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CN104399735A - Pretreatment method for straw biomass - Google Patents

Pretreatment method for straw biomass Download PDF

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CN104399735A
CN104399735A CN201410614372.3A CN201410614372A CN104399735A CN 104399735 A CN104399735 A CN 104399735A CN 201410614372 A CN201410614372 A CN 201410614372A CN 104399735 A CN104399735 A CN 104399735A
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stalk biomass
straw
biomass
stalk
preprocess method
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CN104399735B (en
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卢新社
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Gansu Defu Biotechnology Co ltd
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GANSU XINDE GAS Co Ltd
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Abstract

本发明提供了一种秸秆类生物质的预处理方法,通过原料收集粉碎、原料堆沤、原料浸泡、混合加菌、密封降解的步骤,对秸秆类生物质进行预处理。利用该方法可以有效转化及降解秸秆中富含的纤维素、半纤维素和木质素,工艺简单,便于操作,运行成本低廉,效率高,不会污染环境,为加工秸秆类生物质提供便利。

The invention provides a method for pretreatment of straw-like biomass. The straw-like biomass is pretreated through the steps of collecting and pulverizing raw materials, stacking and retting raw materials, soaking raw materials, mixing and adding bacteria, and sealing and degrading. The method can effectively convert and degrade the cellulose, hemicellulose and lignin rich in straw, the process is simple, easy to operate, low in operation cost, high in efficiency, does not pollute the environment, and provides convenience for processing straw-like biomass.

Description

一种秸秆类生物质的预处理方法A kind of pretreatment method of straw biomass

技术领域technical field

本发明属于生物质利用技术领域,具体是一种秸秆类生物质的预处理方法,更具体的是由秸秆类生物质通过生物化学的方法实现其三大主要组分纤维素、半纤维素和木质素的转化及降解。The invention belongs to the technical field of biomass utilization, and specifically relates to a pretreatment method of straw-like biomass, and more specifically realizes the three main components of cellulose, hemicellulose and Transformation and degradation of lignin.

背景技术Background technique

由于传统能源的日益短缺,使得包括生物质在内的可再生能源的利用正在兴起,有望在未来的能源结构中扮演重要角色,农作物秸秆是地球上最丰富的生物质资源,据不完全统计,全世界每年可产生近20亿吨秸秆,而我国农作物秸秆年产量约为6~7亿吨,居世界之首,除去用于造纸、饲料外,还约有4亿吨秸秆可作为能源物质加以利用。Due to the increasing shortage of traditional energy, the use of renewable energy including biomass is on the rise and is expected to play an important role in the future energy structure. Crop straw is the most abundant biomass resource on the earth. According to incomplete statistics, The world can produce nearly 2 billion tons of straw every year, and the annual output of crop straw in my country is about 600-700 million tons, ranking first in the world. Apart from being used for papermaking and feed, there are about 400 million tons of straw that can be used as energy materials. use.

秸秆类生物质在利用过程中面临的主要技术障碍有两个:一是木质素包裹在纤维素和半纤维素的外面,从而对纤维素和半纤维素的降解构成了一层屏障;二是纤维素自身的高结晶结构不易降解,与非结晶区相比,纤维素的结晶区又占主体地位,可高达70%,因此预处理是利用木质纤维素生物燃料和生物制品的关键途径。There are two main technical obstacles in the utilization of straw-based biomass: one is that lignin is wrapped around the outside of cellulose and hemicellulose, thus forming a barrier to the degradation of cellulose and hemicellulose; the other is that The high crystalline structure of cellulose itself is not easy to degrade. Compared with the non-crystalline area, the crystalline area of cellulose occupies a dominant position, which can be as high as 70%. Therefore, pretreatment is a key way to utilize lignocellulosic biofuels and biological products.

针对秸秆沼气发酵过程中发酵效率低的问题,农业部规划设计研究院自主研发了秸秆一体化两相厌氧消化工艺技术,并将青贮饲料制作工艺改进为适于秸秆厌氧消化的预处理技术,自2009年至今该工艺已在天津、山东、陕西、山西、浙江、湖北等地推广应用近30余座,运行效果良好。Aiming at the problem of low fermentation efficiency in the straw biogas fermentation process, the Planning and Design Research Institute of the Ministry of Agriculture independently developed the straw integrated two-phase anaerobic digestion process technology, and improved the silage production process to a pretreatment technology suitable for straw anaerobic digestion , Since 2009, this process has been promoted and applied in Tianjin, Shandong, Shaanxi, Shanxi, Zhejiang, Hubei and other places for nearly 30 seats, and the operation effect is good.

但是从该工艺的应用情况看,秸秆沼气工程的发酵罐规模都不大,容积多在500~1500m3之间,原因在于需要配置青贮池,为保证原料的稳定性,青贮池容积要求能容纳一个收获季中秸秆用量,占地面积大。以发酵罐规模为1000m3的沼气工程为例,每天约可消纳青贮秸秆10t(约15m3),按运行一年计算,配套青贮池容积需要5400m3,占地约1500m2。因此,传统的场内青贮方式严重制约了该类沼气工程的规模化发展。However, judging from the application of this process, the scale of fermentation tanks in straw biogas projects is not large, and the volume is mostly between 500 and 1500m 3 . The amount of straw used in one harvest season covers a large area. Taking a biogas project with a fermenter size of 1000m 3 as an example, it can consume about 10t (about 15m 3 ) of silage straw per day. Calculated based on one year of operation, the volume of the supporting silage tank needs to be 5400m 3 , covering an area of about 1500m 2 . Therefore, the traditional on-site silage method seriously restricts the large-scale development of this type of biogas project.

中国专利200910194728.1公开了一种秸秆类生物质的分级利用方法,该方法利用气爆技术对秸秆类生物质进行预处理,处理成本高,不利于扩大应用。另外中国专利CN103740767A公开了一种提高秸秆类生物质厌氧消化效率的预处理方法,该预处理方法采用化学药剂进行处理,造成环境污染,药剂浪费,而且处理时间长。Chinese patent 200910194728.1 discloses a method for graded utilization of straw-like biomass. This method uses gas explosion technology to pretreat the straw-like biomass. The processing cost is high, which is not conducive to expanding application. In addition, Chinese patent CN103740767A discloses a pretreatment method for improving the efficiency of anaerobic digestion of straw-like biomass. The pretreatment method uses chemical agents for treatment, causing environmental pollution, waste of agents, and long processing time.

发明内容Contents of the invention

本发明的目的在于针对现有技术存在的不足,提供一种秸秆类生物质的预处理方法,利用该方法可以有效转化及降解秸秆中富含的纤维素、半纤维素和木质素,为加工秸秆类生物质提供便利。The purpose of the present invention is to address the deficiencies in the prior art and provide a method for pretreatment of straw-like biomass, which can effectively transform and degrade the cellulose, hemicellulose and lignin rich in straw, and provide a useful tool for processing Straw biomass provides convenience.

为实现上述目的,本发明提供的具体技术方案如下:In order to achieve the above object, the specific technical solutions provided by the invention are as follows:

一种秸秆类生物质的预处理方法,包括以下步骤:A method for pretreatment of stalk biomass, comprising the following steps:

1)秸秆类生物质整秆收获后,进行干燥处理,使含水率达到15~25%;1) After harvesting the whole stalks of the straw biomass, drying treatment is carried out to make the moisture content reach 15-25%;

2)将步骤1)得到的秸秆类生物质进行粉碎,粉碎细度≦3mm;2) crushing the stalk-like biomass obtained in step 1), with a crushing fineness≦3mm;

3)将步骤2)得到的秸秆类生物质粉末放入浸泡池中,加入沼液使含水量达到40~50%,在55~65℃下进行好氧堆沤4小时;3) Put the straw-based biomass powder obtained in step 2) into a soaking tank, add biogas slurry to make the water content reach 40-50%, and carry out aerobic stack retting at 55-65° C. for 4 hours;

4)加入沼液至秸秆类生物质粉末完全浸入其中,接种EM菌浸泡3~5天;4) Add biogas slurry until the straw biomass powder is completely immersed in it, inoculate with EM bacteria and soak for 3 to 5 days;

5)抽出沼液,然后接种益生菌混合后密闭,使浸泡后的秸秆类生物质粉末在密闭的条件下发酵降解8~10天后取出备用。5) Take out the biogas slurry, inoculate the mixture with probiotics and then seal it up, so that the soaked straw-like biomass powder is fermented and degraded for 8-10 days under the sealed condition, and then taken out for use.

所述秸秆类生物质选择以下物质中的一种或几种:稻草、麦草、豆秸、高粱结、玉米芯、玉米秆和棉花秆。The straw-based biomass is selected from one or more of the following materials: rice straw, wheat straw, bean straw, sorghum knots, corn cobs, corn stalks and cotton stalks.

所述干燥过程,采用自然风干,干燥过程通风除湿。The drying process adopts natural air drying, and the drying process is ventilated and dehumidified.

所述EM菌接种量是秸秆类生物质重量的1‰~1%。The inoculum amount of the EM bacteria is 1‰-1% of the weight of straw-like biomass.

所述益生菌接种量是秸秆类生物质重量的0.5‰~1%,可以全部是乳酸菌,也可以是50%以上乳酸菌与酪酸梭菌、双歧杆菌、嗜酸乳杆菌、放线菌、酵母菌其中的一种或多种混合。The inoculum amount of the probiotics is 0.5‰~1% of the weight of the straw biomass, which can be all lactic acid bacteria, or more than 50% of the lactic acid bacteria and Clostridium butyricum, Bifidobacterium, Lactobacillus acidophilus, actinomycetes, yeast one or more of them.

本发明具有以下有益效果:The present invention has the following beneficial effects:

1.本发明与现有技术相比,工艺简单,便于操作。1. Compared with the prior art, the present invention has simple process and is easy to operate.

2.本发明运行成本低廉,效率高,不会污染环境。2. The present invention has low operating cost, high efficiency and no environmental pollution.

3.本发明采用“好氧堆沤+沼液浸泡+微生物处理”的方法,对秸秆类生物质的三种组分(木质素、纤维素和半纤维素)进行了充分降解和转化,实现秸秆类生物质利用最大化。3. The present invention adopts the method of "aerobic retting + biogas slurry soaking + microbial treatment" to fully degrade and transform the three components (lignin, cellulose and hemicellulose) of straw-like biomass, realizing Maximize the utilization of straw biomass.

附图说明Description of drawings

图1为一种秸秆类生物质的预处理方法的操作流程图Fig. 1 is an operation flow chart of a pretreatment method for straw-like biomass

具体实施方式Detailed ways

实施例1Example 1

玉米秸秆整秆收获后,采用自然风干进行干燥处理,干燥过程通风除湿,使含水率达到15~25%,将干燥后的秸秆类生物质进行粉碎,粉碎细度≦3mm;将得到的秸秆类生物质粉末放入浸泡池中,加入沼液使含水量达到40~50%,在55~65℃下进行好氧堆沤4小时,加入沼液至秸秆类生物质粉末完全浸入其中,接种秸秆类生物质重量的1‰的EM菌浸泡5天,抽出沼液,然后接种乳酸菌混合后密闭,乳酸菌接种量是秸秆类生物质重量的0.5‰,使浸泡后的秸秆类生物质粉末在密闭的条件下发酵降解10天后取出备用。After harvesting the whole stalks of corn stalks, use natural air drying for drying treatment, ventilation and dehumidification during the drying process, so that the moisture content reaches 15-25%, and the dried straw biomass is crushed, and the crushing fineness is ≦ 3mm; the obtained straw Put the biomass powder into the soaking tank, add biogas slurry to make the water content reach 40-50%, carry out aerobic retting at 55-65°C for 4 hours, add biogas slurry until the straw-based biomass powder is completely immersed in it, and inoculate the straw Soak 1‰ of biomass-like EM bacteria for 5 days, extract the biogas slurry, inoculate lactic acid bacteria and mix them and seal them. The inoculum amount of lactic acid bacteria is 0.5‰ of the weight of straw-like biomass. After 10 days of fermentation and degradation under the same conditions, it was taken out for later use.

实施例2Example 2

玉米秸秆整秆收获后,采用自然风干进行干燥处理,干燥过程通风除湿,使含水率达到15~25%,将干燥后的秸秆类生物质进行粉碎,粉碎细度≦3mm;将得到的秸秆类生物质粉末放入浸泡池中,加入沼液是含水量达到40~50%,在55~65℃下进行好氧堆沤4小时,加入沼液至秸秆类生物质粉末完全浸入其中,接种秸秆类生物质重量的1%的EM菌浸泡3天,抽出沼液,然后接种乳酸菌混合后密闭,乳酸菌接种量是秸秆类生物质重量的1‰,使浸泡后的秸秆类生物质粉末在密闭的条件下发酵降解8天后取出备用。After harvesting the whole stalks of corn stalks, use natural air drying for drying treatment, ventilation and dehumidification during the drying process, so that the moisture content reaches 15-25%, and the dried straw biomass is crushed, and the crushing fineness is ≦ 3mm; the obtained straw Put the biomass powder into the immersion tank, add the biogas slurry until the water content reaches 40-50%, carry out aerobic retting at 55-65°C for 4 hours, add the biogas slurry until the straw-like biomass powder is completely immersed in it, and inoculate the straw Soak EM bacteria with 1% of the weight of biomass-like biomass for 3 days, take out the biogas slurry, inoculate lactic acid bacteria and mix them, and seal them. After 8 days of fermentation and degradation under the same conditions, it was taken out for later use.

Claims (6)

1. a preprocess method for stalk biomass, is characterized in that, comprises the following steps:
1), after the whole stalk results of stalk biomass, carry out drying process, make moisture content reach 15 ~ 25%;
2) by step 1) stalk biomass that obtains pulverizes, the broken Xi Du≤3mm of Fen;
3) by step 2) the stalk biomass powder that obtains puts into fermentation vat, and add natural pond liquid and make water content reach 40 ~ 50%, at 55 ~ 65 DEG C, carry out aerobic stack retting 4 hours;
4) add natural pond liquid to be immersed completely to stalk biomass powder, inoculation EM bacterium is soaked 3 ~ 5 days;
5) natural pond liquid is extracted out, airtight after then inoculating probio mixing, make the stalk biomass powder after immersion take out for subsequent use after 8 ~ 10 days in the degraded of airtight condition bottom fermentation.
2. the preprocess method of a kind of stalk biomass according to claim 1, is characterized in that, described stalk biomass selects one or more in following material: straw, wheat straw, beanstalk, Chinese sorghum knot, corncob, cornstalk and Cotton Stalk.
3. the preprocess method of a kind of stalk biomass according to claim 1, is characterized in that, described dry run, adopts natural air drying, dry run ventilation drying.
4. the preprocess method of a kind of stalk biomass according to claim 1, is characterized in that, described EM bacterium inoculum concentration is 1 ‰ ~ 1% of stalk biomass weight.
5. the preprocess method of a kind of stalk biomass according to claim 1, is characterized in that, described probio inoculum concentration is 0.5 ‰ ~ 1 ‰ of stalk biomass weight.
6. the preprocess method of a kind of stalk biomass according to claim 1 or 5, it is characterized in that, described probio can be all lactic acid bacteria, and also can be more than 50% lactic acid bacteria mixes with clostridium butyricum, lactic acid bacteria, Bifidobacterium, lactobacillus acidophilus, actinomyces, saccharomycete wherein one or more.
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CN104844293A (en) * 2015-05-25 2015-08-19 徐震霖 Preparation method and application of organic fertilizers
CN104909852A (en) * 2015-05-25 2015-09-16 徐震霖 Organic fertilizer prepared from wheat straw, and applications thereof
CN108795454A (en) * 2018-06-12 2018-11-13 天津大学 Being pre-processed using biogas slurry stack retting improves the method for stalk pyrolytic gasification combustion gas quality and gasification efficiency
CN109531874A (en) * 2018-08-25 2019-03-29 李双全 The method for being handled with biological method and being separated impurity in the waste mulching film of farmland
CN109734496A (en) * 2017-12-15 2019-05-10 自贡佳禾新能源科技有限公司 A method of biological organic fertilizer is prepared using stalk

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CN104826855A (en) * 2015-05-08 2015-08-12 江苏省农业科学院 Pretreatment method of straws for anaerobic fermentation
CN104844293A (en) * 2015-05-25 2015-08-19 徐震霖 Preparation method and application of organic fertilizers
CN104909852A (en) * 2015-05-25 2015-09-16 徐震霖 Organic fertilizer prepared from wheat straw, and applications thereof
CN109734496A (en) * 2017-12-15 2019-05-10 自贡佳禾新能源科技有限公司 A method of biological organic fertilizer is prepared using stalk
CN108795454A (en) * 2018-06-12 2018-11-13 天津大学 Being pre-processed using biogas slurry stack retting improves the method for stalk pyrolytic gasification combustion gas quality and gasification efficiency
CN109531874A (en) * 2018-08-25 2019-03-29 李双全 The method for being handled with biological method and being separated impurity in the waste mulching film of farmland
CN109531874B (en) * 2018-08-25 2020-12-08 李双全 Method for treating and separating impurities in waste farmland mulching films by biological method

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