91精品国产91久久久久久三级-中文字幕国产免费视频-日本加勒比不卡日韩-性做久久久久久久免费看-国产在线综合网视频-久久久久久久大逼-日韩成人爱爱电影-极品人妻少妇精品一区二区-日韩欧美人妻第一页,久久91亚洲精品久久91,五月婷婷人妻激情,91熟女一区二区三区蜜桃

歡迎進(jìn)入山東恒能環(huán)保能源設(shè)備有限公司

熱線電話

0531-69953988

分類導(dǎo)航
產(chǎn)品展示
聯(lián)系我們
山東恒能環(huán)保能源設(shè)備有限公司

聯(lián)系電話:18678860671

服務(wù)熱線:0531-69953988

聯(lián)系地址:中國(山東)自由貿(mào)易試驗(yàn)區(qū)濟(jì)南片區(qū)孫村街道經(jīng)十東路33688號章錦綜合保稅區(qū)聯(lián)東U谷科創(chuàng)中心5號樓 101

常用的沼氣提純技術(shù),技術(shù)詳解。

(1)脫H2O

脫H2O是因?yàn)閷?dǎo)氣管中如果積累了水會(huì)溶解H2S腐蝕管道,此外當(dāng)沼氣被加壓儲(chǔ)存時(shí),沼氣中的水會(huì)凝結(jié)凍壞儲(chǔ)氣罐。發(fā)酵裝置出來的沼氣中所含的水分形式是飽和水蒸氣,一般采用冷分離法將其除去。通過調(diào)整壓力引起混合氣體溫度發(fā)生變化,使水蒸氣從氣態(tài)冷凝為液態(tài)的水后,將其從沼氣中脫除。此法經(jīng)濟(jì)簡單,被大多數(shù)沼氣工程所采用。
沼氣冷卻的方式有自然降溫及機(jī)械脫水兩種。冷卻溫度還要考慮下一步脫硫過程中不同脫硫劑對水分量的要求,根據(jù)脫硫劑的水分合理量進(jìn)行適當(dāng)?shù)某醪嚼鋮s。
在沼氣輸送過程中,還有一部分水要析出。為了避免析出的水分腐蝕或堵塞管道,常在管路的低處安裝集水器,定期排除集水器中的水。
沼氣提純
(1) H2O removal
H2O removal is due to the fact that H2S will dissolve and corrode the pipeline if water accumulates in the air duct. In addition, when methane is stored under pressure, the water in the methane will condense and freeze the air storage tank. The form of moisture contained in biogas from fermentation unit is saturated steam, which is generally removed by cold separation method. The temperature of the mixed gas is changed by adjusting the pressure, so that water vapor is condensed into liquid water from a gaseous state and then removed from biogas. This method is economical and simple, and is adopted by most biogas projects.
There are two ways of methane cooling: natural cooling and mechanical dehydration. The cooling temperature should also consider the water content requirements of different desulfurizers in the next desulfurization process, and appropriate preliminary cooling should be carried out according to the reasonable water content of the desulfurizer.
In the process of biogas transportation, there is still some water to be separated out. In order to prevent the precipitated water from corroding or blocking the pipeline, a water collector is often installed at the lowest part of the pipeline, and the water in the water collector is regularly drained.
(2)脫H2S
脫H2S是為了避免H2S腐蝕設(shè)備、H2S中毒和如果沼氣燃燒H2S被氧化成SO2或SO3造成更大的危害。
總結(jié)出來的8種H2S脫除方法可以分為物理提純、化學(xué)凈化和生物吸收?,F(xiàn)就3種機(jī)理中常用的方法分析如下。
① 活性炭吸附工藝。在變壓吸附系統(tǒng)中H2S可以通過用KI浸泡過的活性炭去除。此過程中,H2S被轉(zhuǎn)化為單質(zhì)S和H2O,單質(zhì)S就被活性炭吸收了。在連續(xù)運(yùn)行的情況下,系統(tǒng)要包含兩個(gè)吸附裝置。如果活性炭上H2S的濃度超過3ppm,需要進(jìn)行再生。
② 氧化鐵吸收工藝。通過氧化鐵來吸收沼氣中的H2S,此工藝的脫硫原理如下:
Fe2O3?H2O+H2→Fe2S3?H2O+3H2O
(1)此反應(yīng)是放熱反應(yīng),低溫度要求12℃,佳反應(yīng)溫度為25℃~50℃。所以,實(shí)際工程運(yùn)營中,需要加熱來達(dá)到佳反應(yīng)溫度。另外,H2S的脫除是通過在活性氧化鐵表面的水膜中離解成H+和S2+后,再進(jìn)行化學(xué)反應(yīng)。因?yàn)榇朔磻?yīng)需要一定量的水,一般要將脫硫劑的水分含量控制在10%~15%。所以沼氣在前面的脫水過程中溫度不能太低,水分不能脫除得太多,但也應(yīng)避免生成的冷凝水使球狀氧化鐵粘在一起,減少了反應(yīng)表面,從而影響脫硫效果。
此法的脫硫工藝中產(chǎn)生的硫化鐵可以被空氣氧化再生,生成氧化鐵和單質(zhì)S。此工藝的反應(yīng)原理如下,
Fe2S3?H2O+3/2O2→Fe2O3+3S+609kJ
(2)從反應(yīng)式可以看出,再生過程中會(huì)放出大量的熱,因此常常會(huì)發(fā)生自燃。為防止脫硫劑自燃,一般需要對卸除的廢脫硫劑噴灑少量水。另外,在經(jīng)過很多次重復(fù)使用后,氧化鐵的表面上會(huì)覆蓋一層硫單質(zhì),所以就需要更換氧化鐵。通常一個(gè)裝置中要配有兩個(gè)反應(yīng)床,一個(gè)進(jìn)行脫硫時(shí),另一個(gè)可以進(jìn)行再生。
在目前的畜禽養(yǎng)殖場沼氣工程中,氧化鐵吸收工藝被稱為干法脫硫。另外有一種常用的濕法脫硫。濕法脫硫的脫硫劑多用濃度為2%~3%的碳酸鈉溶液。此兩方法的脫硫劑都可以再生。
③ 生物脫硫法。該法是利用無色硫細(xì)菌,如氧化硫硫桿菌、氧化亞鐵硫桿菌等,在一定的溫度、濕度和微氧的條件下,將H2S氧化成單質(zhì)S或H2SO3。脫硫機(jī)理為:①H2S氣體溶解,即由氣相轉(zhuǎn)化為液相;②溶解后的H2S被微生物吸收,轉(zhuǎn)移至微生物體內(nèi);③進(jìn)入微生物細(xì)胞內(nèi)的H2S作為營養(yǎng)物被微生物分解、轉(zhuǎn)化和利用,從而達(dá)到去除H2S的目的。其反應(yīng)方程式如下:
2H2S+3O2→2H2SO3                 
2H2S+ O2→2S+2H2O
大部分的硫氧化細(xì)菌都屬于硫桿菌屬。硫桿菌隨處可見,用來脫除H2S并不需要接種。另外,大多硫桿菌是自養(yǎng)的,厭氧消化物的表面可以提供給它們一個(gè)生長所需的微觀好氧環(huán)境和必需的營養(yǎng)。所以,運(yùn)用生物法脫硫,直接往厭氧消化罐或儲(chǔ)氣罐中通入一定量的O2或空氣并保持一定時(shí)間即可,方法比較簡單。適當(dāng)?shù)臏囟?、反?yīng)時(shí)間和空氣量可以使沼氣中的H2S含量減少至50ppm。
在實(shí)際運(yùn)用中,沼氣中通入O2或空氣的量根據(jù)沼氣中H2S的含量確定,一般為2%~6%的空氣。對于不同甲烷含量的沼氣,空氣中的爆炸范圍不同,所以必需采取一定的安全措施避免沼氣中通入過量的空氣引起爆炸。同時(shí),生物脫硫也存在過程不容易控制、脫除出來的單質(zhì)S容易堵塞填料及損害曝氣頭等缺點(diǎn)。
(2) H2S removal
H2S removal is to avoid H2S corrosion of equipment, H2S poisoning and greater harm if H2S is oxidized to SO2 or SO3 during biogas combustion.
The eight H2S removal methods summarized can be divided into physical purification, chemical purification and biological absorption. Now, the methods commonly used in the three mechanisms are analyzed as follows.
(1) activated carbon adsorption process. H2S can be removed by activated carbon soaked with KI in pressure swing adsorption system. In this process, H2S is converted into elemental S and H2O, and elemental S is absorbed by activated carbon. Under the condition of continuous operation, the system should include two adsorption devices. If the concentration of H2S on activated carbon exceeds 3ppm, regeneration is required.
(2) iron oxide absorption process. The H2S in biogas is absorbed by ferric oxide. The desulfurization principle of this process is as follows:
Fe2O3? H2O+H2→Fe2S3? H2O+3H2O
(1) this reaction is exothermic, the minimum temperature is 12℃, and the optimal reaction temperature is 25℃ ~ 50℃. Therefore, in actual engineering operation, heating is required to reach the optimal reaction temperature. In addition, H2S removal is carried out by dissociating into H+ and S2+ in the water film on the surface of active iron oxide, and then carrying out chemical reaction. Because this reaction requires a certain amount of water, the moisture content of the desulfurizing agent is generally controlled at 10% ~ 15%. Therefore, the temperature of biogas in the previous dehydration process cannot be too low and the moisture cannot be removed too much, but the condensed water generated should also be avoided to make spherical iron oxide stick together, reducing the reaction surface and thus affecting the desulfurization effect.
Iron sulfide produced in the desulfurization process of this method can be oxidized and regenerated by air to produce iron oxide and elemental S .. The reaction principle of this process is as follows.
Fe2S3? H2O+3/2O2→Fe2O3+3S+609kJ
(2) As can be seen from the reaction formula, a large amount of heat will be released during regeneration, so spontaneous combustion often occurs. In order to prevent the desulfurizer from spontaneous combustion, it is generally necessary to spray a small amount of water on the discharged waste desulfurizer. In addition, after repeated use for many times, the surface of iron oxide will be covered with a layer of elemental sulfur, so it is necessary to replace iron oxide. Usually one unit is equipped with two reaction beds, one for desulfurization and the other for regeneration.
In the current biogas project of livestock and poultry farms, iron oxide absorption process is called dry desulfurization. In addition, there is a common wet desulfurization method. The desulfurizer for wet desulfurization is mostly sodium carbonate solution with concentration of 2% ~ 3%. The desulfurizer of both methods can be regenerated.
(3) biological desulfurization method. The method uses colorless sulfur bacteria, such as thiobacillus thiooxidans and thiobacillus ferrooxidans, to oxidize H2S into elemental S or H2SO3 under certain temperature, humidity and micro-oxygen conditions. The desulfurization mechanism is as follows: ①H2S gas dissolves, i.e. changes from gas phase to liquid phase; (2) Dissolved H2S is absorbed by microorganisms and transferred to microorganisms; (3) H2S entering microbial cells is decomposed, transformed and utilized by microorganisms as nutrients, thus achieving the purpose of H2S removal. The reaction equation is as follows:
2H2S+3O2→2H2SO3
2H2S+ O2→2S+2H2O
Most sulfur oxidizing bacteria belong to the genus Thiobacillus. Thiobacillus can be found everywhere, and inoculation is not required for H2S removal. In addition, most thiobacilli are autotrophic, and the surface of anaerobic digests can provide them with a micro aerobic environment and necessary nutrition for growth. Therefore, it is simple to apply biological desulfurization by directly introducing a certain amount of O2 or air into the anaerobic digestion tank or gas storage tank and keeping it for a certain period of time. Proper temperature, reaction time and air volume can reduce H2S content in biogas to 50ppm.
In actual application, the amount of O2 or air introduced into the biogas is determined according to the H2S content in the biogas, which is generally 2% ~ 6% air. For methane with different methane content, the explosion range in the air is different, so certain safety measures must be taken to prevent methane from introducing excessive air to cause explosion. At the same time, biological desulfurization also has the disadvantages that the process is not easy to control, the removed elemental S is easy to block the filler and damage the aeration, etc.
生物脫硫,沼氣脫硫,沼氣提純問題請點(diǎn)擊了解。
 

相關(guān)產(chǎn)品 我們的存在,是為了更好的服務(wù)于沼氣等可燃?xì)怏w凈化及利用行業(yè)
jizzxxxxx69-欧美穿高跟鞋日屄视频-肥老熟妇伦子伦-神马一级又粗又长又大 | 四虎影院久久-亚洲日本va中文字幕久久-wwww.美女-老女人乱婬AAAA片免费看软件 | 吹潮喷水白浆在线播放-亚洲美女插-99久久精品视香蕉蕉-黑人60厘米巨大全进入 | 毛片基地人与兽-色人阁91-17c..一起草 91精品无码少妇三区四区迅雷-中国hairy多毛pics视频大全 亚洲风间-乱色精品无码一区二区国产盗-DVD电影在线观看 亚洲国产日韩欧美今日更新-91av探花 | 搞av高清在线-伊人网在线-我们最主流的亚洲黄色视频网站为脱颖而出汇集了强大的91av在线播放观看国产-jizzjizzjizzjizz日本人 | 一本色爱爱-久久女上位-亚洲永久无码7777kkk-内射日本女人 | 自产一区二区三区国产-ziwei看的网站-国产日产欧产精品精品推荐在线-东凛 色情影片 - 8MAV | 熟女人妻少妇-一本一道加勒比北岛玲-99国产精品一区-赵丽颖色情A级毛片在线 | 俄罗斯美女下面又紧又爽-大香蕉三级电影-亚洲av永久无码精品一区二区国产-国产农村无套内谢视频 樱花影视 免费高清电影电视剧手机版在线观看-玩弄丰满人妻-极品美女想被c-2020最新国产精品视频 | 本庄優花AV101无码播放-一本加勒比hezyo无码人妻-国产亚洲欧美在线专区-水菜丽の黑人在线播放 | 国产成人亚洲精品播放器下载-高清电影全集观看-北条麻妃性爱视频无码-俺去了中文字幕 | 亚洲黄色片DVD在线观看-黑人把少妇干到冒白浆-内射少妇38-最新无码国产在线视频人与 | futa女女疯狂榨精3D-国产亚洲精久久久久久叶玉卿-高清在线播放观看 精品成人A片久久久久久船舶-安徽妇搡BBBB搡BBBB | 黄色片子女生和男人操-美女裸体黄片-中文字幕一区二区三区三州-国产91看片中文字幕日本二区 | 同时也可以进行聊天互动。-麻生希被躁57分钟在线-波多野结衣四虎-欧美黑人大香蕉 | 办公室日本肉丝OL在线视频-伊人色逼网-爱搞逼综合网激情保姆-能看的人与兽网站 | 黑人videos巨大hd粗暴的剧情简介-人妻熟妇91Porn 九色-大香蕉中文第三页-中文字幕150页 | 国产香蕉国产精品偷在线观看-中文字幕一区二区三区-五十岁四川熟女露脸啪啪-友田真希浓厚舌吻 | 人人超碰人人爱国产-初尝人妻少妇酷客影院-91亚洲欧美激情-国产无遮挡又黄又爽动态图 | 品鲁一鲁一区二区-亚洲人毛茸茸孕妇-精品国产av 无码一区二区三区-一级一级免费黄色大片 | 九九精华-北条麻妃人妻熟女无修正-884aa四虎影成人精品一区-无码精品人妻一区二区三区涵爰 | 爆操小仙女-欧美明星久久久A-台湾佬中文字幕在线中文字幕-中文字幕在线视频伊人二区青青天堂 | 亂伦HD裸体按摩HD-日韩a高清极品三级-午夜不卡av免费-国产熟女群搜索91Porn | 亚洲欧美v国产蜜芽tv-蓝光免费观看 国产精品自产拍av在线-国产WjjZZ-三上悠亚青苹果乐园影视 | 熟女自慰100部-午夜中文字幕电影网-北条麻妃一级黄色片-又粗又大又长三级黄片 | 香蕉狼人狠狠干-欧美日韩一区二区综合在线视频-国模精品一区二区三区-黑人添荫道囗吃奶视频 | jizzjizzjizz护士高潮-欧美性生交XXXXX-gogogo免费手机高清在线 日韩高清A片-PGD-736誘惑女教师痴女在线观看 | 亚洲国产成人久久午夜-小莹好湿好紧太爽了电影在线-69XXXXXXXXXXX台湾-日日橹狠狠爱欧美超碰 | 伊人狼人在线-国产视频99-啪啪片动漫-国产精品专区电影院 | 国产免费黄色录像-美女裸体十八禁-日韩无码黄片亚洲Aⅴ-高H文小骚B女高中生 | 国产一区二区三区gay男同-神木麓无码巨乳在线-国产香蕉视频在线播放-亚洲中文字幕无码久久2017 | 国内自拍偷拍网站-DVD在线观看 亚洲欧美在线精品一区二区-国产靠逼大全-超清免费电视剧 久久精品国产亚洲?v久 | 爽妇导航-北条麻妃潮喷-BD英语高清在线 亚洲天堂视频在线观看-自拍偷拍视频网址 | 91精品国产乱码在线观看入-情人教我操逼av-靠逼网站在线观看-色欲狠狠躁天天躁无码中文字幕 | 国产农村妇女AAAAA视频-狼人干依人网-蓬莱仙山国模裸体自慰-国产闺蜜女同疯狂摩擦 | BDBD在线观看 131美女爱做免费高清视频-国产激情一区二区三区成人-www.黄色AV91.wwe-百永纱里奈无码片(SCOP-752) | 北条麻妃丝袜诱惑-1204你懂人妻-麻豆av无码精品一区二区-精品一区二区三区自拍图片区 | 中国free性精品自拍-欧美女人逼-军人丰满双乳好大-台湾九一制片厂三级按摩视频 | 女人自慰一级无遮挡毛片-jzzjzz大片免费观看-超碰在线25-狠狠操社区 | BD英语神马影院手机在线-手机免费有坂深雪电影中文字幕亚洲区-jiZZjiZZji 欧美-男女又爽 又黄 免费蘑菇 | 四十路中出精品区-饭岛爱网站免费入口-老司机熟女网站-91精品免费久久久久久久久 |