CN103843974A - Compound microecologics and application thereof - Google Patents

Compound microecologics and application thereof Download PDF

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CN103843974A
CN103843974A CN201410112422.8A CN201410112422A CN103843974A CN 103843974 A CN103843974 A CN 103843974A CN 201410112422 A CN201410112422 A CN 201410112422A CN 103843974 A CN103843974 A CN 103843974A
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nitrogen
phosphorus
treatment group
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bacillus subtilis
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范寰
张克强
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Agro Environmental Protection Institute Ministry of Agriculture
Tianjin Institute of Animal Husbandry and Veterinary Science
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Tianjin Institute of Animal Husbandry and Veterinary Science
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Abstract

本发明公开了一种复合微生态制剂,它是由枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌按重量份数1:1:1的原料组成。本发明通过对动物益生菌进行组合优化,在不降低生长性能的前提下,筛选一种能有效降低保育猪粪便中氮、磷含量的优化益生菌组合,为利用益生菌有效降低畜禽业带来的环境污染提供科学依据。实验结果表明:复合微生态制剂能够有效提高氮、磷的表观消化率,减少粪便中氮、磷含量,降低畜禽粪便对环境的污染。The invention discloses a composite micro-ecological preparation, which is composed of raw materials of Bacillus subtilis, Saccharomyces cerevisiae and Lactobacillus plantarum in parts by weight of 1:1:1. The present invention optimizes the combination of animal probiotics and screens an optimized combination of probiotics that can effectively reduce the content of nitrogen and phosphorus in the manure of nursery pigs without reducing the growth performance. Provide scientific basis for future environmental pollution. The experimental results show that the compound microecological preparation can effectively improve the apparent digestibility of nitrogen and phosphorus, reduce the content of nitrogen and phosphorus in manure, and reduce the pollution of livestock and poultry manure to the environment.

Description

一种复合微生态制剂及其应用A kind of compound probiotics and its application

技术领域 technical field

本发明属于复合微生态制剂应用技术领域,涉及不同的益生菌组合对保育猪粪污氮、磷减排的影响研究,更具体的说是一种复合微生态制剂及其应用。 The invention belongs to the technical field of application of compound microecological preparations, and relates to the research on the influence of different combinations of probiotics on the reduction of nitrogen and phosphorus emissions from nursery pig manure, and more specifically relates to a compound microecological preparation and its application.

背景技术 Background technique

近年来,随着规模化畜禽养殖业的高速发展,导致环境污染问题日益显现,并受到社会的广泛关注。降低畜禽养殖业带来的环境污染,发展生态环保型畜牧经济,已成为了保持畜牧业可持续发展的关键因子。张永勇(2008)等在断奶仔猪日粮中添加芽孢菌、乳酸菌、双歧杆菌等组成的复合益生素,结果发现添加0.05%的复合益生素,可以显著提高仔猪的日采食量、粗蛋白消化率和血清免疫球蛋白水平。宁豫昌(2009)等研究表明,在断奶仔猪基础日粮中添加8%的微生态制剂,添加微生态制剂组与对照组相比粗蛋白消化率分别提高了7.32% 和11.47%,差异有统计学意义( P<0.05) 。目前较多研究多集中于粗蛋白和粗纤维消化率方面的研究,而对氮、磷排放对环境方面影响的研究尚未开展。本发明旨在通过对动物益生菌进行组合优化,在不降低生长性能的前提下,筛选一种能有效降低保育猪粪便中氮、磷含量的优化益生菌组合,为利用益生菌有效降低畜禽业带来的环境污染提供科学依据。 In recent years, with the rapid development of large-scale livestock and poultry breeding industry, the problem of environmental pollution has become increasingly apparent, and has attracted widespread attention from the society. Reducing the environmental pollution caused by livestock and poultry farming and developing an eco-friendly animal husbandry economy have become the key factors to maintain the sustainable development of animal husbandry. Zhang Yongyong (2008) added compound probiotics composed of spores, lactic acid bacteria, and bifidobacteria to the diet of weaned piglets, and found that adding 0.05% of compound probiotics can significantly improve the daily feed intake and crude protein digestion of piglets. rate and serum immunoglobulin levels. Ning Yuchang (2009) and other studies have shown that adding 8% probiotics to the basic diet of weaned piglets, the crude protein digestibility of the probiotics group increased by 7.32% and 11.47% compared with the control group, the difference was Statistically significant (P<0.05). At present, many studies focus on the digestibility of crude protein and crude fiber, but the research on the impact of nitrogen and phosphorus discharge on the environment has not yet been carried out. The present invention aims to select an optimized probiotic combination that can effectively reduce the nitrogen and phosphorus content in nursery pig manure by optimizing the combination of animal probiotics without reducing the growth performance. Provide scientific basis for environmental pollution caused by industry.

发明内容 Contents of the invention

本发明公开了一种复合微生态制剂,其特征在于它是由枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌按重量份数1:1:1的原料组成。 其中枯草芽孢杆菌用量为0.2-0.9%(w/w)、酿酒酵母菌用量0.2-0.9%(w/w)、植物乳杆菌用量0.2-0.9%(w/w)。 The invention discloses a compound micro-ecological preparation, which is characterized in that it is composed of raw materials of Bacillus subtilis, Saccharomyces cerevisiae and Lactobacillus plantarum in parts by weight of 1:1:1. Among them, the dosage of Bacillus subtilis is 0.2-0.9% (w/w), the dosage of Saccharomyces cerevisiae is 0.2-0.9% (w/w), and the dosage of Lactobacillus plantarum is 0.2-0.9% (w/w).

本发明所述枯草芽孢杆菌活菌数为(1.0×1010cfu/g)、 The viable count of Bacillus subtilis in the present invention is (1.0×10 10 cfu/g),

酿酒酵母菌活菌数为(1.0×1010cfu/g)、 The viable count of Saccharomyces cerevisiae is (1.0×10 10 cfu/g),

植物乳杆菌活菌数为(1.0×1010cfu/g)。 The viable count of Lactobacillus plantarum was (1.0×10 10 cfu/g).

本发明进一步公开了复合微生态制剂在降低畜禽粪便对环境污染方面的应用。特别是在降低保育猪粪污氮、磷含量方面的应用。本发明所述降低保育猪粪污氮磷含量指的是有效提高氮、磷的表观消化率,减少粪便中氮、磷含量。 The invention further discloses the application of the compound microecological preparation in reducing environmental pollution caused by livestock and poultry manure. Especially in the application of reducing the nitrogen and phosphorus content of nursery pig manure. Reducing the nitrogen and phosphorus content of nursery pig manure in the present invention refers to effectively improving the apparent digestibility of nitrogen and phosphorus, and reducing the nitrogen and phosphorus content in manure.

枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌发酵生产方法(按菌种保藏中心提供的培养基配方和培养条件,培养到所需的活菌数即可)。 Fermentation production method of Bacillus subtilis, Saccharomyces cerevisiae, and Lactobacillus plantarum (according to the medium formula and culture conditions provided by the strain collection center, it is enough to cultivate to the required number of viable bacteria).

本发明更加详细的试验及实验结果如下:    The more detailed test and experimental results of the present invention are as follows:

1        材料与方法 1 Materials and methods

1.1  试验材料   1.1 Test material

本试验所使用的枯草芽孢杆菌来源: The source of Bacillus subtilis used in this test:

枯草芽孢杆菌ACCC11025,用量0.2-0.9%; Bacillus subtilis ACCC11025, dosage 0.2-0.9%;

酿酒酵母菌CICC1421,用量0.2-0.9%; Saccharomyces cerevisiae CICC1421, dosage 0.2-0.9%;

植物乳杆菌ACCC11118,用量0.2-0.9%; Lactobacillus plantarum ACCC11118, dosage 0.2-0.9%;

上述益生菌均有市售,然后在实验室保存。 The above-mentioned probiotics are commercially available and then preserved in the laboratory.

1.2  试验动物与试验设计: 1.2 Experimental animals and experimental design:

试验采用单因素试验设计,选取日龄接近,体重35kg(±2kg)的保育猪16头,随机分为四个处理组,每个处理组4个重复。第一组对照组饲喂基础日粮,第二组处理组1在基础日粮的基础上添加0.5%的枯草芽孢杆菌活菌数(1.0×1010cfu/g),第三组处理组2在基础日粮的基础上添加0.5%的枯草芽孢杆菌和0.5%的酿酒酵母菌活菌数(1.0×1010cfu/g)、第四组处理组3在基础日粮的基础上添加0.5%的枯草芽孢杆菌、0.5%的酿酒酵母菌和0.5%的植物乳杆菌活菌数(1.0×1010cfu/g)。基础日粮成分及营养水平见表1。 The experiment adopts a single factor experimental design, selects 16 nursery pigs of similar age and body weight of 35kg (± 2kg), and randomly divides them into four treatment groups, with 4 repetitions in each treatment group. The first group of control group was fed with basal diet, the second group of treatment group 1 added 0.5% live bacteria of Bacillus subtilis (1.0×10 10 cfu/g) on the basis of the basal diet, and the third group of treatment group 2 Add 0.5% of Bacillus subtilis and 0.5% of Saccharomyces cerevisiae live bacteria (1.0×10 10 cfu/g) on the basis of the basic diet, and add 0.5% of the fourth treatment group 3 on the basis of the basic diet Bacillus subtilis, 0.5% Saccharomyces cerevisiae and 0.5% Lactobacillus plantarum live bacteria (1.0×10 10 cfu/g). The composition and nutrient levels of the basal diet are shown in Table 1.

表1 基础日粮组成及营养水平 Table 1 Composition and nutritional level of basal diet

日粮组成Diet Composition 含量%content% 营养水平nutritional level 含量%content% 玉米corn 6262 消化能(MJ/kg)Digestible energy (MJ/kg) 1414 豆粕soybean meal 22twenty two 蛋白质(%)protein(%) 1919 复合预混料Compound premix 1616 钙(%)calcium(%) 0.70.7  the  the 总磷(%)Total phosphorus (%) 0.650.65  the  the 食盐(%)salt(%) 0.30.3  the  the 赖氨酸(%)Lysine (%) 1.351.35  the  the 蛋+胱氨酸(%)Egg + Cystine (%) 0.80.8  the  the 苏氨酸(%)Threonine(%) 0.870.87

1.3  饲养管理   1.3 Feeding management

试验前彻底清扫冲洗栏舍、饲料用具,预试期期间自由采食和饮水。3d预试期后,对试验猪进行饥饿24小时空腹处理,进入正式试验。试验猪采用分栏饲养,粉料饲喂,定时定点定量喂食,转天早晨回收剩余饲料,自由饮水。正试期为1d,每只试验猪在当日24小时内排粪分别独立收集,随拉随收,并及时观察16头猪的排粪及身体状况。 Thoroughly clean and rinse the stalls and feed utensils before the test, and have free access to food and water during the pre-test period. After the 3d pre-test period, the test pigs were starved for 24 hours on an empty stomach, and entered into the formal test. The experimental pigs were reared in separate pens, fed with powder, and fed regularly and quantitatively. The rest of the feed was collected the next morning, and they drank water freely. The main test period is 1 day, and the feces of each test pig are collected independently within 24 hours of the day, and the defecation and physical condition of the 16 pigs are observed in time.

1.4  指标测定 1.4 Index determination

1.4.1  间接法测氮、磷表观消化率  表观消化率的测定采用酸不溶灰分(AIA)间接法(崔宝瑚,1981;徐凤霞,2004),即内源指示剂法。计算公式如下: 1.4.1 Indirect method to measure apparent digestibility of nitrogen and phosphorus Apparent digestibility was measured by acid-insoluble ash (AIA) indirect method (Cui Baohu, 1981; Xu Fengxia, 2004), that is, endogenous indicator method. Calculated as follows:

某养分表观消化率(%)=100×[1-(A/B)×(C/D)] Apparent digestibility of a nutrient (%)=100×[1-(A/B)×(C/D)]

其中A为粪中该养分含量,B为饲料中该养分含量,C为饲料中的酸不溶灰分(AIA)含量,D为粪中酸不溶灰分含量。 Where A is the nutrient content in feces, B is the nutrient content in feed, C is the acid-insoluble ash (AIA) content in feed, and D is the acid-insoluble ash content in feces.

1.4.2  全收粪法氮、磷表观消化率(张忠远,2004)  计算公式如下: 1.4.2 Apparent digestibility of nitrogen and phosphorus in total collection of feces (Zhang Zhongyuan, 2004) The calculation formula is as follows:

某养分表观消化率(%)=100×[(A-B)/A] Apparent digestibility of a nutrient (%)=100×[(A-B)/A]

中A为食入该养分,B为粪中该养分。 A is the nutrient ingested, and B is the nutrient in the feces.

1.5  数据统计分析  试验数据采用SPSS19.0 统计软件进行统计分析, 采用One-way ANOVA 进行方差分析,LSD法结合Duncan’s法进行组间多重比较,结果均以“平均数±标准差”表示。 1.5 Statistical analysis of data The experimental data was analyzed using SPSS19.0 statistical software, and One-way ANOVA was used for analysis of variance, LSD method combined with Duncan's method for multiple comparisons between groups, and the results were expressed as "mean ± standard deviation".

2   结果与分析 2 Results and analysis

2.1 不同微生态制剂对保育猪采食量和增重的影响 2.1 Effects of different probiotics on feed intake and weight gain of nursery pigs

由表2可知, 添加不同微生态制剂对采食量没有明显的变化,差异不显著(P> 0.05);各实验组之间总增重变化不大,差异不明显(P > 0.05)。 It can be seen from Table 2 that the addition of different probiotics did not significantly change the feed intake, and the difference was not significant (P>0.05); the total weight gain among the experimental groups did not change much, and the difference was not significant (P>0.05).

表2  不同微生态制剂对保育猪采食量和增重的影响 Table 2 Effects of different probiotics on feed intake and weight gain of nursery pigs

 the 对照组control group 处理组1treatment group 1 处理组2treatment group 2 处理组3treatment group 3 采食量feed intake 1671.25±68.27a 1671.25±68.27 a 1682.00±13.74 a 1682.00±13.74 a 1651.00±50.98 a 1651.00±50.98 a 1673.75±69.87 a 1673.75±69.87 a 初始总重( kg)Initial gross weight (kg) 56.75±3.77 a 56.75±3.77 a 58.25±3.30 a 58.25±3.30 a 57.75±1.71 a 57.75±1.71 a 56.50±1.91 a 56.50±1.91 a 末总重( kg)Final gross weight (kg) 62.75±3.40 a 62.75±3.40 a 65.75±3.86 a 65.75±3.86 a 61.50±3.00 a 61.50±3.00 a 63.00±6.38 a 63.00±6.38 a 总增重( kg)Total weight gain (kg) 6.00±1.41 a 6.00±1.41 a 7.5±2.89 a 7.5±2.89 a 3.75±2.75 a 3.75±2.75 a 6.50±5.07 a 6.50± 5.07a

注: 同行数据肩注不同小写字母表示差异显著( P < 0. 05 ) Note: The different lowercase letters on the shoulders of peer data indicate significant differences ( P < 0. 05 )

2.2 不同微生态制剂对保育猪氮表观消化率的影响 2.2 Effects of different probiotics on the apparent digestibility of nitrogen in nursery pigs

由表3可知,食入氮含量由于添加的微生态制剂和采食量的不同,使得对照组、处理组1与处理组2、处理组3之间有显著差异(P<0.05);粪便中氮含量随着食入氮水平的变化有降低的趋势,以处理组3最低,差异极显著(P<0.01);AIA间接法测得处理组2、处理组3的氮表观消化率比对照组提高了58.65%、39.00%,差异极显著(P<0.01),处理组1与对照组之间差异不显著(P > 0.05);全收粪法测得处理组1、处理组2、处理组3的氮表观消化率与对照组之间提高了18.16%、8.89%、33.14%,处理组1和处理组2与对照组之间差异不显著。而处理组3与对照组之间差异极显著(P<0.01)。 It can be seen from Table 3 that the ingested nitrogen content was significantly different (P<0.05) among the control group, treatment group 1, treatment group 2, and treatment group 3 due to the difference in the added probiotics and feed intake (P<0.05); The nitrogen content tended to decrease with the change of ingested nitrogen level, and the treatment group 3 was the lowest, and the difference was extremely significant (P<0.01); the apparent digestibility of nitrogen in treatment group 2 and treatment group 3 measured by AIA indirect method was higher than that of the control group group increased by 58.65%, 39.00%, the difference was extremely significant (P<0.01), the difference between treatment group 1 and the control group was not significant (P>0.05); The nitrogen apparent digestibility of group 3 increased by 18.16%, 8.89%, and 33.14% compared with the control group, and there was no significant difference between treatment group 1 and treatment group 2 and the control group. The difference between treatment group 3 and the control group was extremely significant (P<0.01).

表3  不同微生态制剂对保育猪氮表观消化率的影响 Table 3 Effects of different probiotics on the apparent digestibility of nitrogen in nursery pigs

 the 对照组control group 处理组1treatment group 1 处理组2treatment group 2 处理组3treatment group 3 食入N含量(g/d)Ingested N content (g/d) 29.25±1.19ab 29.25± 1.19ab 29.27±0.24ab 29.27± 0.24ab 30.54±0.94a 30.54±0.94 a 28.62±1.19b 28.62± 1.19b 产粪量(g)Manure production (g) 375.25±91.54375.25±91.54 352.75±81.46352.75±81.46 408.50±33.15408.50±33.15 311.25±60.66311.25±60.66 粪中N含量(g/d)N content in feces (g/d) 16.37±2.55Aa 16.37±2.55 Aa 14.01±2.64ABab 14.01±2.64 A Abab 15.86±0.34ABa 15.86±0.34 ABa 11.80±0.88Bb 11.80±0.88 Bb AIA间接法N表观消化率(%)AIA indirect method N apparent digestibility (%) 32.82±1.28Bb 32.82±1.28 Bb 30.66±7.39Bb 30.66±7.39 Bb 52.07±4.75Aa 52.07±4.75 Aa 45.62±3.98Aa 45.62±3.98 Aa 全收粪法N的表观消化率(%)Apparent digestibility of N in total harvested manure method (%) 44.11±7.33Bb 44.11±7.33 Bb 52.12±9.00ABab 52.12± 9.00ABab 48.03±1.71ABb 48.03± 1.71ABb 58.73±3.46Aa 58.73±3.46 Aa

注: 同行数据肩注不同小写字母表示差异显著( P < 0. 05 );不同大写字母表示差异极显著( P < 0. 01 );无字母表示差异不显著( P > 0. 05 ) ,下表同。 Note: different lowercase letters in the shoulders of peer data indicate significant differences ( P < 0. 05 ); different uppercase letters indicate extremely significant differences ( P < 0. 01 ); no letters indicate insignificant differences ( P > 0. 05 ), below The table is the same.

2.3 不同微生态制剂对保育猪磷表观消化率的影响 2.3 Effects of different microecological preparations on the apparent digestibility of phosphorus in nursery pigs

由表4可知,食入磷含量由于添加的微生态制剂和采食量的不同,使得对照组与处理组3和处理组1、处理组2之间有显著差异(P<0.05);粪便中磷含量在对照组,处理组1和处理组2之间较接近,而处理组3为最低,但试验组之间差异不显著(P> 0.05);AIA间接法测得处理组2、处理组3的磷表观消化率比对照组提高了93.80%、71.46%,差异极显著(P<0.01),处理组1与对照组之间差异不显著(P > 0.05);在全收粪法中处理组1、处理组2、处理组3的磷表观消化率与对照组之间提高了24.93%、6.57%、48.99%,处理组1和处理组3与对照组之间差异极显著(P<0.01)。 It can be seen from Table 4 that due to the difference in the added probiotics and feed intake, there were significant differences (P<0.05) between the control group and treatment group 3, treatment group 1, and treatment group 2 (P<0.05); Phosphorus content in the control group, treatment group 1 and treatment group 2 was relatively close, while treatment group 3 was the lowest, but the difference between the test groups was not significant (P> 0.05); AIA indirect method measured the treatment group 2, treatment group Compared with the control group, the apparent digestibility of phosphorus in 3 increased by 93.80% and 71.46%, the difference was extremely significant (P<0.01), and the difference between treatment group 1 and the control group was not significant (P > 0.05); The apparent digestibility of phosphorus in treatment group 1, treatment group 2, and treatment group 3 increased by 24.93%, 6.57%, and 48.99% compared with the control group, and the differences between treatment group 1, treatment group 3 and the control group were extremely significant (P <0.01).

表4  不同微生态制剂对保育猪磷表观消化率的影响 Table 4 Effects of different microecological preparations on the apparent digestibility of phosphorus in nursery pigs

 the 对照组control group 处理组1treatment group 1 处理组2treatment group 2 处理组3treatment group 3 食入P含量(g/d)Ingested P content (g/d) 10.86±0.44Bc 10.86±0.44 Bc 12.62±0.10Aa 12.62±0.10 Aa 11.56±0.36Bb 11.56±0.36 Bb 10.88±0.45Bc 10.88±0.45 Bc 产粪量(g)Manure production (g) 375.25±91.54375.25±91.54 352.75±81.46352.75±81.46 408.50±33.15408.50±33.15 311.25±60.66311.25±60.66 粪中P含量(g/d)P content in feces (g/d) 7.04±0.607.04±0.60 7.07±0.657.07±0.65 7.25±0.297.25±0.29 5.18±0.465.18±0.46 AIA间接法P表观消化率(%)AIA indirect method P apparent digestibility (%) 21.62±4.70Bb 21.62±4.70 Bb 18.07±6.43Bb 18.07±6.43 Bb 41.90±8.58Aa 41.90±8.58 Aa 37.07±7.09Aa 37.07±7.09 Aa 全收粪法P的表观消化率(%)Apparent digestibility of P in the whole collection method (%) 35.17±4.65C 35.17± 4.65C 43.94±4.82B 43.94± 4.82B 37.30±1.11BC 37.30± 1.11BC 52.40±3.61A 52.40± 3.61A

3   讨论 3 Discussion

本试验结果表明,AIA间接法测定各项表观消化率中处理组2和处理组3相对于对照组和处理组1均提高,其中处理组2效果最明显,氮表观消化率提高了58.65%,磷表观消化率提高了93.80%,但处理组2与处理组3之间差异不显著;全收粪法测定各项表观消化率中处理组3效果最明显,能有效提高氮表观消化率33.14%和磷表观消化率48.99%,与其他组差异均极显著,而处理组2与对照组之间差异不显著,处理组1的氮表观消化率与对照组之间存在显著差异。 The results of this test show that the AIA indirect method measured the apparent digestibility of the treatment group 2 and the treatment group 3 compared with the control group and the treatment group 1, and the effect of the treatment group 2 was the most obvious, and the apparent digestibility of nitrogen increased by 58.65%. %, the apparent digestibility of phosphorus increased by 93.80%, but the difference between treatment group 2 and treatment group 3 was not significant; the effect of treatment group 3 was the most obvious in the determination of the apparent digestibility of the total feces method, which can effectively improve the nitrogen table The apparent digestibility of nitrogen was 33.14% and the apparent digestibility of phosphorus was 48.99%, which were significantly different from other groups, but there was no significant difference between the treatment group 2 and the control group. Significant differences.

4 小结 4 Summary

实验结果表明,处理组3即复合微生态制剂按1:1:1组成,特别是枯草芽孢杆菌+植物乳杆菌+酿酒酵母,每一种成分的用量范围为0.2-0.9%,此时效果最佳。复合微生态制剂能够有效提高氮、磷的表观消化率,减少粪便中氮、磷含量,降低畜禽粪便对环境的污染。 The experimental results show that the treatment group 3, that is, the compound probiotics is composed of 1:1:1, especially Bacillus subtilis + Lactobacillus plantarum + Saccharomyces cerevisiae, the dosage range of each component is 0.2-0.9%, and the effect is the best at this time. good. The compound microecological preparation can effectively improve the apparent digestibility of nitrogen and phosphorus, reduce the content of nitrogen and phosphorus in feces, and reduce the pollution of livestock and poultry manure to the environment.

  the

具体实施方式 Detailed ways

下面结合实施例说明本发明,这里所述实施例的方案,不限制本发明,本领域的专业人员按照本发明的精神可以对其进行改进和变化,所述的这些改进和变化都应视为在本发明的范围内,本发明的范围和实质由权利要求来限定。其中枯草芽孢杆菌、植物乳杆菌、酿酒酵母均有市售。 The present invention is illustrated below in conjunction with the examples, the scheme of the examples described here does not limit the present invention, and those skilled in the art can improve and change it according to the spirit of the present invention, and these described improvements and changes should be regarded as Within the scope of the present invention, the scope and spirit of the present invention are defined by the claims. Wherein Bacillus subtilis, Lactobacillus plantarum and Saccharomyces cerevisiae are all commercially available.

实施例1 Example 1

枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌按重量份数1:1:1的原料组成。其中所述枯草芽孢杆菌活菌数(1.0×1010cfu/g)、酿酒酵母菌活菌数为(1.0×1010cfu/g)、植物乳杆菌活菌数为(1.0×1010cfu/g)。 Bacillus subtilis, Saccharomyces cerevisiae and Lactobacillus plantarum are composed of raw materials in parts by weight of 1:1:1. Among them, the viable count of Bacillus subtilis (1.0×10 10 cfu/g), the viable count of Saccharomyces cerevisiae (1.0×10 10 cfu/g), the viable count of Lactobacillus plantarum (1.0×10 10 cfu/g) g).

    枯草芽孢杆菌用量为0.2% (w/w)、酿酒酵母菌用量0.2% (w/w)、植物乳杆菌用量0.2%(w/w)。 The dosage of Bacillus subtilis is 0.2% (w/w), the dosage of Saccharomyces cerevisiae is 0.2% (w/w), and the dosage of Lactobacillus plantarum is 0.2% (w/w).

实施例2 Example 2

枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌按重量份数1:1:1的原料组成。其中所述枯草芽孢杆菌活菌数(1.0×1010cfu/g)、酿酒酵母菌活菌数为(1.0×1010cfu/g)、植物乳杆菌活菌数为(1.0×1010cfu/g)。 Bacillus subtilis, Saccharomyces cerevisiae and Lactobacillus plantarum are composed of raw materials in parts by weight of 1:1:1. Among them, the viable count of Bacillus subtilis (1.0×10 10 cfu/g), the viable count of Saccharomyces cerevisiae (1.0×10 10 cfu/g), the viable count of Lactobacillus plantarum (1.0×10 10 cfu/g) g).

枯草芽孢杆菌用量为0.5%(w/w)、酿酒酵母菌用量0.5%(w/w)、植物乳杆菌用量0.5%(w/w)。 The dosage of Bacillus subtilis is 0.5% (w/w), the dosage of Saccharomyces cerevisiae is 0.5% (w/w), and the dosage of Lactobacillus plantarum is 0.5% (w/w).

实施例3 Example 3

枯草芽孢杆菌、酿酒酵母菌、植物乳杆菌按重量份数1:1:1的原料组成。其中所述枯草芽孢杆菌活菌数(1.0×1010cfu/g)、菌活菌数为(1.0×1010cfu/g)、植物乳杆菌活菌数为(1.0×1010cfu/g)。 Bacillus subtilis, Saccharomyces cerevisiae and Lactobacillus plantarum are composed of raw materials in parts by weight of 1:1:1. Among them, the number of live bacteria of Bacillus subtilis (1.0×10 10 cfu/g), the number of viable bacteria of Bacillus subtilis (1.0×10 10 cfu/g), and the number of viable bacteria of Lactobacillus plantarum (1.0×10 10 cfu/g) .

枯草芽孢杆菌用量为0.9%(w/w)、酿酒酵母菌用量0.9%(w/w)、植物乳杆菌用量0.9%(w/w)。 The dosage of Bacillus subtilis is 0.9% (w/w), the dosage of Saccharomyces cerevisiae is 0.9% (w/w), and the dosage of Lactobacillus plantarum is 0.9% (w/w).

Claims (5)

1. a compound micro-ecological preparation, it is characterized in that it by bacillus subtilis, S. cervisiae, Lactobacillus plantarum by weight the raw material of 1:1:1 form, wherein said bacillus subtilis viable count (1.0 × 10 10cfu/g), S. cervisiae viable count is (1.0 × 10 10cfu/g), Lactobacillus plantarum viable count is (1.0 × 10 10cfu/g).
2. compound micro-ecological preparation claimed in claim 1, wherein bacillus subtilis consumption 0.2-0.9% (w/w), S. cervisiae consumption 0.2-0.9% (w/w), Lactobacillus plantarum consumption 0.2-0.9% (w/w).
3. the application of the compound micro-ecological preparation described in claim 1 or 2 aspect reduction feces of livestock and poultry environmental pollution.
4. the application of the compound micro-ecological preparation described in claim 1 or 2 aspect the dirty the content of nitrogen and phosphorous of reduction child care pig manure.
5. application claimed in claim 4, the dirty the content of nitrogen and phosphorous of wherein said reduction child care pig manure refers to: effectively improve the apparent digestibility of nitrogen, phosphorus, reduce the content of nitrogen and phosphorous in ight soil.
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