , there are overflow outlet pipes and spray liquid return pipes on the wall of the cylinder; there is an inclined plate type spray liquid storage tank inside the elemental sulfur separation area, and an air input pipe, a biogas input pipe and a tapered cloth are arranged longitudinally on the storage tank plate. There is a spray liquid level pipe in the center of the storage tank, and a gas monitoring sampling pipe and a sulfur discharge pipe are installed on the outside of the cylinder wall; the desulfurization cylinder in the biogas desulfurization area is equipped with biological fillers, disc sprinklers and a third gas chamber, and a methane output pipe is arranged on the cylinder wall. In the utility model, the anaerobic reactor and the biological desulfurization device are integrated, and H 2 S is removed in the gas phase, which can promote the release of H 2 S in the liquid phase.

Figure 201020109594

Description

一种沼气生产-脱硫一体化装置 A Biogas Production-Desulfurization Integrated Device

技术领域technical field

本实用新型涉及有机废水厌氧处理装置,尤其涉及一种沼气生产-脱硫一体化装置。The utility model relates to an anaerobic treatment device for organic waste water, in particular to a biogas production-desulfurization integrated device.

背景技术Background technique

沼气发酵是有机废水处理的重要手段之一。由于运行成本低、污泥产量少、可回收沼气,沼气发酵技术受到了环境工程界的青睐。生活污水含有3~6mg/L有机硫和30~60mg/L无机硫,一些工业有机废水(如纸浆废水、制革废水、制药废水等)的硫酸盐含量甚至高达9000mg/L以上。在这些含硫废水的厌氧生物处理过程中,会产生大量硫化氢气体,浓度约为1~20g/m3。硫化氢是一种剧毒有害气体。在空气中及潮湿环境条件下,硫化氢对管道、燃烧器以及其它金属设备、仪器仪表等有强烈腐蚀作用;硫化氢燃烧生成二氧化硫,可直接影响人类身体健康;二氧化硫遇水生成硫酸,则有强烈的腐蚀作用。沼气脱硫是沼气生产中不可或缺的处理工序。Biogas fermentation is one of the important means of organic wastewater treatment. Biogas fermentation technology is favored by environmental engineering circles due to low operating costs, low sludge output, and recyclable biogas. Domestic sewage contains 3-6mg/L organic sulfur and 30-60mg/L inorganic sulfur, and the sulfate content of some industrial organic wastewater (such as pulp wastewater, tannery wastewater, pharmaceutical wastewater, etc.) is even as high as 9000mg/L or more. During the anaerobic biological treatment of these sulfur-containing wastewater, a large amount of hydrogen sulfide gas will be produced, with a concentration of about 1-20 g/m 3 . Hydrogen sulfide is a highly toxic and harmful gas. In the air and under humid environment conditions, hydrogen sulfide has a strong corrosive effect on pipes, burners, and other metal equipment, instruments, etc.; hydrogen sulfide combustion produces sulfur dioxide, which can directly affect human health; Strong corrosive effect. Biogas desulfurization is an indispensable treatment process in biogas production.

沼气脱硫的方法有化学法、物化法和生物法等。目前我国沼气工程上普遍应用的脱硫技术以物理化学法为主(俗称干法脱硫),即用三氧化二铁脱硫剂脱除沼气中的H2S。在常温下,沼气通过脱硫剂床层,硫化氢与活性氧化铁接触,生成三硫化二铁,然后与空气接触,铁的硫化物转化为氧化铁和单质硫。这样的脱硫再生过程可循环多次,直至氧化铁脱硫剂表面的大部分孔隙被硫或其他杂质覆盖而失去活性。氧化铁干法脱硫工艺简单,成熟可靠,造价低(25m3脱硫塔造价约为8万),能达到较高的净化程度。但是,此法处理成本较高(15元/kg(H2S)左右),运行操作麻烦(每4~6个月需更换或再生脱硫剂一次),且废弃的脱硫剂存在二次污染问题。The methods of biogas desulfurization include chemical method, physicochemical method and biological method. At present, the desulfurization technology commonly used in China's biogas projects is mainly based on physical and chemical methods (commonly known as dry desulfurization), that is, using ferric oxide desulfurizer to remove H 2 S in biogas. At normal temperature, biogas passes through the bed of desulfurizer, hydrogen sulfide contacts with active iron oxide to generate iron trisulfide, and then contacts with air, and the iron sulfide is converted into iron oxide and elemental sulfur. Such a desulfurization regeneration process can be cycled many times until most of the pores on the surface of the iron oxide desulfurizer are covered with sulfur or other impurities and lose their activity. The iron oxide dry desulfurization process is simple, mature and reliable, and the cost is low (the cost of a 25m 3 desulfurization tower is about 80,000), which can achieve a high degree of purification. However, the treatment cost of this method is high (about 15 yuan/kg (H 2 S)), the operation is troublesome (the desulfurizer needs to be replaced or regenerated once every 4 to 6 months), and the waste desulfurizer has secondary pollution problems .

与物理法和化学法相比,生物法脱硫具有设备简单、成本低、环保清洁、可回收单质硫等特点,是极具发展潜力的脱硫技术。所谓生物脱硫,就是在合适的温度、湿度、营养和供氧条件下,通过硫细菌的代谢作用将硫化氢转化为单质硫或者硫酸。反应过程为:Compared with physical and chemical methods, biological desulfurization has the characteristics of simple equipment, low cost, environmental protection and cleanness, and recyclable elemental sulfur. It is a desulfurization technology with great development potential. The so-called biological desulfurization is to convert hydrogen sulfide into elemental sulfur or sulfuric acid through the metabolism of sulfur bacteria under suitable temperature, humidity, nutrition and oxygen supply conditions. The reaction process is:

H2S+2O2——H2SO4 H 2 S+2O 2 ——H 2 SO 4

2H2S+O2——2S°+2OH- 2H 2 S+O 2 —— 2S°+2OH -

将沼气生产与沼气脱硫合二为一,开发沼气生物-脱硫一体化装置,不仅可以简化设备,省去沼气输送气泵,还可以原位缓解硫化氢对厌氧消化的抑制作用,提高厌氧反应器对含硫废水的适应性。Combining biogas production and biogas desulfurization to develop biogas bio-desulfurization integrated device can not only simplify the equipment and save the biogas delivery pump, but also relieve the inhibitory effect of hydrogen sulfide on anaerobic digestion in situ and improve the anaerobic reaction The adaptability of the device to sulfur-containing wastewater.

发明内容Contents of the invention

本实用新型的目的是克服现有技术的不足,提供一种沼气生产-脱硫一体化装置。The purpose of the utility model is to overcome the deficiencies of the prior art and provide a biogas production-desulfurization integrated device.

沼气生产-脱硫一体化装置包括沼气生产装置和沼气脱硫装置,沼气生产装置包括沼气生产区I和三相分离区II,沼气脱硫装置包括单质硫分离区III和沼气脱硫区IV,沼气生产区I底部设有排泥管,反应筒的壁上从下到上依次设有进水管、取样管和回流管;三相分离区II内部从下到上依次设有污泥沉淀室、倒漏斗状三相分离器和第一气室,三相分离区筒壁外侧设有溢流出水管和喷淋液回流管;单质硫分离区III内部设有斜板式喷淋液贮槽,斜板式喷淋液贮槽的斜板板面上纵向设有空气输入管、沼气输入管和锥形布气器,斜板中心设有喷淋液液位管,斜板喷淋液贮槽上方设有第二气室,单质硫分离区III筒壁外侧设有气体监测采样管和排硫管;沼气脱硫区IV主体为脱硫筒,脱硫筒内部从下到上依次设有生物填料、盘型喷淋头和第三气室,脱硫筒的壁上设有沼气输出管,盘型喷淋头通过输送管与外部的循环喷淋泵相连。Biogas production-desulfurization integrated device includes biogas production device and biogas desulfurization device, biogas production device includes biogas production area I and three-phase separation area II, biogas desulfurization device includes elemental sulfur separation area III and biogas desulfurization area IV, biogas production area I There is a sludge discharge pipe at the bottom, and a water inlet pipe, a sampling pipe and a return pipe are arranged on the wall of the reaction cylinder from bottom to top; a sludge settling chamber, an inverted funnel-shaped three-phase The phase separator and the first air chamber, the overflow outlet pipe and the spray liquid return pipe are arranged on the outside of the cylinder wall of the three-phase separation area; the inclined plate type spray liquid storage tank is installed inside the elemental sulfur separation area III, There are air input pipe, biogas input pipe and conical air distributor longitudinally on the inclined plate surface of the tank, a spray liquid level pipe is installed in the center of the inclined plate, and a second air chamber is arranged above the inclined plate spray liquid storage tank The gas monitoring sampling pipe and sulfur discharge pipe are installed outside the wall of elemental sulfur separation zone III; the main body of biogas desulfurization zone IV is a desulfurization cylinder, and the interior of the desulfurization cylinder is sequentially equipped with biological fillers, disc sprinklers and the third The gas chamber and the wall of the desulfurization cylinder are provided with biogas output pipes, and the disc-shaped spray head is connected with the external circulating spray pump through the delivery pipe.

所述的沼气生产装置与沼气脱硫装置的体积比为2.5∶1~5∶1。所述的喷淋液液位管上端与斜板式喷淋液贮槽内液体表面齐平,锥形布气器比斜板式喷淋液贮槽内液面高2~4cm,喷淋液液位管下端浸入三相分离区II发酵液液面下3~4cm,斜板式喷淋液贮槽的斜板与水平面夹角α为20°~30°,斜板式喷淋液贮槽的斜板低端与排硫管相连,喷淋液回流管管口设在三相分离区II发酵液液面下5cm。The volume ratio of the biogas production unit to the biogas desulfurization unit is 2.5:1˜5:1. The upper end of the spray liquid level pipe is flush with the liquid surface in the inclined plate type spray liquid storage tank, the conical air distributor is 2-4cm higher than the liquid level in the inclined plate type spray liquid storage tank, and the spray liquid level The lower end of the tube is immersed 3 to 4 cm below the surface of the fermented liquid in the three-phase separation zone II. The angle α between the inclined plate and the horizontal plane of the inclined plate spray liquid storage tank is 20° to 30°, and the inclined plate of the inclined plate spray liquid storage tank is low. The end is connected with the sulfur discharge pipe, and the nozzle of the spray liquid return pipe is set at 5 cm below the liquid surface of the fermentation broth in the three-phase separation zone II.

本实用新型的有益效果有:①厌氧反应器与生物脱硫装置融于一体,沼气边产生边脱硫,无需气泵输送;②以沼气发酵液作为喷淋液,既可利用发酵液中的养分而节省成本,也可利用发酵液中的碱度而强化H2S吸收;③将H2S氧化成单质硫,可回收硫资源;④气相中脱除H2S,可促进液相中H2S释放,从而缓解沼气生产区的H2S抑制;⑤化学转化与生物转化同时进行,沼气脱硫速率快,处理效果好。The beneficial effects of the utility model are as follows: ①The anaerobic reactor and the biological desulfurization device are integrated, and the biogas is desulfurized while generating, without air pump transportation; ②Using the biogas fermentation liquid as the spray liquid, the nutrients in the fermentation liquid can be used Save cost, and use the alkalinity in the fermentation broth to enhance the absorption of H 2 S; ③ oxidize H 2 S to elemental sulfur, which can recover sulfur resources; ④ Remove H 2 S in the gas phase, which can promote H 2 in the liquid phase S release, thereby alleviating the inhibition of H 2 S in the biogas production area; ⑤Chemical conversion and biological conversion are carried out at the same time, the biogas desulfurization rate is fast, and the treatment effect is good.

附图说明Description of drawings

图1是沼气生产-脱硫一体化装置的结构示意图;Fig. 1 is a structural schematic diagram of a biogas production-desulfurization integrated device;

图2是本发明斜板式喷淋液贮槽的剖视图。Fig. 2 is a sectional view of the inclined plate type spray liquid storage tank of the present invention.

图中:排泥管1、进水管2、反应筒3、取样管4、回流管5、污泥沉淀室6、倒漏斗状三相分离器7、溢流出水管8、喷淋液液位管9、第一气室10、空气输入管11、沼气输入管12、气体监测采样管13、第二气室14、生物填料15、盘型喷淋头16、第三气室17、沼气输出管18、循环喷淋泵19、脱硫筒20、锥形布气器21、斜板式喷淋液贮槽22、排硫管23和喷淋液回流管24。In the figure: sludge discharge pipe 1, water inlet pipe 2, reaction cylinder 3, sampling pipe 4, return pipe 5, sludge settling chamber 6, inverted funnel-shaped three-phase separator 7, overflow outlet pipe 8, spray liquid level pipe 9. First air chamber 10, air input pipe 11, biogas input pipe 12, gas monitoring sampling pipe 13, second air chamber 14, biological filler 15, disk-shaped sprinkler head 16, third air chamber 17, biogas output pipe 18. Circulating spray pump 19, desulfurization cylinder 20, conical air distributor 21, sloping plate type spray liquid storage tank 22, sulfur discharge pipe 23 and spray liquid return pipe 24.

具体实施方式Detailed ways

如图1所述,沼气生产-脱硫一体化装置包括沼气生产装置和沼气脱硫装置,沼气生产装置包括沼气生产区I和三相分离区II,沼气脱硫装置包括单质硫分离区III和沼气脱硫区IV,沼气生产区I底部设有排泥管1,反应筒3的壁上从下到上依次设有进水管2、取样管4和回流管5;三相分离区II内部从下到上依次设有污泥沉淀室6、倒漏斗状三相分离器7和第一气室10,三相分离区筒壁外侧设有溢流出水管8和喷淋液回流管24;单质硫分离区III内部设有斜板式喷淋液贮槽22,斜板式喷淋液贮槽22的斜板板面上纵向设有空气输入管11、沼气输入管12和锥形布气器21,斜板中心设有喷淋液液位管9,斜板喷淋液贮槽22上方设有第二气室14,单质硫分离区III筒壁外侧设有气体监测采样管13和排硫管23;沼气脱硫区IV主体为脱硫筒20,脱硫筒20内部从下到上依次设有生物填料15、盘型喷淋头16和第三气室17,脱硫筒20的壁上设有沼气输出管18,盘型喷淋头通过输送管与外部的循环喷淋泵19相连。As shown in Figure 1, the biogas production-desulfurization integrated device includes a biogas production device and a biogas desulfurization device, the biogas production device includes a biogas production area I and a three-phase separation area II, and the biogas desulfurization device includes an elemental sulfur separation area III and a biogas desulfurization area IV, the bottom of the biogas production area I is provided with a sludge discharge pipe 1, and the wall of the reaction cylinder 3 is provided with a water inlet pipe 2, a sampling pipe 4 and a return pipe 5 from bottom to top; A sludge settling chamber 6, an inverted funnel-shaped three-phase separator 7 and a first air chamber 10 are provided, and an overflow outlet pipe 8 and a spray liquid return pipe 24 are provided on the outside of the cylinder wall of the three-phase separation area; inside the elemental sulfur separation area III There is a slant plate type spray liquid storage tank 22, and the slant plate type spray liquid storage tank 22 is provided with an air input pipe 11, a biogas input pipe 12 and a conical air distributor 21 longitudinally on the slant plate surface of the slant plate type spray liquid storage tank 22, and the center of the slant plate is provided with The spray liquid level pipe 9, the second gas chamber 14 is arranged above the inclined plate spray liquid storage tank 22, the gas monitoring sampling pipe 13 and the sulfur discharge pipe 23 are arranged on the outside of the cylinder wall of the elemental sulfur separation zone III; the biogas desulfurization zone IV The main body is a desulfurization cylinder 20, and the inside of the desulfurization cylinder 20 is provided with a biological filler 15, a disc-shaped spray head 16 and a third air chamber 17 in sequence from bottom to top. The shower head is connected with the external circulating spray pump 19 through the delivery pipe.

所述的沼气生产装置与沼气脱硫装置的体积比为2.5∶1~5∶1。所述的喷淋液液位管9上端与斜板式喷淋液储槽22内液体表面齐平,锥形布气器21比斜板式喷淋液储槽22内液面高2~4cm,喷淋液液位管9下端浸入三相分离区II发酵液下3~4cm,斜板式喷淋液贮槽22的斜板与水平面夹角α为20°~30°,斜板式喷淋液贮槽22的斜板低端与排硫管23相连,喷淋液回流管24管口设在三相分离区II发酵液液面下5cm。The volume ratio of the biogas production unit to the biogas desulfurization unit is 2.5:1˜5:1. The upper end of the spray liquid level pipe 9 is flush with the liquid surface in the inclined plate type spray liquid storage tank 22, and the conical air distributor 21 is 2 to 4 cm higher than the liquid level in the inclined plate type spray liquid storage tank 22. The lower end of the shower liquid level pipe 9 is immersed in the three-phase separation zone II fermentation liquid for 3 to 4 cm, and the angle α between the inclined plate and the horizontal plane of the inclined plate type spray liquid storage tank 22 is 20° to 30°, and the inclined plate type spray liquid storage tank The lower end of the inclined plate of 22 links to each other with the sulfur exhaust pipe 23, and the mouth of the nozzle of the spray liquid return pipe 24 is located at 5 cm below the liquid surface of the fermented liquid in the three-phase separation zone II.

本实用新型的工作过程如下The working process of the present utility model is as follows

本实用新型分五个系统工作过程,具体如下:The utility model is divided into five system working processes, which are as follows:

(1)沼气生产系统。主要包括排泥区1、进水管2、反应筒3、取样管4、回流管5、倒漏斗状三相分离器7和溢流出水管8。废水进入沼气生产区I后经微生物作用产生沼气,颗粒污泥随上升的沼气和废水进入倒漏斗状三相分离器实现气液固三相分离。沼气进一步进入沼气脱硫装置,经处理后出水通过溢流出水管排出反应器。发酵液通过回流管5回流可促进液相中H2S释放。(1) Biogas production system. It mainly includes mud discharge area 1, water inlet pipe 2, reaction cylinder 3, sampling pipe 4, return pipe 5, inverted funnel-shaped three-phase separator 7 and overflow outlet pipe 8. After the wastewater enters the biogas production zone I, biogas is produced by microorganisms, and the granular sludge enters the inverted funnel-shaped three-phase separator with the rising biogas and wastewater to realize the three-phase separation of gas, liquid and solid. The biogas further enters the biogas desulfurization device, and the effluent after treatment is discharged from the reactor through the overflow outlet pipe. The reflux of the fermentation broth through the reflux pipe 5 can promote the release of H 2 S in the liquid phase.

(2)空气沼气进气、混合系统。空气输入管11、沼气输入管12和锥形布气器21呈嵌套式组合,上升的空气在锥形布气器内形成一定的真空度,对其下方的第一气室10具有抽提作用,可以促进液相中的硫化氢逸出。锥形布气器呈盘状分布,空气与沼气通过锥形布气器后,在第二气室充分混合,再上升通过填料15,在合适的温度、湿度、营养和供氧条件下,微生物完成脱硫反应,净化沼气经过沼气输出管18排出。(2) Air biogas intake and mixing system. The air input pipe 11, the biogas input pipe 12 and the conical air distributor 21 form a nested combination, and the rising air forms a certain degree of vacuum in the conical air distributor, which can extract the first air chamber 10 below it. The effect can promote the release of hydrogen sulfide in the liquid phase. The cone-shaped air distributor is distributed in a disc shape. After the air and biogas pass through the cone-shaped air distributor, they are fully mixed in the second air chamber, and then rise through the packing 15. Under appropriate temperature, humidity, nutrition and oxygen supply conditions, microorganisms After the desulfurization reaction is completed, the purified biogas is discharged through the biogas output pipe 18 .

(3)生物填料系统。脱硫筒20内充填钢丝球填料,形成一个立体的网状结构,供微生物生长。填料中的铁与气相中的硫化氢及喷淋液中的硫化物发生化学反应,可将硫固定,在合适的温度、湿度、营养和供氧条件下,附着在填料表面的微生物将固定的硫转化成单质硫或硫酸盐。边固硫边脱硫,脱硫剂表面不断更新。快速的化学固定与生物转化相结合,脱硫效果好、速率快。(3) Biological filler system. The desulfurization cylinder 20 is filled with steel ball packing to form a three-dimensional network structure for the growth of microorganisms. The iron in the filler chemically reacts with the hydrogen sulfide in the gas phase and the sulfide in the spray liquid to fix the sulfur. Under the appropriate temperature, humidity, nutrition and oxygen supply conditions, the microorganisms attached to the surface of the filler will be fixed. Sulfur is converted to elemental sulfur or sulfate. Desulfurization is performed while fixing sulfur, and the surface of the desulfurizer is constantly updated. Combining rapid chemical fixation and biotransformation, the desulfurization effect is good and the rate is fast.

(4)单质硫收集排放系统。斜板喷淋液贮槽22与水平面夹角为20~30°,经喷淋液冲刷脱落的单质硫进入斜板喷淋液贮槽22,在重力作用下,淋洗下来的单质硫转移至斜板喷淋液贮槽22底部,经排硫管23排出,喷淋液从喷淋液液位管回流至三相分离区II。(4) Elemental sulfur collection and discharge system. The angle between the inclined plate spray liquid storage tank 22 and the horizontal plane is 20-30°, the elemental sulfur washed off by the spray liquid enters the inclined plate spray liquid storage tank 22, and under the action of gravity, the elemental sulfur washed down is transferred to The bottom of the inclined plate spray liquid storage tank 22 is discharged through the sulfur discharge pipe 23, and the spray liquid flows back from the spray liquid level pipe to the three-phase separation zone II.

(5)供氧系统。采用测氧探头对沼气中的氧气进行监测,通过气体转子流量计调节曝气量大小,保证沼气脱硫装置中氧气含量达到生物脱硫的要求,实现硫化氢向单质硫的转化,以达到回收单质硫的目的。(5) Oxygen supply system. The oxygen in the biogas is monitored by the oxygen measuring probe, and the aeration volume is adjusted by the gas rotameter to ensure that the oxygen content in the biogas desulfurization device meets the requirements of biological desulfurization, and realize the conversion of hydrogen sulfide to elemental sulfur, so as to achieve the recovery of elemental sulfur the goal of.

Claims (3)

1. biogas production-desulfurization integrated device, it is characterized in that comprising biogas production device and methane-desulfurizing device, the biogas production device comprises biogas production district I and three-phase separation area II, methane-desulfurizing device comprises elemental sulfur separation area II I and biogas desulfurization district IV, I bottom in biogas production district is provided with shore pipe (1), is provided with water inlet pipe (2), stopple coupon (4) and return line (5) on the wall of reaction tube (3) from top to bottom successively; Three-phase separation area II inside is provided with sludge settling chamber (6), the triphase separator of falling the funnel-form (7) and first air chamber (10) from top to bottom successively, and the three-phase separation area II barrel outside is provided with and overflows water pipe (8) and spray liquid return line (24); Elemental sulfur separation area II I inside is provided with ramp type spray liquid storage tank (22), vertically be provided with air input tube (11), biogas input tube (12) and taper gas pipe (21) on the swash plate plate face of ramp type spray liquid storage tank (22), the swash plate center is provided with spray liquid liquid level tube (9), swash plate spray liquid storage tank (22) top is provided with second air chamber (14), and the elemental sulfur separation area II I barrel outside is provided with gas-monitoring sampling tube (13) and sulphur discharging pipeline (23); IV main body in biogas desulfurization district is desulfurization tube (20), desulfurization tube (20) inside is provided with biologic packing material (15), dish-type spray header (16) and the 3rd air chamber (17) from top to bottom successively, the wall of desulfurization tube (20) is provided with biogas output tube (18), and the dish-type spray header links to each other by the circulated sprinkling pump (19) of transfer lime with the outside.
2. biogas production-desulfurization integrated device according to claim 1 is characterized in that: the volume ratio of described biogas production device and methane-desulfurizing device is 2.5: 1~5: 1.
3. biogas production-desulfurization integrated device according to claim 1, it is characterized in that: described spray liquid liquid level tube (9) upper end flushes with the interior fluid surface of ramp type spray liquid storage tank (22), taper gas pipe (21) is than the high 2~4cm of the interior liquid level of ramp type spray liquid storage tank (22), 3~4cm under the fermented liquid liquid level at immersion three-phase separation area II place, spray liquid liquid level tube (9) lower end, the swash plate of ramp type spray liquid storage tank (22) and horizontal plane angle α are 20 °~30 °, the swash plate low side of ramp type spray liquid storage tank (22) links to each other with sulphur discharging pipeline (23), and spray liquid return line (24) mouth of pipe is located at 5cm under the three-phase separation area II fermented liquid liquid level.
CN2010201095947U 2010-02-05 2010-02-05 A Biogas Production-Desulfurization Integrated Device Expired - Lifetime CN201648109U (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101760425B (en) * 2010-02-05 2012-05-23 浙江大学 Biogas production-desulfurization integrated device
CN105793200A (en) * 2013-06-14 2016-07-20 R+I联合公司 Desulfurization method and equipment for biogas residue and biogas of digester
CN109603732A (en) * 2018-11-13 2019-04-12 中国石油天然气股份有限公司 Self-activating deoxidizing and desulfurizing packing structure
CN112546985A (en) * 2020-12-01 2021-03-26 安徽工程大学 In-situ biogas desulfurization device and method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101760425B (en) * 2010-02-05 2012-05-23 浙江大学 Biogas production-desulfurization integrated device
CN105793200A (en) * 2013-06-14 2016-07-20 R+I联合公司 Desulfurization method and equipment for biogas residue and biogas of digester
CN105793200B (en) * 2013-06-14 2018-01-12 R+I联合公司 Desulfurization method and equipment for biogas residue and biogas of digester
CN109603732A (en) * 2018-11-13 2019-04-12 中国石油天然气股份有限公司 Self-activating deoxidizing and desulfurizing packing structure
CN109603732B (en) * 2018-11-13 2021-01-29 中国石油天然气股份有限公司 Self-activating deoxidization desulfurization filler structure
CN112546985A (en) * 2020-12-01 2021-03-26 安徽工程大学 In-situ biogas desulfurization device and method

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