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CN108911859A - A kind of preparation method of middle microelement microorganism fertilizer - Google Patents

A kind of preparation method of middle microelement microorganism fertilizer Download PDF

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CN108911859A
CN108911859A CN201810906073.5A CN201810906073A CN108911859A CN 108911859 A CN108911859 A CN 108911859A CN 201810906073 A CN201810906073 A CN 201810906073A CN 108911859 A CN108911859 A CN 108911859A
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microbial inoculum
fermentation
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fertilizer
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CN108911859B (en
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夏红霞
朱启红
刘希东
沈勇
辛良群
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Liaoning Yimushen Agricultural Technology Co ltd
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Chongqing University of Arts and Sciences
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05DINORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D3/00Calcareous fertilisers
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

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Abstract

一种中微量元素生物肥的制备方法是以食用菌废弃菌渣、豆渣、粉煤灰、中微量元素盐、发酵菌菌剂、功能菌菌剂为原料,分别经过三次发酵制备而得。本发明是制备的生物有机肥中有益菌大于3.5亿/g、总养分含量高达18.1%、中微量元素含量高达7.2%,故制备的中微量元素生物有机肥既可以满足植物生长所需要的大量元素,又及时补充植物生长所需要的中微量营业元素,还可以通过固氮、解磷以及解钾菌进一步促进植物生长,并可通过病菌抑制菌进行生物防治,确保植物正常生长,制备过程多种物料不会结团起块,混合均匀,本品制得的生物肥发芽率高,幼苗长势好,发芽率高达98%。A preparation method of a medium-trace element biological fertilizer is prepared by three times of fermentation using waste edible fungus dregs, bean dregs, fly ash, medium-trace element salt, fermenting bacteria agent, and functional bacteria agent as raw materials. In the present invention, the beneficial bacteria in the prepared bio-organic fertilizer are greater than 350 million/g, the total nutrient content is as high as 18.1%, and the content of medium and trace elements is as high as 7.2%, so the prepared bio-organic fertilizer with medium and trace elements can meet the large amount required for plant growth. It can also supplement the medium and trace business elements needed for plant growth in a timely manner. It can also further promote plant growth through nitrogen fixation, phosphorus solubilization and potassium solubilization bacteria, and can carry out biological control by inhibiting bacteria to ensure the normal growth of plants. The preparation process is various. The material will not agglomerate and be mixed evenly. The biological fertilizer produced by this product has a high germination rate, and the seedlings grow well, with a germination rate as high as 98%.

Description

一种中微量元素微生物肥的制备方法A kind of preparation method of medium and trace element microbial fertilizer

技术领域technical field

本发明涉及微生物应用技术领域,具体涉及一种中微量微元素生物肥的制备方法。The invention relates to the technical field of microbe application, in particular to a preparation method of medium-trace and micro-element biological fertilizer.

背景技术Background technique

化肥在农业生产中起着重要作用。有专家认为,在其他生产因素不变的情况下,施用化肥可增加农业产量40%~60%;但长期使用化肥,易造成土壤养分结构失调,部分营养元素缺失,土壤物理性状变差,部分地块有害金属和有害病菌超标,进而导致作物营养失调,造成农产品品质降低。此外,土壤中残余的过量水溶性养分易被雨水和农田灌水淋溶到地下水及河流中,造成大面积的农业面源污染。Chemical fertilizers play an important role in agricultural production. Some experts believe that the application of chemical fertilizers can increase agricultural output by 40% to 60% when other production factors remain unchanged; Harmful metals and harmful bacteria in the land exceed the standard, which will lead to nutritional imbalance of crops and reduce the quality of agricultural products. In addition, the excess water-soluble nutrients remaining in the soil are easily leached into groundwater and rivers by rainwater and farmland irrigation, causing large-scale agricultural non-point source pollution.

有机肥具有养分全、肥效长、无污染的特点,向农田中施用有机肥不仅可增加土壤有机质含量,提高土壤蓄水、保肥能力,还可以改善土壤的理化性状和团粒结构,补充有益元素,并提高农产品品质。 但普通有机肥中微量元素种类和含量均较少,不能满足植物生长所需,直接影响了作物生长和农产品的品质。Organic fertilizer has the characteristics of complete nutrition, long fertilizer effect and no pollution. Applying organic fertilizer to farmland can not only increase the content of soil organic matter, improve soil water storage and fertilizer retention capacity, but also improve the physical and chemical properties and aggregate structure of soil, and supplement beneficial elements , and improve the quality of agricultural products. However, the types and contents of trace elements in ordinary organic fertilizers are small, which cannot meet the needs of plant growth and directly affect the growth of crops and the quality of agricultural products.

食用菌废料又称菌渣、菌糠、下脚料等,是食用菌栽培后的培养料。相关研究表明,食用菌菌渣中含有大量可利用的营养元素,如粗蛋白、粗脂肪、粗纤维、微量元素等,还含有多糖类、有机酸、酶、酚类等化学物质,是一种可被资源化利用的有机废弃物质。到目前为止,已有将废弃菌渣直接还田或将菌渣简单堆肥后制备有机肥研究。但废弃菌包中的营养物质大部分是以大分子形态存在,难于被植物直接吸收利用,既严重影响废弃菌包的农用效率,又会对环境承载造成相当大的压力,造成污染、影响农业可持续发展。并且,在制备有机肥过程中,不易混合均匀,制得的生物肥应用于种子发芽率低,幼苗长势较差。Edible fungus waste, also known as mushroom residue, fungus chaff, leftovers, etc., is the culture material after the cultivation of edible fungi. Relevant studies have shown that edible fungus residues contain a large number of available nutrients, such as crude protein, crude fat, crude fiber, trace elements, etc., and also contain polysaccharides, organic acids, enzymes, phenols and other chemical substances. An organic waste material that can be used as a resource. So far, there have been studies on the preparation of organic fertilizers by directly returning the waste fungus residue to the field or simply composting the fungus residue. However, most of the nutrients in the discarded bacterial packs exist in the form of macromolecules, which are difficult to be directly absorbed and utilized by plants. This not only seriously affects the agricultural efficiency of the discarded bacterial packs, but also puts considerable pressure on the environment, causing pollution and affecting agriculture. sustainable development. Moreover, in the process of preparing the organic fertilizer, it is not easy to mix evenly, and the prepared biological fertilizer has a low germination rate when applied to seeds, and the growth of the seedlings is relatively poor.

发明内容Contents of the invention

本发明的目的在于提供一种中微量元素生物肥的制备方法。The object of the present invention is to provide a kind of preparation method of medium and trace element biological fertilizer.

本发明的目的是通过如下技术措施实现的:The purpose of the present invention is achieved through the following technical measures:

一种中微量元素生物肥的制备方法,其特征在于:它是以食用菌废弃菌渣、豆渣、粉煤灰、中微量元素盐、发酵菌菌剂、功能菌菌剂为原料,分别经过三次发酵制备而得。A method for preparing medium-trace element biological fertilizer is characterized in that it uses edible fungus waste residue, bean dregs, fly ash, medium-trace element salt, fermenting bacteria agent, and functional bacteria agent as raw materials, and undergoes three separate processes. Prepared by fermentation.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述食用菌废弃菌渣优选为金针菇废弃菌渣、香菇废弃菌渣中的一种。Furthermore, a method for preparing medium and trace element biological fertilizer is characterized in that: the waste residue of edible fungi is preferably one of waste residue of Flammulina velutipes and waste residue of Lentinus edodes.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述发酵菌菌剂包括发酵菌A菌剂和发酵菌B菌剂,其中所述发酵菌A菌剂为枯草芽孢杆菌菌剂、纤维素酶、黑曲霉菌剂、白腐真菌菌剂组成的复合菌剂,其混合质量比为枯草芽孢杆菌菌剂:纤维素酶:黑曲霉菌剂:白腐真菌菌剂=1~10:1~10:1~5:1~5,其中所述发酵菌B为绵毛嗜热丝孢菌菌剂、长赤细菌菌剂、丝状菌菌剂、酵母菌菌剂组成的复合菌菌剂,其质量比为绵毛嗜热丝孢菌菌剂:长赤细菌菌剂:丝状菌菌剂:酵母菌菌剂=为1~10:1~10:1~5:1~5。Further, a method for preparing medium and trace element biological fertilizer, characterized in that: the fermenting bacteria agent includes fermenting bacteria A and fermenting bacteria B, wherein the fermenting bacteria A is Bacillus subtilis inoculum , cellulase, Aspergillus niger agent, and white rot fungus agent. : 1 ~ 10: 1 ~ 5: 1 ~ 5, wherein the fermenting bacteria B is a composite bacterium composed of Thermomyces lanuginosa, Rhodobacter inoculum, filamentous fungus, and saccharomyces Inoculum, its mass ratio is Thermomyces lanuginosa inoculum: Rhodobacter longum inoculum: Filamentous fungus inoculum: Saccharomyces inoculum = 1~10: 1~10: 1~5: 1~5 .

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述功能菌菌剂由根瘤菌菌剂、褐球固氮菌菌剂、枯草芽孢杆菌菌剂、巨大芽孢杆菌菌剂、地衣芽孢杆菌菌剂、苏云金芽孢杆菌菌剂、淡紫色拟青霉菌剂、绿色木霉菌剂混合组成的复合功能菌菌剂,其质量比为根瘤菌菌剂:褐球固氮菌菌剂:枯草芽孢杆菌菌剂:巨大芽孢杆菌菌剂:地衣芽孢杆菌菌剂:苏云金芽孢杆菌菌剂:淡紫色拟青霉菌剂:绿色木霉菌剂为1~10:1~10:1~5:1~5:1~5:1~5:1~5:1~5。Further, a method for preparing medium and trace element biological fertilizers is characterized in that: the functional bacterial agent is composed of rhizobia bacterial agent, pheobacterium nitrogen-fixing bacterial agent, Bacillus subtilis bacterial agent, Bacillus megaterium bacterial agent, Bacillus licheniformis bacterial agent Bacillus bacteria agent, Bacillus thuringiensis agent, Paecilomyces lavender agent, and Trichoderma viride agent are mixed together to form a composite functional agent, the mass ratio of which is rhizobium agent: brown nitrogen-fixing bacteria agent: Bacillus subtilis Agent: Bacillus megaterium Agent: Bacillus licheniformis Agent: Bacillus thuringiensis Agent: Paecilomyces lavender Agent: Trichoderma viride 1~10: 1~10: 1~5: 1~5: 1~ 5: 1~5: 1~5: 1~5.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述枯草芽孢杆菌为CGMCC,编号1.12938;所述黑曲霉为CGMCC,编号3.13901;所述白腐真菌为GDMCC,编号GIM3.393;所述绵毛嗜热丝孢菌为CCTCC,编号CCTCC AF 200043,所述长赤细菌为GDMCC,编号GIM1.491,所述丝状菌为CGMCC,编号1.15179;所述酵母菌为GDMCC,编号GIM2.210;所述根瘤菌为CGMCC,编号1.15570;所述褐球固氮菌为GDMCC,编号GIM1.272;所述巨大芽孢杆菌为CGMCC,编号1.9072;所述地衣芽孢杆菌为CGMCC,编号1.9048;所述苏云金芽孢杆菌为CGMCC,编号1.7902;所述淡紫色拟青霉为GDMCC,编号GIM3.405;所述绿色木霉为CGMCC,编号3.11450。Further, a method for preparing medium and trace element biological fertilizer, characterized in that: the Bacillus subtilis is CGMCC, number 1.12938; the Aspergillus niger is CGMCC, number 3.13901; the white rot fungus is GDMCC, number GIM3.393 The Thermomyces lanuginosa is CCTCC, numbering CCTCC AF 200043, the long red bacterium is GDMCC, numbering GIM1.491, and the filamentous fungus is CGMCC, numbering 1.15179; the saccharomycete is GDMCC, numbering GIM2.210; the rhizobia is CGMCC, numbering 1.15570; the brown spheroid azotobacter is GDMCC, numbering GIM1.272; the Bacillus megaterium is CGMCC, numbering 1.9072; the Bacillus licheniformis is CGMCC, numbering 1.9048; The Bacillus thuringiensis is CGMCC, number 1.7902; the Paecilomyces lilacinus is GDMCC, number GIM3.405; the Trichoderma viride is CGMCC, number 3.11450.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述三次发酵中第一次发酵是将去除泥沙后的食用菌废弃菌渣、豆渣与发酵菌A菌剂按质量比为7:2:1倒入好氧堆肥实验装置中的反应罐,补充适量清水至生物质堆含水量为38~42%,依次打开电源开关、搅拌开关、升温开关和空气泵,并将温度设置为30~60℃,温度上升至设置温度后关闭升温开关,密闭继续发酵3~7天,发酵期间反应罐气压维持在0.1~0.15Mpa;所述发酵菌A菌剂中枯草芽孢杆菌菌剂、纤维素酶、黑曲霉菌剂、白腐真菌菌剂的质量比优选为2:4:3:1。Further, a method for preparing medium and trace element biological fertilizer is characterized in that: the first fermentation in the three fermentations is to remove the discarded edible fungus dregs, bean dregs and fermentative bacteria A in a mass ratio of 7:2:1 Pour into the reaction tank in the aerobic composting experimental device, add an appropriate amount of clean water until the water content of the biomass pile is 38~42%, turn on the power switch, stirring switch, heating switch and air pump in turn, and set the temperature 30~60°C, turn off the temperature rise switch after the temperature rises to the set temperature, and continue to ferment for 3~7 days in an airtight environment. During the fermentation, the pressure of the reaction tank is maintained at 0.1~0.15Mpa; The mass ratio of cellulase, Aspergillus niger agent and white rot fungus agent is preferably 2:4:3:1.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述三次发酵中第二次发酵是向第一次发酵后的生物质堆中加入粉碎后的粉煤灰、中微量元素盐以及发酵菌B菌剂,上述物质按质量比10~40:1~10:1~10:1~10充分混匀,补充适量清水至生物质堆含水量为40%~70%,依次打开电源开关、搅拌开关、升温开关和空气泵,将温度迅速提升至60~100℃,温度上升至设置温度后关闭升温开关,继续发酵1~3天,发酵期间反应罐气压维持在0.1~0.15Mpa,所述发酵菌B菌剂中绵毛嗜热丝孢菌菌剂、长赤细菌菌剂、丝状菌菌剂、酵母菌菌剂的质量比优选为3:2:3:2。Further, a method for preparing medium and trace element biological fertilizer is characterized in that: the second fermentation in the three fermentations is to add pulverized fly ash and medium and trace element salt to the biomass pile after the first fermentation As well as the fermentation bacteria B bacterial agent, the above substances are fully mixed according to the mass ratio of 10~40:1~10:1~10:1~10, and an appropriate amount of water is added until the water content of the biomass pile is 40%~70%, and the power is turned on in turn Switch, stirring switch, heating switch and air pump to quickly raise the temperature to 60~100°C, turn off the heating switch after the temperature rises to the set temperature, and continue fermentation for 1~3 days. During the fermentation, the pressure of the reaction tank is maintained at 0.1~0.15Mpa, The mass ratio of Thermomyces lanuginosa inoculum, Rhodobacter inoculum, filamentous inoculum and saccharomyces inoculum in the fermenting bacteria B inoculum is preferably 3:2:3:2.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述三次发酵中第三次发酵是第二次发酵结束后,将生物质从发酵罐中倒出,堆放于发酵场中,待温度降低至40~60℃时加入功能菌菌剂,上述物质按质量比10~40:1~10充分混匀,补充适量清水至生物质堆含水量为40%~60%,在40~60℃条件下发酵3~6天,发酵期间生物质堆内温度不超过60℃,发酵结束即获得中微量元素生物有机肥。Further, a method for preparing medium and trace element biological fertilizer is characterized in that: the third fermentation in the three fermentations is after the second fermentation ends, the biomass is poured out from the fermentation tank and stacked in the fermentation field, When the temperature drops to 40~60℃, add functional bacteria agent, mix the above substances thoroughly according to the mass ratio of 10~40:1~10, add appropriate amount of water until the water content of the biomass pile is 40%~60%, at 40~ Ferment at 60°C for 3 to 6 days. During the fermentation period, the temperature in the biomass heap does not exceed 60°C. After the fermentation, the medium and trace element bio-organic fertilizer is obtained.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述第一次发酵温度优选为40℃,发酵时间优选为5天,发酵期间反应罐气压优选为0.10Mpa;所述第二次发酵中粉煤灰、中微量元素盐以及发酵菌B菌剂质量比优选为34:8:3:5,所述生物质堆含水量优选为40%,发酵温度优选为90℃,发酵时间优选为1天,反应罐气压优选为0.12Mpa,所述粉煤灰需经过筛分处理,去除烧尽的灰分,再粉碎过50~100目土壤筛,并用0.1mol/L~0.5mol/L的NaOH溶液浸泡24小时进行活化处理,所述粉煤灰与氢氧化钠溶液的质量体积比为1:1;所述第三次发酵中所述功能菌中根瘤菌菌剂、褐球固氮菌菌剂、枯草芽孢杆菌菌剂、巨大芽孢杆菌菌剂、地衣芽孢杆菌菌剂、苏云金芽孢杆菌菌剂、淡紫色拟青霉菌剂、绿色木霉菌剂质量比优选为2:1:1:1:2:1:1:1,所述生物质堆含水量优选为50%,发酵时间优选为4天。Further, a method for preparing medium and trace element biological fertilizer is characterized in that: the first fermentation temperature is preferably 40°C, the fermentation time is preferably 5 days, and the pressure of the reaction tank during fermentation is preferably 0.10Mpa; the second In the secondary fermentation, the mass ratio of fly ash, medium and trace element salts, and fermentation bacteria B bacterial agent is preferably 34:8:3:5, the water content of the biomass pile is preferably 40%, the fermentation temperature is preferably 90°C, and the fermentation time It is preferably 1 day, and the pressure of the reaction tank is preferably 0.12Mpa. The fly ash needs to be sieved to remove the burnt ash, and then crushed through a 50-100 mesh soil sieve, and mixed with 0.1mol/L-0.5mol/L Soak in NaOH solution for 24 hours and carry out activation treatment, the mass volume ratio of described fly ash and sodium hydroxide solution is 1:1; Inoculum, Bacillus subtilis inoculum, Bacillus megaterium inoculum, Bacillus licheniformis inoculum, Bacillus thuringiensis inoculum, Paecilomyces lavender inoculum, Trichoderma viride mass ratio is preferably 2:1:1:1: 2:1:1:1, the moisture content of the biomass pile is preferably 50%, and the fermentation time is preferably 4 days.

进一步,一种中微量元素生物肥的制备方法,其特征在于:所述第二次发酵中中微量元素盐是由CaCl2、MgSO4、CaO·SiO2、Fe2(SO4)3、H3BO3、MnSO4、CuSO4、ZnSO4、Na2MoO4组成的混合物,其摩尔比为0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01,所述氢氧化钠浓度优选为0.2mol/L。Further, a method for preparing medium and trace element biological fertilizer is characterized in that: the medium and trace element salt in the second fermentation is composed of CaCl 2 , MgSO 4 , CaO·SiO 2 , Fe 2 (SO 4 ) 3 , H 3 A mixture composed of BO 3 , MnSO 4 , CuSO 4 , ZnSO 4 , and Na 2 MoO 4 , the molar ratio of which is 0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01, and the concentration of sodium hydroxide is preferably 0.2mol/L.

进一步,一种中微量元素生物肥的制备方法,所述制备过程中用到的菌剂,其活菌数均为2000~3000个/g。Further, a method for preparing medium and trace element biological fertilizer, the number of viable bacteria used in the preparation process is 2000-3000/g.

本发明具有如下的有益效果:The present invention has following beneficial effect:

本发明是利用食用菌废弃菌渣、豆渣、粉煤灰、中微量元素盐、发酵菌、功能菌等物质按一定比例混合,经过多次发酵制备的生物有机肥,制备的微生物有机肥中有益菌活性高、有益菌大于3.5亿/g,各成分、基质的合理搭配使得长期放置达30个月、其含有的有益菌仍然能很好地保持了有益菌的高活性,不会出现拮抗、早衰现象,很好地发挥了固氮、解磷以及解钾菌的促进植物生长功效,通过病菌抑制菌进行生物防治,确保植物正常生长;且总养分含量高达18.1%、中微量元素含量高达7.2%,制备的中微量元素生物有机肥既可以满足植物生长所需要的大量元素,又及时补充植物生长所需要的中微量营氧元素。制备过程多种物料不会结团起块,混合均匀,本发明制得的生物肥发芽率高,幼苗长势好,发芽率高达98%。The present invention is a bio-organic fertilizer prepared by using edible fungus waste residues, bean dregs, fly ash, medium and trace element salts, fermenting bacteria, functional bacteria and other substances in a certain proportion, and is prepared through multiple fermentations. The prepared microbial organic fertilizer is beneficial The bacteria activity is high, the beneficial bacteria are more than 350 million/g, and the reasonable combination of the ingredients and the matrix makes it possible to store the beneficial bacteria for 30 months, and the beneficial bacteria contained in it can still maintain the high activity of the beneficial bacteria, and there will be no antagonism, Premature senility, which has played a good role in promoting plant growth by nitrogen-fixing, phosphorus-solubilizing and potassium-solubilizing bacteria, and biological control through pathogen-inhibiting bacteria to ensure the normal growth of plants; and the total nutrient content is as high as 18.1%, and the content of medium and trace elements is as high as 7.2%. , the prepared medium and trace element bio-organic fertilizer can not only meet the macronutrients required by plant growth, but also supplement the medium and trace oxygen elements required by plant growth in time. During the preparation process, various materials will not agglomerate and be evenly mixed. The biological fertilizer prepared by the invention has a high germination rate, and the seedlings grow well, with a germination rate as high as 98%.

具体实施方式Detailed ways

下面通过实施例对本发明进行具体的描述,有必要在此指出的是以下实施例只用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,在不背离本发明精神和实质的情况下,对本发明方法、步骤或条件所作的修改或替换,均属于本发明的范围。The present invention is specifically described below by the examples. It is necessary to point out that the following examples are only used to further illustrate the present invention, and cannot be interpreted as limiting the protection scope of the present invention. Without departing from the spirit and essence of the present invention All modifications or replacements made to the methods, steps or conditions of the present invention fall within the scope of the present invention.

实施例1Example 1

1. 将去除泥沙后的食用菌废弃菌渣、豆渣与发酵菌A菌剂按质量比为7:2:1倒入好氧堆肥实验装置中的反应罐,补充适量清水至生物质堆含水量为40%,依次打开电源开关、搅拌开关、升温开关和空气泵,并将温度设置为40℃,温度上升至设置温度后关闭升温开关,密闭继续发酵5天即完成第一次发酵,发酵期间反应罐气压维持在0.10Mpa;所述食用菌废弃菌渣是金针菇废弃菌渣;所述发酵菌A菌剂由枯草芽孢杆菌菌剂、纤维素酶、黑曲霉菌剂、白腐真菌菌剂组成,其质量比为2:4:3:1。1. Pour the discarded edible fungus dregs, bean dregs, and fermentative bacteria agent A after removing sediment into the reaction tank in the aerobic composting experimental device according to the mass ratio of 7:2:1, and add appropriate amount of water until the biomass pile contains The water volume is 40%, turn on the power switch, stirring switch, heating switch and air pump in turn, and set the temperature to 40°C, turn off the heating switch after the temperature rises to the set temperature, and continue to ferment for 5 days in an airtight environment to complete the first fermentation. During the period, the air pressure of the reaction tank was maintained at 0.10Mpa; the waste slag of the edible fungus was the waste slag of Flammulina velutipes; Composition, its mass ratio is 2:4:3:1.

2. 向第一次发酵后的生物质堆中加入粉碎后的粉煤灰、中微量元素盐以及发酵菌B菌剂,上述物质按质量比34:8:3:5充分混匀,补充适量清水至生物质堆含水量为40%,依次打开电源开关、搅拌开关、升温开关和空气泵,将温度迅速提升至90℃,温度上升至设置温度后关闭升温开关,继续发酵1天即完成第二次发酵,发酵期间反应罐气压维持在0.12Mpa,所述发酵菌B菌剂由绵毛嗜热丝孢菌菌剂、长赤细菌菌剂、丝状菌菌剂、酵母菌菌剂组成,其质量比为3:2:3:2;所述粉煤灰需经过筛分处理,去除烧尽的灰分,再粉碎过80目土壤筛,并用0.2mol/L的NaOH溶液浸泡24小时进行活化处理,所述粉煤灰与氢氧化钠溶液的质量体积比为1:1;其中微量元素盐是由CaCl2、MgSO4、CaO·SiO2、Fe2(SO4)3、H3BO3、MnSO4、CuSO4、ZnSO4、Na2MoO4组成的混合物,其摩尔比为0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01。2. Add pulverized fly ash, medium and trace element salts and fermentation bacteria B inoculum to the biomass pile after the first fermentation. The above substances are fully mixed according to the mass ratio of 34:8:3:5, and an appropriate amount is added. Clean the water until the water content of the biomass pile is 40%, turn on the power switch, stirring switch, heating switch and air pump in sequence, and quickly raise the temperature to 90°C, turn off the heating switch after the temperature rises to the set temperature, and continue fermentation for 1 day to complete the second stage During secondary fermentation, the air pressure of the reaction tank is maintained at 0.12Mpa, and the fermenting bacteria B inoculum is composed of Thermomyces lanuginosa inoculum, Rhodobacter inoculum, filamentous inoculum, and yeast inoculum. The mass ratio is 3:2:3:2; the fly ash needs to be sieved to remove the burnt ash, then crushed through an 80-mesh soil sieve, and soaked in 0.2mol/L NaOH solution for 24 hours to activate treatment, the mass volume ratio of the fly ash to the sodium hydroxide solution is 1:1; wherein the trace element salt is composed of CaCl 2 , MgSO 4 , CaO·SiO 2 , Fe 2 (SO 4 ) 3 , H 3 BO 3 , MnSO 4 , CuSO 4 , ZnSO 4 , and Na 2 MoO 4 , the molar ratio of which is 0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01.

3. 第二次发酵结束后,将生物质从发酵罐中倒出,堆放于发酵场中,待温度降低至50℃时加入功能菌菌剂,上述物质按质量比10:5充分混匀,补充适量清水至生物质堆含水量为50%,在50℃条件下发酵4天,发酵期间生物质堆内温度不超过60℃,发酵结束即获得中微量元素生物有机肥;所述功能菌菌剂由根瘤菌菌剂、褐球固氮菌菌剂、枯草芽孢杆菌菌剂、巨大芽孢杆菌菌剂、地衣芽孢杆菌菌剂、苏云金芽孢杆菌菌剂、淡紫色拟青霉菌剂、绿色木霉菌剂混合组成的复合功能菌菌剂,其质量比为2:1:1:1:2:1:1:1。3. After the second fermentation, pour out the biomass from the fermentation tank and stack it in the fermentation field. When the temperature drops to 50°C, add the functional bacterial agent. The above-mentioned substances are fully mixed according to the mass ratio of 10:5. Supplement an appropriate amount of water until the water content of the biomass pile is 50%, and ferment at 50°C for 4 days. During the fermentation period, the temperature in the biomass pile does not exceed 60°C. After the fermentation is completed, the medium and trace element bio-organic fertilizer is obtained; the functional bacteria The agent is mixed with rhizobium bacteria agent, brown nitrogen-fixing bacteria agent, Bacillus subtilis agent, Bacillus megaterium agent, Bacillus licheniformis agent, Bacillus thuringiensis agent, Paecilomyces lavender agent and Trichoderma viride agent The composition of the composite functional bacterial agent has a mass ratio of 2:1:1:1:2:1:1:1.

实验1:种子萌发及幼苗生长试验Experiment 1: Seed Germination and Seedling Growth Experiment

(1)分别向经过高温消毒的培养皿中加入500g土壤3份,分别加入50g实施例1制得的生物肥、加入50g购至河北德沃多肥料有限公司生产的德沃多生物有机肥,将土壤与生物肥充分混匀后待用;余下一份不加任何肥料,作为空白对比。(1) Add 3 parts of 500g soil to the high-temperature sterilized petri dish, respectively add 50g of the bio-fertilizer prepared in Example 1, and add 50g of Dewodo bio-organic fertilizer purchased from Hebei Dewodo Fertilizer Co., Ltd., Mix the soil and bio-fertilizer thoroughly before use; the remaining portion without any fertilizer is used as a blank comparison.

(2)挑选10颗大小均一、颗粒饱满的木耳种子均匀分布于培养皿中,将培养皿放入恒温培养箱中进行恒温培养(25℃、避光)。以不加生物肥处理为对照,每一处理均重复3次。种子临用前用1%的NaClO溶液浸泡30min,用去离子水洗净、风干后待用。(2) Select 10 fungus seeds with uniform size and full grains and distribute them evenly in the petri dish, and put the petri dish into a constant temperature incubator for constant temperature cultivation (25°C, protected from light). The treatment without bio-fertilizer was used as the control, and each treatment was repeated 3 times. The seeds were soaked in 1% NaClO solution for 30 minutes before use, washed with deionized water, and air-dried before use.

(3)待对照处理种子萌发率基本不变时停止萌发实验,记录各试验处理种子的萌发率以及相关参数;(3) Stop the germination experiment when the germination rate of the seeds of the control treatment is basically unchanged, and record the germination rate and related parameters of the seeds of each experimental treatment;

(4)分别选取各处理中萌发一致的种子于培养箱中继续培养,10d后记录幼苗株高、生物量、叶面积等,并记录幼苗生长期间的患病情况。(4) Select the seeds that germinate consistently in each treatment and continue to cultivate them in the incubator. After 10 days, record the seedling height, biomass, leaf area, etc., and record the disease status of the seedlings during their growth.

经过分析发现,利用本发明所述技术方案制备的中微量元素生物有机肥中有益菌大于3.5亿/g生物肥、总养分含量为18.1%、中微量元素含量为7.2%。利用制备的生物有机肥种植木耳菜种子(以加入河北德沃多肥料有限公司生产的德沃多生物有机肥为对照)萌发率比对照和不施肥处理分别高12.1%和19.3%,木耳菜生物量比市售生物有机肥和不施肥处理分别高25.1%、49.3%,株高比市售生物有机肥和不施肥处理分别高27.1%、53.4%,叶面积分别大22.9%、41.7%,幼苗患病率比市售生物有机肥和不施肥处理分别低12.4%和19.9%。After analysis, it is found that the beneficial bacteria in the medium-trace element bio-organic fertilizer prepared by the technical scheme of the present invention are more than 350 million/g bio-fertilizer, the total nutrient content is 18.1%, and the medium-trace element content is 7.2%. Using the prepared bio-organic fertilizer to plant Auricularia auricula seeds (with the addition of Dewoduo bio-organic fertilizer produced by Hebei Dewoduo Fertilizer Co., Ltd. as a control) the germination rate was 12.1% and 19.3% higher than that of the control and no fertilization treatment, respectively. The yield was 25.1% and 49.3% higher than the commercially available bio-organic fertilizer and no fertilization treatment, the plant height was 27.1% and 53.4% higher than the commercially available bio-organic fertilizer and no fertilization treatment, and the leaf area was 22.9% and 41.7% larger, respectively. The disease rate was 12.4% and 19.9% lower than that of commercial bio-organic fertilizer and no fertilization, respectively.

实施例2Example 2

1. 将去除泥沙后的食用菌废弃菌渣、豆渣与发酵菌A菌剂按质量比为7:2:1倒入好氧堆肥实验装置中的反应罐,补充适量清水至生物质堆含水量为38%,依次打开电源开关、搅拌开关、升温开关和空气泵,并将温度设置为30℃,温度上升至设置温度后关闭升温开关,密闭继续发酵7天即完成第一次发酵,发酵期间反应罐气压维持在0.13Mpa;所述食用菌废弃菌渣是香菇废弃菌渣;所述发酵菌A菌剂由枯草芽孢杆菌菌剂、纤维素酶、黑曲霉菌剂、白腐真菌菌剂组成,其质量比为3:5:2:2。1. Pour the discarded edible fungus dregs, bean dregs, and fermentative bacteria agent A after removing sediment into the reaction tank in the aerobic composting experimental device according to the mass ratio of 7:2:1, and add appropriate amount of water until the biomass pile contains The water volume is 38%, turn on the power switch, stirring switch, heating switch and air pump in sequence, and set the temperature to 30°C, turn off the heating switch after the temperature rises to the set temperature, and continue to ferment in an airtight environment for 7 days to complete the first fermentation. During the period, the air pressure of the reaction tank was maintained at 0.13Mpa; the waste slag of the edible fungus was the waste slag of shiitake mushrooms; Composition, its mass ratio is 3:5:2:2.

2. 向第一次发酵后的生物质堆中加入粉碎后的粉煤灰、中微量元素盐以及发酵菌B菌剂,上述物质按质量比32:7:6:2充分混匀,补充适量清水至生物质堆含水量为60%,依次打开电源开关、搅拌开关、升温开关和空气泵,将温度迅速提升至80℃,温度上升至设置温度后关闭升温开关,继续发酵3天即完成第二次发酵,发酵期间反应罐气压维持在0.15Mpa,所述发酵菌B菌剂由绵毛嗜热丝孢菌菌剂、长赤细菌菌剂、丝状菌菌剂、酵母菌菌剂组成,其质量比为5:6:2:1;所述粉煤灰需经过筛分处理,去除烧尽的灰分,再粉碎过60目土壤筛,并用0.1mol/L的NaOH溶液浸泡24小时进行活化处理,所述粉煤灰与氢氧化钠溶液的质量体积比为1:1;其中微量元素盐是由CaCl2、MgSO4、CaO·SiO2、Fe2(SO4)3、H3BO3、MnSO4、CuSO4、ZnSO4、Na2MoO4组成的混合物,其摩尔比为0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01。2. Add pulverized fly ash, medium and trace element salts, and fermentation bacteria B inoculum to the biomass pile after the first fermentation. The above substances are fully mixed according to the mass ratio of 32:7:6:2, and an appropriate amount is added. Clean the water until the water content of the biomass pile is 60%, turn on the power switch, stirring switch, heating switch and air pump in sequence, and quickly raise the temperature to 80°C, turn off the heating switch after the temperature rises to the set temperature, and continue to ferment for 3 days to complete the second stage During the secondary fermentation, the air pressure of the reaction tank is maintained at 0.15Mpa, and the fermenting bacteria B inoculum is composed of Thermomyces lanuginosa inoculum, Erythrobacter inoculum, filamentous inoculum, and saccharomyces inoculum. The mass ratio is 5:6:2:1; the fly ash needs to be sieved to remove the burnt ash, then crushed through a 60-mesh soil sieve, and soaked in 0.1mol/L NaOH solution for 24 hours to activate treatment, the mass volume ratio of the fly ash to the sodium hydroxide solution is 1:1; wherein the trace element salt is composed of CaCl 2 , MgSO 4 , CaO·SiO 2 , Fe 2 (SO 4 ) 3 , H 3 BO 3 , MnSO 4 , CuSO 4 , ZnSO 4 , and Na 2 MoO 4 , the molar ratio of which is 0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01.

3. 第二次发酵结束后,将生物质从发酵罐中倒出,堆放于发酵场中,待温度降低至50℃时加入功能菌菌剂,上述物质按质量比20:8充分混匀,补充适量清水至生物质堆含水量为40%,在40℃条件下发酵6天,发酵结束即获得中微量元素生物有机肥;所述功能菌由根瘤菌菌剂、褐球固氮菌菌剂、枯草芽孢杆菌菌剂、巨大芽孢杆菌菌剂、地衣芽孢杆菌菌剂、苏云金芽孢杆菌菌剂、淡紫色拟青霉菌剂、绿色木霉菌剂混合组成的复合功能菌菌剂,其质量比为3:5:3:2:1:2:2:1。3. After the second fermentation, pour out the biomass from the fermentation tank and stack it in the fermentation field. When the temperature drops to 50°C, add the functional bacterial agent. The above substances are fully mixed according to the mass ratio of 20:8. Supplement an appropriate amount of clear water until the water content of the biomass pile is 40%, ferment at 40°C for 6 days, and obtain medium and trace element bio-organic fertilizer after the fermentation is completed; Bacillus subtilis inoculum, Bacillus megaterium inoculum, Bacillus licheniformis inoculum, Bacillus thuringiensis inoculum, Paecilomyces lavender inoculum, Trichoderma viride inoculum mixed composite functional inoculum, its mass ratio is 3: 5:3:2:1:2:2:1.

按实施例1的实验方法进行种子萌发及幼苗生长试验,实验结果表明,利用本发明实施例2技术方案制备的中微量元素生物有机肥中有益菌大于3.5亿/g(生物肥、总养分含量为17.6%、中微量元素含量为6.7%。利用制备的生物有机肥种植木耳菜种子(以加入河北德沃多肥料有限公司生产的德沃多生物有机肥为对照)萌发率比对照和不施肥处理分别高11.5%和18.2%,木耳菜生物量比市售生物有机肥和不施肥处理分别高23.8%、47.2%,株高比市售生物有机肥和不施肥处理分别高25.8%、49.3%,叶面积分别大20.7%、39.3%,幼苗患病率比市售生物有机肥和不施肥处理分别低10.8%和17.2%。Carry out seed germination and seedling growth test by the experimental method of embodiment 1, experimental result shows, utilizes the beneficial bacteria in the microelement bio-organic fertilizer prepared by the technical scheme of embodiment 2 of the present invention to be greater than 350 million/g (biological fertilizer, total nutrient content It is 17.6%, and the microelement content is 6.7%. Utilize the prepared bio-organic fertilizer to plant Agaric agaric seeds (with adding the Dewoduo bio-organic fertilizer produced by Hebei Dewoduo Fertilizer Co., Ltd. as a control) the germination rate is higher than that of the control and no fertilization The treatments were 11.5% and 18.2% higher, the biomass of fungus was 23.8% and 47.2% higher than the commercial bio-organic fertilizer and no fertilization, and the plant height was 25.8% and 49.3% higher than the commercial bio-organic fertilizer and no fertilization. , the leaf area was 20.7% and 39.3% larger, respectively, and the disease rate of seedlings was 10.8% and 17.2% lower than the commercially available bio-organic fertilizer and no fertilization treatments, respectively.

实施例3Example 3

1. 将去除泥沙后的食用菌废弃菌渣、豆渣与发酵菌A菌剂按质量比为7:2:1倒入好氧堆肥实验装置中的反应罐,补充适量清水至生物质堆含水量为42%,依次打开电源开关、搅拌开关、升温开关和空气泵,并将温度设置为60℃,温度上升至设置温度后关闭升温开关,密闭继续发酵5天即完成第一次发酵,发酵期间反应罐气压维持在0.15Mpa;所述食用菌废弃菌渣是金针菇废弃菌渣;所述发酵菌A菌剂由枯草芽孢杆菌菌剂、纤维素酶菌剂、黑曲霉菌剂、白腐真菌菌剂组成,其质量比为5:2:1:2。1. Pour the discarded edible fungus dregs, bean dregs, and fermentative bacteria agent A after removing sediment into the reaction tank in the aerobic composting experimental device according to the mass ratio of 7:2:1, and add appropriate amount of water until the biomass pile contains The water volume is 42%, turn on the power switch, stirring switch, heating switch and air pump in sequence, and set the temperature to 60°C, turn off the heating switch after the temperature rises to the set temperature, and continue to ferment in a closed container for 5 days to complete the first fermentation. During the period, the air pressure of the reaction tank was maintained at 0.15Mpa; the waste slag of the edible fungus was the waste slag of Flammulina velutipes; Bacteria composition, its mass ratio is 5:2:1:2.

2. 向第一次发酵后的生物质堆中加入粉碎后的粉煤灰、中微量元素盐以及发酵菌B菌剂,上述物质按质量比25:7:6:2充分混匀,补充适量清水至生物质堆含水量为50%,依次打开电源开关、搅拌开关、升温开关和空气泵,将温度迅速提升至60℃,温度上升至设置温度后关闭升温开关,继续发酵2天即完成第二次发酵,发酵期间反应罐气压维持在0.13Mpa,所述发酵菌B菌剂由绵毛嗜热丝孢菌菌剂、长赤细菌菌剂、丝状菌菌剂、酵母菌菌剂组成,其质量比为5:3:2:2;所述粉煤灰需经过筛分处理,去除烧尽的灰分,再粉碎过70目土壤筛,并用0.5mol/L的NaOH溶液浸泡24小时进行活化处理,所述粉煤灰与氢氧化钠溶液的质量体积比为1:1;其中微量元素盐是由CaCl2、MgSO4、CaO·SiO2、Fe2(SO4)3、H3BO3、MnSO4、CuSO4、ZnSO4、Na2MoO4组成的混合物,其摩尔比为0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01。2. Add pulverized fly ash, medium and trace element salts and fermentation bacteria B inoculum to the biomass pile after the first fermentation. The above substances are fully mixed according to the mass ratio of 25:7:6:2, and an appropriate amount is added. Clean the water until the water content of the biomass pile is 50%, turn on the power switch, stirring switch, heating switch and air pump in sequence, and quickly raise the temperature to 60°C, turn off the heating switch after the temperature rises to the set temperature, and continue to ferment for 2 days to complete the second stage During the secondary fermentation, the air pressure of the reaction tank was maintained at 0.13Mpa, and the fermenting bacteria B inoculum was composed of Thermomyces lanuginosa inoculum, Erythrobacter inoculum, filamentous inoculum, and saccharomyces inoculum. The mass ratio is 5:3:2:2; the fly ash needs to be sieved to remove the burnt ash, then crushed through a 70-mesh soil sieve, and activated by soaking in 0.5mol/L NaOH solution for 24 hours treatment, the mass volume ratio of the fly ash to the sodium hydroxide solution is 1:1; wherein the trace element salt is composed of CaCl 2 , MgSO 4 , CaO·SiO 2 , Fe 2 (SO 4 ) 3 , H 3 BO 3 , MnSO 4 , CuSO 4 , ZnSO 4 , and Na 2 MoO 4 , the molar ratio of which is 0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01.

3. 第二次发酵结束后,将生物质从发酵罐中倒出,堆放于发酵场中,待温度降低至60℃时加入功能菌菌剂,上述物质按质量比22:8充分混匀,补充适量清水至生物质堆含水量为40%,在55℃条件下发酵4天,发酵期间生物质堆内温度不超过60℃,发酵结束即获得中微量元素生物有机肥;所述功能菌菌剂由根瘤菌菌剂、褐球固氮菌菌剂、枯草芽孢杆菌菌剂、巨大芽孢杆菌菌剂、地衣芽孢杆菌菌剂、苏云金芽孢杆菌菌剂、淡紫色拟青霉菌剂、绿色木霉菌剂混合组成的复合功能菌菌剂,其质量比为5:3:1:2:1:3:1:1。3. After the second fermentation, pour out the biomass from the fermentation tank and stack it in the fermentation field. When the temperature drops to 60°C, add the functional bacterial agent. The above-mentioned substances are fully mixed according to the mass ratio of 22:8. Add appropriate amount of clean water until the water content of the biomass pile is 40%, ferment at 55°C for 4 days, the temperature in the biomass pile does not exceed 60°C during the fermentation, and obtain medium and trace element bio-organic fertilizer at the end of the fermentation; the functional bacteria The agent is mixed with rhizobium bacteria agent, brown nitrogen-fixing bacteria agent, Bacillus subtilis agent, Bacillus megaterium agent, Bacillus licheniformis agent, Bacillus thuringiensis agent, Paecilomyces lavender agent and Trichoderma viride agent The composition of the composite functional bacterial agent has a mass ratio of 5:3:1:2:1:3:1:1.

按实施例1的实验方法进行种子萌发及幼苗生长试验,实验结果表明,利用本发明实施例2技术方案制备的中微量元素生物有机肥中有益菌大于3.5亿/g生物肥、总养分含量为17.9%、中微量元素含量为7.2%。利用制备的生物有机肥种植木耳菜种子(以加入河北德沃多肥料有限公司生产的德沃多生物有机肥为对照)萌发率比对照和不施肥处理分别高12.7%和19.6%(,木耳菜生物量比市售生物有机肥和不施肥处理分别高22.7%、48.3%,株高比市售生物有机肥和不施肥处理分别高26.7%、50.2%,叶面积分别大21.2%、40.7%,幼苗患病率比市售生物有机肥和不施肥处理分别低11.3%和18.5%。Carry out seed germination and seedling growth test by the experimental method of embodiment 1, experimental result shows, utilizes the beneficial bacteria in the microelement bio-organic fertilizer prepared by the technical scheme of embodiment 2 of the present invention to be greater than 350 million/g biological fertilizer, and the total nutrient content is 17.9%, and the content of medium and trace elements is 7.2%. Using the prepared bio-organic fertilizer to plant Auricularia auricula seeds (with the addition of Dewoduo bio-organic fertilizer produced by Hebei Dewoduo Fertilizer Co., Ltd. as a control) the germination rate was 12.7% and 19.6% higher than that of the control and no fertilization treatment respectively (Agaricus auriculae The biomass was 22.7% and 48.3% higher than the commercial bio-organic fertilizer and no fertilization treatment, the plant height was 26.7% and 50.2% higher than the commercial bio-organic fertilizer and no fertilization treatment, and the leaf area was 21.2% and 40.7% larger, respectively. The disease rate of seedlings was 11.3% and 18.5% lower than that of the commercial bio-organic fertilizer and no fertilization, respectively.

Claims (10)

1. a kind of preparation method of middle microelement bio-fertilizer, it is characterised in that:It is with waste edible fungus chaff, bean dregs, powder Coal ash, middle trace element salt, fermentation bacteria agent, function bacteria agent are raw material, are prepared respectively by fermentation three times.
2. a kind of preparation method of middle microelement bio-fertilizer as described in claim 1, it is characterised in that:The waste edible fungus Abandoning bacteria residue is preferably one of needle mushroom waste bacterial slag, mushroom waste bacterial slag.
3. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 2, it is characterised in that:The zymophyte bacterium Agent includes zymophyte A microbial inoculum and zymophyte B microbial inoculum, wherein the zymophyte A microbial inoculum is bacillus subtilis microbial agent, cellulose The composite bacteria agent that enzyme, aspergillus niger microbial inoculum, white-rot fungi microbial inoculum form, mixing mass ratio are bacillus subtilis microbial agent:Fiber Plain enzyme:Aspergillus niger microbial inoculum:White-rot fungi microbial inoculum=1 ~ 10:1~10:1~5:1 ~ 5, wherein the zymophyte B is the thermophilic silk spore of wool The compound bacteria agent that bacteria agent, long red bacterium microbial inoculum, Filamentous bacteria agent, yeast bacteria agent form, mass ratio are that wool is thermophilic Hyphomycete microbial inoculum:Long red bacterium microbial inoculum:Filamentous bacteria agent:Yeast bacteria agent=it is 1 ~ 10:1~10:1~5:1~5.
4. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 3, it is characterised in that:The function bacterium bacterium Agent is by Rhizobium Inoculant, blown-ball Azotobacter microbial inoculum, bacillus subtilis microbial agent, bacillus megaterium microbial inoculum, bacillus licheniformis The compound functional bacteria bacterium of microbial inoculum, bacillus thuringiensis microbial inoculum, paecilomyces lilacinus microbial inoculum, Trichoderma viride microbial inoculum mixing composition Agent, mass ratio are Rhizobium Inoculant:Blown-ball Azotobacter microbial inoculum:Bacillus subtilis microbial agent:Bacillus megaterium microbial inoculum:Lichens Gemma bacillus agent:Bacillus thuringiensis microbial inoculum:Paecilomyces lilacinus microbial inoculum:Trichoderma viride microbial inoculum is 1 ~ 10:1~10:1~5: 1~5:1~5:1~5:1~5:1~5.
5. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 4, it is characterised in that:The withered grass gemma Bacillus is CGMCC, number 1.12938;The aspergillus niger is CGMCC, number 3.13901;The white-rot fungi is GDMCC, is compiled Number GIM3.393;The thermophilic hyphomycete of wool is CCTCC, number CCTCC AF 200043, and the red bacterium of length is GDMCC, Number GIM1.491, the der Pilz are CGMCC, number 1.15179;The saccharomycete is GDMCC, number GIM2.210;Institute Stating rhizobium is CGMCC, number 1.15570;The blown-ball Azotobacter is GDMCC, number GIM1.272;The huge gemma bar Bacterium is CGMCC, number 1.9072;The bacillus licheniformis is CGMCC, number 1.9048;The bacillus thuringiensis is CGMCC, number 1.7902;The paecilomyces lilacinus is GDMCC, number GIM3.405;The Trichoderma viride is CGMCC, is compiled Numbers 3.11450.
6. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 5, it is characterised in that:It is described to ferment three times It is 7 that middle first time fermentation is by waste edible fungus chaff, bean dregs and the zymophyte A microbial inoculum after removal silt in mass ratio:2:1 falls Enter the reactor tank in aerobic compost experimental provision, supplement proper amount of clear water to pile of biomass water content is 38 ~ 42%, successively opens electricity Source switch, stirring switch, heating switch and air pump, and be 30 ~ 60 DEG C by temperature setting, temperature is closed after rising to setting temperature Heating switch is closed, closed to continue fermentation 3 ~ 7 days, fermentation present invention tank air pressure maintains 0.1 ~ 0.15Mpa;The zymophyte A Bacillus subtilis microbial agent in microbial inoculum, cellulase, aspergillus niger microbial inoculum, white-rot fungi microbial inoculum mass ratio be preferably 2:4:3:1.
7. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 6, it is characterised in that:It is described to ferment three times In second fermentation be that smashed flyash, middle trace element salt and hair is added in pile of biomass after fermenting to first time Yeast-like fungi B microbial inoculum, above-mentioned substance in mass ratio 10 ~ 40:1~10:1~10:1 ~ 10 mixes well, supplement proper amount of clear water to pile of biomass Water content is 40% ~ 70%, successively turns on the power switch, stirs switch, heating switch and air pump, temperature is promoted to rapidly 60 ~ 100 DEG C, temperature closes heating switch after rising to setting temperature, continues fermentation 1 ~ 3 day, and fermentation present invention tank air pressure maintains The thermophilic hyphomycete microbial inoculum of wool, long red bacterium microbial inoculum, Filamentous bacteria agent, ferment in 0.1 ~ 0.15Mpa, the zymophyte B microbial inoculum The mass ratio of female bacteria agent is preferably 3:2:3:2.
8. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 7, it is characterised in that:It is described to ferment three times The fermentation of middle third time is for the second time after fermentation, biomass to be poured out from fermentor, is stacked in fermentation field, drops to temperature Function bacteria agent, above-mentioned substance in mass ratio 10 ~ 40 are added when down to 40 ~ 60 DEG C:1 ~ 10 mixes well, and supplement proper amount of clear water is extremely Pile of biomass water content is 40% ~ 60%, is fermented 3 ~ 6 days under the conditions of 40 ~ 60 DEG C, temperature is no more than in pile of biomass during fermentation 60 DEG C, fermentation ends are microelement biological organic fertilizer in obtaining.
9. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 8, it is characterised in that:The first time hair Ferment temperature is preferably 40 DEG C, and fermentation time is preferably 5 days, and fermentation present invention tank air pressure is preferably 0.10Mpa;Described second Flyash, middle trace element salt and zymophyte B microbial inoculum mass ratio are preferably 34 in fermentation:8:3:5, the pile of biomass is aqueous Amount preferably 40%, fermentation temperature is preferably 90 DEG C, and fermentation time is preferably 1 day, and reactor tank air pressure is preferably 0.12Mpa, described Flyash need to pass through screening process, remove the ash content of burning-up, then crushed 50 ~ 100 mesh soil sieves, and with 0.1mol/L ~ The NaOH solution of 0.5mol/L, which is impregnated 24 hours, to be activated, the mass volume ratio of the flyash and sodium hydroxide solution It is 1:1;Rhizobium Inoculant in function bacterium described in third time fermentation, blown-ball Azotobacter microbial inoculum, bacillus subtilis microbial agent, Bacillus megaterium microbial inoculum, bacillus licheniformis agent, bacillus thuringiensis microbial inoculum, paecilomyces lilacinus microbial inoculum, green wood Mould agent mass ratio is preferably 2:1:1:1:2:1:1:1, the pile of biomass water content is preferably 50%, and fermentation time is preferably 4 It.
10. a kind of preparation method of middle microelement bio-fertilizer as claimed in claim 9, it is characterised in that:Described second Middle trace element salt is by CaCl in fermentation2、MgSO4、CaO·SiO2、Fe2(SO4)3、H3BO3、MnSO4、CuSO4、ZnSO4、 Na2MoO4The mixture of composition, molar ratio 0.1:0.1:0.05:0.05:0.01:0.01:0.05:0.05:0.01, it is described Naoh concentration is preferably 0.2mol/L.
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109761461A (en) * 2019-03-15 2019-05-17 重庆城市管理职业学院 A method of utilizing microbiological treatment excess sludge
CN112094160A (en) * 2019-05-28 2020-12-18 世多乐(青岛)农业科技有限公司 Biological organic fertilizer and preparation method thereof
CN112919981A (en) * 2021-04-13 2021-06-08 福建恒生态建筑工程有限公司 Process for composting branches and excrement

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103570383A (en) * 2012-07-27 2014-02-12 孙悦迎 Method utilizing waste and bacterium dreg generated during process of producing edible fungi from straw raw materials to produce microorganism organic bacterium fertilizer
CN104261911A (en) * 2014-09-22 2015-01-07 烟台中正新技术有限公司 Method for preparing organic fertilizer by using plant residues as raw material
CN104774054A (en) * 2015-04-28 2015-07-15 永州万喜登农业发展有限公司 Bio-organic fertilizer
CN104892058A (en) * 2015-05-11 2015-09-09 陕西举众科技开发有限公司 Organic fertilizer
CN105152705A (en) * 2015-08-28 2015-12-16 安徽欧杰利生态肥业有限公司 Bio-organic fertilizer based on agricultural and forestry wastes and production method of bio-organic fertilizer
CN105198528A (en) * 2015-09-23 2015-12-30 无锡市阳山镇福寿水蜜桃专业合作社 Mushroom residue organic fertilizer and preparation method thereof
CN107935769A (en) * 2017-11-24 2018-04-20 张家口根力多生态农业科技有限公司 A kind of new soil recuperation agent and preparation method thereof
CN108250002A (en) * 2018-04-14 2018-07-06 潍坊奥丰作物植保服务有限公司 A kind of complex micro organism fungicide containing Chinese herbal medicine and preparation method thereof

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103570383A (en) * 2012-07-27 2014-02-12 孙悦迎 Method utilizing waste and bacterium dreg generated during process of producing edible fungi from straw raw materials to produce microorganism organic bacterium fertilizer
CN104261911A (en) * 2014-09-22 2015-01-07 烟台中正新技术有限公司 Method for preparing organic fertilizer by using plant residues as raw material
CN104774054A (en) * 2015-04-28 2015-07-15 永州万喜登农业发展有限公司 Bio-organic fertilizer
CN104892058A (en) * 2015-05-11 2015-09-09 陕西举众科技开发有限公司 Organic fertilizer
CN105152705A (en) * 2015-08-28 2015-12-16 安徽欧杰利生态肥业有限公司 Bio-organic fertilizer based on agricultural and forestry wastes and production method of bio-organic fertilizer
CN105198528A (en) * 2015-09-23 2015-12-30 无锡市阳山镇福寿水蜜桃专业合作社 Mushroom residue organic fertilizer and preparation method thereof
CN107935769A (en) * 2017-11-24 2018-04-20 张家口根力多生态农业科技有限公司 A kind of new soil recuperation agent and preparation method thereof
CN108250002A (en) * 2018-04-14 2018-07-06 潍坊奥丰作物植保服务有限公司 A kind of complex micro organism fungicide containing Chinese herbal medicine and preparation method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
战佳宇等: "《固体废物协同处置与综合利用》", 31 December 2014, 中国建材工业出版社 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109761461A (en) * 2019-03-15 2019-05-17 重庆城市管理职业学院 A method of utilizing microbiological treatment excess sludge
CN109761461B (en) * 2019-03-15 2022-06-07 重庆城市管理职业学院 Method for treating excess sludge by using microorganisms
CN112094160A (en) * 2019-05-28 2020-12-18 世多乐(青岛)农业科技有限公司 Biological organic fertilizer and preparation method thereof
CN112919981A (en) * 2021-04-13 2021-06-08 福建恒生态建筑工程有限公司 Process for composting branches and excrement

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