CN115677398B - Solid-state fermentation composite fish offal and tobacco waste organic fertilizer and production method and application thereof - Google Patents
Solid-state fermentation composite fish offal and tobacco waste organic fertilizer and production method and application thereof Download PDFInfo
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Abstract
本发明提供了一种固态发酵复合鱼下脚料和烟草废弃物有机肥及生产方法和应用,本发明利用微生物发酵技术,以低廉的复合鱼下脚料和烟草废弃物为发酵底物,混入无机盐和无机氮源,制成固体发酵培养基,向其接种枯草芽孢杆菌、红酵母和米根霉的复合菌剂进行固态发酵后可获得发酵有机肥,成本低、制备方法简便,具有增加蔬菜产量提高品质及增加土壤养分等功能。
The invention provides a solid-state fermentation composite fish scraps and tobacco waste organic fertilizer and a production method and application thereof. The invention utilizes microbial fermentation technology, takes cheap composite fish scraps and tobacco waste as fermentation substrates, mixes inorganic salts and inorganic nitrogen sources to prepare solid fermentation medium, and inoculates composite bacterial agents of Bacillus subtilis, red yeast and Rhizopus oryzae to obtain fermented organic fertilizer after solid-state fermentation. The invention has low cost and simple preparation method, and has the functions of increasing vegetable yield, improving quality, increasing soil nutrients and the like.
Description
技术领域Technical Field
本发明属于肥料领域,具体涉及一种固态发酵复合鱼下脚料和烟草废弃物有机肥及生产方法和应用。The invention belongs to the field of fertilizers, and in particular relates to a solid-state fermented composite fish scraps and tobacco waste organic fertilizer and a production method and application thereof.
背景技术Background Art
在农业生产中,有机肥在农业市场广受青睐,国内外施用的有机肥多以有机废弃物为源制备富含有机质的高效肥。在水产品加工过程中,未被利用的鱼类副产物占40-55%,包括鱼头、鱼骨、鱼尾、鱼皮、鱼内脏等。鱼下脚料中含有大量的优质蛋白及多种活性物质,目前,鱼下脚料主要用于制备生物活性肽、加工动物饲料、鱼蛋白肥料、用于氮源培养基等。In agricultural production, organic fertilizers are widely favored in the agricultural market. Most of the organic fertilizers used at home and abroad are high-efficiency fertilizers rich in organic matter prepared from organic waste. In the process of aquatic product processing, 40-55% of fish by-products are not used, including fish heads, fish bones, fish tails, fish skins, fish viscera, etc. Fish waste contains a large amount of high-quality protein and a variety of active substances. At present, fish waste is mainly used to prepare bioactive peptides, process animal feed, fish protein fertilizer, and nitrogen source culture medium.
随着我国对绿色农业发展的重视,开发其它农业有机废物转化有机高效土壤肥料成为了现代农业可持续发展的新途径。因此,水产品下脚料资源的转化逐渐成为热点,丰富的低值鱼类资源及水产品加工下脚料等可成为重要的绿色生态有机肥源,能增加水产品加工业的附加值和避免环境污染。As my country attaches great importance to the development of green agriculture, the development of other agricultural organic wastes to transform organic high-efficiency soil fertilizers has become a new way for the sustainable development of modern agriculture. Therefore, the transformation of aquatic product waste resources has gradually become a hot topic. Abundant low-value fish resources and aquatic product processing waste can become an important source of green ecological organic fertilizers, which can increase the added value of the aquatic product processing industry and avoid environmental pollution.
鱼蛋白肥料作为一种功能型肥料,受到种植者的关注。该肥料因含有小分子多肽、氨基酸、牛磺酸、维生素等多种活性物质及丰富的钙、镁等中微量元素。鱼废物可以加工成稳定的液体或固体形式的肥料,并与其他材料结合生产鱼堆肥或作为厌氧消化的基质,具有改善土壤微生物活性和土壤结构以及刺激根系生长来改善土壤的潜力。As a functional fertilizer, fish protein fertilizer has attracted the attention of growers. This fertilizer contains a variety of active substances such as small molecule peptides, amino acids, taurine, vitamins, and rich trace elements such as calcium and magnesium. Fish waste can be processed into stable liquid or solid fertilizers and combined with other materials to produce fish compost or as a substrate for anaerobic digestion. It has the potential to improve soil by improving soil microbial activity and soil structure and stimulating root growth.
烟草废弃物中含有大量植物易于吸收的钾、磷等营养元素,是制备育苗基质的绿色、成本低廉的资源,也可用于制作活性炭、有机肥料及鸡饲料。而烟草废弃物中有烟碱存在,直接还田处理会导致植物生长指标降低,还会造成环境污染,利用微生物发酵技术处理烟草废弃物可减少废弃物中有害成分,同时有利于土壤结构的改良和养分的补充。Tobacco waste contains a large amount of nutrients such as potassium and phosphorus that are easily absorbed by plants. It is a green and low-cost resource for preparing seedling substrates. It can also be used to make activated carbon, organic fertilizers and chicken feed. Nicotine exists in tobacco waste. Directly returning it to the field will lead to reduced plant growth indicators and cause environmental pollution. Using microbial fermentation technology to treat tobacco waste can reduce harmful components in the waste, and at the same time is conducive to the improvement of soil structure and the supplement of nutrients.
鱼类下脚料含有丰富的营养物质如矿物质、脂肪、蛋白质等,目前关于鱼类下脚料利用多集中在制备液体鱼蛋白肥料农业,鱼类下脚料与植物废弃秸秆为发酵底物的研究较少。Fish waste contains rich nutrients such as minerals, fats, proteins, etc. Currently, the utilization of fish waste is mainly focused on the preparation of liquid fish protein fertilizer in agriculture, and there is less research on fish waste and plant waste straw as fermentation substrates.
发明内容Summary of the invention
本发明的目的在于提供一种固态发酵复合鱼下脚料和烟草废弃物有机肥及生产方法,利用鱼下脚料和烟草废弃物,经过微生物发酵后,废弃物中蛋白质、脂质和纤维素等大分子被分解,进而转化成植物可直接吸收利用的营养物质。The purpose of the present invention is to provide a solid-state fermentation composite fish scraps and tobacco waste organic fertilizer and a production method, which utilizes fish scraps and tobacco waste. After microbial fermentation, macromolecules such as protein, lipid and cellulose in the waste are decomposed and then converted into nutrients that can be directly absorbed and utilized by plants.
本发明还有一个目的在于提供一种固态发酵复合鱼下脚料和烟草废弃物有机肥的应用,用于农作物肥料,直接作为基肥施用。本发明制备的发酵有机肥能促进作物生长,提高土壤养分,为有机废弃物的高值化利用提供新的方向,使之用于农业中农作物的有机肥料。Another object of the present invention is to provide an application of solid-state fermented composite fish waste and tobacco waste organic fertilizer for crop fertilizer, which is directly applied as base fertilizer. The fermented organic fertilizer prepared by the present invention can promote crop growth, improve soil nutrients, and provide a new direction for the high-value utilization of organic waste, so that it can be used as an organic fertilizer for crops in agriculture.
本发明具体技术方案如下:The specific technical solutions of the present invention are as follows:
一种固态发酵复合鱼下脚料和烟草废弃物有机肥的生产方法,为:利用鱼下脚料和烟草废弃物混合为发酵基质,混入无机盐和无机氮源,高温灭菌后,接种混合菌剂,进行固态发酵,制成的固态有机肥。A method for producing solid-state fermentation composite fish scraps and tobacco waste organic fertilizer comprises: mixing fish scraps and tobacco waste as a fermentation matrix, mixing in inorganic salts and inorganic nitrogen sources, sterilizing at high temperature, inoculating a mixed bacterial agent, and performing solid-state fermentation to produce solid organic fertilizer.
所述鱼下脚料为:鱼头、鱼内脏、鱼鳍、鱼尾、鱼骨或其残留鱼肉混合物,经121℃高温灭菌、组织搅碎机搅碎、50℃干燥处理,即得;所述鱼下脚料为鲫鱼、草鱼或鲢鱼的鱼下脚料。The fish scraps are: fish heads, fish viscera, fish fins, fish tails, fish bones or a mixture of residual fish meat thereof, which are sterilized at 121° C., crushed by a tissue grinder, and dried at 50° C.; the fish scraps are fish scraps of crucian carp, grass carp or silver carp.
所述烟草废弃物为卷烟厂废弃的烟叶、烟梗任意一种或两种的混合物,50℃烘箱干燥后粉碎至颗粒状。The tobacco waste is any one or a mixture of tobacco leaves and tobacco stems discarded from cigarette factories, which are dried in an oven at 50° C. and then crushed into particles.
所述烟草废弃物质量为鱼下脚料和烟草废弃物总质量的5-40%;优选的烟草废弃物质量为鱼下脚料和烟草废弃物总质量的30%;The mass of the tobacco waste is 5-40% of the total mass of the fish scraps and the tobacco waste; preferably, the mass of the tobacco waste is 30% of the total mass of the fish scraps and the tobacco waste;
所述无机盐用量为鱼下脚料和烟草废弃物总质量的0.5-1.5%,优选为0.5%;The amount of the inorganic salt is 0.5-1.5% of the total mass of the fish scraps and tobacco waste, preferably 0.5%;
所述无机盐选自磷酸氢二钾K2HPO4、磷酸二氢钾KH2PO4或氯化钠NaCl;优选的为氯化钠NaCl;The inorganic salt is selected from potassium dihydrogen phosphate (K 2 HPO 4 ) , potassium dihydrogen phosphate (KH 2 PO 4) or sodium chloride (NaCl); preferably sodium chloride (NaCl);
所述无机氮源用量为鱼下脚料和烟草废弃物总质量的0.5-2.0%,优选为1.0%;The amount of the inorganic nitrogen source is 0.5-2.0% of the total mass of the fish scraps and tobacco waste, preferably 1.0%;
所述无机氮源选自硝酸铵NH4NO3或硝酸钠NaNO3;优选的为硝酸铵NH4NO3;The inorganic nitrogen source is selected from ammonium nitrate NH 4 NO 3 or sodium nitrate NaNO 3 ; preferably ammonium nitrate NH 4 NO 3 ;
所述混合菌剂接菌量以鱼下脚料和烟草废弃物总质量计,为1×1010 -5×1010CFU/g;优选为4×1010CFU/g;The inoculation amount of the mixed bacterial agent is 1×10 10 -5×10 10 CFU/g, preferably 4×10 10 CFU/g, based on the total mass of fish scraps and tobacco waste.
所述混合菌剂为枯草芽孢杆菌、红酵母和米根霉的混合菌;枯草芽孢杆菌、红酵母和米根霉的菌株活菌总数比例为2:1:3;The mixed bacterial agent is a mixed bacteria of Bacillus subtilis, red yeast and Rhizopus oryzae; the total number of live bacteria of the strains of Bacillus subtilis, red yeast and Rhizopus oryzae is 2:1:3;
所述固态发酵,发酵温度为30℃-36℃;发酵时间为20天;优选34℃;The solid-state fermentation temperature is 30°C-36°C and the fermentation time is 20 days, preferably 34°C;
本发明提供的一种固态发酵复合鱼下脚料和烟草废弃物有机肥,采用上述方法制备得到。The invention provides a solid-state fermentation composite fish scraps and tobacco waste organic fertilizer, which is prepared by adopting the above method.
本发明提供的一种固态发酵复合鱼下脚料和烟草废弃物有机肥的应用,用于农作物肥料。The invention provides an application of solid-state fermented composite fish scraps and tobacco waste organic fertilizer for use as crop fertilizer.
所述固态发酵复合鱼下脚料和烟草废弃物有机肥的应用方法为:将固态发酵复合鱼下脚料和烟草废弃物有机肥和土壤混合,混合比例为10-30g/kg土壤。The application method of the solid-state fermentation composite fish scraps and tobacco waste organic fertilizer is as follows: the solid-state fermentation composite fish scraps and tobacco waste organic fertilizer are mixed with soil at a mixing ratio of 10-30 g/kg soil.
所述固态发酵复合鱼下脚料和烟草废弃物有机肥尤其适用于作为上海青和辣椒的肥料,能促进其生长,提高叶绿素含量。The solid-state fermentation composite fish scraps and tobacco waste organic fertilizer is particularly suitable for being used as a fertilizer for Shanghai greens and peppers, and can promote their growth and increase the chlorophyll content.
所述固态发酵复合鱼下脚料和烟草废弃物有机肥能提高土壤的铵态氮、有效磷、速效钾含量,土壤的铵态氮含量提高到55-360mg/kg,有效磷含量提高到82-190mg/kg、速效钾含量提高到36-105mg/kg;提高土壤中的脲酶活性3.0-3.6mg/g、蔗糖酶活性1.5mg/g-1.9mg/g、过氧化氢酶活性3.5(U/h·g)-4.00(U/h·g)。The solid-state fermentation composite fish scraps and tobacco waste organic fertilizer can increase the ammonium nitrogen, available phosphorus and quick-acting potassium contents of the soil, wherein the ammonium nitrogen content of the soil is increased to 55-360 mg/kg, the available phosphorus content is increased to 82-190 mg/kg, and the quick-acting potassium content is increased to 36-105 mg/kg; and the urease activity in the soil is increased by 3.0-3.6 mg/g, the sucrase activity is increased by 1.5 mg/g-1.9 mg/g, and the catalase activity is increased by 3.5 (U/h·g)-4.00 (U/h·g).
本发明制备的生物有机肥对改良土壤,对农作物培育壮苗具有良好效果。The biological organic fertilizer prepared by the invention has good effects on improving soil and cultivating strong seedlings of crops.
本发明利用微生物发酵技术,以低廉的复合鱼下脚料和烟草废弃物为发酵底物,混入无机盐和无机氮源,制成固体发酵培养基,向其接种枯草芽孢杆菌、红酵母和米根霉的复合菌剂进行固态发酵后可获得发酵有机肥,成本低、制备方法简便,具有增加蔬菜产量提高品质及增加土壤养分等功能。The present invention utilizes microbial fermentation technology, takes cheap composite fish scraps and tobacco waste as fermentation substrates, mixes inorganic salts and inorganic nitrogen sources to prepare solid fermentation medium, and inoculates composite bacterial agents of Bacillus subtilis, red yeast and Rhizopus oryzae to obtain fermented organic fertilizer after solid-state fermentation. The invention has low cost and simple preparation method, and has the functions of increasing vegetable yield, improving quality, increasing soil nutrients and the like.
本发明采用的枯草芽孢杆菌、红酵母和米根霉混合菌株发酵存在协调互作优势:在发酵试验中,酵母菌和米根霉同步糖化发酵,米根霉可产生纤维素酶,利用发酵基质中的纤维素、淀粉等生成糖,而红酵母则利用糖进行生长代谢,减轻了产物抑制效应,又促进了酵母的生长,提高了发酵率。枯草芽孢杆菌可产生多种生物活性物质,如消化酶、维生素、有机酸、小肽和促生长因子等。因此,利用菌种的协同作用提高对底物的利用效率,优于单菌种发酵。且,本发明采用有机废弃物固态发酵法制成有机肥,使用的鱼下脚料中富含蛋白、脂质等营养物质,烟草废弃物中含有大量植物易于吸收的钾、磷等营养元素,是绿色、成本低廉的肥料资源,且易于获取,同时可增加水产品加工业的附加值和避免环境污染。利用混合微生物以固态条件发酵鱼下脚料和烟草废弃物,添加0.5%氯化钠和1%硝酸铵,以混合菌株枯草芽孢杆菌、红酵母、米根霉为发酵菌剂,在固态发酵的条件为烟草废弃物添加量30%、接菌量4×1010CFU/g、发酵温度34℃,经发酵周期20天后可获得有机肥,发酵方法操作简单。The mixed strain fermentation of Bacillus subtilis, red yeast and Rhizopus oryzae adopted in the present invention has the advantage of coordinated interaction: in the fermentation test, yeast and Rhizopus oryzae are saccharified and fermented synchronously, Rhizopus oryzae can produce cellulase, and utilize cellulose, starch and the like in the fermentation matrix to generate sugar, while red yeast utilizes sugar for growth metabolism, which reduces the product inhibition effect, promotes the growth of yeast, and improves the fermentation rate. Bacillus subtilis can produce a variety of biologically active substances, such as digestive enzymes, vitamins, organic acids, small peptides and growth-promoting factors. Therefore, the synergistic effect of strains is used to improve the utilization efficiency of substrates, which is better than single strain fermentation. Moreover, the present invention adopts the solid-state fermentation method of organic waste to make organic fertilizer, and the fish scraps used are rich in nutrients such as protein and lipids, and the tobacco waste contains a large amount of nutrients such as potassium and phosphorus that are easily absorbed by plants. It is a green, low-cost fertilizer resource, and it is easy to obtain, and it can increase the added value of the aquatic product processing industry and avoid environmental pollution. Fish scraps and tobacco waste were fermented under solid conditions using mixed microorganisms, 0.5% sodium chloride and 1% ammonium nitrate were added, mixed strains of Bacillus subtilis, red yeast and Rhizopus oryzae were used as fermentation agents, and the solid fermentation conditions were 30% tobacco waste addition, 4×10 10 CFU/g inoculation amount and 34°C fermentation temperature. Organic fertilizer could be obtained after a fermentation period of 20 days, and the fermentation method was simple to operate.
经过本发明方法固态发酵有机肥的肥效高,发酵有机肥作为基肥施用时,施加基肥为20g/kg时,青菜和辣椒的苗高分别为4.5cm和5.3cm,增加了95.65%和32.5%;其鲜重比不施加发酵肥的对照组的鲜重分别增加0.129g和0.1627g,干重增加0.006g和0.0042g。青菜与辣椒的叶绿素含量分别为17.124mg/g和16.278mg/g,与对照组相比提高了18.53%和195.4%,存在显著差异。发酵有机肥作为基肥施用后,土壤中铵态氮含量为355mg/kg、有效磷172.33mg/kg、速效钾36.63mg/kg,与对照组相比显著提高。此外,土壤中脲酶、过氧化氢酶和蔗糖酶的酶活性也有所提高,而土壤酶活性是评价土壤理化性质和肥力状况的重要指标,可间接地反应出土壤中某些营养物质的转化情况,可见发酵有机肥能增加土壤养分,为植物提供营养物质。The solid-state fermented organic fertilizer of the present invention has high fertilizer efficiency. When the fermented organic fertilizer is applied as base fertilizer, when the base fertilizer is 20g/kg, the seedling height of green vegetables and peppers is 4.5cm and 5.3cm respectively, which increases by 95.65% and 32.5%; the fresh weight is increased by 0.129g and 0.1627g respectively, and the dry weight is increased by 0.006g and 0.0042g compared with the fresh weight of the control group without applying fermented fertilizer. The chlorophyll content of green vegetables and peppers is 17.124mg/g and 16.278mg/g respectively, which is 18.53% and 195.4% higher than that of the control group, and there is a significant difference. After the fermented organic fertilizer is applied as base fertilizer, the ammonium nitrogen content in the soil is 355mg/kg, the effective phosphorus is 172.33mg/kg, and the quick-acting potassium is 36.63mg/kg, which is significantly higher than that of the control group. In addition, the enzyme activities of urease, catalase and sucrase in the soil also increased. Soil enzyme activity is an important indicator for evaluating the physical and chemical properties and fertility of the soil, and can indirectly reflect the conversion of certain nutrients in the soil. It can be seen that fermented organic fertilizer can increase soil nutrients and provide nutrients for plants.
与现有技术相比,本发明以混合鱼下脚料和烟草废弃物为主要原料,利用微生物固态发酵制成供植物生长所需的有机肥料,为水产和烟草工业的废弃物处理带来新的方法,解决废弃物造成环境压力的问题。Compared with the prior art, the present invention uses mixed fish scraps and tobacco waste as main raw materials, and utilizes microbial solid fermentation to produce organic fertilizer required for plant growth, thus providing a new method for waste treatment in the aquatic and tobacco industries and solving the problem of environmental pressure caused by waste.
附图说明BRIEF DESCRIPTION OF THE DRAWINGS
图1为蛋白酶活检测平板;Fig. 1 is a protease activity detection plate;
图2为脂酶酶活检测平板;Fig. 2 is a lipase activity detection plate;
图3为纤维素酶活检测平板;Fig. 3 is a cellulase activity detection plate;
图4为不同无机氮源、无机盐对活菌总数的影响;a为不同无机氮源对活菌总数的影响;b为不同无机盐对活菌总数的影响;Figure 4 shows the effects of different inorganic nitrogen sources and inorganic salts on the total number of viable bacteria; a shows the effects of different inorganic nitrogen sources on the total number of viable bacteria; b shows the effects of different inorganic salts on the total number of viable bacteria;
图5为氯化钠和硝酸铵的含量对活菌总数的影响;Figure 5 shows the effect of sodium chloride and ammonium nitrate content on the total number of viable bacteria;
图6为不同发酵条件对发酵底物的影响;FIG6 shows the effect of different fermentation conditions on the fermentation substrate;
图7为发酵过程中有机质、有效磷、速效钾、纤维素含量变化趋势;a为有机质含量,b为有效磷含量、c为速效钾含量,d为纤维素含量;Figure 7 shows the changing trends of organic matter, available phosphorus, available potassium, and cellulose content during the fermentation process; a is the organic matter content, b is the available phosphorus content, c is the available potassium content, and d is the cellulose content;
图8为发酵肥对青菜生长的影响;Figure 8 shows the effect of fermented fertilizer on the growth of green vegetables;
图9为发酵肥对辣椒生长的影响;Figure 9 shows the effect of fermented fertilizer on pepper growth;
图10为发酵肥对蔬菜叶绿素含量的影响;Figure 10 shows the effect of fermented fertilizer on chlorophyll content of vegetables;
图11为发酵肥对土壤脲酶活性的影响;Figure 11 shows the effect of fermented fertilizer on soil urease activity;
图12为发酵肥对土壤蔗糖酶活性的影响;FIG12 shows the effect of fermented fertilizer on soil sucrase activity;
图13为发酵肥对土壤过氧化氢酶活性的影响。Figure 13 shows the effect of fermented fertilizer on soil catalase activity.
具体实施方式DETAILED DESCRIPTION
下面结合以下实施例对本发明进一步说明。The present invention is further described below in conjunction with the following examples.
实施例1Example 1
一种固态发酵复合鱼下脚料和烟草废弃物有机肥的生产方法,为:利用鱼下脚料和烟草废弃物混合为发酵基质,混入无机盐和无机氮源,高温灭菌后,接种混合菌剂,进行固态发酵,制成的固态有机肥。A method for producing solid-state fermentation composite fish scraps and tobacco waste organic fertilizer comprises: mixing fish scraps and tobacco waste as a fermentation matrix, mixing in inorganic salts and inorganic nitrogen sources, sterilizing at high temperature, inoculating a mixed bacterial agent, and performing solid-state fermentation to produce solid organic fertilizer.
所述鱼下脚料为:鱼头、鱼内脏、鱼鳍、鱼尾、鱼骨或其残留鱼肉混合物,经高温灭菌、搅碎、干燥处理,即得;所述鱼下脚料为鲫鱼、草鱼或鲢鱼的鱼下脚料。所述烟草废弃物为卷烟厂废弃的烟叶或烟梗任意一种或两种的混合物,50℃烘箱干燥后粉碎至颗粒状。实施例1所用的鱼下脚料和烟草废弃物基本理化性质见表1。The fish scraps are fish heads, fish viscera, fish fins, fish tails, fish bones or a mixture of residual fish meat thereof, which are sterilized at high temperature, crushed and dried; the fish scraps are fish scraps of crucian carp, grass carp or silver carp. The tobacco waste is a mixture of any one or both of tobacco leaves or tobacco stems discarded from a cigarette factory, which are dried in an oven at 50°C and crushed into granules. The basic physical and chemical properties of the fish scraps and tobacco waste used in Example 1 are shown in Table 1.
表1鱼下脚料和烟草废弃物基本理化性质Table 1 Basic physical and chemical properties of fish scraps and tobacco waste
所述烟草废弃物质量为鱼下脚料和烟草废弃物总质量的30%;所述无机盐选自氯化钠NaCl;所述无机氮源选自硝酸铵NH4NO3;所述无机盐用量为鱼下脚料和烟草废弃物总质量的0.5%;所述无机氮源用量为鱼下脚料和烟草废弃物总质量的1.0%;所述混合菌剂接菌4.0×1010CFU/g;所述混合菌剂为枯草芽孢杆菌、红酵母和米根霉的混合菌;枯草芽孢杆菌、红酵母和米根霉的菌株比例为2:1:3;所述固态发酵,发酵温度为34℃,进行20天发酵。The mass of the tobacco waste is 30% of the total mass of the fish scraps and the tobacco waste; the inorganic salt is selected from sodium chloride NaCl; the inorganic nitrogen source is selected from ammonium nitrate NH4NO3 ; the amount of the inorganic salt is 0.5% of the total mass of the fish scraps and the tobacco waste; the amount of the inorganic nitrogen source is 1.0% of the total mass of the fish scraps and the tobacco waste; the mixed bacterial agent is inoculated with 4.0× 1010 CFU/g; the mixed bacterial agent is a mixed bacteria of Bacillus subtilis, red yeast and Rhizopus oryzae; the strain ratio of Bacillus subtilis, red yeast and Rhizopus oryzae is 2:1:3; the solid-state fermentation is performed at a fermentation temperature of 34°C for 20 days.
实施例2Example 2
对枯草芽孢杆菌、红酵母和米根霉的菌株的活化及酶活检测,具体如下:The activation and enzyme activity detection of Bacillus subtilis, red yeast and Rhizopus oryzae strains are as follows:
发酵菌株的活化:Activation of fermentation strains:
枯草芽孢杆菌Bacillus subtilis、红酵母Rhodotorula taiwanensis、米根霉Rhizopus oryzae为市售菌株,菌株在LB或PDA固体培养基上划线培养,挑取单菌落接种液体培养基中,培养24h后,作为发酵液。Bacillus subtilis, Rhodotorula taiwanensis, and Rhizopus oryzae are commercially available strains. The strains are streaked on LB or PDA solid medium, and a single colony is picked and inoculated into a liquid medium. After culturing for 24 hours, the resultant is used as a fermentation broth.
发酵菌株的酶活性检测:Enzyme activity detection of fermentation strains:
酶活性测定采用水解圈检测方法,在蛋白酶、酯酶和纤维素酶酶活检测培养基上打孔(直径1cm),分别接入200μl上述发酵液到平板孔中,每种菌株重复3皿,红酵母和米根霉在28℃,枯草芽孢杆菌在35℃培养。培养5d后,纤维素培养基用1mg/mL的刚果红染色1h,倒掉染液后,1mol/L NaCl溶液浸泡1h,观察有无透明圈产生。结果如图1-图3所示。The enzyme activity was determined by the hydrolysis circle detection method. A hole (1 cm in diameter) was punched on the protease, esterase and cellulase enzyme activity detection medium, and 200 μl of the above fermentation liquid was respectively inoculated into the plate well. Each strain was repeated 3 times. Red yeast and Rhizopus oryzae were cultured at 28°C, and Bacillus subtilis was cultured at 35°C. After 5 days of culture, the cellulose culture medium was stained with 1 mg/mL Congo red for 1 hour. After the stain was poured out, it was immersed in 1 mol/L NaCl solution for 1 hour to observe whether a transparent circle was generated. The results are shown in Figures 1 to 3.
由图1、2和3所示,平板上有明显的水解圈,菌株枯草芽孢杆菌和米根霉有产蛋白酶、酯酶和纤维素酶的能力,红酵母具有产蛋白酶和酯酶的能力。也进一步说明了本发明采用枯草芽孢杆菌、红酵母和米根霉,能够发酵鱼下脚料和烟草废弃物。As shown in Figures 1, 2 and 3, there are obvious hydrolysis circles on the plate, and the strains Bacillus subtilis and Rhizopus oryzae have the ability to produce protease, esterase and cellulase, and red yeast has the ability to produce protease and esterase. It also further illustrates that the present invention uses Bacillus subtilis, red yeast and Rhizopus oryzae to ferment fish scraps and tobacco waste.
实施例3Example 3
按照实施例1的方法,改变培养基、无机氮源、无机盐的添加量和原料选择、调整烟草废弃物用量比、混合菌剂中枯草芽孢杆菌、红酵母和米根霉的菌株比例、接菌量、发酵温度等,对比发酵结果,具体如下:According to the method of Example 1, the addition amount of culture medium, inorganic nitrogen source, inorganic salt and raw material selection were changed, the usage ratio of tobacco waste, the strain ratio of Bacillus subtilis, red yeast and Rhizopus oryzae in the mixed inoculum, the inoculation amount, the fermentation temperature, etc. were adjusted, and the fermentation results were compared, as follows:
1)发酵基质作为培养基对菌株数量的变化1) Changes in the number of strains using fermentation substrate as culture medium
在实施例2发酵液的基础上,在LB、PDA和以鱼下脚料和烟草组成的混合发酵基质的液体培养基中分别接入5%的单菌发酵液和混合菌液(枯草芽孢杆菌:红酵母:米根霉的比例1:1:1),培养2天后,采用稀释涂布平板法计算微生物总数。Based on the fermentation broth of Example 2, 5% of single-bacteria fermentation broth and mixed bacterial broth (Bacillus subtilis: red yeast: Rhizopus oryzae ratio of 1:1:1) were inoculated into LB, PDA and liquid culture medium of mixed fermentation matrix composed of fish scraps and tobacco, respectively. After culturing for 2 days, the total number of microorganisms was calculated by the dilution spread plate method.
表2不同培养基中菌种的数量变化Table 2 Changes in the number of bacterial species in different culture media
表2中,细菌是枯草芽孢杆菌,真菌是红酵母和米根霉。In Table 2, the bacteria is Bacillus subtilis, and the fungi are Rhodotorula yeast and Rhizopus oryzae.
2)发酵基质优化2) Fermentation matrix optimization
在实施例1发酵基质的基础上,分别添加含氮量相同的无机氮源((NH4)2SO4、NH4NO3、NH4Cl、和NaNO3)与无机盐(K2HPO4、KH2PO4、MgSO4和NaCl),枯草芽孢杆菌、红酵母、米根霉的比例为1:1:1接种混合菌株;接菌量4×1010CFU/g,34℃发酵3d,采用平板计数法计算微生物总数,设置添加量为0、0.5%、1%、1.5%、2%,结果如图4、图5所示,在相同的成分和条件下,以硝酸铵为无机氮源、氯化钠为无机盐离子,活菌总数分别为3.3×108CFU/mL、2.21×108CFU/mL,并改变其浓度探究对菌种生长的影响,随着氯化钠含量的增加,活菌数的数量呈下降趋势;而活菌总数随着硝酸铵含量的增加而増加,在1%含量时,活菌总数最大为4.2×108CFU/mL,当大于1%时,活菌总数开始下降,因此在发酵基质中添加0.5%氯化钠和1%硝酸铵。进一步证明最适合菌种生长的无机氮源和无机盐为NH4NO3和NaCl,本发明选择的NH4NO3和NaCl最优。On the basis of the fermentation substrate of Example 1, inorganic nitrogen sources ((NH4) 2SO4 , NH4NO3 , NH4Cl , and NaNO3 ) and inorganic salts ( K2HPO4 , KH2PO4 , MgSO4 , and NaCl ) with the same nitrogen content were added respectively, and the ratio of Bacillus subtilis, red yeast, and Rhizopus oryzae was 1:1:1 for inoculation of mixed strains; the inoculation amount was 4× 1010 CFU/g, and the fermentation was carried out at 34°C for 3 days. The total number of microorganisms was calculated by the plate count method, and the addition amount was set to 0, 0.5%, 1%, 1.5%, and 2%. The results are shown in Figures 4 and 5. Under the same composition and conditions, with ammonium nitrate as the inorganic nitrogen source and sodium chloride as the inorganic salt ion, the total number of viable bacteria was 3.3×108 CFU/mL, 2.21× 108 CFU/mL, and 1.67× 108 CFU/mL, respectively. CFU/mL, and changing its concentration to explore the effect on bacterial growth, with the increase of sodium chloride content, the number of viable bacteria showed a downward trend; while the total number of viable bacteria increased with the increase of ammonium nitrate content, at 1%, the maximum total number of viable bacteria was 4.2×10 8 CFU/mL, when it was greater than 1%, the total number of viable bacteria began to decrease, so 0.5% sodium chloride and 1% ammonium nitrate were added to the fermentation matrix. It is further proved that the most suitable inorganic nitrogen source and inorganic salt for bacterial growth are NH 4 NO 3 and NaCl, and the NH 4 NO 3 and NaCl selected by the present invention are the best.
3)烟草添加量对发酵效果的影响3) Effect of tobacco addition on fermentation effect
称取发酵底物为20g,将烟草的添加量设为(5%、10%、20%、30%、40%)。置于50ml三角瓶中,灭菌后接入混合菌剂,接菌量4×1010CFU/g,枯草芽孢杆菌、红酵母、米根霉的比例为2:1:3,34℃培养3d。Weigh 20g of fermentation substrate, set the amount of tobacco added to (5%, 10%, 20%, 30%, 40%), place in a 50ml conical flask, sterilize, inoculate with mixed bacterial agent, inoculate amount 4×10 10 CFU/g, the ratio of Bacillus subtilis, red yeast, and Rhizopus oryzae is 2:1:3, and culture at 34℃ for 3 days.
4)接菌量对发酵效果影响4) Effect of inoculation amount on fermentation effect
称取发酵底物20g,烟草含量在30%,置于50ml三角瓶中。灭菌后接种菌株枯草芽孢杆菌、红酵母、米根霉的比例为2:1:3,终浓度为1、2、3、4、5×1010CFU/g,34℃培养3d。Weigh 20g of fermentation substrate with a tobacco content of 30% and place it in a 50ml Erlenmeyer flask. After sterilization, inoculate the strains of Bacillus subtilis, red yeast, and Rhizopus oryzae in a ratio of 2:1:3, with final concentrations of 1, 2, 3, 4, and 5×10 10 CFU/g, and culture at 34°C for 3 days.
5)各菌株比例对发酵效果的影响5) Effect of the ratio of each strain on the fermentation effect
称取发酵底物20g,烟草含量在30%,置于50ml三角瓶中。灭菌后接种菌株枯草芽孢杆菌、红酵母、米根霉,将枯草芽孢杆菌、红酵母、米根霉的比例设置为2:1:1、2:1:2、2:1:3、2:1:4、2:1:5,34℃发酵3d。Weigh 20g of fermentation substrate with a tobacco content of 30% and place it in a 50ml conical flask. After sterilization, inoculate strains of Bacillus subtilis, red yeast and Rhizopus oryzae, and set the ratio of Bacillus subtilis, red yeast and Rhizopus oryzae to 2:1:1, 2:1:2, 2:1:3, 2:1:4 and 2:1:5, and ferment at 34°C for 3 days.
6)温度对发酵效果影响的探究6) Study on the effect of temperature on fermentation effect
发酵菌株中,芽孢杆菌最适生长温度为30-37℃,红酵母最适生长温度为27-36℃。米根霉的最适温度为28-37℃,故选择26℃、28℃、30℃、32℃、34℃、36℃进行实验对比。Among the fermentation strains, the optimum growth temperature of Bacillus is 30-37°C, and the optimum growth temperature of red yeast is 27-36°C. The optimum temperature of Rhizopus oryzae is 28-37°C, so 26°C, 28°C, 30°C, 32°C, 34°C, and 36°C were selected for experimental comparison.
按照以上方法发酵后,根据发酵液中可溶性肽含量来判断各因素对发酵效果的影响,结果如图6所示。可以看出,在混合菌株的固态发酵中,可溶性肽的含量先是随着烟草添加量的增加而上升的(图6中a),当达到40%,含量最低,其原因有可能是烟草中的烟碱成分对菌株有抑制作用,影响菌株生长及酶活性。接菌量在4×1010CFU/g时可溶性肽含量最高(图6中b),超过此接菌量时,菌株没有充分与底物结合,所以发酵效果较次,接种量太多导致菌种间生长竞争,生长过快导致营养缺乏,所以发酵液中可溶性肽含量也不高。混合菌株枯草芽孢杆菌:红酵母:米根霉的最适比例为2:1:3。适宜的温度有利于微生物的正常代谢活动,当温度较低时,微生物体内的酶类等物质代谢缓慢,微生物的生长代谢随之变缓,可溶性肽含量较低;当温度升至34℃时,可溶性肽含量达到最高峰,此时最适合微生物的生长代谢的条件,之后随着温度的升高,有些菌种不适宜而生命活动减缓甚至消失,微生物发酵作用随之减缓,导致可溶性肽含量的下降。After fermentation according to the above method, the influence of various factors on the fermentation effect was judged according to the content of soluble peptides in the fermentation broth, and the results are shown in Figure 6. It can be seen that in the solid-state fermentation of mixed strains, the content of soluble peptides first increased with the increase of tobacco addition (a in Figure 6), and when it reached 40%, the content was the lowest. The reason may be that the nicotine component in tobacco has an inhibitory effect on the strain, affecting the growth and enzyme activity of the strain. The soluble peptide content is the highest when the inoculation amount is 4×10 10 CFU/g (b in Figure 6). When the inoculation amount exceeds this, the strain does not fully bind to the substrate, so the fermentation effect is poor. Too much inoculation leads to growth competition between strains, and too fast growth leads to nutrient deficiency, so the soluble peptide content in the fermentation broth is not high. The optimal ratio of mixed strains of Bacillus subtilis: red yeast: Rhizopus oryzae is 2:1:3. Suitable temperature is conducive to the normal metabolic activities of microorganisms. When the temperature is low, the metabolism of enzymes and other substances in the microorganisms is slow, the growth metabolism of the microorganisms slows down, and the soluble peptide content is low; when the temperature rises to 34°C, the soluble peptide content reaches its peak, which is the most suitable condition for the growth and metabolism of microorganisms. After that, as the temperature rises, some strains are not suitable and their life activities slow down or even disappear, and the microbial fermentation slows down, resulting in a decrease in the soluble peptide content.
7)复合菌株发酵的正交试验对比7) Orthogonal test comparison of composite strain fermentation
按照实施例1的方法,选取烟草添加量、接菌量、温度为变量进行对比,对比条件如表1,证明本发明实施例1的发酵条件最优。According to the method of Example 1, the amount of tobacco added, the amount of inoculation, and the temperature were selected as variables for comparison. The comparison conditions are shown in Table 1, which proves that the fermentation conditions of Example 1 of the present invention are optimal.
表3发酵工艺优化Table 3 Fermentation process optimization
表4发酵工艺优化的正交试验设计结果Table 4 Results of orthogonal experimental design for fermentation process optimization
注:表中数据为平均值±标准差。Ki值为因素i水平所对应的试验指标之和。Note: The data in the table are mean ± standard deviation. K i value is the sum of the test indicators corresponding to the level of factor i.
在混合菌株比例为枯草芽孢杆菌:红酵母:米根霉的最佳配比为2:1:3时,从表3的极差分析结果可以看出,以可溶性肽含量为指标主次因素顺序为B>C>A;最优水平组合为A2B2C3,即烟草废弃物添加量30%、接菌量4×1010CFU/g、发酵温度34℃、经试验验证本发明实施例1设置的条件是最优的。When the optimal ratio of the mixed strain ratio is Bacillus subtilis: red yeast: Rhizopus oryzae is 2:1:3, it can be seen from the range analysis results in Table 3 that the order of primary and secondary factors with soluble peptide content as an indicator is B>C>A; the optimal level combination is A 2 B 2 C 3 , that is, the tobacco waste addition amount is 30%, the inoculation amount is 4×10 10 CFU/g, and the fermentation temperature is 34°C. It is verified by experiments that the conditions set in Example 1 of the present invention are optimal.
实施例4Example 4
一种固态发酵复合鱼下脚料和烟草废弃物有机肥的应用,用于农作物肥料。The invention discloses an application of solid-state fermented composite fish scraps and tobacco waste organic fertilizer for use as crop fertilizer.
首先,按照实施例1方法发酵,每2天采集样品,采样前充分混匀。每个样品风干后用于铵态氮、有效磷、速效钾和有机质分析。纤维素的测定采用浓硫酸水解法;可溶性肽的测定采用福林酚法;含水率、pH、全氮和有机质测定方法参照中华人民共和国农业行业标准(NY525-2012)有机肥料行业标准;铵态氮、有效磷和速效钾测定采用TFC各型浓度直读土壤化肥速测仪。结果如图7所示。First, fermentation was performed according to the method of Example 1, and samples were collected every 2 days and mixed thoroughly before sampling. Each sample was air-dried and used for analysis of ammonium nitrogen, available phosphorus, available potassium and organic matter. The determination of cellulose was carried out by concentrated sulfuric acid hydrolysis; the determination of soluble peptides was carried out by Folin phenol method; the determination methods of moisture content, pH, total nitrogen and organic matter were based on the organic fertilizer industry standard of the Agricultural Industry Standard of the People's Republic of China (NY525-2012); the determination of ammonium nitrogen, available phosphorus and available potassium was carried out by TFC various types of direct-reading soil fertilizer rapid testers. The results are shown in Figure 7.
在发酵周期20d中,有机质含量呈逐渐下降趋势(图7中a),后下降了34.27%,表示有机废物经过较充分的发酵,有机质易被分解和利用。有效磷和有效钾钾含量都显著增加(图7中b、7中c),分别增加了137.2%、193.63%,到发酵结束时,有机质、有效磷、有效钾的含量分别为47.26%、3.76%、7.78%,都高于我国有机肥质量标准(NY525-2012)。而发酵产物中的纤维素也在发酵过程中降解了65.15%。发酵肥理化质量检测如表5所示。During the 20 days of fermentation, the organic matter content showed a gradual downward trend (Figure 7a), and then decreased by 34.27%, indicating that the organic waste was fully fermented and the organic matter was easily decomposed and utilized. The contents of available phosphorus and available potassium increased significantly (Figure 7b, 7c), increasing by 137.2% and 193.63%, respectively. At the end of fermentation, the contents of organic matter, available phosphorus, and available potassium were 47.26%, 3.76%, and 7.78%, respectively, all higher than the quality standards of organic fertilizers in my country (NY525-2012). The cellulose in the fermentation product was also degraded by 65.15% during the fermentation process. The physical and chemical quality test of the fermented fertilizer is shown in Table 5.
表5发酵肥理化质量检测结果Table 5 Physical and chemical quality test results of fermented fertilizer
根据以上结果,说明本发明方法发酵后,有机肥有效成分较高,适合作为农作物有机肥。According to the above results, it is shown that after fermentation by the method of the present invention, the organic fertilizer has a high effective component and is suitable as an organic fertilizer for crops.
将以上发酵后的有机肥应用:Apply the above fermented organic fertilizer:
试验设置4个处理,分别为CK:不添加肥的园土;T1:施肥量10g/kg;T2:施肥量为20g/kg;T3:施肥量30g/kg。按照以上比例,将实施例1制备的有机肥与园土混合一次性作为基肥施用。每个处理组分别播种20粒青菜和辣椒种子,每个处理组设置3个重复。置于光照恒温培养箱中生长。光照培养箱条件为光照强度5000lx,光暗比12h:12h,25℃。培养15d后测量蔬菜的茎长、鲜重、干重和叶绿素等,得到最适宜的作物播种施肥量。The experiment set up 4 treatments, namely CK: garden soil without adding fertilizer; T1: fertilizer amount of 10g/kg; T2: fertilizer amount of 20g/kg; T3: fertilizer amount of 30g/kg. According to the above proportions, the organic fertilizer prepared in Example 1 was mixed with garden soil and applied as a base fertilizer at one time. 20 green vegetable and pepper seeds were sown in each treatment group, and 3 replicates were set for each treatment group. They were placed in a light constant temperature incubator for growth. The conditions of the light incubator were light intensity of 5000lx, light-dark ratio of 12h:12h, and 25°C. After 15 days of cultivation, the stem length, fresh weight, dry weight and chlorophyll of the vegetables were measured to obtain the most suitable crop sowing and fertilization amount.
并将不同处理的土壤样品风干,用于土壤理化性质及酶活的测定。土壤脲酶活性采用苯酚-次氯酸钠比色法测定;土壤过氧化氢酶活性采用高锰酸钾滴定法测定;土壤蔗糖酶活采用3,5-二硝基水杨酸比色法。The soil samples with different treatments were air-dried and used for the determination of soil physical and chemical properties and enzyme activities. The soil urease activity was determined by phenol-sodium hypochlorite colorimetry, the soil catalase activity was determined by potassium permanganate titration, and the soil sucrase activity was determined by 3,5-dinitrosalicylic acid colorimetry.
1)不同施肥量对蔬菜茎长、鲜重和干重的影响1) Effects of different fertilization rates on stem length, fresh weight and dry weight of vegetables
由表6、图8和图9可以看出,发酵肥对蔬菜的生长有明显的促进作用。相比于对照组,在发酵肥作为基肥时的处理组T1、T2、T3组均可提高青菜种子的发芽率,促进青菜和辣椒种子的茎长、鲜重和干重。T2组施加基肥为20g/kg时效果最好。青菜和辣椒的苗高分别为4.5cm和5.3cm,增加了95.65%和32.5%;其鲜重比不施加发酵肥的鲜重分别增加0.129g和0.1627g,干重增加0.006g和0.0042g。可见施用发酵肥后,蔬菜的生长效果优于土壤基质。It can be seen from Table 6, Figure 8 and Figure 9 that fermented fertilizer has a significant promoting effect on the growth of vegetables. Compared with the control group, the treatment groups T1, T2 and T3 when fermented fertilizer was used as basal fertilizer can improve the germination rate of green vegetable seeds, and promote the stem length, fresh weight and dry weight of green vegetable and pepper seeds. The best effect was achieved when the basal fertilizer of group T2 was 20g/kg. The seedling heights of green vegetables and peppers were 4.5cm and 5.3cm, respectively, an increase of 95.65% and 32.5%; their fresh weight increased by 0.129g and 0.1627g, respectively, and their dry weight increased by 0.006g and 0.0042g compared with the fresh weight without fermented fertilizer. It can be seen that after the application of fermented fertilizer, the growth effect of vegetables is better than that of soil matrix.
表6发酵肥对蔬菜茎长、鲜重、干重的影响Table 6 Effects of fermented fertilizer on stem length, fresh weight and dry weight of vegetables
注:表中数据为平均值±标准差;*表示不同处理间差异达到5%显著水平。下同。Note: The data in the table are mean ± standard deviation; * indicates that the difference between different treatments reaches 5% significant level. The same below.
2)不同施肥量对蔬菜叶绿素含量的影响2) Effects of different fertilization amounts on chlorophyll content in vegetables
叶绿素含量常作为评定植物适应环境能力和生长状况的一个重要指标。由图9可知,不同施肥量对蔬菜叶片叶绿素的含量影响不同。随着施肥量的增加,叶绿素含量呈上升的趋势,达到20g/kg时,叶绿素的含量最高,青菜与辣椒的叶绿素含量分别为17.124mg/g和16.278mg/g,与对照组相比提高了18.53%和195.4%,存在显著差异。Chlorophyll content is often used as an important indicator to assess the ability of plants to adapt to the environment and their growth status. As shown in Figure 9, different amounts of fertilizer have different effects on the chlorophyll content of vegetable leaves. As the amount of fertilizer increases, the chlorophyll content shows an upward trend. When it reaches 20g/kg, the chlorophyll content is the highest. The chlorophyll content of green vegetables and peppers is 17.124mg/g and 16.278mg/g, respectively, which is 18.53% and 195.4% higher than the control group, showing significant differences.
3)发酵肥对土壤养分的影响3) Effect of fermented fertilizer on soil nutrients
表7不同处理的土壤种植蔬菜后土壤氮磷钾的检测结果Table 7 Test results of soil nitrogen, phosphorus and potassium after planting vegetables in soils with different treatments
土壤为植物提供生理活动所需要的矿物质元素,氮肥可以提高植物的光合速率,增加植物体内抗氧化物酶的活性,促进植物生长;磷和钾能调节植物的代谢过程,促使植物良好发育。对不同处理组的土壤养分进行测定,如表5所示,施肥的T1、T2、T3处理组均可明显提高土壤中铵态氮、有效磷、速效钾的含量。随着施肥量的增加,在20g/kg/亩的T2组中铵态氮含量最高;速效钾在T2组最少,可见施用有机肥为土壤提供养分,而在微生物的作用下,分解释放出植物所需的各种元素,加快肥料的转化率,提高肥料的转化程度,增强肥效,为植物提供营养来源。Soil provides plants with mineral elements needed for physiological activities. Nitrogen fertilizer can increase the photosynthetic rate of plants, increase the activity of antioxidant enzymes in plants, and promote plant growth; phosphorus and potassium can regulate the metabolic process of plants and promote good development of plants. The soil nutrients of different treatment groups were measured. As shown in Table 5, the fertilized T1, T2, and T3 treatment groups can significantly increase the content of ammonium nitrogen, available phosphorus, and available potassium in the soil. With the increase in the amount of fertilizer, the ammonium nitrogen content was the highest in the T2 group of 20g/kg/mu; the available potassium was the least in the T2 group. It can be seen that the application of organic fertilizer provides nutrients for the soil, and under the action of microorganisms, it decomposes and releases various elements needed by plants, accelerates the conversion rate of fertilizers, improves the degree of fertilizer conversion, enhances fertilizer efficiency, and provides a source of nutrition for plants.
4)发酵肥对土壤酶活的影响4) Effects of fermented fertilizer on soil enzyme activity
土壤中的脲酶是氮素循环的关键酶类,能促进尿素的水解,形成的NH3是植物的氮源之一,其活性可反映土壤的供氮能力和水平。对不同处理组的土壤脲酶活性测定,并进行分析结果,如图11所示,T2处理组脲酶活性最高为3.565mg/g,显著高于对照组,T1、T3组脲酶活性分别为2.890mg/g和3.342mg/g,与对照组差别不显著。Urease in soil is a key enzyme in the nitrogen cycle, which can promote the hydrolysis of urea. The formed NH 3 is one of the nitrogen sources for plants, and its activity can reflect the nitrogen supply capacity and level of the soil. The soil urease activity of different treatment groups was measured and the results were analyzed. As shown in Figure 11, the urease activity of the T2 treatment group was the highest at 3.565 mg/g, which was significantly higher than that of the control group. The urease activities of the T1 and T3 groups were 2.890 mg/g and 3.342 mg/g, respectively, which were not significantly different from the control group.
蔗糖酶来自植物根系和微生物,能催化蔗糖水解成葡萄糖和蔗糖,对土壤的碳和氮循环起到重要的作用。由图12可见,未添加发酵肥的园土中,蔗糖酶活性为0.527mg/g,处理组T1、T2、T3的蔗糖酶活性分别为1.760mg/g、1.863mg/g、1.570mg/g,与对照组相比,添加不同量的发酵肥后蔗糖酶活大大增加,其中T2处理组的酶活性最大,随着添加发酵肥的量增大,蔗糖酶活有下降趋势,但仍有显著差异。Sucrase comes from plant roots and microorganisms, can catalyze the hydrolysis of sucrose into glucose and sucrose, and plays an important role in the carbon and nitrogen cycle of the soil. As shown in Figure 12, in the garden soil without adding fermented fertilizer, the sucrase activity is 0.527 mg/g, and the sucrase activities of treatment groups T1, T2, and T3 are 1.760 mg/g, 1.863 mg/g, and 1.570 mg/g, respectively. Compared with the control group, the sucrase activity increased greatly after adding different amounts of fermented fertilizer, among which the enzyme activity of the T2 treatment group was the largest. As the amount of fermented fertilizer added increased, the sucrase activity tended to decrease, but there was still a significant difference.
过氧化氢是生物呼吸过程中有机物发生生物化学氧化反应而产生的,其积累会对生物和土壤产生毒害作用,而土壤中的过氧化氢酶能酶促过氧化氢分解为水和氧,从而解除过氧化氢的毒害作用。由图13可见,随着发酵肥的增加,过氧化氢酶活性先增加后下降,T1、T2组的过氧化氢酶活性分别为4.00(U/h·g)和3.591(U/h·g),与对照组相比,分别提高了25.74%和12.89%,差异显著。Hydrogen peroxide is produced by the biochemical oxidation reaction of organic matter during the process of biological respiration. Its accumulation will have a toxic effect on organisms and soil. The catalase in the soil can enzymatically decompose hydrogen peroxide into water and oxygen, thereby eliminating the toxic effect of hydrogen peroxide. As shown in Figure 13, with the increase of fermentation fertilizer, the catalase activity first increased and then decreased. The catalase activities of the T1 and T2 groups were 4.00 (U/h·g) and 3.591 (U/h·g), respectively, which were increased by 25.74% and 12.89% respectively compared with the control group, with significant differences.
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