[go: up one dir, main page]

CN103194407B - Straw-decomposition composite microbial preparation and preparation method thereof - Google Patents

Straw-decomposition composite microbial preparation and preparation method thereof Download PDF

Info

Publication number
CN103194407B
CN103194407B CN201310091888.XA CN201310091888A CN103194407B CN 103194407 B CN103194407 B CN 103194407B CN 201310091888 A CN201310091888 A CN 201310091888A CN 103194407 B CN103194407 B CN 103194407B
Authority
CN
China
Prior art keywords
preparation
bacillus
rice straw
staphylococcus
cgmcc
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201310091888.XA
Other languages
Chinese (zh)
Other versions
CN103194407A (en
Inventor
倪国荣
涂国全
魏赛金
潘晓华
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanchang City Longda Biological Technology Development Co Ltd
Original Assignee
Jiangxi Agricultural University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jiangxi Agricultural University filed Critical Jiangxi Agricultural University
Priority to CN201310091888.XA priority Critical patent/CN103194407B/en
Publication of CN103194407A publication Critical patent/CN103194407A/en
Application granted granted Critical
Publication of CN103194407B publication Critical patent/CN103194407B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Fertilizers (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

本发明涉及一种稻草腐解复合微生物制剂及其制备方法,该制剂由韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌和黑曲霉按照一定的质量百分比混合制成,适用于水稻秸秆的直接全量还田,能显著加快稻草腐解速度,有利于移栽茬口的迁移;且可以提高有机质含量,提高土壤酶活性,改善土壤理化性质,提高下季水稻产量;同时还可以改良土壤,提高水肥利用率,减肥增效,降低稻草焚烧对环境的污染,综合效益显著。The invention relates to a rice straw decomposing composite microbial preparation and a preparation method thereof. The preparation is composed of Bacillus welschii, Bacillus amyloliquefaciens, Bacillus megaterium, staphylococcus, Achromobacter xylosoxidans and Aspergillus niger according to a certain mass percentage It is made by mixing and is suitable for the direct full-scale return of rice straw to the field. It can significantly speed up the decomposition rate of rice straw and facilitate the migration of transplanted stubble; it can also increase the content of organic matter, increase the activity of soil enzymes, improve the physical and chemical properties of soil, and improve the quality of rice in the next season. At the same time, it can also improve the soil, increase the utilization rate of water and fertilizer, reduce weight and increase efficiency, and reduce the environmental pollution caused by rice straw burning. The comprehensive benefits are remarkable.

Description

一种稻草腐解复合微生物制剂及其制备方法A kind of rice straw decomposing compound microbial preparation and preparation method thereof

技术领域     technical field

本发明涉及一种微生物制剂,属于微生物技术领域,用于稻草直接全量还田,具体涉及稻草腐解复合微生物制剂及其制备方法和使用方法。 The invention relates to a microbial preparation, which belongs to the technical field of microorganisms, and is used for returning rice straw directly to the field in full, in particular to a rice straw decomposing composite microbial preparation and a preparation method and a use method thereof.

背景技术     Background technique

我国年产稻草约2亿吨,不仅资源丰富和可再生,而且稻草中含有大量的氮、磷、钾、硅及丰富的有机质。稻草焚烧,不仅造成资源的极大浪费和对环境的严重污染,也大大减少了土壤有机质的投入,严重影响着土壤的可持续耕作。进行稻草还田,能有效地提高土壤有机质积累和养分含量;改变土壤腐殖质组成及特性;改善土壤的物理性状;增加土壤微生物种类和数量,提高生物活度和土壤酶的活性,从而促进作物生长发育,提高作物产量,节省生产成本。 my country's annual output of rice straw is about 200 million tons, which is not only rich in resources and renewable, but also contains a large amount of nitrogen, phosphorus, potassium, silicon and rich organic matter. Rice straw burning not only causes a great waste of resources and serious pollution to the environment, but also greatly reduces the input of soil organic matter, which seriously affects the sustainable cultivation of soil. Returning straw to the field can effectively increase the accumulation of soil organic matter and nutrient content; change the composition and characteristics of soil humus; improve the physical properties of the soil; increase the types and quantities of soil microorganisms, increase the biological activity and soil enzyme activity, thereby promoting crop growth development, increase crop yields, and save production costs.

但是,稻草还田由于在秸秆分解过程中存在微生物与作物“争氮”现象,在管理不当的情况下还会影响作物的生长。随着机械收割的发展,稻草全量还田迅速发展,如何促进稻草的快速分解腐烂,是当前水稻生产中亟待解决的一个重大问题,基于此,研究开发促进稻草快速腐熟的微生物菌剂具有重要意义。 However, due to the "nitrogen competition" phenomenon between microorganisms and crops in the process of straw decomposition, rice straw returning to the field will also affect the growth of crops in the case of improper management. With the development of mechanical harvesting, the rapid development of rice straw returning to the field in full, how to promote the rapid decomposition and decay of rice straw is a major problem to be solved in current rice production. .

发明内容     Invention content

本发明所述解决的技术问题在于,提供一种用于稻草直接全量还田的稻草腐解复合微生物制剂及其制备方法,该制剂腐熟速度快,方法易行,操作简便。 The technical problem to be solved by the present invention is to provide a rice straw decomposing compound microbial preparation and a preparation method thereof, which is used for direct returning full amount of rice straw to the field, and the preparation has a fast decomposing speed, easy method and simple operation.

为实现上述目的,本发明采用的技术方案为:一种稻草腐解复合微生物制剂,包括: In order to achieve the above object, the technical solution adopted in the present invention is: a kind of rice straw decomposing compound microbial preparation, comprising:

黑曲霉Aspergillus niger、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心( 简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7162; Aspergillus niger , the depository unit is the General Microbiology Center of China Committee for Culture Collection of Microorganisms (CGMCC for short, address: No. 3, Yard 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip Code 100101), and the preservation date is On January 18, 2013, the deposit number is CGMCC No.7162;

韦氏芽孢杆菌Bacillus weihenstephanensis、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心( 简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7158; Bacillus weihenstephanensis , the depository unit is the General Microbiology Center of China Committee for the Collection of Microbial Cultures (CGMCC for short, address: No. 3, Yard 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip code 100101), deposit The date is January 18, 2013, and the deposit number is CGMCC No.7158;

葡萄球菌Staphylococcus condimenti、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心( 简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7161; The staphylococcus Staphylococcus condimenti , the preservation unit is the General Microbiology Center of the China Committee for Microbial Culture Collection (CGMCC for short, address: No. 3, No. 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip code 100101), and the preservation date is On January 18, 2013, the deposit number is CGMCC No.7161;

解淀粉芽孢杆菌Bacillus amyloliquefaciens、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心(简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7159; Amyloliquefaciens Bacillus amyloliquefaciens , the depository unit is the General Microbiology Center of China Committee for Culture Collection of Microbial Cultures (CGMCC for short, address: No. 3, Yard 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip code 100101), deposit The date is January 18, 2013, and the deposit number is CGMCC No.7159;

木糖氧化无色杆菌Achromobacter xylosoxidans、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心( 简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7157; Achromobacter xylosoxidans , preserved by the General Microorganism Center of China Committee for Culture Collection of Microorganisms (CGMCC for short, address: No. 3, Yard No. 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip code 100101) , the date of deposit is January 18, 2013, and the deposit number is CGMCC No.7157;

巨大芽孢杆菌Bacillus megaterium、保藏单位为中国微生物菌种保藏管理委员会普通微生物中心( 简称CGMCC,地址: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,邮编100101)、保藏日期为2013年1月18日、保藏编号为CGMCC No.7160。 Bacillus megaterium , the depository unit is the General Microbiology Center of China Committee for Culture Collection of Microorganisms (CGMCC for short, address: No. 3, Yard 1, Beichen West Road, Chaoyang District, Beijing, Institute of Microbiology, Chinese Academy of Sciences, Zip code 100101), and the date of deposit On January 18, 2013, the deposit number is CGMCC No.7160.

一种稻草腐解复合微生物制剂,其特征在于,它由下述质量百分比的菌种配制: A rice straw decomposing compound microbial preparation is characterized in that it is prepared by the bacterial classification of the following mass percentages:

木糖氧化无色杆菌   1%—35%     巨大芽孢杆菌      2%—25% Achromobacter xylosoxidans 1%—35% Bacillus megaterium 2%—25%

韦氏芽孢杆菌       5%—25%     葡萄球菌       0.5%—20% Bacillus wechnerii 5%—25% Staphylococcus 0.5%—20%

解淀粉芽孢杆菌     8%—25%     黑曲霉            15%—55% Bacillus amyloliquefaciens 8%—25% Aspergillus niger 15%—55%

一种稻草腐解复合微生物制剂的制备方法,其步骤是: A preparation method of rice straw decomposing compound microbial preparation, the steps are:

1)黑曲霉的培养:将黑曲霉接种于马铃薯培养基上,培养温度为28~30℃,作一级种子斜面;然后接种到固体发酵培养基上作扩大培养,至产品中孢子数达到1.0~3.0×108个/克; 1) Cultivation of Aspergillus niger: Inoculate Aspergillus niger on potato medium at a culture temperature of 28-30°C as a first-grade seed slant; then inoculate it on a solid fermentation medium for expanded cultivation until the number of spores in the product reaches 1.0 ~3.0× 108 pcs/g;

2)韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌的培养:将韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌试管斜面种,分别先接种在牛肉膏蛋白胨培养基上,培养温度为28~30℃,作一级种子斜面培养;然后接种到三角瓶里液体发酵培养基内做振荡二级液体培养;然后再转入发酵罐里液体发酵培养基内作三级液体发酵,至产品中活菌数达到1.0~2.0×109个/ml; 2) Cultivation of Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, and Achromobacter xylose oxidation: Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, xylose oxidizing bacteria Chromobacterium test tube slant species were first inoculated on beef extract peptone medium at a culture temperature of 28-30°C for primary seed slant culture; then inoculated into the liquid fermentation medium in the Erlenmeyer flask for shaking secondary liquid culture; Then transfer it to the liquid fermentation medium in the fermenter for three-stage liquid fermentation until the number of viable bacteria in the product reaches 1.0~2.0× 109 /ml;

3)将上述韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌混合而成的细菌发酵液用吸附剂按固液比为4:1进行吸附,阴凉风干后得到各细菌固体制剂,水分含量17%~20%,活菌数>1.5×1010个/克; 3) Bacterial fermentation broth mixed with the above-mentioned Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, and Achromobacter xyloseoxidans is adsorbed with an adsorbent at a solid-to-liquid ratio of 4:1, and air-dried in a cool place Finally, each bacterial solid preparation was obtained, with a moisture content of 17% to 20%, and the number of viable bacteria > 1.5× 1010 /g;

4)将以上黑曲霉固体培养物进行阴凉风干后,碾磨过筛,即制成高效分解稻草真菌固体制剂,水分含量17%~20%,其孢子浓度>1.0×1010个/克; 4) Dry the above solid culture of Aspergillus niger in a cool air, then grind and sieve to make a solid preparation of rice straw fungus with a moisture content of 17%-20% and a spore concentration of >1.0× 1010 /g;

5)将上述的细菌固体制剂和真菌固体制剂按一定质量百分比混合后,按质量标准检验,成品按重量进行分装,即得稻草腐解复合微生物制剂。 5) Mix the above-mentioned bacterial solid preparation and fungal solid preparation according to a certain mass percentage, inspect according to the quality standard, and pack the finished product according to weight to obtain the rice straw decomposing compound microbial preparation.

所述固体发酵培养基的重量组份为:豆渣50g,稻草粉10g,MgSO4·7H2O 0.1g,KH2PO4 0.1g,CaCO3 0.1g,拌匀后在温度为121℃进行灭菌1h。 The weight components of the solid fermentation medium are: 50g of bean dregs, 10g of rice straw powder, 0.1g of MgSO 4 7H 2 O, 0.1g of KH 2 PO 4 , 0.1g of CaCO 3 . Bacteria 1h.

所述液体发酵培养基的重量组份为:蛋白胨5g,稻草粉10g,MgSO4·7H2O 0.3g,KH2PO4 0.5g,NaCl 0.5g,ZnSO0.3g,自来水1000mL,pH自然, 在温度为121℃进行灭菌30min。 The weight components of the liquid fermentation medium are: peptone 5g, rice straw powder 10g, MgSO 4 7H 2 O 0.3g, KH 2 PO 4 0.5g, NaCl 0.5g, ZnSO 4 0.3g, tap water 1000mL, pH natural, Sterilize at a temperature of 121° C. for 30 minutes.

所述吸附剂为草炭、小麦胚粉、脱脂的玉米胚粉、玉米芯碎片、粗麸皮、大豆细粉或吸水性强的谷物类,以及至少其中二种成份的组合。 The adsorbent is peat, wheat germ flour, defatted corn germ flour, corn cob fragments, coarse bran, soybean fine powder or grains with strong water absorption, and a combination of at least two of them.

所述的稻草腐解复合微生物制剂在稻草直接全量还田中的应用。 The application of the rice straw decomposing compound microbial preparation in the direct full amount of rice straw returning to the field.

本发明的优点是:施用稻草腐解复合微生物制剂能显著加快稻草腐解速度,6-8天就能完全分解还田的稻草,不影响下季水稻的移栽,有利于移栽茬口的迁移;且可以提高有机质含量,提高土壤酶活性,改善土壤理化性质,提高下季水稻产量;同时还可以改良土壤,提高水肥利用率,减肥增效,降低稻草焚烧对环境的污染,综合效益显著。     The invention has the advantages that: the application of the rice straw decomposing compound microbial preparation can significantly accelerate the rice straw decomposition rate, and the rice straw returned to the field can be completely decomposed within 6-8 days, which does not affect the transplanting of the next season rice, and is beneficial to the migration of the transplanted stubble ; and can increase organic matter content, increase soil enzyme activity, improve soil physical and chemical properties, and increase rice yield in the next season; at the same time, it can also improve soil, increase water and fertilizer utilization efficiency, reduce weight and increase efficiency, and reduce environmental pollution caused by rice straw burning. The comprehensive benefits are significant. 

具体实施方式 Detailed ways

以下结合实施例对本发明作进一步说明,稻草腐解复合微生物制剂适用于水稻秸秆的还田,稻草腐解复合微生物制剂的菌剂包括黑曲霉、韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌。 The present invention will be further described below in conjunction with the examples. The rice straw decomposing compound microbial preparation is suitable for returning rice stalks to the field. , Staphylococcus, Achromobacter xyloseoxidans.

一种稻草腐解复合微生物制剂,它由下述质量百分比的菌种配制: A kind of rice straw decomposing compound microbial preparation, it is prepared by the bacterial classification of following mass percentage:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 1%—35%1%—35% 巨大芽孢杆菌Bacillus megaterium 2%—25%2%—25% 韦氏芽孢杆菌Bacillus welcheei 5%—25%5%—25% 葡萄球菌staphylococcus 0.5%—20%0.5%—20% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 8%—25%8%—25% 黑曲霉Aspergillus niger 15%—55%15%—55%

 一种稻草腐解复合微生物制剂,它的最优范围由以下质量百分比的菌种配制: A rice straw decomposing compound microbial preparation, its optimal range is formulated by the bacterial classification of the following mass percentages:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 5%—25%5%—25% 巨大芽孢杆菌Bacillus megaterium 5%—15%5%—15% 韦氏芽孢杆菌Bacillus welcheei 10%—20%10%—20% 葡萄球菌staphylococcus 5%—10%5%—10% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 10%—20%10%—20% 黑曲霉Aspergillus niger 25%—50%25%—50%

一种稻草腐解复合微生物制剂,它的最佳配比由以下质量百分比的菌种配制: A kind of rice straw decomposing compound microbial preparation, its optimum proportion is formulated by the bacterial classification of following mass percentage:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 12%12% 巨大芽孢杆菌Bacillus megaterium 8%8% 韦氏芽孢杆菌Bacillus welcheei 14%14% 葡萄球菌staphylococcus 10%10% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 12%12% 黑曲霉Aspergillus niger 44%44%

一种稻草腐解复合微生物制剂,它的另一最佳配比由以下质量百分比的菌种配制: A kind of rice straw decomposing composite microbial preparation, another optimal proportion of it is formulated by the bacterial classification of following mass percentage:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 20%20% 巨大芽孢杆菌Bacillus megaterium 15%15% 韦氏芽孢杆菌Bacillus welcheei 10%10% 葡萄球菌staphylococcus 5%5% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 20%20% 黑曲霉Aspergillus niger 30%30%

实施例1:一种稻草腐解复合微生物制剂,它由下述质量百分比原料配制而成: Embodiment 1: a kind of rice straw decomposes compound microbial preparation, it is formulated by following mass percent raw material:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 12%12% 巨大芽孢杆菌Bacillus megaterium 8%8% 韦氏芽孢杆菌Bacillus welcheei 14%14% 葡萄球菌staphylococcus 10%10% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 12%12% 黑曲霉Aspergillus niger 44%44%

表中黑曲霉、木糖氧化无色杆菌、韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌均保藏于中国微生物菌种保藏管理委员会普通微生物中心、简称CGMCC。 The Aspergillus niger, Achromobacter xyloseoxidans, Bacillus welschii, Bacillus amyloliquefaciens, Bacillus megaterium and Staphylococcus in the table are all preserved in the General Microorganism Center of China Committee for Culture Collection of Microorganisms, referred to as CGMCC.

一种稻草腐解复合微生物制剂的制备方法,其步骤是: A preparation method of rice straw decomposing compound microbial preparation, the steps are:

1.各菌种的单独扩大培养: 1. Separate expansion culture of each strain:

1)黑曲霉的培养:将黑曲霉接种于马铃薯培养基(参照微生物学实验教材)上,培养温度为28℃,作一级种子斜面,然后接种到三角瓶里做振荡二级液体培养,然后接种到固体发酵培养基上作三级培养,至产品中孢子数达到1.0-3.0×108个/克。 1) Cultivation of Aspergillus niger: Inoculate Aspergillus niger on potato medium (refer to microbiology experiment textbook) at a culture temperature of 28°C, make a first-level seed slant, then inoculate it into a triangular flask for shaking secondary liquid culture, and then Inoculate it on a solid fermentation medium for tertiary cultivation until the number of spores in the product reaches 1.0-3.0× 108 /g.

2)韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌的培养:将韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌试管斜面种分别首先接种在牛肉膏蛋白胨培养基(参照微生物学实验教材)上,培养温度为28℃,作一级种子斜面培养,然后接种到三角瓶里液体发酵培养基做振荡二级液体培养,然后转入发酵罐里液体发酵培养基作三级液体发酵,至产品中活菌数达到1.0~2.0×109个/ml。 2) Cultivation of Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, and Achromobacter xylose oxidation: Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, xylose oxidizing bacteria Chromobacterium test tube slant species were first inoculated on beef extract peptone medium (refer to microbiology experiment textbook) respectively, and the culture temperature was 28°C for primary seed slant culture, and then inoculated into the liquid fermentation medium in the Erlenmeyer flask for secondary shaking Liquid culture, and then transferred to the liquid fermentation medium in the fermenter for three-stage liquid fermentation, until the number of viable bacteria in the product reaches 1.0~2.0×10 9 /ml.

2.高效分解水稻秸秆的细菌制剂的制备: 2. Preparation of bacterial preparations for efficiently decomposing rice straw:

将上述韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌、木糖氧化无色杆菌等细菌发酵液用吸附剂按固液比4:1的比例吸附,阴凉风干后即可得到高效分解稻草的各细菌固体制剂,水分含量17%~20%,活菌数>1.5×1010个/克。 Adsorb the bacterial fermentation liquid of the above-mentioned Bacillus wei, Bacillus amyloliquefaciens, Bacillus megaterium, Staphylococcus, Achromobacter xylosoxidans, etc. with an adsorbent at a solid-to-liquid ratio of 4:1, and dry it in a cool air to obtain high-efficiency Various bacterial solid preparations for decomposing rice straw, the water content is 17%~20%, and the number of viable bacteria is >1.5×10 10 /g.

3.高效分解水稻秸秆真菌制剂的制备: 3. Preparation of fungal preparations for efficiently decomposing rice straw:

将以上黑曲霉固体培养物进行阴凉风干后,碾磨过筛,即制成高效分解稻草真菌固体制剂,水分含量17%~20%,其孢子浓度>1.0×1010个/克。 Dry the above solid culture of Aspergillus niger in a cool air, then grind and sieve to prepare a solid preparation of rice straw fungus with a moisture content of 17%-20% and a spore concentration of >1.0×10 10 /g.

4.高效分解水稻秸秆的复合微生物制剂制备: 4. Preparation of compound microbial preparations for efficiently decomposing rice straw:

将上述的复合细菌制剂和真菌制剂按一定的质量比混合搅拌后,按质量标准检验,成品按重量进行分装,即得稻草腐解复合微生物制剂。 After the above-mentioned composite bacterial preparation and fungal preparation are mixed and stirred according to a certain mass ratio, they are inspected according to quality standards, and the finished products are divided and packaged according to weight to obtain the rice straw decomposing composite microbial preparation.

实施例2:Example 2:

一种稻草腐解复合微生物制剂,它由下述质量百分比原料配制而成: A kind of rice straw decomposing compound microbial preparation, it is formulated by following mass percent raw material:

菌种bacteria 质量百分比mass percentage 菌种bacteria 质量百分比mass percentage 木糖氧化无色杆菌Achromobacter xylosoxidans 20%20% 巨大芽孢杆菌Bacillus megaterium 15%15% 韦氏芽孢杆菌Bacillus welcheei 10%10% 葡萄球菌staphylococcus 5%5% 解淀粉芽孢杆菌Bacillus amyloliquefaciens 20%20% 黑曲霉Aspergillus niger 30%30%

表中黑曲霉、木糖氧化无色杆菌、韦氏芽孢杆菌、解淀粉芽孢杆菌、巨大芽孢杆菌、葡萄球菌均保藏于中国微生物菌种保藏管理委员会普通微生物中心、简称CGMCC。 The Aspergillus niger, Achromobacter xyloseoxidans, Bacillus welschii, Bacillus amyloliquefaciens, Bacillus megaterium and Staphylococcus in the table are all preserved in the General Microorganism Center of China Committee for Culture Collection of Microorganisms, referred to as CGMCC.

其制备步骤与实施例1相同。 Its preparation steps are identical with embodiment 1.

试验案例1:稻草腐解复合微生物制剂试验于2009年晚季在江西省进贤县温圳镇杨溪村进行。供试土壤的pH 值6.5,含有机质42.3 g·kg-1,全氮1.87 g·kg-1,碱解氮151 mg·kg-1,速效磷6.0mg·kg-1,速效钾178 mg·kg-1。前茬为早稻,早稻收获后进行机割全量还田,稻草由收割机切成10 cm长度,进行旋耕移栽。 Test case 1: The test of rice straw decomposing compound microbial preparation was carried out in Yangxi Village, Wenzhen Town, Jinxian County, Jiangxi Province in the late season of 2009. The pH value of the tested soil was 6.5, containing 42.3 g·kg -1 of organic matter, 1.87 g·kg -1 of total nitrogen, 151 mg·kg -1 of alkaline nitrogen, 6.0 mg·kg -1 of available phosphorus, and 178 mg·kg of available potassium kg -1 . The previous stubble was early rice, and after the early rice was harvested, it was machine-cut and returned to the field in full. The rice straw was cut into 10 cm length by the harvester, and then transplanted by rotary tillage.

试验设四个处理:(1)稻草不还田对照,即将机械收割后的早稻稻草全部清除出试验田块;(2)稻草全量还田;(3)稻草全量还田+稻草腐解复合微生物制剂,稻草腐解复合微生物制剂用量为30 kg·hm-2;(4)稻草全量还田+腐秆灵,腐秆灵用量为30 kg·hm-2Four treatments were set up in the experiment: (1) Control without rice straw returning to the field, that is, all the early rice straw after mechanical harvesting was removed from the test field; (2) Full amount of rice straw was returned to the field; (3) Full amount of rice straw was returned to the field + rice straw decomposed compound microbial preparation , the dosage of rice straw decomposing compound microbial preparation was 30 kg·hm -2 ; (4) the whole amount of rice straw was returned to the field + Huzhuling, and the dosage of Huzhuling was 30 kg·hm -2 .

试验结果分析: Analysis of test results:

1)秸秆颜色变化:稻草腐解复合微生物制剂处理三天后,从颜色上看,不添加本制剂的基本没有变化,而添加本制剂处理的稻草表面明显有许多的黑点;两个对照处理的稻草较硬,添加本制剂处理的秸秆变软。本制剂处理8天后,没有添加本制剂的稻草刚出现黑色,而使用本制剂处理的稻草颜色已经很黑;从稻草强度上讲,不加本制剂的不容易拉断,本制剂处理的一碰即断。 1) Color change of straw: After three days of treatment with rice straw decomposing compound microbial preparation, from the point of view of color, there is basically no change in the color without adding this preparation, but there are obviously many black spots on the surface of rice straw treated with this preparation; the two control treatments The straw is hard, but the straw treated with this preparation becomes soft. After 8 days of treatment with this preparation, the rice straw without this preparation just appeared black, while the color of the rice straw treated with this preparation was already very black; in terms of strength, the straw without this preparation was not easy to break, and the rice straw treated with this preparation was not easy to break. Instantly break.

2)土壤理化性质影响:稻草全量还田并添加本制剂能够显著提高土壤中细菌、真菌和放线菌的数量,增强蔗糖酶、脲酶、过氧化氢酶和纤维素酶的活力。 2) Effects on soil physical and chemical properties: Returning full amount of rice straw to the field and adding this preparation can significantly increase the number of bacteria, fungi and actinomycetes in the soil, and enhance the activities of invertase, urease, catalase and cellulase.

3)对晚稻产量影响:实验数据显示,稻草全量还田添加本制剂能够提高晚稻的单穗粒数、结实率、千粒重和产量。稻草还田添加本制剂能够显著提高晚稻的产量,且比单一稻草全量还田的增产效果更加明显。 3) Effect on late rice yield: Experimental data show that the addition of this preparation can increase the number of grains per panicle, seed setting rate, 1000-grain weight and yield of late rice. Rice straw returning to the field Adding this preparation can significantly increase the yield of late rice, and the effect of increasing yield is more obvious than that of a single rice straw returning to the field in full.

本发明的稻草腐解复合微生物制剂的使用方法:1)稻草平铺,水稻收获时将稻草切成长度为8~12cm小段,均匀平铺于田间; The method of using the rice straw decomposing compound microbial preparation of the present invention: 1) Spread the rice straw flatly, cut the rice straw into small sections with a length of 8-12 cm when the rice is harvested, and spread it evenly in the field;

2)施用稻草腐解复合微生物制剂,每公顷为25~45kg,均匀撒施于水稻秸秆表面,每公顷用尿素75~150kg,撒于到稻草表面调节碳氮比; 2) Apply rice straw decomposing compound microbial preparation, 25-45kg per hectare, evenly spread on the surface of rice straw, 75-150kg of urea per hectare, sprinkle on the surface of rice straw to adjust the carbon-nitrogen ratio;

3)翻耕,灌水浸泡后立即进行旋耕,将稻草与稻草腐解复合微生物制剂混匀一起翻耕入地下,隔夜后即可进行移栽; 3) Turn tillage, immediately perform rotary tillage after soaking in water, mix the rice straw with the rice straw decomposing compound microbial preparation and turn it into the ground together, and transplant it after overnight;

4)后期管理,按照常规管理进行水肥管理。 4) Post-management, water and fertilizer management shall be carried out according to conventional management.

试验案例2:试验在江西农业大学科技园水稻试验田进行,供试土壤pH6.2,有机质20.01g/kg,全氮0.158g/kg,碱解氮80.08 mg/kg,有效磷18.32 mg/kg,速效钾63.2 mg/kg。试验设 6个处理,分别为稻草不还田、稻草还田、稻草还田+本制剂、稻草不还田+化肥、稻草还田+化肥、稻草还田+化肥+本制剂。早稻于3月9日播种,4月4日移栽,行株距为23.1cm×13.2cm。试验采用随机区组排列,重复3次,小区面积10 m2(2m×5m),小区间筑埂并用塑料薄膜包埋,防止水肥流动。小区做好后,将人工切割成10 cm左右长度的晚稻稻草均匀撒入小区,灌水后再均匀撒施本制剂,并人工脚踩入田。稻草还田量为风干稻草0.5 kg/m2,自制本制剂施用量为5 g/m2。尿素施用量为36 g/m2,按基肥:分蘖肥:穗肥=5:2:3施用;氯化钾施用量为30 g/m2,按基肥:穗肥=7:3施用;过磷酸钙施用量为62.5 g/m2,在整地时一次性施用。 Test case 2: The test was carried out in the rice test field of Jiangxi Agricultural University Science and Technology Park. The test soil had pH 6.2, organic matter 20.01g/kg, total nitrogen 0.158g/kg, alkaline nitrogen 80.08 mg/kg, available phosphorus 18.32 mg/kg, Available potassium 63.2 mg/kg. Six treatments were set up in the experiment, namely, no returning rice straw, returning rice straw, returning rice straw+this preparation, not returning rice straw+chemical fertilizer, returning rice straw+chemical fertilizer, returning rice straw+chemical fertilizer+this preparation. The early rice was sown on March 9 and transplanted on April 4, with a row-to-plant spacing of 23.1cm×13.2cm. The experiment was arranged in random blocks and repeated 3 times. The area of the plot was 10 m 2 (2m×5m). Ridges were built between the plots and embedded with plastic film to prevent the flow of water and fertilizer. After the plot is completed, the late rice straw that is manually cut to a length of about 10 cm is evenly sprinkled into the plot, and then the preparation is evenly sprinkled after irrigation, and manually stepped into the field. The amount of rice straw returned to the field is 0.5 kg/m 2 of air-dried rice straw, and the application rate of this self-made preparation is 5 g/m 2 . The application rate of urea was 36 g/m 2 , applied according to base fertilizer: tiller fertilizer: ear fertilizer = 5:2:3; the application rate of potassium chloride was 30 g/m 2 , applied according to base fertilizer: ear fertilizer = 7:3; The application rate of calcium phosphate is 62.5 g/m 2 , and it is applied once when preparing the soil.

试验结果分析: Analysis of test results:

1)对土壤理化性质的影响:稻草还田配施化肥与本制剂可以有效地提高土壤细菌、真菌、放线菌数量,增强蔗糖酶、脲酶、过氧化氢酶的活性。与稻草不还田施肥和不施肥相比,稻草还田配施化肥与本制剂,提高了土壤不同形态有机碳含量和碳库管理指数,其中活性有机碳、碳库管理指数分别提高了10.33~28.88%、12.85~30%。 1) Effects on physical and chemical properties of soil: Returning rice straw to the field with chemical fertilizers and this preparation can effectively increase the number of soil bacteria, fungi, and actinomycetes, and enhance the activities of invertase, urease, and catalase. Compared with fertilization without rice straw returning to the field and without fertilization, the application of chemical fertilizers and this preparation with rice straw returning to the field increased the content of different forms of organic carbon in the soil and the carbon pool management index, among which the active organic carbon and carbon pool management index increased by 10.33~ 28.88%, 12.85~30%.

2)对水稻产量的影响:稻草还田配施化肥与菌剂处理的产量显著高于其他处理,其产量增幅3.56~23.29%。 2) Effects on rice yield: The yield of rice straw returning to the field combined with chemical fertilizers and bacterial agents was significantly higher than that of other treatments, and the yield increased by 3.56-23.29%.

本发明稻草腐解复合微生物制剂的注意事项: Matters needing attention of the rice straw decomposing compound microbial preparation of the present invention:

1)产品存放于阴凉干燥处,避免强光暴晒。 1) Store the product in a cool and dry place, avoid strong light exposure.

2)避免与强酸、强碱、易挥发性化学品及杀菌剂混放、混用。 2) Avoid mixing and using with strong acids, strong alkalis, volatile chemicals and fungicides.

3)增施氮肥施为了调节碳氮比,避免微生物繁殖前期与作物争夺养分影响 3) Increase the application of nitrogen fertilizer in order to adjust the carbon-nitrogen ratio and avoid the influence of microorganisms competing for nutrients with crops in the early stage of reproduction

4)根据不同田块环境温度和肥力等条件,可酌情调整用量。 4) According to the environmental temperature and fertility of different fields, the dosage can be adjusted as appropriate.

Claims (5)

1. a straw decomposition complex microorganism preparations, is characterized in that, it is prepared by the bacterial classification of following mass percent:
Preserving number is the Achromobacter xylosoxidans (Achromobacter xylosoxidans) 1%-35% of CGMCC No.7157
Preserving number is the bacillus megaterium (Bacillus megaterium) 2%-25% of CGMCC No.7160
Preserving number is the Bacillus weihenstephanensis (Bacillus weihenstephanensis) 5%-25% of CGMCC No.7158
Preserving number is the staphylococcus (Staphylococcus condimenti) 0.5%-20% of CGMCC No.7161
Preserving number is the bacillus amyloliquefaciens (Bacillus amyloliquefaciens) 8%-25% of CGMCC No.7159
Preserving number is the aspergillus niger (Aspergillus niger) 15%-55% of CGMCC No.7162.
2. a preparation method for straw decomposition complex microorganism preparations as claimed in claim 1, is characterized in that, the steps include:
1) cultivation of aspergillus niger: aspergillus niger is inoculated on potato culture, culture temperature is 28 ~ 30 DEG C, makes first order seed inclined-plane; Then be inoculated on solid fermentation substratum and make enlarged culturing, reach 1.0 ~ 3.0 × 10 to product miospore number 8individual/gram;
2) cultivation of Bacillus weihenstephanensis, bacillus amyloliquefaciens, bacillus megaterium, staphylococcus, Achromobacter xylosoxidans: by Bacillus weihenstephanensis, bacillus amyloliquefaciens, bacillus megaterium, staphylococcus, Achromobacter xylosoxidans test tube slant kind, first be seeded in respectively on beef-protein medium, culture temperature is 28 ~ 30 DEG C, makes first order seed slant culture; Then be inoculated in triangular flask and in liquid fermentation medium, do the cultivation of vibration secondary liquid; And then proceed in fermentor tank and make tertiary liquid fermentation in liquid fermentation medium, to product, viable count reaches 1.0 ~ 2.0 × 10 9individual/ml;
3) the ferment product sorbent material above-mentioned Bacillus weihenstephanensis, bacillus amyloliquefaciens, bacillus megaterium, staphylococcus, Achromobacter xylosoxidans mixed is that 4:1 adsorbs by solid-to-liquid ratio, each bacterial solids preparation is obtained after cool place is air-dry, moisture content 17% ~ 20%, viable count > 1.5 × 10 10individual/gram;
4) above aspergillus niger solid culture is carried out cool place air-dry after, mill and sieve, namely make efficient-decomposition straw fungus solids preparation, moisture content 17% ~ 20%, its spore concentration > 1.0 × 10 10individual/gram;
5) by after above-mentioned bacterial solids preparation and the mixing of fungus solids preparation, by quality standard inspection, finished product carries out packing by weight, obtains straw decomposition complex microorganism preparations.
3. preparation method according to claim 2, is characterized in that, the composition by weight of described solid fermentation substratum is: bean dregs 50g, rice straw powder 10g, MgSO 47H 2o 0.1g, KH 2pO 40.1g, CaCO 30.1g, pH nature, is 121 DEG C in temperature after mixing thoroughly and carries out sterilizing 1h.
4. preparation method according to claim 2, is characterized in that, the composition by weight of described liquid fermentation medium is: peptone 5g, rice straw powder 10g, MgSO 47H 2o 0.3g, KH 2pO 40.5g, NaCl 0.5g, ZnSO 40.3g, tap water 1000mL, pH nature, is 121 DEG C in temperature and carries out sterilizing 30min.
5. preparation method according to claim 2, is characterized in that, described sorbent material is the combination of the peat composed of rotten mosses, wheat-germ meal, the maize powder of degreasing, corn cob fragment, bran or soybean fine powder and at least wherein two kinds of compositions.
CN201310091888.XA 2013-03-21 2013-03-21 Straw-decomposition composite microbial preparation and preparation method thereof Active CN103194407B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310091888.XA CN103194407B (en) 2013-03-21 2013-03-21 Straw-decomposition composite microbial preparation and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310091888.XA CN103194407B (en) 2013-03-21 2013-03-21 Straw-decomposition composite microbial preparation and preparation method thereof

Publications (2)

Publication Number Publication Date
CN103194407A CN103194407A (en) 2013-07-10
CN103194407B true CN103194407B (en) 2015-05-13

Family

ID=48717226

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310091888.XA Active CN103194407B (en) 2013-03-21 2013-03-21 Straw-decomposition composite microbial preparation and preparation method thereof

Country Status (1)

Country Link
CN (1) CN103194407B (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104789490B (en) * 2015-03-18 2018-05-18 杨凌绿都生物科技有限公司 A kind of complex microorganism decomposing microbial inoculum, preparation method and application
CN104962489B (en) * 2015-04-15 2018-02-02 嘉兴华斌生物科技有限公司 A kind of liquid straw decomposing inoculant and preparation and application
CN105272482A (en) * 2015-11-25 2016-01-27 江西农业大学 Mechanically-transplanted rice seedling raising matrix prepared by taking composted straws as raw materials and preparation method of mechanically-transplanted rice seedling raising matrix
CN105567604A (en) * 2016-02-16 2016-05-11 江苏中通生物科技有限公司 Compound microorganism bacterium agent and preparation method thereof
CN106277087A (en) * 2016-08-17 2017-01-04 潘明华 A kind of composite processing nitro compound waste water and preparation method thereof
CN107285399A (en) * 2017-07-03 2017-10-24 安徽天顺环保设备股份有限公司 A kind of filtrate for being used to handle heavy metals in industrial wastewater
CN108314585A (en) * 2018-03-15 2018-07-24 黄淮学院 Agriculture probiotics conversion stalk and the method for cultivating excrement production biological organic fertilizer
CN111808778B (en) * 2020-07-29 2021-05-14 东北农业大学 Bacillus wegener for preventing and treating verticillium wilt and culture method thereof, microbial inoculum and preparation method and application thereof
CN114230402B (en) * 2020-08-10 2023-03-03 浙江省农业科学院 Efficient decomposed liquid bacterial fertilizer and preparation method and application thereof
CN112048452B (en) * 2020-09-02 2022-03-22 浙江工业大学 Efficient calcium-mineralized bacillus and application thereof in concrete crack repair
CN112094159A (en) * 2020-09-22 2020-12-18 标优美生态工程盐城有限公司 Method for preparing organic fertilizer by fermenting straw through solar energy auxiliary heating
CN113826461A (en) * 2021-09-26 2021-12-24 宿迁市设施园艺研究院 Solanaceous vegetable straw in-situ returning method

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1304912A (en) * 2000-12-31 2001-07-25 李承海 Process for preparing microecological organic fertilizer
CN101486597A (en) * 2008-01-18 2009-07-22 天津市农业资源与环境研究所 Microbial composite microorganism inoculant for producing biological organic fertilizer from decomposed organic wastes
CN102161971A (en) * 2011-04-26 2011-08-24 杨洪岩 Fermentation inoculum for producing cellulase and hemicellulase
CN102229900A (en) * 2011-05-20 2011-11-02 周剑平 Compound probiotics preparation for biological organic fertilizers and preparation method thereof
CN102234616A (en) * 2010-04-28 2011-11-09 中国科学院沈阳应用生态研究所 Corrosion promoting agent for straw, its preparation method and application
CN102515951A (en) * 2011-12-14 2012-06-27 湖南省微生物研究所 Tobacco composite microbial fertilizer and its preparation method

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1304912A (en) * 2000-12-31 2001-07-25 李承海 Process for preparing microecological organic fertilizer
CN101486597A (en) * 2008-01-18 2009-07-22 天津市农业资源与环境研究所 Microbial composite microorganism inoculant for producing biological organic fertilizer from decomposed organic wastes
CN102234616A (en) * 2010-04-28 2011-11-09 中国科学院沈阳应用生态研究所 Corrosion promoting agent for straw, its preparation method and application
CN102161971A (en) * 2011-04-26 2011-08-24 杨洪岩 Fermentation inoculum for producing cellulase and hemicellulase
CN102229900A (en) * 2011-05-20 2011-11-02 周剑平 Compound probiotics preparation for biological organic fertilizers and preparation method thereof
CN102515951A (en) * 2011-12-14 2012-06-27 湖南省微生物研究所 Tobacco composite microbial fertilizer and its preparation method

Also Published As

Publication number Publication date
CN103194407A (en) 2013-07-10

Similar Documents

Publication Publication Date Title
CN103194407B (en) Straw-decomposition composite microbial preparation and preparation method thereof
CN102212494B (en) Organic matter decomposing inoculant, and preparation method and application thereof
CN101497870B (en) Microbial complex bacterial agent and use thereof
CN101712566B (en) Preparation method of soil moisturizing bio-fertilizer
CN102643120A (en) Preparation method of organic fertilizer
CN105175077A (en) Fruit cucumber culture medium and preparation method thereof
CN104774772B (en) It is a kind of with the straw decomposition microbial inoculum of getting fat effect and its application
CN109704840A (en) A kind of decomposing agent and its decomposed purposes to layer manure
CN108821875A (en) A kind of preparation method of high-activity microorganism fertilizer
CN111357612B (en) Composite microbial matrix for watermelon planting and preparation method and application thereof
CN106045677A (en) A kind of preparation method of special organic compound biological fertilizer for fruit trees
CN112602397A (en) Soil biological disinfection method for vegetable greenhouse in continuous cropping facility
CN106034744A (en) A method for producing oyster mushrooms by utilizing mulberry stalks and bagasse
CN101948780A (en) Antagonist bacterium for preventing and treating continuous cropping hot pepper epidemic disease and microbial organic fertilizer thereof
CN106518389A (en) Biofertilizer with edible fungus residue as raw material and preparation thereof
CN103351188B (en) Preparation method of agricultural organic fertilizer by treating pure straws as raw material
CN110066194A (en) Novel more bacterium composite microbe fertilizers of one kind and its preparation method and application
CN101928161B (en) Method for preparing direct seeding compression nutrition pot raw material
CN115197023B (en) A kind of biological organic fertilizer with gardening waste as matrix and preparation method thereof
CN112430163A (en) Biological fertilizer for relieving continuous cropping obstacle of watermelon with pressed sand
CN106045679A (en) A kind of preparation method of special organic compound biological fertilizer for peanut
CN103173387B (en) Growth-promoting bacteria for facilitating growth of rape and microbial organic fertilizer
CN105037045B (en) A kind of soybean nutritional liquid and preparation method thereof and application method
CN105439736B (en) Preparation method of solanaceous vegetable seedling culture substrate
CN110590458A (en) Jasmine bio-organic fertilizer capable of improving soil and preparation method thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20171205

Address after: No. 382, Shang Fang Road, Qingshan Lake District, Nanchang, Jiangxi

Patentee after: Nanchang City Longda Biological Technology Development Co Ltd

Address before: 330045 Jiangxi city of Nanchang Province Economic and Technological Development Zone Zhimin Road No. 1101, Jiangxi Agricultural University

Patentee before: Jiangxi Agriculture University