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CN111057665B - Cellulose degrading bacterium n3 for producing IAA and application thereof - Google Patents

Cellulose degrading bacterium n3 for producing IAA and application thereof Download PDF

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CN111057665B
CN111057665B CN201911267554.7A CN201911267554A CN111057665B CN 111057665 B CN111057665 B CN 111057665B CN 201911267554 A CN201911267554 A CN 201911267554A CN 111057665 B CN111057665 B CN 111057665B
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马超
吴婧
聂彩娥
王玉宝
吴凉萍
张子赟
柴如山
田达
朱林
郜红建
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Anhui Huizhi Nongchuang Biotechnology Co ltd
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Abstract

The invention provides an IAA-producing cellulose degrading bacterium n3 and application thereof, and relates to the technical field of agricultural microorganisms, wherein the cellulose degrading bacterium n3 is preserved in China general microbiological culture Collection center with the preservation number of CGMCC No. 18613. The cellulose degrading bacteria n3 have strong capability of producing CMC enzyme, and can produce IAA, the CMC enzyme has the highest activity reaching 24.96U/mL, and the highest secretion of IAA can reach 19.07 mg/L. Therefore, the cellulose degrading bacteria n3 can be used for preparing a straw decomposition promoting microbial inoculum for producing IAA and/or CMC enzyme or having a growth promoting function, so that the cellulose degrading bacteria n3 can be applied to straw decomposition promoting and crop growth promoting, and straw returning efficiency and crop yield improvement are realized.

Description

一株产IAA的纤维素降解菌n3及其应用A cellulose-degrading bacteria n3 producing IAA and its application

技术领域technical field

本发明属于农业微生物技术领域,具体涉及一株产IAA的纤维素降解菌 n3及其应用。The invention belongs to the technical field of agricultural microorganisms, in particular to an IAA-producing cellulose degrading bacteria n3 and its application.

背景技术Background technique

秸秆还田是当今世界上普遍重视的一项培肥地力的作物增加产量的措施,在杜绝了秸秆焚烧过程造成的大气污染的同时还能在改善土壤物理性状、提高土壤有机质水平、增加土壤生物活性和提高土壤养分供应水平等方面发挥重要作用。秸秆中有机质及氮磷钾等营养元素丰富,可转换为作物易吸收利用的养分形式,充分利用秸秆还田的积极效应可有效提高资源利用,实现作物增产,促进养分循环。Straw returning to the field is a measure that is widely valued in the world today to increase the yield of crops that improve soil fertility. While eliminating the air pollution caused by the straw burning process, it can also improve soil physical properties, improve soil organic matter levels, and increase soil biological properties. It plays an important role in improving the level of soil nutrient supply and so on. Straw is rich in nutrients such as organic matter and nitrogen, phosphorus and potassium, which can be converted into nutrient forms that are easily absorbed and utilized by crops. Making full use of the positive effect of returning straw to the field can effectively improve resource utilization, increase crop yield, and promote nutrient cycling.

秸秆主要由木质素、纤维素、半纤维素等难降解的物质组成,其中尤以纤维素含量最高,自然状态下秸秆腐解速度较慢。目前,国内外学者普遍认为秸秆还田时配施具产纤维素降解酶(如:羧甲基纤维素降解酶,CMC)的腐秆菌以加速秸秆等废弃物腐熟。但是,由于腐秆剂中的功能微生物是否能够成功定殖会受到土壤资源丰富度和土著微生物竞争强度等影响,因此腐秆剂的区域匹配性要求高,不同地区不同土壤中施用的腐秆剂也应该有所差异,因此需要尽量在应用区筛选菌株制备腐秆菌剂以提高该地区秸秆腐秆程度及速率。Straw is mainly composed of lignin, cellulose, hemicellulose and other refractory substances, of which cellulose content is the highest, and the decomposition rate of straw is slow in natural state. At present, scholars at home and abroad generally believe that when straw is returned to the field, stalk-decomposing fungi that produce cellulose-degrading enzymes (such as carboxymethyl cellulose degrading enzyme, CMC) are used to accelerate the decomposing of straw and other wastes. However, whether the functional microorganisms in the stalk agent can be successfully colonized will be affected by the abundance of soil resources and the competition intensity of indigenous microorganisms, so the regional matching of stalk rot agents is required. There should also be differences, so it is necessary to screen strains in the application area to prepare stalk rot inoculants to improve the degree and rate of stalk rot in this area.

砂姜黑土具有干缩湿涨、易旱易涝、土壤耕性差及肥力水平低的不良性状,对作物生长造成不良影响,是我国典型的低产土壤。砂姜黑土土质黏重、土壤结构较差,在生产中易出现“旱、涝、僵、瘦”等问题,土壤微生物与耕层土壤肥力活性均较低,不利于外源菌株的定殖,因此一般腐秆剂在砂姜黑土上施用的效果较差。砂姜黑土多为麦玉轮作区,轮作时间间隔短暂,施用腐秆剂后若秸秆腐解不完全,一方面会导致前茬作物来不及腐解而在土壤中长期积存、滞留,从而影响下一季作物的播种;另一方面是由于土壤中未完全腐解的秸秆会导致麦玉种子无法与土壤结合,造成麦玉种子萌发困难,并且还会和作物争夺养分,导致作物出苗率降低、产量下降。Sand ginger black soil has the bad characters of dry shrinkage and wet expansion, easy drought and waterlogging, poor soil tillage and low fertility level, which has adverse effects on crop growth. It is a typical low-yield soil in my country. The sand ginger black soil is sticky and heavy, and the soil structure is poor. It is prone to problems such as "drought, waterlogging, stiffness and thinness" in production. Therefore, the general application of stalk rot agent on sand ginger black soil is less effective. Sand ginger black soil is mostly a wheat and jade rotation area, and the rotation interval is short. If the straw is not completely decomposed after the application of the stalk agent, on the one hand, the previous crop will not have time to decompose and will accumulate and stay in the soil for a long time, thus affecting the next season. Sowing of crops; on the other hand, the incompletely decomposed straw in the soil will cause the wheat and jade seeds to be unable to combine with the soil, making it difficult for the wheat and jade seeds to germinate, and will compete with the crops for nutrients, resulting in a decrease in the emergence rate and yield of the crops. .

吲哚乙酸(IAA)是植物激素的一种,是产生调节植物生长素的信号物质,在植物体内普遍存在,是一种植物体内普遍存在的内源生长素。生长素对生长的促进作用主要是促进细胞的生长,特别是细胞的伸长,对作物生长,提高产量方面有着积极的意义。因此,采用高效促腐兼具促生功能的菌株有利于砂姜黑土麦玉轮作体系作物的生长发育并保持土壤优良性状。Indoleacetic acid (IAA) is a kind of plant hormone, which is a signal substance that produces and regulates auxin. It is ubiquitous in plants and is an endogenous auxin that is ubiquitous in plants. The growth-promoting effect of auxin is mainly to promote the growth of cells, especially the elongation of cells, which has positive significance for crop growth and yield improvement. Therefore, the use of high-efficiency rot-promoting and growth-promoting strains is conducive to the growth and development of crops in the sand ginger black soil wheat-jade rotation system and maintains excellent soil properties.

目前,国内外大多数学者只对某一株菌的纤维素降解能力或者是促生能力进行研究,致力于研究某一菌株的某项功能,但鲜见具有多重功能的菌株。At present, most scholars at home and abroad only study the cellulose-degrading ability or growth-promoting ability of a certain strain, and are committed to studying a certain function of a certain strain, but strains with multiple functions are rarely seen.

发明内容SUMMARY OF THE INVENTION

有鉴于此,本发明的目的在于提供一株筛选自砂姜黑土的高效产CMC 纤维素降解菌n3,可提高纤维素降解率、促腐秸秆,从而促进还田秸秆腐解,提升秸秆还田效率;另外该菌还能高产IAA,促进作物种子萌发和生长,实现农作物增产。In view of this, the purpose of the present invention is to provide a high-efficiency CMC-producing cellulose-degrading bacteria n3 screened from sand ginger black soil, which can improve the cellulose degradation rate and promote the decomposition of straw, thereby promoting the decomposition of returning straw, and improving the return of straw to the field. In addition, the bacteria can also produce high IAA, promote the germination and growth of crop seeds, and increase crop yield.

为了实现上述发明目的,本发明提供以下技术方案:In order to achieve the above-mentioned purpose of the invention, the present invention provides the following technical solutions:

本发明提供了一株产IAA的纤维素降解菌n3,保藏于中国普通微生物菌种保藏管理中心,保藏编号为CGMCC No.18613。The invention provides an IAA-producing cellulose-degrading bacteria n3, which is preserved in the China General Microorganism Culture Collection and Management Center, and the preservation number is CGMCC No.18613.

本发明还提供了所述纤维素降解菌n3在制备IAA和/或CMC酶中的应用。The present invention also provides the application of the cellulose-degrading bacteria n3 in the preparation of IAA and/or CMC enzymes.

优选的,在利用所述纤维素降解菌n3制备IAA时,包括以下步骤:调节含有100mg/LL-色氨酸的LB培养基的pH值为6.0~9.0,接种所述纤维素降解菌n3的菌悬液,震荡培养;所述菌悬液的体积为所述LB培养基体积的 1%;所述菌悬液的OD600值为0.8~1.2。Preferably, when using the cellulose-degrading bacteria n3 to prepare IAA, the following steps are included: adjusting the pH of the LB medium containing 100 mg/LL-tryptophan to 6.0-9.0, and inoculating the cellulose-degrading bacteria n3 The bacterial suspension is shaken and cultured; the volume of the bacterial suspension is 1% of the volume of the LB medium; the OD 600 value of the bacterial suspension is 0.8-1.2.

优选的,所述振荡培养的温度为28~30℃,震荡速度为160~180rpm。Preferably, the temperature of the shaking culture is 28-30°C, and the shaking speed is 160-180 rpm.

优选的,在利用所述纤维素降解菌n3制备CMC酶时,包括以下步骤:将液体发酵培养基调节pH值为4.0~6.0,接种所述纤维素降解菌n3,震荡培养;所述纤维素降解菌n3的接种体积为所述液体发酵培养基体积的1%;所述液体发酵培养基包括以下浓度的原料:氯化钠6g/L、七水硫酸镁0.1g/L、氯化钙0.1g/L、磷酸二氢钾0.5g/L、酵母膏10g/L和秸秆20g/L。Preferably, when using the cellulose-degrading bacteria n3 to prepare the CMC enzyme, the following steps are included: adjusting the pH of the liquid fermentation medium to 4.0-6.0, inoculating the cellulose-degrading bacteria n3, and shaking culture; the cellulose The inoculation volume of degrading bacteria n3 is 1% of the volume of the liquid fermentation medium; the liquid fermentation medium includes raw materials with the following concentrations: sodium chloride 6g/L, magnesium sulfate heptahydrate 0.1g/L, calcium chloride 0.1 g/L, potassium dihydrogen phosphate 0.5g/L, yeast extract 10g/L and straw 20g/L.

优选的,所述LB培养基或液体发酵培养基中还包括以下质量百分含量的组分:0.1%碳源、1%氮源。Preferably, the LB medium or the liquid fermentation medium further includes the following components by mass percentage: 0.1% carbon source and 1% nitrogen source.

优选的,所述碳源包括葡萄糖、甘露醇、蔗糖、麦芽糖、木糖、乳糖和果糖中的一种或多种;Preferably, the carbon source includes one or more of glucose, mannitol, sucrose, maltose, xylose, lactose and fructose;

所述氮源包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素和蛋白胨的一种或多种。The nitrogen source includes one or more of potassium nitrate, ammonium sulfate, ammonium nitrate, yeast powder, glutamic acid, urea and peptone.

本发明还提供了所述纤维素降解菌n3在制备促腐促生菌剂中的应用。The present invention also provides the application of the cellulose-degrading bacteria n3 in the preparation of a decay-promoting and growth-promoting bacterial agent.

优选的,所述促腐促生菌剂的类型为菌水剂;所述菌水剂在应用时,以所述纤维素降解菌n3的量计,接种量为1~9×106CFU/g秸秆或1~9×107 CFU/g土壤。Preferably, the type of the decay-promoting bacteria agent is bacteria water agent; when the bacteria water agent is applied, the inoculation amount is 1-9×10 6 CFU/ g straw or 1~9×10 7 CFU/g soil.

本发明还提供了所述纤维素降解菌n3在促进秸秆还田效率和农作物增产中的应用。The invention also provides the application of the cellulose-degrading bacteria n3 in promoting straw returning efficiency and increasing crop yield.

本发明提供了一株产IAA的纤维素降解菌n3,保藏于中国普通微生物菌种保藏管理中心,保藏编号为CGMCC No.18613。本发明所述纤维素降解菌n3表面光滑,菌落较小,边缘整齐,不透明,略带黄色;纤维素降解菌 n3为革兰氏阴性菌,好氧,化能异养,接触酶阳性,M.R试验阴性,VP试验阴性,淀粉水解阴性,明胶水解阴性,柠檬酸盐利用阴性。The invention provides an IAA-producing cellulose-degrading bacteria n3, which is preserved in the China General Microorganism Culture Collection and Management Center, and the preservation number is CGMCC No.18613. The cellulose-degrading bacteria n3 of the invention has a smooth surface, small colonies, neat edges, opaque, slightly yellow; the cellulose-degrading bacteria n3 are Gram-negative bacteria, aerobic, chemoheterotrophic, contact enzyme positive, M.R. The test was negative, the VP test was negative, the starch hydrolysis was negative, the gelatin hydrolysis was negative, and the citrate utilization was negative.

本发明所述纤维素降解菌n3能高产吲哚乙酸,且产CMC酶能力较强,具有较高的作物促生和秸秆促腐能力,IAA的分泌量最高可达19.07mg/L, CMC酶活力最高可达到24.96U/mL。因此可将所述纤维素降解菌n3用于制备兼具促生功能的腐秆菌剂,从而应用于秸秆促腐、促进秸秆还田效率和农作物增产中。The cellulose-degrading bacteria n3 of the invention can produce high indole acetic acid, and has strong CMC enzyme production ability, and has higher crop growth-promoting and straw rot-promoting abilities. The highest activity can reach 24.96U/mL. Therefore, the cellulose-degrading bacteria n3 can be used to prepare a stalk rot inoculant with both a growth-promoting function, so as to be used in promoting straw rot, promoting straw returning efficiency and increasing crop yield.

本发明所述纤维素降解菌n3能够一菌多用,发挥菌株的最大效能,一方面可以促进作物生长,增加作物产量;另一方面可加速纤维素降解,促腐秸秆,大力推进秸秆还田,具有作为功能微生物肥料的潜力,为推进农业绿色发展作贡献。The cellulose-degrading bacteria n3 of the invention can be used for multiple purposes, and exert the maximum efficiency of the strain. On the one hand, it can promote the growth of crops and increase the yield of crops; It has the potential as a functional microbial fertilizer and contributes to promoting the green development of agriculture.

生物保藏信息biological deposit information

纤维素降解菌n3,分类命名为玉米固氮螺菌(Azospirillum zeae),于2019 年09月23日保藏于中国普通微生物菌种保藏管理中心,地址为北京市朝阳区北辰西路1号院3号中国科学院微生物研究所,保藏号为CGMCC No.18613。Cellulose degrading bacteria n3, classified as Azospirillum zeae, was deposited in the China General Microorganism Collection and Management Center on September 23, 2019, and the address is No. 3, Yard 1, Beichen West Road, Chaoyang District, Beijing Institute of Microbiology, Chinese Academy of Sciences, the deposit number is CGMCC No.18613.

附图说明Description of drawings

图1为本发明提供的纤维素降解菌n3的菌落图;Fig. 1 is the colony diagram of cellulose degrading bacteria n3 provided by the present invention;

图2为不同菌株的产CMC酶能力;Fig. 2 is the ability of producing CMC enzyme of different strains;

图3为不同菌株的产IAA能力;Fig. 3 is the IAA production ability of different strains;

图4根据16S rDNA序列构建的n3菌株的系统发育树;Fig. 4 phylogenetic tree of n3 strain constructed according to 16S rDNA sequence;

图5为不同pH对纤维素降解菌n3产CMC酶活力的影响图;Figure 5 is a graph showing the effect of different pH on the activity of CMC enzyme produced by cellulose-degrading bacteria n3;

图6为不同装液量对纤维素降解菌n3产CMC酶活力的影响图;Figure 6 is a graph showing the effect of different liquid loadings on the activity of CMC enzyme produced by cellulose-degrading bacteria n3;

图7为不同氮源对纤维素降解菌n3产CMC酶活力的影响图;Figure 7 is a graph showing the effect of different nitrogen sources on the activity of CMC enzyme produced by cellulose-degrading bacteria n3;

图8为不同培养时间对纤维素降解菌n3产IAA的影响图;Figure 8 is a graph showing the effect of different incubation times on the production of IAA by cellulose-degrading bacteria n3;

图9为不同培养时间对纤维素降解菌n3生长状况的影响图;Figure 9 is a graph showing the effect of different incubation times on the growth of cellulose-degrading bacteria n3;

图10为不同装液量对纤维素降解菌n3产IAA的影响图;Figure 10 is a graph showing the effect of different liquid loadings on the production of IAA by cellulose-degrading bacteria n3;

图11为不同装液量对纤维素降解菌n3生长状况的影响图;Figure 11 is a graph showing the effect of different liquid loadings on the growth of cellulose-degrading bacteria n3;

图12为不同初始pH对纤维素降解菌n3产IAA的影响图;Figure 12 is a graph showing the effect of different initial pH on the production of IAA by cellulose-degrading bacteria n3;

图13为不同初始pH对纤维素降解菌n3生长状况的影响图;Figure 13 is a graph showing the effect of different initial pH on the growth of cellulose-degrading bacteria n3;

图14为不同碳源对纤维素降解菌n3产IAA的影响图;Figure 14 is a graph showing the effect of different carbon sources on the production of IAA by cellulose-degrading bacteria n3;

图15为不同碳源对纤维素降解菌n3生长状况的影响图;Figure 15 is a graph showing the effect of different carbon sources on the growth of cellulose-degrading bacteria n3;

图16为不同氮源对纤维素降解菌n3产IAA的影响图;Figure 16 is a graph showing the effect of different nitrogen sources on the production of IAA by cellulose-degrading bacteria n3;

图17为不同氮源对纤维素降解菌n3生长状况的影响图;Figure 17 is a graph showing the effect of different nitrogen sources on the growth of cellulose-degrading bacteria n3;

图18为不同菌株秸秆促腐能力的影响图。Figure 18 is a graph showing the effect of different strains on the rot-promoting ability of straw.

具体实施方式Detailed ways

本发明提供了一株产IAA的纤维素降解菌n3,保藏于中国普通微生物菌种保藏管理中心,保藏编号为CGMCC No.18613。The invention provides an IAA-producing cellulose-degrading bacteria n3, which is preserved in the China General Microorganism Culture Collection and Management Center, and the preservation number is CGMCC No.18613.

本发明所述纤维素降解菌n3从安徽省蒙城县内农业示范科技园区内采集砂姜黑土中筛选得到,经验证后,所述纤维素降解菌n3为革兰氏阴性菌,好氧,化能异养,接触酶阳性,M.R试验阴性,VP试验阴性,淀粉水解阴性,明胶水解阴性,柠檬酸盐利用阴性;菌落结构如图1所示,表面光滑,菌落较小,边缘整齐,不透明,略带黄色。The cellulose-degrading bacteria n3 of the present invention is screened from the black soil collected in the agricultural demonstration science and technology park in Mengcheng County, Anhui Province. After verification, the cellulose-degrading bacteria n3 are Gram-negative bacteria, aerobic, Chemoheterotrophic, contact enzyme positive, M.R test negative, VP test negative, starch hydrolysis negative, gelatin hydrolysis negative, citrate utilization negative; the colony structure is shown in Figure 1, the surface is smooth, the colonies are small, the edges are neat and opaque , slightly yellowish.

本发明还提供了所述纤维素降解菌n3在制备IAA和/或CMC酶中的应用。The present invention also provides the application of the cellulose-degrading bacteria n3 in the preparation of IAA and/or CMC enzymes.

本发明在利用所述纤维素降解菌n3制备IAA时,优选包括以下步骤:调节含有100mg/L L-色氨酸的LB培养基的pH值为6.0~9.0,接种所述纤维素降解菌n3的菌悬液,震荡培养;所述菌悬液是利用接种环从固体培养基上挑取一环菌体,将其接入含6ml LB培养基的25ml试管中,随后将试管加塞置于30℃、180rpm摇床中过夜培养所得;所述菌悬液的OD600值为 0.8~1.2,接种体积为所述LB培养基体积的1%。在本发明中,进行所述震荡培养时,培养基的装液量优选为25mL/250mL,培养时间优选为15h,此时培育出的纤维素降解菌n3产IAA的量最高且菌株生长能力最佳。本发明所述振荡培养的温度优选为28~30℃,震荡速度优选为160~180rpm。When using the cellulose-degrading bacteria n3 to prepare IAA, the present invention preferably includes the following steps: adjusting the pH of the LB medium containing 100 mg/L L-tryptophan to 6.0-9.0, inoculating the cellulose-degrading bacteria n3 The bacterial suspension was shaken and cultivated; the bacterial suspension was to use an inoculation loop to pick a ring of thalli from the solid medium, and insert it into a 25ml test tube containing 6ml of LB medium, and then the test tube was stoppered and placed at 30 Obtained by overnight culture in a shaker at 180 rpm; the OD 600 value of the bacterial suspension is 0.8-1.2, and the inoculation volume is 1% of the volume of the LB medium. In the present invention, when carrying out the shaking culture, the liquid filling amount of the medium is preferably 25mL/250mL, and the culture time is preferably 15h. At this time, the cultivated cellulose-degrading bacteria n3 produces the highest amount of IAA and the best strain growth ability. good. The temperature of the shaking culture in the present invention is preferably 28-30° C., and the shaking speed is preferably 160-180 rpm.

本发明在利用所述纤维素降解菌n3制备CMC酶时,优选包括以下步骤:将液体发酵培养基调节pH值为4.0~6.0,接种所述纤维素降解菌n3,震荡培养;所述纤维素降解菌n3的接种体积为所述LB培养基体积的1%;所述液体发酵包括以下浓度的原料:氯化钠6g/L、七水硫酸镁0.1g/L、氯化钙0.1 g/L、磷酸二氢钾0.5g/L、酵母膏10g/L和秸秆20g/L。When using the cellulose-degrading bacteria n3 to prepare the CMC enzyme, the present invention preferably includes the following steps: adjusting the pH of the liquid fermentation medium to 4.0-6.0, inoculating the cellulose-degrading bacteria n3, and shaking culture; the cellulose The inoculation volume of degrading bacteria n3 is 1% of the volume of the LB medium; the liquid fermentation includes raw materials with the following concentrations: sodium chloride 6g/L, magnesium sulfate heptahydrate 0.1g/L, calcium chloride 0.1 g/L , potassium dihydrogen phosphate 0.5g/L, yeast extract 10g/L and straw 20g/L.

在本发明中,所述LB培养基或液体发酵培养基中优选还包括以下质量百分含量的组分:0.1%碳源、1%氮源。本发明所述LB培养基中碳源优选包括葡萄糖、甘露醇、蔗糖、麦芽糖、木糖、乳糖和果糖中的一种或多种,更优选为甘露醇;所述氮源优选包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素和蛋白胨的一种或多种,更优选为酵母粉。本发明所述液体培养基中氮源优选包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素和蛋白胨的一种或多种,更优选为酵母粉或蛋白胨。In the present invention, the LB medium or the liquid fermentation medium preferably further includes the following components by mass: 0.1% carbon source, 1% nitrogen source. The carbon source in the LB medium of the present invention preferably includes one or more of glucose, mannitol, sucrose, maltose, xylose, lactose and fructose, more preferably mannitol; the nitrogen source preferably includes potassium nitrate, One or more of ammonium sulfate, ammonium nitrate, yeast powder, glutamic acid, urea and peptone, more preferably yeast powder. The nitrogen source in the liquid medium of the present invention preferably includes one or more of potassium nitrate, ammonium sulfate, ammonium nitrate, yeast powder, glutamic acid, urea and peptone, more preferably yeast powder or peptone.

本发明还提供了所述纤维素降解菌n3在制备促腐促生菌剂中的应用。The present invention also provides the application of the cellulose-degrading bacteria n3 in the preparation of a decay-promoting and growth-promoting bacterial agent.

本发明所述促腐促生菌剂的类型优选为菌水剂;所述菌水剂在应用时,以所述纤维素降解菌n3的量计,其接种量优选为1~9×106CFU/g秸秆或 1~9×107CFU/g土壤,更优选为5×106CFU/g秸秆或5×107CFU/g土壤。The type of the decay-promoting bacteria agent of the present invention is preferably bacteria water agent; when the bacteria water agent is applied, the inoculation amount is preferably 1-9×10 6 based on the amount of the cellulose-degrading bacteria n3 CFU/g straw or 1-9×10 7 CFU/g soil, more preferably 5×10 6 CFU/g straw or 5×10 7 CFU/g soil.

本发明还提供了所述纤维素降解菌n3在促进秸秆还田效率和农作物增产中的应用。本发明所述应用中纤维素降解菌n3的使用方法和施用量与上述相同,在此不再赘述。The invention also provides the application of the cellulose-degrading bacteria n3 in promoting straw returning efficiency and increasing crop yield. The use method and application amount of the cellulose-degrading bacteria n3 in the application of the present invention are the same as above, and will not be repeated here.

下面结合实施例对本发明提供的一株产IAA的纤维素降解菌n3及其应用进行详细的说明,但是不能把它们理解为对本发明保护范围的限定。A cellulose-degrading bacterium n3 producing IAA and its application will be described in detail below with reference to the examples, but they should not be construed as limiting the protection scope of the present invention.

实施例1Example 1

1、试剂准备:1. Reagent preparation:

LB培养基:蛋白胨10g,酵母提取物5g,氯化钠10g,蒸馏水1000mL,调节pH7.0~7.2,121℃灭菌20分钟(固体培养基在此配方上加琼脂20g)。LB medium: 10 g of peptone, 5 g of yeast extract, 10 g of sodium chloride, 1000 mL of distilled water, adjusted to pH 7.0-7.2, and sterilized at 121°C for 20 minutes (add 20 g of agar to this recipe for solid medium).

无机盐培养基:硫酸铵2.0g,磷酸二氢钠0.5g,磷酸氢二钾0.5g,七水硫酸镁0.2g,二氯化钙0.1g,蒸馏水1000mL,调pH 7.0~7.2,121℃灭菌20分钟。Inorganic salt medium: ammonium sulfate 2.0g, sodium dihydrogen phosphate 0.5g, dipotassium hydrogen phosphate 0.5g, magnesium sulfate heptahydrate 0.2g, calcium dichloride 0.1g, distilled water 1000mL, adjusted to pH 7.0~7.2, sterilized at 121°C bacteria for 20 minutes.

液体发酵培养基:氯化钠6g,七水硫酸镁0.1g,氯化钙0.1g,磷酸二氢钾0.5g,酵母膏10g,秸秆20g,蒸馏水1000mL,121℃灭菌20分钟。Liquid fermentation medium: 6 g of sodium chloride, 0.1 g of magnesium sulfate heptahydrate, 0.1 g of calcium chloride, 0.5 g of potassium dihydrogen phosphate, 10 g of yeast extract, 20 g of straw, 1000 mL of distilled water, sterilized at 121°C for 20 minutes.

富集培养基:羧甲基纤维素钠20g,微晶纤维素5g,纤维素粉5g,磷酸氢二钾1g,硝酸1g,七水硫酸镁0.2g,二水氯化铜0.1g,三氯化铁0.02g,蒸馏水1000mL。121℃灭菌20分钟。Enrichment medium: sodium carboxymethyl cellulose 20g, microcrystalline cellulose 5g, cellulose powder 5g, dipotassium hydrogen phosphate 1g, nitric acid 1g, magnesium sulfate heptahydrate 0.2g, copper chloride dihydrate 0.1g, trichloride Iron 0.02g, distilled water 1000mL. Sterilize at 121°C for 20 minutes.

羧甲基纤维素培养基:羧甲基纤维素钠15g,硝酸铵1g,酵母膏1g,七水硫酸镁0.5g,磷酸二氢钾1g,琼脂15g,蒸馏水1000mL。121℃灭菌 20分钟。Carboxymethyl cellulose medium: 15 g of sodium carboxymethyl cellulose, 1 g of ammonium nitrate, 1 g of yeast extract, 0.5 g of magnesium sulfate heptahydrate, 1 g of potassium dihydrogen phosphate, 15 g of agar, and 1000 mL of distilled water. Sterilize at 121°C for 20 minutes.

2、菌株筛选2. Strain screening

将从安徽省蒙城县内农业示范科技园区内采取的砂姜黑土称取10g土壤样品接种于90mL无菌水中,28℃,150rpm摇床震荡30min,在无菌操作台中,取1mL土壤悬液,加入9mL无菌水,制成浓度为10-1的原液。稀释平板法分离纯化菌株,纯培养的菌株置于4℃冰箱中保存。Weigh 10g soil samples from the sand ginger black soil collected in the Agricultural Demonstration Science and Technology Park in Mengcheng County, Anhui Province, inoculate 10g soil samples in 90mL sterile water, shake at 28°C, 150rpm shaker for 30min, and take 1mL soil suspension in the sterile operation table. , add 9 mL of sterile water to make a stock solution with a concentration of 10 -1 . The strains were isolated and purified by the dilution plate method, and the pure cultured strains were stored in a refrigerator at 4°C.

供试土壤的基本性质如表1所示:The basic properties of the tested soils are shown in Table 1:

表1供试土壤的基本性质Table 1 Basic properties of the tested soils

Figure RE-GDA0002389795870000061
Figure RE-GDA0002389795870000061

Figure RE-GDA0002389795870000071
Figure RE-GDA0002389795870000071

再将分离、纯化获得的菌株分别接种在羧甲基纤维素钠选择培养基上,刚果红染色法放置20min后测量菌落直径(D)和透明圈直径(H),根据 H/D值大小,初步判断菌株降解纤维素能力的强弱。The strains obtained by separation and purification were then inoculated on the sodium carboxymethyl cellulose selective medium, and the colony diameter (D) and the diameter of the transparent circle (H) were measured after the Congo red staining method was placed for 20 minutes. According to the H/D value, Preliminary judgment on the strength of the strain's ability to degrade cellulose.

用刚果红染色法筛选出具有纤维素降解能力的所有菌株,根据H/D结果表明,n3菌株降解纤维素能力最高。All strains with cellulose-degrading ability were screened by Congo red staining. According to the H/D results, the n3 strain had the highest cellulose-degrading ability.

粗酶液制备:将菌种接种于以小麦秸秆粉为唯一碳源的液体培养基中 37℃液体摇瓶培养60h,把发酵液于4℃、5000r·min-1离心10min,上清液即为粗酶液。取0.2mL上清液于25mL干燥刻度试管中,加入1.8mL 1%CMC-Na溶液(pH值4.8,0.1mol/L的柠檬酸-柠檬酸钠缓冲液配制)50℃水浴30min后加入DNS试剂3.0mL,沸水浴5min,终止反应并显色。冷水淋浴冷却,定容至25mL摇匀,用520nm波长下测定吸光度。空白对照为酶液在沸水浴中15min使其失活,其它条件不变。Preparation of crude enzyme solution: inoculate the strains in a liquid medium with wheat straw powder as the sole carbon source and cultivate in a liquid shake flask at 37°C for 60 hours. For the crude enzyme solution. Take 0.2 mL of supernatant into a 25 mL dry scale test tube, add 1.8 mL of 1% CMC-Na solution (pH 4.8, prepared with 0.1 mol/L citric acid-sodium citrate buffer) in a water bath at 50°C for 30 min and then add DNS reagent 3.0mL, boiling water bath for 5min, stop the reaction and develop color. Cool in a cold shower, dilute to 25 mL, shake well, and measure the absorbance at a wavelength of 520 nm. For the blank control, the enzyme solution was inactivated in a boiling water bath for 15 min, and other conditions remained unchanged.

本试验酶活力X=1000×G×25/0.2×30×180。The enzyme activity in this test is X=1000×G×25/0.2×30×180.

式中:X:样品的酶活力(U枷);1000:换算倍数;G:标准曲线上光吸收值所对应的葡萄糖毫克数;25:定容体积(mL);0.2:加酶量(mL);30为作用时间(min);180:葡萄糖的分子量(g/moL)。在上述条件下,酶活力按照国际单位规定定义为:每分钟催化底物(羧甲基纤维素钠)水解生成1pmol葡萄糖的酶量为1个酶活力单位U。In the formula: X: the enzyme activity of the sample (U flail); 1000: conversion multiple; G: the number of milligrams of glucose corresponding to the light absorption value on the standard curve; 25: volume of constant volume (mL); 0.2: amount of enzyme added (mL) ); 30 is the action time (min); 180: the molecular weight of glucose (g/moL). Under the above conditions, the enzyme activity is defined according to the international unit regulations as: the amount of enzyme that catalyzes the hydrolysis of the substrate (sodium carboxymethyl cellulose) to generate 1 pmol of glucose per minute is 1 enzyme activity unit U.

筛选出的8株菌中n3降解纤维素能力最强,显著高于其他菌株,CMC 酶活力可达20.60U·mL-1Among the 8 strains screened out, n3 had the strongest ability to degrade cellulose, which was significantly higher than that of other strains, and the CMC enzyme activity could reach 20.60U·mL -1 .

定性测定:将具有纤维素降解功能细菌接种于含有L-色氨酸(100 mg·L-1)的LB液体培养基,30℃,180rpm,培养1d,取100μL菌悬液滴于白色陶瓷板上,同时加入100μLSalkowski比色液(50mL 35%HClO4,1 mL 0.5mol·L-1FeCl3,遮光保存),将白色陶瓷板在室温下遮光放置30分钟后对其进行观察,颜色变红者表示其能分泌吲哚乙酸,颜色的深浅代表着其产吲哚乙酸能力的高低,不变色代表其不产吲哚乙酸,阳性对照为100μL 未接种菌液的LB培养基加入100μL Salkowski比色液。Qualitative determination: Inoculate bacteria with cellulose degradation function in LB liquid medium containing L-tryptophan (100 mg·L -1 ) at 30°C, 180 rpm, culture for 1 d, take 100 μL of bacterial suspension and drop it on a white ceramic plate At the same time, 100μL Salkowski colorimetric solution (50mL 35% HClO 4 , 1 mL 0.5mol·L -1 FeCl 3 , stored in the dark) was added at the same time, and the white ceramic plate was placed under light for 30 minutes at room temperature to observe it, and the color turned red It can secrete indole acetic acid, the depth of color represents the level of its ability to produce indole acetic acid, and no color change means it does not produce indole acetic acid. The positive control is 100 μL of LB medium without inoculation, adding 100 μL of Salkowski colorimetric liquid.

定量测定:对通过定性分析筛选出的具有分泌IAA能力的菌株进行定量测定,培养条件同定性测定,先用分光光度法测定菌悬液的OD600值,然后吸取5mL菌悬液于10000rpm离心10分钟,取2mL上清液加入等体积 Salkowski比色液,室温遮光静置30分钟,在波长为530nm时,测定其OD 值,通过IAA标准曲线计算菌悬液中IAA含量。Quantitative determination: quantitatively determine the strains with the ability to secrete IAA screened out by qualitative analysis, the culture conditions are qualitatively determined, first measure the OD 600 value of the bacterial suspension by spectrophotometry, then draw 5mL of the bacterial suspension and centrifuge it at 10000rpm for 10 minutes. minutes, take 2 mL of supernatant and add an equal volume of Salkowski colorimetric solution, let stand for 30 minutes in the shade at room temperature, measure its OD value at a wavelength of 530 nm, and calculate the IAA content in the bacterial suspension by IAA standard curve.

通过IAA定性分析,有5株菌具有产IAA能力,分别为n1、n3、n4、 n5、n8,又通过定量测定,结果表明,n3菌株产IAA能力最强,浓度可达 19.07mg·L-1,显著高于其它菌株。Through the qualitative analysis of IAA, 5 strains have the ability to produce IAA, namely n1, n3, n4, n5, n8, and through quantitative determination, the results show that the n3 strain has the strongest ability to produce IAA, and the concentration can reach 19.07 mg·L - 1 , significantly higher than other strains.

通过以上测定即可筛选出产CMC酶和IAA能力最强,且具有较高的小麦秸秆促腐能力的纤维素降解菌n3。The cellulose-degrading bacteria n3, which has the strongest ability to produce CMC enzymes and IAA, and has a higher ability to promote the decay of wheat straw, can be screened through the above determination.

将上述方法筛选分离出的菌株经南京公司进行测序,根据所获得的16S rDNA(SEQID NO.1)序列结果,在GenBank数据库中进行比对,Blast搜索同源序列,使用MEGA5.0软件,用Neighbour-Joining法构建系统发育树。结合形态学分析及该菌株的生理生化结果特征,鉴定为玉米固氮螺菌 (azospirillumzeae)。该菌根据16S rDNA序列构建的n3菌株的系统发育树,如图4所示。The strains screened and isolated by the above method were sequenced by Nanjing Company, and compared in the GenBank database according to the obtained 16S rDNA (SEQID NO.1) sequence results, Blast searched for homologous sequences, using MEGA5.0 software, Phylogenetic tree was constructed by Neighbour-Joining method. Combined with morphological analysis and physiological and biochemical characteristics of the strain, it was identified as azospirillumzeae. The phylogenetic tree of the n3 strain constructed according to the 16S rDNA sequence is shown in Figure 4.

对该菌的生理生化性质进行统计,如表2所示:Physiological and biochemical properties of the bacteria were counted, as shown in Table 2:

表2纤维素降解菌n3的生理生化特征Table 2 Physiological and biochemical characteristics of cellulose-degrading bacteria n3

Figure RE-GDA0002389795870000081
Figure RE-GDA0002389795870000081

注:+表示阳性反应,-表示阴性反应Note: + means positive reaction, - means negative reaction

实施例2Example 2

针对不同pH、通气量、不同氮源测试对菌株产CMC酶能力的影响Effects of different pH, ventilation and nitrogen sources on the ability of strains to produce CMC enzyme

1、培养基初始pH对产CMC酶能力影响1. The effect of initial pH of medium on the ability to produce CMC enzyme

将菌种接种于以小麦秸秆粉为唯一碳源的液体发酵培养基中,37℃液体摇瓶培养60h,用分光光度计测定其OD520值。设置初始pH分别为4、5、6、 7、8、9、10,培养60h后用分光光度计测定其产CMC酶的含量。The strains were inoculated into the liquid fermentation medium with wheat straw powder as the sole carbon source, cultured in liquid shake flasks at 37°C for 60h, and their OD 520 values were measured with a spectrophotometer. The initial pH was set at 4, 5, 6, 7, 8, 9, and 10, respectively. After culturing for 60 h, the content of CMC enzyme produced was measured with a spectrophotometer.

结果如图2所示:在pH值为5.0时,CMC酶活力最高,达到24.96U·mL-1, pH值为4.0时酶活次之,为24.85U·mL-1,表明n3菌株有较强的的耐酸能力,在pH为4.0、5.0时CMC酶活力显著高于其他pH条件下的酶活。The results are shown in Figure 2: when the pH value is 5.0, the CMC enzyme activity is the highest, reaching 24.96U·mL -1 , and when the pH value is 4.0, the enzyme activity is the second, which is 24.85U·mL -1 , indicating that the n3 strain has more Strong acid resistance, CMC enzyme activity at pH 4.0 and 5.0 is significantly higher than that under other pH conditions.

2、通气量对产CMC酶能力影响2. The effect of ventilation volume on the ability to produce CMC enzyme

将菌种接种于以小麦秸秆粉为唯一碳源的液体发酵培养基中,37℃液体摇瓶培养60h,用分光光度计测定其OD520值。设置25、50、75、100、150 mL的培养液装于250mL的三角瓶中,培养60h后用分光光度计测定其产 CMC酶的含量。The strains were inoculated into the liquid fermentation medium with wheat straw powder as the sole carbon source, cultured in liquid shake flasks at 37°C for 60h, and their OD 520 values were measured with a spectrophotometer. Set 25, 50, 75, 100, 150 mL of culture solution in a 250 mL Erlenmeyer flask. After culturing for 60 h, the content of CMC enzyme produced was measured with a spectrophotometer.

结果如图3所示:当250mL三角瓶装液量为25mL,通气量最大时,n3 菌株产CMC酶活力最高,为15.33U·mL-1The results are shown in Figure 3: when the liquid volume of the 250mL conical flask is 25mL and the ventilation volume is the largest, the n3 strain produces the highest CMC enzyme activity, which is 15.33U·mL -1 .

3、氮源对产CMC酶能力影响3. The effect of nitrogen sources on the ability to produce CMC enzymes

在以小麦秸秆粉为唯一碳源的液体发酵培养基中分别加入0.1%(m/V) 的氮源,氮源包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素、蛋白胨,37℃液体摇瓶培养60h,用分光分度计测定菌株CMC酶的含量。0.1% (m/V) nitrogen source was added to the liquid fermentation medium with wheat straw powder as the sole carbon source. The nitrogen sources included potassium nitrate, ammonium sulfate, ammonium nitrate, yeast powder, glutamic acid, urea, and peptone. , 37 ℃ liquid shake flask cultured for 60h, using a spectrophotometer to determine the content of strain CMC enzyme.

结果如图4所示:不同氮源对n3菌株产CMC酶能力的影响不同,其中以酵母粉、蛋白胨为氮源时,产CMC酶能力最显著,分别高达18.30、16.02 U·mL-1The results are shown in Figure 4: Different nitrogen sources have different effects on the ability of n3 strain to produce CMC enzyme. When yeast powder and peptone are used as nitrogen sources, the ability to produce CMC enzyme is the most significant, up to 18.30 and 16.02 U·mL -1 , respectively.

实施例3Example 3

测试不同pH、通气量、不同时间、不同碳源、不同氮源对菌株IAA产量和菌株生长量的影响Test the effects of different pH, aeration, different time, different carbon sources, and different nitrogen sources on the yield of strain IAA and the growth of strains

1、发酵时间对菌株IAA产量和菌株生长量的影响1. The effect of fermentation time on strain IAA yield and strain growth

将含有100mg·L-1L-色氨酸的50mL LB液体培养基(IAA检测培养基) 装于250mL三角瓶中,按照1%(V/V)的接种量接种OD值约为1的菌悬液,30℃,180rpm摇床培养,分别在10、15、20、32、44、56h动态取样,测定菌株生长情况(OD600)和产IAA能力(OD530),每个处理设三个重复。Put 50 mL of LB liquid medium (IAA detection medium) containing 100 mg·L -1 L-tryptophan in a 250 mL conical flask, and inoculate bacteria with an OD value of about 1 at an inoculum of 1% (V/V). The suspension was cultured at 30°C with a shaker at 180 rpm, and samples were dynamically sampled at 10, 15, 20, 32, 44, and 56 h, respectively, to determine the growth of the strain (OD 600 ) and the ability to produce IAA (OD 530 ). repeat.

结果如图5所示:在20h时OD600达到最大值,20h之后菌株生长出现衰落趋势,产IAA含量与菌株生长状况基本一致,在10~15h,菌株产IAA 含量呈对数增长,在15h时IAA含量达到最高,为18.66mg·L-1,在15h之后,菌株产IAA能力逐渐下降。The results are shown in Figure 5: OD 600 reached the maximum value at 20h, and the growth of the strain showed a declining trend after 20h. The content of IAA produced was basically consistent with the growth status of the strain. At 10-15h, the content of IAA produced by the strain increased logarithmically, and at 15h The IAA content reached the highest at 18.66 mg·L -1 . After 15 h, the ability of the strain to produce IAA gradually decreased.

2、pH值对菌株IAA产量和菌株生长量的影响2. The effect of pH value on the yield of strain IAA and the growth of strain

将含有100mg·L-1L-色氨酸的LB培养基分别调节到不同的pH(4、5、 6、7、8、9、10),取50mL LB液体培养基装于250mL三角瓶中,按照1% (V/V)的接种量接种OD值约为1的菌悬液,30℃,180rpm摇床培养24h,分别在10、15、20、32、44、56h动态取样,测定菌株生长情况(OD600) 和产IAA能力(OD530),每个处理设三个重复。The LB medium containing 100 mg·L -1 L-tryptophan was adjusted to different pH (4, 5, 6, 7, 8, 9, 10) respectively, and 50 mL of LB liquid medium was placed in a 250 mL conical flask. , according to the inoculum of 1% (V/V), inoculate a bacterial suspension with an OD value of about 1, cultivate at 30 ° C, 180 rpm shaker for 24 hours, and dynamically sample at 10, 15, 20, 32, 44, and 56 hours, respectively, and determine the strain. Growth ( OD600 ) and IAA-producing capacity ( OD530 ) were performed in triplicate for each treatment.

结果如图6所示:在pH为6.0时,菌株OD600值和OD530值均达到最大, OD600为0.70,产IAA浓度为19.03mg·L-1。砂姜黑土自身pH为酸性,表明菌株的生活习性与砂姜黑土相吻合。在pH 7.0~9.0之间,菌株生长情况和产 IAA含量相对稳定。The results are shown in Figure 6: when the pH was 6.0, the OD 600 and OD 530 values of the strain both reached the maximum, the OD 600 was 0.70, and the IAA concentration was 19.03 mg·L -1 . The pH of the sand ginger black soil itself is acidic, indicating that the living habits of the strains are consistent with the sand ginger black soil. Between pH 7.0 and 9.0, the growth and IAA content of the strain were relatively stable.

3、通气量对菌株IAA产量和菌株生长量的影响3. The effect of ventilation on the yield of strain IAA and the growth of strain

将含有100mg·L-1L-色氨酸LB液体培养基按25mL,50mL,75mL, 100mL,150mL装于250mL三角瓶中,按照1%(V/V)的接种量接种OD 值约为1的菌悬液,30℃,180rpm摇床培养,分别在10、15、20、32、44、 56h动态取样,测定菌株生长情况(OD600)和产IAA能力(OD530),每个处理设三个重复。Pack the LB liquid medium containing 100mg·L -1 L-tryptophan into 250mL conical flasks in 25mL, 50mL, 75mL, 100mL, 150mL, and inoculate the OD value of about 1% (V/V) according to the inoculation amount. The bacterial suspension was cultured at 30°C with a shaker at 180 rpm, and samples were dynamically sampled at 10, 15, 20, 32, 44, and 56 h, respectively, to determine the growth of the strain (OD 600 ) and the ability to produce IAA (OD 530 ). Three repetitions.

结果如图7所示:由于菌株n3是好氧细菌,250mL三角瓶装液量为25 mL时,其生长状况和产IAA条件达到最优,随着装液量的增加,n3菌株的生长趋势和产IAA含量总体上呈下降趋势。The results are shown in Figure 7: Since strain n3 is aerobic bacteria, when the liquid volume of the 250mL conical flask is 25 mL, its growth status and IAA production conditions are optimal. The IAA content generally showed a downward trend.

4、氮源对菌株IAA产量和菌株生长量的影响4. The effect of nitrogen source on the yield and growth of strain IAA

在不包括硫酸铵的无机盐培养基(含有100mg·L-1L-色氨酸)中分别加入0.1%(W/V)的氮源,氮源包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素、蛋白胨,取50mL装于250mL三角瓶中,按照1%(V/V)的接种量接种OD值约为1的菌悬液,30℃,180rpm摇床培养24h,分别在10、 15、20、32、44、56h动态取样,测定菌株生长情况(OD600)和产IAA能力(OD530)。0.1% (W/V) nitrogen sources were added to the inorganic salt medium (containing 100 mg·L -1 L-tryptophan) excluding ammonium sulfate, including potassium nitrate, ammonium sulfate, ammonium nitrate, yeast Powder, glutamic acid, urea, peptone, take 50 mL and put it in a 250 mL conical flask, inoculate a bacterial suspension with an OD value of about 1 according to the inoculum of 1% (V/V), and cultivate at 30 ° C, 180 rpm shaker for 24 h, Dynamic sampling was performed at 10, 15, 20, 32, 44, and 56 h, respectively, and the growth (OD 600 ) and IAA-producing ability (OD 530 ) of the strain were determined.

结果如图8所示:以酵母粉为氮源时,n3菌株的生长量(OD600)最大,为0.64,同时以酵母粉为氮源时,菌株产IAA含量(OD530)最高,高达36.18 mg·L-1The results are shown in Figure 8: when the yeast powder was used as the nitrogen source, the growth amount (OD 600 ) of the n3 strain was the largest, which was 0.64. At the same time, when the yeast powder was used as the nitrogen source, the strain produced the highest IAA content (OD 530 ), which was as high as 36.18 mg·L -1 .

5、碳源对菌株IAA产量和菌株生长量的影响5. The effect of carbon source on the yield and growth of strain IAA

在无机盐培养基(含有100mg·L-1L-色氨酸)中分别加入1%(W/V) 的碳源,碳源分别有葡萄糖、甘露醇、蔗糖、麦芽糖、木糖、乳糖、果糖,取50mL装于250mL三角瓶中,按照1%(V/V)的接种量接种OD值约为 1的菌悬液,30℃,180rpm摇床培养24h,分别在10、15、20、32、44、 56h动态取样,测定菌株生长情况(OD600)和产IAA能力(OD530)。Add 1% (W/V) carbon source to the inorganic salt medium (containing 100 mg·L -1 L-tryptophan), respectively, the carbon sources are glucose, mannitol, sucrose, maltose, xylose, lactose, Fructose, take 50mL and put it in a 250mL conical flask, inoculate a bacterial suspension with an OD value of about 1 according to the inoculum of 1% (V/V), and culture it at 30 ° C and 180 rpm for 24 hours. Dynamic sampling was performed at 32, 44, and 56 h, and the growth status (OD 600 ) and IAA-producing ability (OD 530 ) of the strain were determined.

结果如图9所示:以甘露醇为碳源时,产IAA能力最高,可达7.36mg·L-1,菌株生长量也达到最大。The results are shown in Figure 9: when mannitol was used as the carbon source, the ability to produce IAA was the highest, reaching 7.36 mg·L -1 , and the growth of the strain also reached the maximum.

实施例4:Example 4:

菌剂的秸秆促腐试验Experiment of straw rot-promoting test of inoculum

试验过程:称取粉碎后过20目筛的小麦秸秆粉5g于250mL三角瓶中,加水30mL,加硝酸钠2g,加入10mL离心重悬到无菌水中的菌液,使得菌液浓度达到108cfu·mL-1左右,培养15d后将秸秆取出,用蒸馏水反复清洗侧壁,80℃烘干至恒重,另设无菌水替代菌液,其它步骤一致,作为对照处理,每个处理三个重复。Test process: Weigh 5g of wheat straw powder that has passed through a 20-mesh sieve after being crushed into a 250mL conical flask, add 30mL of water, add 2g of sodium nitrate, and add 10mL of bacterial liquid that has been centrifuged and resuspended in sterile water, so that the concentration of the bacterial liquid reaches 10 8 About cfu·mL -1 , after culturing for 15 days, the straw was taken out, the side wall was repeatedly washed with distilled water, dried at 80 °C to constant weight, and sterile water was used to replace the bacterial liquid. The other steps were the same. As a control treatment, each treatment three repetitions.

降解试验如图15所示:经过15天的降解,加入菌剂的处理小麦秸秆的降解率达到15.1%,高于对照9.8%。The degradation test is shown in Figure 15: after 15 days of degradation, the degradation rate of the treated wheat straw with the inoculum reached 15.1%, which was 9.8% higher than that of the control.

实施例5:Example 5:

菌剂的玉米促生试验Growth-promoting test of inoculum in corn

试验土壤:取自安徽省蒙城县农业示范园Test soil: Taken from the Agricultural Demonstration Park of Mengcheng County, Anhui Province

试验方法:将玉米种子均匀的铺在附有洁净滤纸的培养皿中,用蒸馏水在28℃下浸泡2天,选择出芽良好整齐的种子播种。以花盆(上口直径5cm、下底直径3cm、高5cm)为培养容器,每盆装土5.0kg,种植玉米2株,将供试菌株n3培养后制成菌水剂,按照5×108CFU/g的接种量接种到土壤中,以不接菌剂为对照,每组5个重复。播种前,分别用上述菌液浸泡经催芽的玉米种子。每盆放入土壤距离上沿1cm,将浸泡后的种子播种到盆里,再覆盖一层浮土,玉米每盆播种一粒种子,每种处理种植5盆。播种后将花盆置于人工气候箱中(白天30℃,夜晚25℃。光照时间为16小时)。所有处理在相同条件下随机排列,在同一时间进行浸盆浇水。N、K肥的用量分别为每盆尿素2.0g、氯化钾1.4g。Test method: Spread corn seeds evenly in a petri dish with clean filter paper, soak them in distilled water at 28°C for 2 days, and select well-sprouted seeds for sowing. Take the flowerpot (diameter of upper mouth 5cm, diameter of lower bottom 3cm, height 5cm) as a culture container, each pot is filled with soil 5.0kg, and 2 corn plants are planted. The inoculum amount of 8 CFU/g was inoculated into the soil, and no inoculum was used as the control, with 5 replicates in each group. Before sowing, soak the germinated corn seeds with the above bacterial solution respectively. Put the soil into each pot at a distance of 1 cm from the upper edge, sow the soaked seeds into the pot, and then cover with a layer of floating soil. Sow one corn seed per pot, and plant 5 pots for each treatment. After sowing, the pots were placed in an artificial climate box (30° C. during the day and 25° C. at night. Lighting time was 16 hours). All treatments were randomly arranged under the same conditions, and immersion pot watering was performed at the same time. The dosages of N and K fertilizers were 2.0 g of urea and 1.4 g of potassium chloride per pot, respectively.

样品收获:玉米生长49天后采样,测量玉米的株高、植株干重、鲜重。Sample harvesting: The corn was sampled after 49 days of growth, and the plant height, dry weight and fresh weight of the corn were measured.

表3接种菌株n3对玉米植株的影响Table 3 Effects of inoculated strain n3 on maize plants

Figure RE-GDA0002389795870000121
Figure RE-GDA0002389795870000121

注:*表示两处理间有显著性差异(P<0.05),**表示两处理间有极显著差异(P<0.01)Note: * means there is a significant difference between the two treatments (P<0.05), ** means there is a very significant difference between the two treatments (P<0.01)

结果如表3所示:菌株n3有促进植株生长的作用,在本试验中,经过接菌处理的后,玉米植株的株高、SPAD值较对照处理增加且差异显著 (P<0.5);全钾较对照处理差异极显著(P<0.01)。其中玉米株高、SPAD值较对照处理分别增长18.3%、5.24%,全钾较对照增长15.6%。综上:接菌植株在形态和养分吸收上明显优于对照处理。The results are shown in Table 3: strain n3 has the effect of promoting plant growth. In this experiment, after inoculation treatment, the plant height and SPAD value of maize plants increased compared with the control treatment, and the difference was significant (P<0.5); Potassium was significantly different from the control treatment (P<0.01). Among them, the plant height and SPAD value of maize increased by 18.3% and 5.24% respectively compared with the control treatment, and the total potassium increased by 15.6% compared with the control. In conclusion: the inoculated plants were significantly better than the control treatment in terms of morphology and nutrient absorption.

本发明提供了一株产IAA的纤维素降解菌n3及其应用,具有产IAA和 CMC酶的能力,可促腐秸秆、提高纤维素降解率,从而促进秸秆还田效率,减轻环境污染,实现农作物增产。The invention provides an IAA-producing cellulose-degrading bacterium n3 and its application, which has the ability to produce IAA and CMC enzymes, can promote the rot of straw and improve the cellulose degradation rate, thereby promoting the efficiency of straw returning to the field, reducing environmental pollution, and realizing Crop yields increased.

以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above are only the preferred embodiments of the present invention. It should be pointed out that for those skilled in the art, without departing from the principles of the present invention, several improvements and modifications can be made. It should be regarded as the protection scope of the present invention.

序列表sequence listing

<110> 安徽农业大学<110> Anhui Agricultural University

<120> 一株产IAA的纤维素降解菌n3及其应用<120> A cellulose-degrading bacterium n3 producing IAA and its application

<160> 1<160> 1

<170> SIPOSequenceListing 1.0<170> SIPOSequenceListing 1.0

<210> 1<210> 1

<211> 560<211> 560

<212> DNA<212> DNA

<213> Azospirillum zeae<213> Azospirillum zeae

<400> 1<400> 1

cctacgggag gcagcagtgg ggaatattgg acaatgggcg caagcctgat ccagcaatgc 60cctacgggag gcagcagtgg ggaatattgg acaatgggcg caagcctgat ccagcaatgc 60

cgcgtgagtg atgaaggcct tagggttgta aagctctttc gcacgcgacg atgatgacgg 120cgcgtgagtg atgaaggcct tagggttgta aagctctttc gcacgcgacg atgatgacgg 120

cagcgtgaga agaagccccg gctaacttcg tgccagcagc cgcggtaata cgaagggggc 180cagcgtgaga agaagccccg gctaacttcg tgccagcagc cgcggtaata cgaagggggc 180

tagcgttgtt cggaattact gggcgtaaag ggcgcgtagg cggcctgttt agtcagaagt 240tagcgttgtt cggaattact gggcgtaaag ggcgcgtagg cggcctgttt agtcagaagt 240

gaaagctccg ggctcaacct gggaatagct tttgatactg gcaggcttga gttccggaga 300gaaagctccg ggctcaacct gggaatagct tttgatactg gcaggcttga gttccggaga 300

ggatggtgga attcccagtg tagaggtgaa attcgtagat attgggaaga acaccggtgg 360ggatggtgga attcccagtg tagaggtgaa attcgtagat attgggaaga acaccggtgg 360

cgaaggcggc catctggacg gacactgacg ctgaggcgcg aaagcgtggg gagcaaacag 420cgaaggcggc catctggacg gacactgacg ctgaggcgcg aaagcgtggg gagcaaacag 420

gattagatac cctggtagtc cacgccgtaa acgatgaatg ctagacgtcg gggtgcatgc 480gattagatac cctggtagtc cacgccgtaa acgatgaatg ctagacgtcg gggtgcatgc 480

acttcggtgt cgccgctaac gcattaagca ttccgcctgg ggagtacggc cgcaaggtta 540acttcggtgt cgccgctaac gcattaagca ttccgcctgg ggagtacggc cgcaaggtta 540

aaactcaaag gaattgacgg 560aaactcaaag gaattgacgg 560

Claims (10)

1.一株产IAA的纤维素降解菌玉米固氮螺菌(Azospirillum zeae) n3,其特征在于,保藏于中国普通微生物菌种保藏管理中心,保藏编号为CGMCC No.18613。1. A cellulose-degrading bacteria Azospirillum zeae ( Azospirillum zeae ) n3 that produces IAA, is characterized in that, it is preserved in China General Microorganism Culture Collection and Management Center, and the deposit number is CGMCC No.18613. 2.权利要求1所述纤维素降解菌玉米固氮螺菌n3在制备IAA和/或CMC酶中的应用。2. The application of the cellulose-degrading bacteria Azospirillum zeae n3 according to claim 1 in the preparation of IAA and/or CMC enzymes. 3.根据权利要求2所述应用,其特征在于,在利用所述纤维素降解菌玉米固氮螺菌n3制备IAA时,包括以下步骤:调节含有100mg/L L-色氨酸的LB培养基的pH值为6.0~9.0,接种所述纤维素降解菌玉米固氮螺菌n3的菌悬液,震荡培养;所述菌悬液的体积为所述LB培养基体积的1%;所述菌悬液的OD600值为0.8~1.2。3. application according to claim 2 is characterized in that, when utilizing described cellulose degrading bacteria Azospirillum zeae n3 to prepare IAA, comprising the following steps: regulate the LB medium containing 100mg/L L-tryptophan. The pH value is 6.0-9.0, inoculate the bacterial suspension of the cellulose-degrading bacteria Azospirillum zeae n3, and shake culture; the volume of the bacterial suspension is 1% of the volume of the LB medium; the bacterial suspension The OD 600 value is 0.8 to 1.2. 4.根据权利要求3所述应用,其特征在于,所述振荡培养的温度为28~30℃,震荡速度为160~180rpm。4 . The application according to claim 3 , wherein the temperature of the shaking culture is 28-30° C., and the shaking speed is 160-180 rpm. 5 . 5.根据权利要求2所述应用,其特征在于,在利用所述纤维素降解菌玉米固氮螺菌n3制备CMC酶时,包括以下步骤:将液体发酵培养基调节pH值为4.0~6.0,接种所述纤维素降解菌玉米固氮螺菌n3,震荡培养;所述纤维素降解菌玉米固氮螺菌n3的接种体积为所述液体发酵培养基体积的1%;所述液体发酵培养基包括以下浓度的原料:氯化钠6g/L、七水硫酸镁0.1g/L、氯化钙0.1g/L、磷酸二氢钾0.5g/L、酵母膏10g/L和秸秆20g/L。5. application according to claim 2, is characterized in that, when utilizing described cellulose degrading bacteria Azospirillum zeae n3 to prepare CMC enzyme, comprises the following steps: adjusting the pH value of liquid fermentation medium to 4.0~6.0, inoculating The cellulose-degrading bacterium Azospirillum zeae n3 was cultured with shaking; the inoculation volume of the cellulose-degrading bacterium Azospirillum zeae n3 was 1% of the volume of the liquid fermentation medium; the liquid fermentation medium included the following concentrations Raw materials: sodium chloride 6g/L, magnesium sulfate heptahydrate 0.1g/L, calcium chloride 0.1g/L, potassium dihydrogen phosphate 0.5g/L, yeast extract 10g/L and straw 20g/L. 6.根据权利要求5所述的应用,其特征在于,所述LB培养基或液体发酵培养基中还包括以下质量百分含量的组分:0.1%碳源、1%氮源。6 . The application according to claim 5 , wherein the LB medium or the liquid fermentation medium further comprises the following components by mass: 0.1% carbon source and 1% nitrogen source. 7 . 7.根据权利要求6所述的应用,其特征在于,所述碳源包括葡萄糖、甘露醇、蔗糖、麦芽糖、木糖、乳糖和果糖中的一种或多种;7. The application according to claim 6, wherein the carbon source comprises one or more of glucose, mannitol, sucrose, maltose, xylose, lactose and fructose; 所述氮源包括硝酸钾、硫酸铵、硝酸铵、酵母粉、谷氨酸、尿素和蛋白胨中的一种或多种。The nitrogen source includes one or more of potassium nitrate, ammonium sulfate, ammonium nitrate, yeast powder, glutamic acid, urea and peptone. 8.权利要求1所述纤维素降解菌玉米固氮螺菌n3在制备促腐促生菌剂中的应用。8. The application of the cellulose-degrading bacteria Azospirillum zeae n3 according to claim 1 in the preparation of a decay-promoting and growth-promoting microbial agent. 9.根据权利要求8所述应用,其特征在于,所述促腐促生菌剂的类型为菌水剂;所述菌水剂在应用时,以所述纤维素降解菌玉米固氮螺菌n3的量计,接种量为1~9×106CFU/g秸秆或1~9×107CFU/g土壤。9. application according to claim 8, it is characterized in that, the type of described decay-promoting bacteria agent is bacteria water agent; When described bacteria water agent is in application, with described cellulose degrading bacteria Azospirillum zeae n3 The inoculum amount is 1-9×10 6 CFU/g straw or 1-9×10 7 CFU/g soil. 10.权利要求1所述纤维素降解菌玉米固氮螺菌n3在促进秸秆还田效率和农作物增产中的应用。10 . The application of the cellulose-degrading bacteria Azospirillum maize n3 according to claim 1 in promoting straw returning efficiency and increasing crop yield. 11 .
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