CN106978347A - The screening and its application in improvement booth vegetable soil hardening of one plant of dissolving phosphor and dissolving potassium bacillus - Google Patents
The screening and its application in improvement booth vegetable soil hardening of one plant of dissolving phosphor and dissolving potassium bacillus Download PDFInfo
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Abstract
本发明涉及一株解磷解钾芽孢杆菌JJMSH1的筛选及其在改良大棚蔬菜土壤板结中的应用,该菌株具有良好的解磷解钾功能。该菌种筛选自蔬菜大棚植物根际土壤,使用有机磷培养基进行富集,无机磷和硅酸盐培养基依次筛选,使用钼锑抗比色法以及火焰光度法依次检测有效磷和速效钾含量,最终选定JJMSH1为理想菌株。通过革兰氏染色以及芽孢染色鉴定其为革兰氏阳性芽孢杆菌属。使用该发明菌株处理大棚板结土壤,土壤中有效磷和速效钾含量相对有较为明显的提高,OD600达到1.5菌剂稀释100倍后作用于土壤,有效磷含量增加了35.7%,速效钾含量增加了26.1%。The invention relates to the screening of a phosphate-solubilizing and potassium-solubilizing Bacillus JJMSH1 and its application in improving soil compaction of vegetables in greenhouses. The strain was screened from the rhizosphere soil of vegetable greenhouse plants, enriched with organic phosphorus medium, screened with inorganic phosphorus and silicate medium in turn, and detected available phosphorus and available potassium with molybdenum antimony anti-colorimetry and flame photometry content, finally selected JJMSH1 as the ideal strain. It was identified as Gram-positive Bacillus by Gram staining and spore staining. Use this inventive bacterial strain to treat the compacted soil in greenhouses, the content of available phosphorus and available potassium in the soil is relatively significantly improved, and the OD600 reaches 1.5. After the bacterial agent is diluted 100 times and acts on the soil, the content of available phosphorus increases by 35.7%, and the content of available potassium increases by 100 times. 26.1%.
Description
技术领域technical field
本发明设计农业及微生物领域,特别是本菌株具有解磷解钾效果可在一定程度上改善大棚土壤板结的现象。The invention is designed in the fields of agriculture and microorganisms, especially the strain has the effect of dissolving phosphorus and potassium, and can improve the phenomenon of soil compaction in greenhouses to a certain extent.
背景技术Background technique
磷和钾都是植物生长所必须的营养要素,磷广泛参与植物的光合作用和体内的生化反应,钾与植物的新陈代谢及生长密切相关。土壤中的磷主要的以有机磷和无机磷形式存在,有机磷大部分以植酸、核酸、磷脂的形态存在,不能被直接吸收,必须在微生物作用下转变成无机磷的形态才能被吸收。土壤中95%以上的磷不能被植物直接吸收利用。土壤中可溶性钾含量比较低,但是土壤中含有大量的含钾矿物,只是它们主要以稳定的硅铝酸盐形式存在,90%以上的钾不能为作物吸收利用。土壤中的含钾硅酸盐矿物只有在理化因素和微生物的作用下,通过分化和分解逐步释放出速效钾供作物生长利用。土壤中可溶性钾的含量还在以很高的速度不断下降,造成土壤中速效钾的缺乏,导致土壤肥力下降。我们在农业上通常通过施用化肥的方法进行磷和钾的补充。但是施加化肥容易造成土壤结构的破坏,以及造成不必要的污染。而且施用化肥磷和钾也不能充分利用,尤其是磷肥利用率低于30%,大部分的磷固化在土壤中不能被利用。Both phosphorus and potassium are essential nutrients for plant growth. Phosphorus is widely involved in plant photosynthesis and biochemical reactions in the body, and potassium is closely related to plant metabolism and growth. Phosphorus in the soil mainly exists in the form of organic phosphorus and inorganic phosphorus. Most of the organic phosphorus exists in the form of phytic acid, nucleic acid, and phospholipids, which cannot be absorbed directly. It must be transformed into the form of inorganic phosphorus under the action of microorganisms to be absorbed. More than 95% of the phosphorus in the soil cannot be directly absorbed and utilized by plants. The soluble potassium content in the soil is relatively low, but the soil contains a large amount of potassium-containing minerals, but they mainly exist in the form of stable aluminosilicates, and more than 90% of the potassium cannot be absorbed and utilized by crops. Potassium-containing silicate minerals in the soil can only gradually release available potassium through differentiation and decomposition under the action of physical and chemical factors and microorganisms for crop growth and utilization. The content of soluble potassium in the soil is still declining at a high rate, resulting in the lack of available potassium in the soil, resulting in a decline in soil fertility. In agriculture, we usually supplement phosphorus and potassium by applying chemical fertilizers. However, the application of chemical fertilizers is likely to cause damage to the soil structure and cause unnecessary pollution. Moreover, the application of chemical fertilizers phosphorus and potassium cannot be fully utilized, especially the utilization rate of phosphorus fertilizer is lower than 30%, and most of the phosphorus is solidified in the soil and cannot be used.
大棚蔬菜是一种能够创造出优质高效的经济作物的农业生产方法,是当前农民致富奔小康的一条非常重要的途径。但随着栽培时间的积累,施肥技术的不当,很容易出现土壤板结的现象,严重地影响了温室蔬菜的可持续发展。土壤板结非常大的一个原因就是氮肥施加过多,有效磷、速效钾以及其他微量元素少。土壤中磷和钾含量含量虽然丰富,但是不能直接被吸收,微生物对改良土壤根际环境,促进土壤中有效磷和钾的释放,提高土壤肥力有很大作用,所以解磷解钾菌株可有效地缓解土壤元素失衡,使土壤元素得到充分利用。Greenhouse vegetables are an agricultural production method that can create high-quality and efficient economic crops, and it is a very important way for farmers to become rich and well-off. However, with the accumulation of cultivation time and improper fertilization techniques, soil compaction is easy to occur, which seriously affects the sustainable development of greenhouse vegetables. One of the reasons for the large soil compaction is that too much nitrogen fertilizer is applied, and available phosphorus, available potassium and other trace elements are insufficient. Although the content of phosphorus and potassium in the soil is rich, they cannot be absorbed directly. Microorganisms play a great role in improving the soil rhizosphere environment, promoting the release of available phosphorus and potassium in the soil, and improving soil fertility. Therefore, phosphorus and potassium-dissolving strains can effectively It can effectively alleviate the imbalance of soil elements and make full use of soil elements.
发明内容Contents of the invention
本发明的第一个目的是得到具有良好解磷解钾功能的菌株。The first object of the present invention is to obtain a bacterial strain with good phosphorus and potassium dissolving functions.
本发明的第二个目的是所筛选菌株能够对大棚板结土壤起到一定的改善作用,增强作物的生长力,为开发相关菌剂提供技术支撑。相应的减少相关经济损失,提高收益,有利于生态健康发展和农业的可持续发展。The second purpose of the present invention is that the screened bacterial strain can improve the hardened soil in greenhouses, enhance the growth of crops, and provide technical support for the development of related bacterial agents. Correspondingly reduce relevant economic losses and increase income, which is conducive to the healthy development of ecology and the sustainable development of agriculture.
实施例一、菌种筛选Embodiment one, strain screening
芽孢杆菌JJMSH1分离自蔬菜大棚土壤,为实现该发明,初筛使用有机磷培养基富集,再使用无机磷培养基复筛,之后将具有解磷功能的菌株点接到硅酸盐细菌培养基。故可同时获得可能具有解磷解钾效果的菌株。Bacillus JJMSH1 was isolated from the soil of vegetable greenhouses. In order to realize this invention, organic phosphorus medium was used for primary screening to enrich, and then inorganic phosphorus medium was used for rescreening, and then the strains with phosphorus-solubilizing function were spot-connected to silicate bacterial medium . Therefore, strains that may have the effect of dissolving phosphorus and potassium can be obtained at the same time.
首先使用有机磷培养基进行富集,取1g大棚蔬菜根际土样于100ml富集培养基中,28℃200r/min富集2d。之后取无菌生理盐水稀释梯度至10-8然后将-6,-7,-8三个梯度涂布于无机磷培养基,30℃培养,每天观察长势,观察无机磷培养基水解圈,并记录其溶磷圈与菌落直径的直径比(JJMSH1直径比为4.1),将具有水解圈的菌落点接于硅酸盐培养基并注意观察菌落形态,选取在培养基上长势较旺盛的菌落,将获得的菌株保存于LB斜面,最终选取5株水解圈较大在钾矿石培养基上长势良好的菌株Firstly, use organic phosphorus medium for enrichment, take 1g greenhouse vegetable rhizosphere soil sample in 100ml enrichment medium, enrich at 28°C and 200r/min for 2 days. After that, dilute the gradient with sterile normal saline to 10-8, then spread the three gradients of -6, -7, and -8 on the inorganic phosphorus medium, culture at 30°C, observe the growth every day, observe the hydrolysis circle of the inorganic phosphorus medium, and Record the diameter ratio of its phosphorus-dissolving circle to the diameter of the colony (the JJMSH1 diameter ratio is 4.1), connect the colony with the hydrolysis circle to the silicate medium and pay attention to the colony shape, and select the vigorous colony on the medium. Save the obtained strains on the LB slope, and finally select 5 strains with larger hydrolysis circles and grow well on the potassium ore medium
筛选、培养、保存用培养基Media for screening, culturing, and storage
1.有机磷培养基,蒙金娜基础培养基加蛋黄液(1000ml):葡萄糖10g,NH4SO4 0.5g,NaCl0.3g,KCl0.3g,7H2O.MgSO40.3g,7H2O.FeSO4 0.03g,4H2O.MnSO 0.03g,CaCO3 5g,(NH4)3PO40.5g,酵母膏0.4g,调pH7,121℃20min,之后加蛋黄液10ml(无菌生理盐水与鸡蛋黄1:1)(固体加20g琼脂)1. Organic phosphorus medium, Montina basal medium plus egg yolk liquid (1000ml): glucose 10g, NH 4 SO 4 0.5g, NaCl 0.3g, KCl 0.3g, 7H 2 O. MgSO 40.3g, 7H 2 O. FeSO 4 0.03g, 4H 2 O.MnSO 0.03g, CaCO 3 5g, (NH 4 ) 3 PO 4 0.5g, yeast extract 0.4g, adjust pH to 7, 121°C for 20min, then add 10ml egg yolk liquid (sterile normal saline and Egg yolk 1:1) (solid plus 20g agar)
2.无机磷培养基,蒙金娜基础培养基加Ca3(PO3)2:葡萄糖10g,NH4SO4 0.5g,NaCl0.3g,KCl0.3g,7H2O.MgSO40.3g,7H2O.FeSO4 0.03g,4H2O.MnSO 0.03g,CaCO3 5g,Ca3(PO3)22g,(固体加20g琼脂)调pH7,121℃灭菌20min2. Inorganic phosphorus medium, Montina basal medium plus Ca 3 (PO 3 ) 2 : Glucose 10g, NH 4 SO 4 0.5g, NaCl 0.3g, KCl 0.3g, 7H 2 O.MgSO4 0.3g, 7H 2 O.FeSO 4 0.03g, 4H 2 O.MnSO 0.03g, CaCO 3 5g, Ca 3 (PO 3 ) 2 2g, (solid plus 20g agar) adjust pH to 7, sterilize at 121°C for 20min
3.硅酸盐细菌培养基:蔗糖5g,MgS04·7H20 0.5g,FeCl30.005g,Na2HPO4 2g,钾长石粉(800目,含K2O:9.8%)2g,水1000mL,(琼脂20g),调节pH7,121℃灭菌20min3. Silicate bacteria medium: sucrose 5g, MgS04 7H20 0.5g, FeCl30.005g, Na2HPO4 2g, potassium feldspar powder (800 mesh, containing K2O: 9.8%) 2g, water 1000mL, (agar 20g), adjust pH7 , sterilized at 121°C for 20min
4.LB:胰蛋白胨10g/L,酵母提取物5g/L,NaCl10g/L,琼脂(固)调节PH7,121℃灭菌20min,之后置于室温倾斜15°左右自然冷却凝固,置于4℃冰箱备用。4. LB: tryptone 10g/L, yeast extract 5g/L, NaCl 10g/L, agar (solid) to adjust the pH to 7, sterilize at 121°C for 20min, then place it at room temperature with an inclination of about 15° to cool and solidify naturally, and place it at 4°C Refrigerator for spare.
将分离到的菌株使用LB培养基进行活化,之后分别接入三种液体培养基,分别为无机磷、有机磷、硅酸盐细菌培养基,接种量为2%,200r/min,培养5d测定其磷钾含量。The isolated strains were activated with LB medium, and then inserted into three kinds of liquid medium, namely inorganic phosphorus, organic phosphorus, and silicate bacterial medium, with an inoculum size of 2%, 200r/min, and cultured for 5 days. its phosphorus and potassium content.
实施例二、有效磷速效钾测定Embodiment two, the determination of available phosphorus and available potassium
本发明使用钼锑抗比色法测有效磷含量,火焰光度法测速效钾含量The present invention uses the molybdenum antimony anti-colorimetric method to measure the available phosphorus content, and the flame photometry to measure the available potassium content
钼锑抗比色法测有效磷Determination of available phosphorus by molybdenum antimony anti-colorimetric method
钼锑抗比色法原理:用2,4-二硝基酚作为指示剂,可溶性磷酸盐可与钼锑抗显色剂反应,生成磷钼蓝,于660nm波长处进行比色测定,根据标准曲线计算出有效磷的含量,通过有效磷的浓度大小表示微生物溶磷能力的高低。The principle of molybdenum antimony anticolorimetric method: 2,4-dinitrophenol is used as indicator, and soluble phosphate can react with molybdenum antimony antichromogenic agent to generate phosphomolybdenum blue. The colorimetric determination is carried out at a wavelength of 660nm, according to the standard The curve calculates the content of available phosphorus, and the concentration of available phosphorus indicates the level of microbial phosphorus-dissolving ability.
钼锑抗比色法常用试剂Commonly used reagents for molybdenum antimony anti-colorimetric method
1.钼锑抗贮存液:取98%浓硫酸153ml缓缓地倾入约400ml蒸馏水中,搅拌、冷却。然后称取l0.0g钼酸铵溶于约60℃的300m1水中,冷却。然后将上述硫酸溶液缓缓加入此钼酸铵溶液中,再加入5g/L酒石酸锑钾溶液100ml,最后用水稀释至lL,盛于棕色瓶中,放于阴暗处保存1. Molybdenum antimony anti-storage solution: Take 153ml of 98% concentrated sulfuric acid and slowly pour it into about 400ml of distilled water, stir and cool. Then weigh 10.0g of ammonium molybdate, dissolve it in 300ml of water at about 60°C, and cool it. Then slowly add the above sulfuric acid solution into the ammonium molybdate solution, then add 100ml of 5g/L antimony potassium tartrate solution, and finally dilute to 1L with water, put it in a brown bottle, and store it in a dark place
2.钼锑抗显色剂:抗坏血酸1.5g,溶于l00ml钼锑抗贮存液中,现配现用2. Molybdenum-antimony antichromogenic agent: 1.5g of ascorbic acid, dissolved in 100ml molybdenum-antimony anti-coloring agent, ready for immediate use
3.磷标准溶液(10mg/L):磷酸二氢钾于100℃烘箱烘干2h,冷却,取0.439g,溶解于100ml蒸馏水中,加入5ml98%浓硫酸,定容至1L,稀释10倍即为10mg/L磷标准溶液3. Phosphorus standard solution (10mg/L): Potassium dihydrogen phosphate was dried in an oven at 100°C for 2 hours, cooled, 0.439g was taken, dissolved in 100ml of distilled water, added 5ml of 98% concentrated sulfuric acid, dilute to 1L, and diluted 10 times. 10mg/L phosphorus standard solution
磷标准曲线绘制:分别吸取5mg/L磷标准溶液0、2、4、6、8、10、12ml,分别加水稀释至26.3m1,加入5ml钼锑抗显色剂,摇匀后定容,即得0、0.2、0.4、0.6、0.8、1.0、1.2mg/L磷溶液,20℃下放置4h后,以0mg/L磷标准液为对照溶液,其余磷标准溶液与待测液同时比色,并记录在660nm下的吸光度。以测得的吸光度为纵坐标,磷浓度(mg/L)为横坐标,绘制成标准磷曲线Phosphorus standard curve drawing: draw 0, 2, 4, 6, 8, 10, 12ml of 5mg/L phosphorus standard solution respectively, add water to dilute to 26.3m1 respectively, add 5ml of molybdenum antimony anti-chromogenic agent, shake well and make up to volume, that is Get 0, 0.2, 0.4, 0.6, 0.8, 1.0, 1.2 mg/L phosphorus solutions, place them at 20°C for 4 hours, use 0 mg/L phosphorus standard solution as the control solution, and compare the color of the remaining phosphorus standard solutions with the test solution at the same time. And record the absorbance at 660nm. Take the measured absorbance as the ordinate and the phosphorus concentration (mg/L) as the abscissa to draw a standard phosphorus curve
取发酵液50ml,4000r/min离心30min,取上清液,用蒸馏水稀释适50倍后,取25ml,滴加2~3滴2,4-二硝基酚指示剂溶液,用1mol/L氢氧化钠溶液或硫酸溶液调节pH至溶液刚呈现微黄,加入钼锑抗显色剂5m1摇匀,定容至刻度。空白试验发酵液做相同的处理。660nm处比色,测定吸光度,以空白试验发酵液为对照液调零点,读取吸光度值,在工作曲线上查出磷标准液的浓度,计算得到。Take 50ml of fermentation broth, centrifuge at 4000r/min for 30min, take the supernatant, dilute it with distilled water to 50 times, take 25ml, add dropwise 2-3 drops of 2,4-dinitrophenol indicator solution, and use 1mol/L hydrogen Sodium oxide solution or sulfuric acid solution to adjust the pH until the solution just appears slightly yellow, add molybdenum antimony anti-color agent 5m1 shake well, dilute to the mark. The blank test fermentation broth was treated in the same way. Colorimetric at 660nm, measure the absorbance, set the zero point with the blank test fermentation broth as the control solution, read the absorbance value, find out the concentration of the phosphorus standard solution on the working curve, and calculate it.
通过检测得到菌株JJMSH1菌株无机磷培养基有效磷含量为59.81mg/L培养基,其他四株菌JJMSH2、3、4、5分别为,23.10、41.32、39.28、65.45mg/LThrough testing, the available phosphorus content of the inorganic phosphorus medium of the strain JJMSH1 is 59.81 mg/L medium, and the other four strains JJMSH2, 3, 4, and 5 are 23.10, 41.32, 39.28, and 65.45 mg/L, respectively.
菌株JJMSH1菌株有机磷培养基有效磷含量为41.23mg/L培养基,其他四株菌JJMSH2、3、4、5分别为,29.88、40.51、39.11、17.82mg/LThe available phosphorus content of strain JJMSH1 strain organic phosphorus medium is 41.23 mg/L medium, and the other four strains JJMSH2, 3, 4, and 5 are 29.88, 40.51, 39.11, and 17.82 mg/L respectively
火焰光度法测速效钾Determination of available potassium by flame photometry
1.1mol/L中性醋酸铵溶液:称取纯醋酸铵77.09g加水溶解,定容至近1L,检测pH,用醋酸和氨水调节至ph71.1mol/L neutral ammonium acetate solution: Weigh 77.09g of pure ammonium acetate, add water to dissolve, set the volume to nearly 1L, check the pH, adjust to pH7 with acetic acid and ammonia water
2.钾的标准溶液配制:KCl100℃摄氏度烘干2h,称取0.1907g溶于1mol/L醋酸铵溶液中,定容至1L,即为含100ug/mL K标准液0,2.5,5,7.5,10,15,20mL放入50mL容量瓶中,用1mol/L醋酸铵溶液定容,即为0、5、10、15、20、30、40ug/mL K标准系列溶液2. Potassium standard solution preparation: KCl was dried at 100°C for 2 hours, weighed 0.1907g and dissolved in 1mol/L ammonium acetate solution, and set the volume to 1L, which was 100ug/mL K standard solution 0, 2.5, 5, 7.5 , 10, 15, 20mL into a 50mL volumetric flask, with 1mol/L ammonium acetate solution to volume, that is, 0, 5, 10, 15, 20, 30, 40ug/mL K standard series solutions
将菌液取25ml全部倾入蒸发皿中,在水浴锅上浓缩至5ml左右,加2ml过氧化氢继续蒸发,不断搅动,反复加几次,直到粘液物质完全消化为止。3500r/min离心10min,将上清液收集在50ml容量瓶中,用蒸馏水定容。对照培养基做相同处理。滤液和钾的标准液一起在火焰光度计上测定Pour all 25ml of the bacterial solution into an evaporating dish, concentrate on a water bath to about 5ml, add 2ml of hydrogen peroxide to continue evaporating, keep stirring, and add several times until the mucus substance is completely digested. Centrifuge at 3500r/min for 10min, collect the supernatant in a 50ml volumetric flask, and distill it to volume. The control medium was treated in the same way. The filtrate and the standard solution of potassium are measured on a flame photometer
检测得到菌株JJMSH1菌株无机磷培养基速效钾含量为28.56mg/L培养基,其他四株菌JJMSH2、3、4、5分别为,23.11、7.32、19.18、22.37mg/LThe available potassium content of the inorganic phosphorus medium of the strain JJMSH1 was detected to be 28.56 mg/L medium, and the other four strains JJMSH2, 3, 4, and 5 were 23.11, 7.32, 19.18, and 22.37 mg/L, respectively.
选定菌株JJMSH1为较为理想菌株The selected strain JJMSH1 is an ideal strain
实施例三、菌株JJMSH1菌种鉴定Embodiment three, bacterial strain JJMSH1 strain identification
菌落表面形态粗糙、不透明、颜色乳白色少许偏黄,类似于芽孢杆菌属某些菌株菌落形态The surface of the colony is rough, opaque, and the color is milky white and slightly yellowish, similar to the colony morphology of certain strains of Bacillus
革兰氏染色以及芽孢染色Gram stain and spore stain
革兰氏染色:涂片固定,结晶紫初染1分钟,自来水冲洗,注意不要把菌体冲掉,碘液媒染约1分钟,水洗,用吸水纸吸去水分,95%酒精一滴,15~20秒后水洗,吸去水分,蕃红染色液复染1分钟后,自来水冲洗,油镜观察。Gram staining: fix the smear, stain with crystal violet for 1 minute, rinse with tap water, be careful not to wash off the bacteria, mordant with iodine solution for about 1 minute, wash with water, absorb water with absorbent paper, 1 drop of 95% alcohol, 15~ After 20 seconds, wash with water, absorb the water, counterstain with safranin staining solution for 1 minute, rinse with tap water, and observe with an oil microscope.
本发明菌株经过革兰氏染色,鉴定为阳性菌,菌体为长杆状,偶见有类似未着色芽孢产生。The bacterial strain of the present invention is identified as a positive bacterium through Gram staining, and the bacterium is long rod-shaped, and similar uncolored spores are occasionally produced.
芽孢染色Spore staining
涂片、干燥、固定,滴加3—5滴孔雀绿染液,载玻片在火焰上加热,使染液冒蒸汽但勿沸腾,勿使染液蒸干,约4—5分钟,水洗至孔雀绿不再褪色为止,番红复染1分钟,水洗,干燥后,油镜观察Smear, dry, and fix, add 3-5 drops of malachite green dyeing solution dropwise, heat the glass slide on the flame, make the dyeing solution steam but do not boil, do not let the dyeing solution evaporate dry, about 4-5 minutes, wash with water until Until the malachite green no longer fades, safranin counterstained for 1 minute, washed with water, dried, and observed with an oil lens
观察到有少许绿色芽孢以及大量红色菌体A few green spores and a large number of red bacteria were observed
本发明鉴定为芽孢杆菌The present invention is identified as Bacillus
实施例四、芽孢杆菌发酵Embodiment four, bacillus fermentation
菌株JJMSH1于100mlLB液体培养基中活化,35℃200r/min活化,然后接种于10L发酵罐,培养基包括胰蛋白胨:5-10g/L,酵母提取物:5-10g/L,氯化钠:2-10g/L,转速300rpm,温度25-35℃,培养12-24h,然后取合适梯度进行菌落计数为100亿/mL。The strain JJMSH1 was activated in 100ml LB liquid medium, activated at 35°C and 200r/min, and then inoculated in a 10L fermenter. The medium included tryptone: 5-10g/L, yeast extract: 5-10g/L, sodium chloride: 2-10g/L, speed 300rpm, temperature 25-35°C, culture for 12-24h, then take a suitable gradient for colony counting to 10 billion/mL.
实施例四、大棚土壤应用试验Embodiment four, greenhouse soil application test
将菌液分别稀释100、200、400倍。The bacterial solution was diluted 100, 200, 400 times respectively.
大棚板结土壤4000目筛子过筛Sieve through a 4000-mesh sieve for compacted soil in greenhouses
取12个1L烧杯,分别标号1~12,121℃灭菌20min,分别装入相同的已过筛大棚板结土壤0.5kg,,1~3为对照组,4~12为实验组,实验组各喷50ml菌液,每3个为一个稀释倍数,对照组每个喷相同体积的无菌水Take 12 1L beakers, labeled 1~12 respectively, sterilize at 121°C for 20 minutes, and fill them with 0.5 kg of the same sieved greenhouse compaction soil, 1~3 is the control group, 4~12 is the experimental group, and each experimental group Spray 50ml of bacterial solution, every 3 is a dilution factor, each spray the same volume of sterile water in the control group
25℃培养15dCulture at 25°C for 15 days
土壤有效磷含量测定Determination of available phosphorus content in soil
每个样品分别取土样2gTake 2g of soil sample for each sample
加入50ml0.5mol/L NaHCO3溶液,25℃180r/min震荡30min,8000r/min取上清25ml,相同的方法做一组空白用于标零,具体见实施例二Add 50ml of 0.5mol/L NaHCO 3 solution, shake at 180r/min at 25°C for 30min, take 25ml of the supernatant at 8000r/min, make a set of blanks for zeroing in the same way, see Example 2 for details
对照组有效磷含量为9.75mg/kg,实验组喷洒稀释100倍菌剂土样有效磷含量约为13.23mg/kg,喷洒稀释200倍菌剂土样有效磷含量约为12.11mg/kg,喷洒稀释400倍菌剂土样有效磷含量约为10.87mg/kgThe available phosphorus content of the control group was 9.75mg/kg, the available phosphorus content of the experimental group was about 13.23mg/kg, and the effective phosphorus content of the soil sample was about 12.11mg/kg after spraying and diluting the 100-fold bacterial agent in the experimental group. The effective phosphorus content of the soil sample diluted 400 times is about 10.87mg/kg
稀释100、200、400倍有效磷含量分别增加了35.7%、24.2%、11.9%The effective phosphorus content increased by 35.7%, 24.2%, and 11.9% when diluted 100, 200, and 400 times
土壤速效钾含量测定Soil Available Potassium Determination
每个样品分别取土样2gTake 2g of soil sample for each sample
加入50ml1mol/L醋酸铵溶液,25℃180r/min震荡30min,8000r/min取上清25ml,相同的方法做一组空白用于标零,具体见实施例二Add 50ml of 1mol/L ammonium acetate solution, shake at 180r/min at 25°C for 30min, take 25ml of the supernatant at 8000r/min, make a set of blanks for zeroing in the same way, see Example 2 for details
对照组速效钾含量为5.01mg/kg,实验组喷洒稀释100倍菌剂土样有效磷含量约为6.32mg/kg,喷洒稀释200倍菌剂土样有效磷含量约为5.77mg/kg,喷洒稀释400倍菌剂土样有效磷含量约为5.27mg/kgThe content of available potassium in the control group was 5.01mg/kg, the available phosphorus content of the experimental group was about 6.32mg/kg when spraying and diluting 100 times the bacteria agent, and the available phosphorus content of the soil sample when spraying and diluting 200 times the bacteria agent was about 5.77mg/kg. The effective phosphorus content of the soil sample diluted 400 times is about 5.27mg/kg
稀释100、200、400倍速效钾含量分别增加了26.1%、15.2%、5.2%Diluted 100, 200, 400 times the available potassium content increased by 26.1%, 15.2%, 5.2% respectively
<110> 中国科学院过程工程研究所<110> Institute of Process Engineering, Chinese Academy of Sciences
<120> 一株解磷解钾芽孢杆菌的筛选及其在改良大棚蔬菜土壤板结中的应用<120> Screening of a strain of Bacillus phosphate and potassium solubles and its application in improving soil compaction of vegetables in greenhouses
<130> 2017<130> 2017
<160> 1<160> 1
<170> PatentIn version 3.5<170> PatentIn version 3.5
<210> 1<210> 1
<211> 1442<211> 1442
<212> DNA<212>DNA
<213> Bacillus subtilis JJMSH1<213> Bacillus subtilis JJMSH1
<400> 1<400> 1
ggggcgggtg ctatacatgc agtcgagccc acagatggga gcttgctccc tgatgttagc 60ggggcgggtg ctatacatgc agtcgagccc acagatggga gcttgctccc tgatgttagc 60
ggcggacggg tgagtaacac gtgggtaacc tgcctgtaag actgggataa ctccgggaaa 120ggcggacggg tgagtaacac gtgggtaacc tgcctgtaag actgggataa ctccgggaaa 120
ccggggctaa taccggatgg ttgtttgaac cgcatggttc agacataaaa ggtggcttcg 180ccggggctaa taccggatgg ttgtttgaac cgcatggttc agacataaaa ggtggcttcg 180
gctaccactt acagatggac ccgcggcgca ttagctagtt ggtgaggtaa cggctcacca 240gctaccactt acagatggac ccgcggcgca ttagctagtt ggtgaggtaa cggctcacca 240
aggcgacgat gcgtagccga cctgagaggg tgatcggcca cactgggact gagacaccgc 300aggcgacgat gcgtagccga cctgagaggg tgatcggcca cactgggact gagacaccgc 300
ccagactcct acgggagcca gcagtaggga atcttccgca atggacgaaa gtctgacgga 360ccagactcct acgggagcca gcagtaggga atcttccgca atggacgaaa gtctgacgga 360
gcaacgccgc gtgagtgatg aaggttttcg gatcgtattg ctctgttgtt agggaagaac 420gcaacgccgc gtgagtgatg aaggttttcg gatcgtattg ctctgttgtt agggaagaac 420
aagtgccgtt caaatagggc ggcaccttga cggtacctaa ccagaaagcc acggctaact 480aagtgccgtt caaatagggc ggcaccttga cggtacctaa ccagaaagcc acggctaact 480
acgtgccagc agccgcggta atacgtaggt ggcaagcgtt gtccggaatt attgggcgta 540acgtgccagc agccgcggta atacgtaggt ggcaagcgtt gtccggaatt attgggcgta 540
aagggctcgc aggcggtttc ttaagtctga tgtgaaagcc cccggctcaa ccggggaggg 600aagggctcgc aggcggtttc ttaagtctga tgtgaaagcc cccggctcaa ccggggaggg 600
tcattggaaa ctggggaact tgagtgcaga agaggagagt ggaattccac gtgtagcggt 660tcattggaaa ctggggaact tgagtgcaga agaggagagt ggaattccac gtgtagcggt 660
gaaatgcgta gagatgtgga ggaacaccag tggcgttggc gactctctcc tctgtaactg 720gaaatgcgta gagatgtgga ggaacaccag tggcgttggc gactctctcc tctgtaactg 720
acgctgagga gcgaaagcgt ggggagcgaa caggattaga taccctggta gtccacgccg 780acgctgagga gcgaaagcgt ggggagcgaa caggattaga taccctggta gtccacgccg 780
taaacgatga gtgctaagtg ttagggggta accgcccctt agtgctgcag ctaacgcatt 840taaacgatga gtgctaagtg ttagggggta accgcccctt agtgctgcag ctaacgcatt 840
aagcactccg cctggggaga acggtcgcaa gactgaaact caaacgaatt gacgggcccc 900aagcactccg cctggggaga acggtcgcaa gactgaaact caaacgaatt gacggggcccc 900
cgcacaagcg gtggagcatg acctttaatt cgaagcaacg cgaagaacct taccaggtct 960cgcacaagcg gtggagcatg acctttaatt cgaagcaacg cgaagaacct taccaggtct 960
tgacatcctc tgacaatcct agagatagga cgtccccttc gggggcagag tgacaggtgg 1020tgacatcctc tgacaatcct agagatagga cgtccccttc gggggcagag tgacaggtgg 1020
tgcatggttg tcgtcagctc gtgtcgtgag atgttgggtt aagtcccgca acgagcgcaa 1080tgcatggttg tcgtcagctc gtgtcgtgag atgttgggtt aagtcccgca acgagcgcaa 1080
cccttgatct tagttgccag cattcagttg ggcactctaa ggtgactgcc ggtgacaaac 1140cccttgatct tagttgccag cattcagttg ggcactctaa ggtgactgcc ggtgacaaac 1140
cggaggaagg tggggatgac gtcaaatcat catgcccctt atgacctggg ctacacacgt 1200cggaggaagg tggggatgac gtcaaatcat catgcccctt atgacctggg ctacacacgt 1200
gctacaatgg acagaacaaa gggcagcgaa accgcgaggt taagccaatc ccacaaatct 1260gctacaatgg acagaacaaa gggcagcgaa accgcgaggt taagccaatc ccacaaatct 1260
gttctcagtt cggatcgcag tctgcaactc gactgcgtga agctggaatc gctagtaatc 1320gttctcagtt cggatcgcag tctgcaactc gactgcgtga agctggaatc gctagtaatc 1320
gcggatcagc atgccgcggt gaatacgttc ccgggccttg tacacaccgc ccgtcacacc 1380gcggatcagc atgccgcggt gaatacgttc ccgggccttg tacacaccgc ccgtcacacc 1380
acgagagttt gtaacacccg aagtcggtga ggtaacctaa aggagccagc cgccgaagaa 1440acgagagttt gtaacacccg aagtcggtga ggtaacctaa aggagccagc cgccgaagaa 1440
gt 1442GT 1442
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| CN113150788A (en) * | 2021-04-22 | 2021-07-23 | 浙江树人学院(浙江树人大学) | Preparation method and application of seaweed oligosaccharide composite microbial material for preventing soil hardening |
| CN113293116A (en) * | 2021-07-10 | 2021-08-24 | 西南林业大学 | Bacillus bacteria with phosphate solubilizing capability and application thereof |
| CN114105409A (en) * | 2021-11-19 | 2022-03-01 | 苏州中晟环境修复有限公司 | Method for treating antimony in underground water polluted by printing and dyeing wastewater |
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| WO2025027461A1 (en) * | 2023-07-28 | 2025-02-06 | Intermag Spółka Z Ograniczoną Odpowiedzialnością | Bacterial strains of bacillus amyloliquefaciens species and applicaiton of strains bacillus amyloliquefaciens species in plant cultivation |
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