CN114686535A - A method for pretreating alcoholic fermentation wastewater to improve the conversion rate of oily yeast and control the composition of oily fatty acids - Google Patents
A method for pretreating alcoholic fermentation wastewater to improve the conversion rate of oily yeast and control the composition of oily fatty acids Download PDFInfo
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Abstract
本发明公开了一种预处理醇类发酵废水提高油脂酵母转化率并调控微生物油脂脂肪酸组成的方法,通过分析不同条件下不同脱毒剂对发酵抑制剂的去除特点,根据油脂酵母对醇类废水的转化效率和脂肪酸组成的不同需求控制脱毒条件,工艺简单可行、成本低廉、能显著减少发酵抑制物对油脂酵母的毒害,在提高油脂酵母转化效率的同时,通过不同脱毒剂对醇类废水中发酵抑制物的去除程度不同,调控油脂酵母发酵产生微生物油脂脂肪酸的组成,获得附加值更高的富含高不饱和脂肪酸的产品。The invention discloses a method for pretreating alcoholic fermentation wastewater to improve the conversion rate of oleaginous yeast and regulating the composition of microbial oils and fatty acids. Detoxification conditions are controlled by different requirements of transformation efficiency and fatty acid composition, the process is simple and feasible, low cost, and can significantly reduce the toxicity of fermentation inhibitors to oil yeast. The degree of removal of fermentation inhibitors in wastewater is different, and the composition of microbial oil fatty acids produced by oil yeast fermentation is controlled to obtain products with higher added value and rich in high unsaturated fatty acids.
Description
技术领域:Technical field:
本发明涉及一种预处理醇类发酵废水提高油脂酵母转化率并调控微生物油脂脂肪酸组成的方法。The invention relates to a method for pretreating alcoholic fermentation wastewater, improving the conversion rate of oil yeast and regulating the composition of microbial oil and fatty acid.
背景技术:Background technique:
以木质纤维素作为原料生产的乙醇、丁醇等被认为是一种能够替代石油的最具前景的可再生燃料。其生产原理是将富含木质纤维素的原料经过预处理和酶解手段水解成富含可利用糖(葡萄糖、木糖、纤维二糖、阿拉伯糖等)的纤维素水解液,再经过发酵和精馏工艺获得醇类,醇类发酵生产过程中会产生大量废水,直接排放会对环境造成极大污染。醇类发酵废水富含有机酸成分、发酵残糖以及木质纤维素原料水解与后续发酵过程中残存的副产物,COD一般可达20000mg/L以上,而油脂酵母可以利用醇类发酵废水中的残糖和有机酸生产微生物油脂并降低COD,因此利用油脂酵母将醇类发酵废水中的营养成分转化为微生物油脂的路线经济可行。但在工业上,醇类发酵废水的脱毒工艺和脂肪酸组成的调控工艺一直是制约生物燃料发展的瓶颈。Ethanol and butanol produced from lignocellulose are considered to be the most promising renewable fuels that can replace petroleum. The production principle is to hydrolyze the raw materials rich in lignocellulose into a cellulose hydrolyzate rich in available sugars (glucose, xylose, cellobiose, arabinose, etc.) through pretreatment and enzymatic hydrolysis, and then undergo fermentation and Alcohols are obtained by rectification process, and a large amount of waste water will be produced during the fermentation production of alcohols, and direct discharge will cause great pollution to the environment. Alcohol fermentation wastewater is rich in organic acid components, fermentation residual sugar and by-products remaining in the hydrolysis of lignocellulosic raw materials and subsequent fermentation processes. Sugars and organic acids produce microbial oils and reduce COD, so the route of converting nutrients in alcoholic fermentation wastewater into microbial oils using oleaginous yeast is economically feasible. However, in industry, the detoxification process of alcohol fermentation wastewater and the control process of fatty acid composition have always been the bottleneck restricting the development of biofuels.
木质纤维素的预处理工艺会产生醛类(糠醛、5-羟甲基糠醛)和酚类等副产物。这些副产物在后期醇类发酵中难以被微生物吸收利用,发酵结束后会随废水排出。预处理过程的剧烈条件也会产生大量难降解的色素物质。稀酸处理和氨纤维爆破等预处理手段也会使废水中的硫酸盐和氨氮含量很高。这些发酵抑制物对于油脂酵母发酵的抑制作用主要表现在对菌体生长、糖代谢过程和油脂积累的抑制。因而发酵抑制物的去除,对油脂酵母利用醇类废水进行发酵生产微生物油脂有重要的意义。而微生物油脂的脂肪酸组成与植物油脂接近,主要组成成分以C16、C18系脂肪酸为主,如棕榈酸、硬脂酸、油酸和亚麻酸等,不仅可以用作食品上重要油脂的替代品(如可可脂等),还可以提供有益人类健康的各类功能性油脂。总体而言,微生物油脂的油脂脂肪酸组成决定了微生物油脂的用途。因此,寻找一种简单、高效、周期短的调控微生物油脂脂肪酸组成方法十分重要。The pretreatment process of lignocellulose produces by-products such as aldehydes (furfural, 5-hydroxymethylfurfural) and phenols. These by-products are difficult to be absorbed and utilized by microorganisms in the later alcohol fermentation, and will be discharged with wastewater after the fermentation. The severe conditions of the pretreatment process also produce a large amount of refractory pigment substances. Pretreatment methods such as dilute acid treatment and ammonia fiber blasting can also lead to high levels of sulfate and ammonia nitrogen in wastewater. The inhibitory effect of these fermentation inhibitors on the fermentation of oleaginous yeast is mainly manifested in the inhibition of bacterial growth, sugar metabolism process and oil accumulation. Therefore, the removal of fermentation inhibitors is of great significance for the production of microbial oils by oleaginous yeasts using alcohol waste water for fermentation. The fatty acid composition of microbial oil is close to that of vegetable oil, and its main components are mainly C16 and C18 fatty acids, such as palmitic acid, stearic acid, oleic acid and linolenic acid, etc., which can not only be used as a substitute for important oils and fats in food ( Such as cocoa butter, etc.), and can also provide various functional oils that are beneficial to human health. Overall, the lipid fatty acid composition of microbial lipids determines the usefulness of microbial lipids. Therefore, it is very important to find a simple, efficient and short-cycle method for regulating the fatty acid composition of microbial oils.
发明内容:Invention content:
本发明的目的是提供一种预处理醇类发酵废水提高油脂酵母转化率并调控微生物油脂脂肪酸组成的方法,加入脱毒剂,显著减少发酵抑制物对油脂酵母的毒害,在提高油脂酵母转化效率的同时,通过不同脱毒剂对醇类废水中发酵抑制物的去除程度不同,调控油脂酵母发酵产生微生物油脂脂肪酸的组成,获得附加值更高的富含高不饱和脂肪酸的产品。The object of the present invention is to provide a method for pretreating alcoholic fermentation wastewater to improve the conversion rate of oil yeast and regulating the composition of microbial oil and fatty acids, adding a detoxifier, significantly reducing the toxicity of fermentation inhibitors to oil yeast, and improving the conversion efficiency of oil yeast. At the same time, different detoxifiers can remove different degrees of fermentation inhibitors in alcoholic wastewater, control the composition of microbial oil fatty acids produced by oil yeast fermentation, and obtain products rich in high unsaturated fatty acids with higher added value.
本发明是通过以下技术方案予以实现的:The present invention is achieved through the following technical solutions:
一种预处理醇类发酵废水提高油脂酵母转化率并调控微生物油脂脂肪酸组成的方法,该方法包括以下步骤:A method for pretreating alcoholic fermentation wastewater to improve the conversion rate of oil yeast and regulating the composition of microbial oil and fatty acid, the method comprises the following steps:
a、滤去醇类发酵废水中的固形物后,按0.5wt%~5wt%的比例加入脱毒剂,搅拌反应一段时间后过滤或沉淀除去脱毒剂使滤液中糠醛含量≤5g/L、5-羟甲基糠醛含量≤5g/L、酚类含量≤6g/L、氨氮含量为≤3g/L、透光率≤70%得到脱毒后的滤液;所述的脱毒剂为活性炭、凹凸棒石、沸石、极性或非极性的大孔吸附树脂的一种;a. After filtering out the solids in the alcoholic fermentation wastewater, add a detoxifying agent in a proportion of 0.5wt% to 5wt%, and after stirring and reacting for a period of time, filter or precipitate to remove the detoxifying agent, so that the furfural content in the filtrate is ≤5g/L, 5-Hydroxymethylfurfural content≤5g/L, phenolic content≤6g/L, ammonia nitrogen content≤3g/L, light transmittance≤70% to obtain the detoxified filtrate; the detoxification agent is activated carbon, A kind of attapulgite, zeolite, polar or non-polar macroporous adsorption resin;
b、取脱毒后的滤液接入油脂酵母种子液进行好氧发酵。b. Take the detoxified filtrate and connect it to the oil yeast seed liquid for aerobic fermentation.
所述搅拌包括桨式搅拌、螺旋推进式搅拌、锚式搅拌、框式搅拌等其中的一种,搅拌速度为50~300rpm/min,时间为0.5~2h。The stirring includes one of paddle stirring, screw propelling stirring, anchor stirring, frame stirring, etc. The stirring speed is 50-300 rpm/min, and the time is 0.5-2 h.
所述油脂酵母是Rhodotorula glutinis、Trichosporon cutaneum、Rhodosporidium toruloides、Lipomyces starkeyi、Cryptococcus albidus、Trichosporon dermatis、Trichosporn coremiiforme、Yarrowia lipolytica中的一种或一种以上。The oleaginous yeast is one or more of Rhodotorula glutinis, Trichosporon cutaneum, Rhodosporidium toruloides, Lipomyces starkeyi, Cryptococcus albidus, Trichosporon dermatis, Trichosporn coremiiforme, and Yarrowia lipolytica.
本发明通过不同脱毒剂对醇类废水中发酵抑制物的去除程度不同,在提高油脂酵母转化效率的同时,调控油脂酵母发酵产生微生物油脂脂肪酸的组成。The invention uses different detoxifiers to remove different degrees of fermentation inhibitors in alcoholic wastewater, and at the same time improves the conversion efficiency of oil yeast, the composition of microbial oil fatty acid produced by fermentation of oil yeast is regulated.
本发明的有益效果如下:本发明针对经过发酵且高温蒸馏后的醇类发酵废水组成成分复杂、发酵抑制物丰富,通过分析不同条件下不同脱毒剂对发酵抑制剂的去除特点,根据油脂酵母对醇类废水的转化效率和脂肪酸组成的不同需求控制脱毒条件,工艺简单可行、成本低廉、能显著减少发酵抑制物对油脂酵母的毒害,在提高油脂酵母转化效率的同时,通过不同脱毒剂对醇类废水中发酵抑制物的去除程度不同,调控油脂酵母发酵产生微生物油脂脂肪酸的组成,获得附加值更高的富含高不饱和脂肪酸的产品。The beneficial effects of the present invention are as follows: the present invention aims at the complex composition of the alcoholic fermentation wastewater after fermentation and high-temperature distillation, and the fermentation inhibitors are abundant. The detoxification conditions are controlled according to the different requirements of the conversion efficiency and fatty acid composition of alcohol wastewater. The process is simple and feasible, the cost is low, and the toxicity of fermentation inhibitors to oil yeast can be significantly reduced. The degree of removal of fermentation inhibitors in alcoholic wastewater is different, and the composition of microbial oil fatty acids produced by the fermentation of oil yeast is controlled to obtain products with higher added value and rich in high unsaturated fatty acids.
具体实施方式:Detailed ways:
以下是对本发明的进一步说明,而不是对本发明的限制。The following is a further description of the present invention, rather than a limitation of the present invention.
实施例1:Example 1:
利用活性炭对乙醇发酵废水进行脱毒处理,处理完成后利用Trichosporoncutaneum进行发酵。Activated carbon was used to detoxify the ethanol fermentation wastewater, and Trichosporoncutaneum was used for fermentation after the treatment.
将Trichosporon cutaneum从试管中接入50mL的活化培养基中,20℃,活化培养24h,得到Trichosporon cutaneum种子液,所述的活化培养基为:葡萄糖20g/L、蛋白胨10g/L、酵母粉10g/L,余量为水。Insert Trichosporon cutaneum from the test tube into 50 mL of activation medium, and at 20° C., activate and cultivate for 24 hours to obtain Trichosporon cutaneum seed liquid. The activated medium is: glucose 20g/L, peptone 10g/L, yeast powder 10g/L L, the balance is water.
对照组乙醇发酵废水培养基中不使用活性炭进行脱毒,直接将种子液接入培养基进行发酵。In the control group, activated carbon was not used in the medium of ethanol fermentation wastewater for detoxification, and the seed liquid was directly connected to the medium for fermentation.
在乙醇发酵废水中分别按0.5wt%、5wt%的比例加入活性炭,采用桨式搅拌的方式,搅拌条件为50rpm/min下搅拌0.5h,搅拌完成后采用过滤的方法去除活性炭,取滤液测定醛类(糠醛、5-羟甲基糠醛)、酚类、氨氮含量,并测定透光率;再调节pH后接入油脂酵母种子液进行好氧发酵,离心收集乙醇发酵废水中的酵母菌体,发酵底物根据排放要求进行后续处理。不同活性炭添加量对发酵抑制物各组分的脱毒情况见表1。不同活性炭添加量对微生物油脂脂肪酸含量的调控情况见表2。不同活性炭添加量对油脂酵母转化效率的调控情况见表3。Activated carbon was added to the ethanol fermentation wastewater in the proportions of 0.5wt% and 5wt% respectively, and the paddle stirring method was adopted. The stirring condition was 50rpm/min for 0.5h. After the stirring was completed, the activated carbon was removed by filtration, and the filtrate was taken to determine the aldehyde. (furfural, 5-hydroxymethylfurfural), phenols, ammonia nitrogen content, and measure the light transmittance; after adjusting the pH, the oil yeast seed liquid was connected to carry out aerobic fermentation, and the yeast cells in the ethanol fermentation wastewater were collected by centrifugation. Fermentation substrates are subsequently processed according to discharge requirements. Table 1 shows the detoxification of each component of fermentation inhibitor with different activated carbon additions. The regulation of different amounts of activated carbon on the fatty acid content of microbial oils is shown in Table 2. The regulation of different amounts of activated carbon on the transformation efficiency of oil yeast is shown in Table 3.
表1Table 1
表2Table 2
表3table 3
实施例2:Example 2:
利用凹凸棒石对乙醇发酵废水进行脱毒处理,处理完成后利用Rhodosporidiumtoruloides进行发酵。The ethanol fermentation wastewater was detoxified by attapulgite, and then fermented by Rhodosporidium toruloides after the treatment.
将Rhodosporidium toruloides从试管中接入50mL的活化培养基中,20℃,活化培养24h,得到Rhodosporidium toruloides种子液,所述的活化培养基为:葡萄糖20g/L、蛋白胨10g/L、酵母粉10g/L,余量为水。Put Rhodosporidium toruloides from the test tube into 50 mL of activation medium, 20 ° C, activate and cultivate for 24 hours, to obtain Rhodosporidium toruloides seed liquid, the activation medium is: glucose 20g/L, peptone 10g/L, yeast powder 10g/L L, the balance is water.
对照组乙醇发酵废水培养基中不使用凹凸棒石进行脱毒,直接将种子液进行发酵。In the control group, the attapulgite was not used for detoxification in the ethanol fermentation wastewater medium, and the seed liquor was directly fermented.
在乙醇发酵废水中分别按2wt%的比例加入凹凸棒石,采用锚式搅拌的方式分别搅拌0.5、2h,转速为200rpm/min,搅拌完成后采用过滤的方法去除凹凸棒石,取滤液测定醛类(糠醛、5-羟甲基糠醛)、酚类、氨氮含量,并测定透光率;再调节pH后接入油脂酵母种子液进行好氧发酵,离心收集乙醇发酵废水中的酵母菌体,发酵底物根据排放要求进行后续处理。Attapulgite was added to the ethanol fermentation wastewater in a proportion of 2wt%, and the attapulgite was respectively stirred by anchor stirring for 0.5 and 2 hours, and the rotation speed was 200 rpm/min. (furfural, 5-hydroxymethylfurfural), phenols, ammonia nitrogen content, and measure the light transmittance; after adjusting the pH, the oil yeast seed liquid was connected to carry out aerobic fermentation, and the yeast cells in the ethanol fermentation wastewater were collected by centrifugation. Fermentation substrates are subsequently processed according to discharge requirements.
表4显示了不同搅拌时间里发酵抑制物各组分的脱毒情况。表5显示了不同搅拌时间对微生物油脂脂肪酸含量的调控情况。表6显示了不同搅拌时间对油脂酵母转化效率的调控情况。Table 4 shows the detoxification of each component of the fermentation inhibitor at different stirring times. Table 5 shows the regulation of different stirring time on the fatty acid content of microbial oil. Table 6 shows the regulation of the transformation efficiency of oil yeast by different stirring times.
表4Table 4
表5table 5
表6Table 6
实施例3:Example 3:
利用极性大孔吸附树脂对丁醇发酵废水进行脱毒处理,处理完成后利用Rhodotorula glutinis和Lipomyces starkeyi进行混菌发酵。The butanol fermentation wastewater was detoxified by polar macroporous adsorption resin, and Rhodotorula glutinis and Lipomyces starkeyi were used for mixed bacterial fermentation after the treatment.
将Rhodosporidium toruloides和Lipomyces starkeyi分别从试管中接入50mL的活化培养基中,20℃,活化培养24h,得到种子液,所述的活化培养基为:葡萄糖20g/L、蛋白胨10g/L、酵母粉10g/L,余量为水。The Rhodosporidium toruloides and Lipomyces starkeyi were respectively inserted into 50 mL of activated medium from the test tube, and activated for 24 hours at 20°C to obtain seed liquid. The activated medium was: glucose 20g/L, peptone 10g/L, yeast powder 10g/L, the balance is water.
对照组丁醇发酵废水培养基中不使用极性大孔吸附树脂进行脱毒,直接将种子液接入培养基进行发酵。In the control group, the butanol fermentation wastewater medium did not use polar macroporous adsorption resin for detoxification, and the seed liquid was directly connected to the medium for fermentation.
在丁醇发酵废水中分别按2wt%的比例加入极性大孔吸附树脂,采用螺旋式推进搅拌的方式搅拌2h,转速和为100rpm/min,搅拌完成后采用沉淀的方法去除极性大孔吸附树脂,取滤液测定醛类(糠醛、5-羟甲基糠醛)、酚类、氨氮含量,并测定透光率;再调节pH后接入油脂酵母种子液进行好氧发酵,离心收集丁醇发酵废水中的酵母菌体,发酵底物根据排放要求进行后续处理The polar macroporous adsorption resin was added to the butanol fermentation wastewater in a proportion of 2 wt%, and stirred for 2 hours by means of screw propeller stirring, and the sum of the rotational speed was 100 rpm/min. After the stirring was completed, the polar macroporous adsorption was removed by precipitation. Resin, take the filtrate to measure the content of aldehydes (furfural, 5-hydroxymethyl furfural), phenols, ammonia nitrogen, and measure the light transmittance; adjust the pH and then insert the oil yeast seed liquid for aerobic fermentation, and collect butanol fermentation by centrifugation Yeast cells in wastewater, and fermentation substrates are subject to subsequent treatment according to discharge requirements
实验结果:(1)按质量分数计,在不使用极性大孔吸附树脂进行脱毒的滤液中,糠醛含量为1.357g/L、5-羟甲基糠醛含量为2.504g/L、总酚含量为4.658g/L,氨氮含量为1.023g/L。而使用极性大孔吸附树脂进行脱毒的滤液中,糠醛含量为0.854g/L,5-羟甲基糠醛含量为0.574g/L、总酚含量为1.214g/L,氨氮含量为0.548g/L。(2)按质量分数计,在不使用极性大孔吸附树脂进行脱毒的发酵培养基中,Rhodotorula glutinis和Lipomycesstarkeyi进行混菌发酵产生的微生物油脂的油脂含量为8.1%,油脂产量为0.89g/L,脂肪酸组成为:棕榈酸38.1%,硬脂酸31.8%,油酸10.4%,亚油酸12.1%,其他7.6%。在使用极性大孔吸附树脂进行脱毒后的发酵培养基中,产生的微生物油脂的油脂含量为12.5%,油脂产量为1.02g/L,脂肪酸组成为:棕榈酸31.9%,硬脂酸32.6%,油酸14.7%,亚油酸16.8%,其他4%。Experimental results: (1) In terms of mass fraction, in the filtrate without polar macroporous adsorption resin for detoxification, the furfural content was 1.357g/L, the 5-hydroxymethylfurfural content was 2.504g/L, and the total phenolic The content is 4.658g/L, and the ammonia nitrogen content is 1.023g/L. In the filtrate detoxified by polar macroporous adsorption resin, the furfural content was 0.854g/L, the 5-hydroxymethylfurfural content was 0.574g/L, the total phenol content was 1.214g/L, and the ammonia nitrogen content was 0.548g /L. (2) In terms of mass fraction, in the fermentation medium without the use of polar macroporous adsorption resin for detoxification, the oil content of the microbial oil produced by the mixed fermentation of Rhodotorula glutinis and Lipomycesstarkeyi was 8.1%, and the oil yield was 0.89g /L, the fatty acid composition was: palmitic acid 38.1%, stearic acid 31.8%, oleic acid 10.4%, linoleic acid 12.1%, and others 7.6%. In the fermentation medium after detoxification with polar macroporous adsorption resin, the oil content of the produced microbial oil was 12.5%, the oil yield was 1.02 g/L, and the fatty acid composition was: palmitic acid 31.9%, stearic acid 32.6% %, oleic acid 14.7%, linoleic acid 16.8%, other 4%.
实施例4:Example 4:
利用非极性大孔吸附树脂对丁醇发酵废水进行脱毒处理,处理完成后利用Trichosporn coremiiforme进行发酵。The butanol fermentation wastewater was detoxified with non-polar macroporous adsorption resin, and then fermented with Trichosporn coremiiforme after the treatment.
将Trichosporn coremiiforme从试管中接入50mL的活化培养基中,20℃,活化培养24h,得到Trichosporn coremiiforme种子液,所述的活化培养基为:葡萄糖20g/L、蛋白胨10g/L、酵母粉10g/L,余量为水。The Trichosporn coremiiforme was inserted into 50 mL of activation medium from the test tube, and activated at 20° C. for 24 hours to obtain Trichosporn coremiiforme seed liquid. The activated medium was: glucose 20g/L, peptone 10g/L, yeast powder 10g/L L, the balance is water.
对照组丁醇发酵废水培养基中不使用非极性大孔吸附树脂进行脱毒,直接将种子液接入培养基进行发酵。In the control group, non-polar macroporous adsorption resin was not used in the medium of butanol fermentation wastewater for detoxification, and the seed liquid was directly connected to the medium for fermentation.
在丁醇发酵废水中按2wt%比例加入非极性大孔吸附树脂,采用桨式搅拌的方式,搅拌时间为1h,转速分别为50、300rpm/min,搅拌完成后采用过滤的方法去除非极性大孔吸附树脂,取滤液测定醛类(糠醛、5-羟甲基糠醛)、酚类、氨氮含量,并测定透光率;再调节pH后接入油脂酵母种子液进行好氧发酵,离心收集乙醇发酵废水中的酵母菌体,发酵底物根据排放要求进行后续处理。表7显示了不同转速下脱毒对发酵抑制物各组分的影响,表8显示了不同转速下脱毒对微生物油脂脂肪酸含量的影响,表9显示了不同非极性大孔吸附树脂添加量对油脂酵母转化效率的调控情况。The non-polar macroporous adsorption resin was added to the butanol fermentation wastewater in a proportion of 2wt%, and the stirring method was adopted. The stirring time was 1h, and the rotating speed was 50 and 300 rpm/min respectively. After stirring, the non-polar macroporous adsorption resin was removed by filtering. macroporous adsorption resin, the filtrate was taken to measure the content of aldehydes (furfural, 5-hydroxymethylfurfural), phenols and ammonia nitrogen, and the light transmittance was measured; after adjusting the pH, it was connected to the oil yeast seed liquid for aerobic fermentation, and centrifugation The yeast cells in the ethanol fermentation wastewater are collected, and the fermentation substrate is subjected to subsequent treatment according to the discharge requirements. Table 7 shows the effect of detoxification on the components of fermentation inhibitors at different speeds, Table 8 shows the effect of detoxification on the fatty acid content of microbial oils at different speeds, and Table 9 shows the addition amount of different non-polar macroporous adsorption resins Regulation of the transformation efficiency of oleaginous yeast.
表7Table 7
表8Table 8
表9Table 9
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