CN103708863B - Rural organic wastes piles rotten fermentation process - Google Patents
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Abstract
The invention discloses rural organic wastes and pile rotten fermentation process.This rural organic wastes piles rotten fermentation process, comprise agricultural crop straw, organic composition that becomes thoroughly decomposed in livestock and poultry cultivation ight soil and rural area solid life refuse carries out being mixed to get the rotten fermentation raw material of heap, in the rotten fermentation raw material of described heap, add organic material composting microbial inoculum obtain heap body material, described heap body material is made heap body to carry out first time fermentation and obtain for the first time fermentation heap body material, second time fermentation heap body material is obtained by carrying out second time fermentation after described first time fermentation heap body material turning, fertilizer is obtained by carrying out third time fermentation after the turning of described second time fermentation heap body material.
Description
Technical field
The present invention relates to a kind of rural organic wastes and pile rotten fermentation process.
Background technology
Current due to dealing with improperly rural organic wastes such as the organic compositions that becomes thoroughly decomposed (the residual body of rubbish from cooking, melon and fruit peel and vegetables) in agricultural crop straw, livestock and poultry cultivation ight soil, rural area solid life refuse, the problem of environmental pollution caused is very serious.How these rural organic wastes are effectively processed, alleviate its impact on environment, become a problem demanding prompt solution.
Summary of the invention
It is simple and easy to do that technical problem to be solved by this invention is to provide a kind of zymotechnique, and the rural organic wastes being very suitable for applying in Rural areas piles rotten fermentation process.
Rural organic wastes provided by the present invention piles rotten fermentation process, comprise agricultural crop straw, organic composition that becomes thoroughly decomposed in livestock and poultry cultivation ight soil and rural area solid life refuse carries out being mixed to get the rotten fermentation raw material of heap, in the rotten fermentation raw material of described heap, add organic material composting microbial inoculum obtain heap body material, described heap body material is made heap body to carry out first time fermentation and obtain for the first time fermentation heap body material, second time fermentation heap body material is obtained by carrying out second time fermentation after described first time fermentation heap body material turning, fertilizer is obtained by carrying out third time fermentation after the turning of described second time fermentation heap body material.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and organic the becoming thoroughly decomposed in the solid life refuse of described rural area becomes the mixture of the residual body of vegetables, melon and fruit peel and rubbish from cooking.
Above-mentioned rural organic wastes is piled in rotten fermentation process, the mass ratio of the organic composition that becomes thoroughly decomposed in described agricultural crop straw, described livestock and poultry cultivation ight soil and described rural area solid life refuse can be 1:(1.5-2.5): (0.7-2.5), wherein, the quality of described agricultural crop straw in water content for 15%, the quality of described livestock and poultry cultivation ight soil in water content 30%, the quality of the organic composition that becomes thoroughly decomposed in the solid life refuse of described rural area in water content for 45%.
In the specific embodiment of the present invention, the mass ratio of the organic composition that becomes thoroughly decomposed in described agricultural crop straw, described livestock and poultry cultivation ight soil and described rural area solid life refuse is 1:2.5:1.5,3:5:2 or 1:1.5:2.5.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and the water content of described heap body material can be 55%-60%(as 60%).
In an embodiment of the invention, described agricultural crop straw is maize straw, described livestock and poultry cultivation ight soil is cow dung, and the organic composition that becomes thoroughly decomposed in the solid life refuse of described rural area is mixed according to the mass ratio of 1:2:2 by the residual body of vegetables, melon and fruit peel and rubbish from cooking.Wherein, the residual body of vegetables is Collina and discarded Chinese cabbage leaf, and melon and fruit peel is Watermelon rind, and rubbish from cooking is leftovers and leftovers; The quality of the residual body of vegetables, melon and fruit peel and rubbish from cooking with 45% water content meter.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and described heap body can be rectangular parallelepiped, and the length of described heap body is 6 meters, and wide is 3 meters, and height can be 1.4 meters-1.6 meters (as 1.5 meters); And/or,
The fermentation of described first time, the fermentation of described second time, the fermentation of described third time all temperature be 20-35 DEG C (as 30-35 DEG C), relative humidity is that 50%-80%(is as 60%) environment in carry out fermentation 7 days.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and the activeconstituents of described organic material composting microbial inoculum is made up of viride and yeast saccharomyces cerevisiae.
Above-mentioned rural organic wastes is piled in rotten fermentation process, described viride is numbered ACCC30206 China Committee for Culture Collection of Microorganisms's agricultural microorganism center, and described yeast saccharomyces cerevisiae is numbered ACCC20065 China Committee for Culture Collection of Microorganisms's agricultural microorganism center.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and in described organic material composting microbial inoculum, colony-forming unit (cfu) the number ratio of described viride and described yeast saccharomyces cerevisiae can be (1-2): (1-2), as 1:1.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and viride described in described organic material composting microbial inoculum and described yeast saccharomyces cerevisiae can exist with the form of the fermented liquid of viable cell, viable cell by cultivating, the filtrate of cell culture or the mixture of cell and filtrate.The formulation of described microbial inoculum can be multiple formulation, as liquor, emulsion, suspension agent, pulvis, granule, wettable powder or water dispersible granules.
Above-mentioned rural organic wastes is piled in rotten fermentation process, and the proportioning of the rotten fermentation raw material of described heap and described organic material composting microbial inoculum is that to add total thalline content in every kilogram of rotten fermentation raw material of described heap be 5 × 10
9the described organic material composting microbial inoculum of cfu.
Above-mentioned rural organic wastes is piled rotten fermentation process preparing the application in fertilizer and is also belonged to protection scope of the present invention.
Above-mentioned rural organic wastes is piled fertilizer prepared by rotten fermentation process improving the application in cultivated plant output and is also belonged to protection scope of the present invention.
The invention provides a kind of method of raising cultivated plant output specifically.
The method of raising cultivated plant output provided by the present invention, comprises and in the soil of described cultivated plant, to apply above-mentioned rural organic wastes pile fertilizer prepared by rotten fermentation process, improve the output of described cultivated plant.
In the method for above-mentioned raising cultivated plant output, described raising cultivated plant output can be and improves cucumber yield (cucumber fruits output) or improve yield of hot pepper (pepper fruit output).
In the method for above-mentioned raising cultivated plant output, when cultivated plant be cucumber or capsicum time, the consumption of described fertilizer is the 10 grams of described fertilizers of cultivated plant described in every strain.
Experiment proves, rural organic wastes of the present invention piles organic fertilizer prepared by rotten fermentation process all has significant effect of increasing production to cucumber and green pepper, and cucumber production promoting can be made to be 21.98%, and green pepper can be made to increase production 19.71%.It is the effective way of it being carried out to recycling that rural organic wastes carries out piling rotten fermentation by the present invention, and this zymotechnique is simple and easy to do, is very suitable for applying in Rural areas.Reasonably rural organic wastes is carried out recycling, both can preserve the ecological environment, and turn improve economic benefit, be conducive to realizing the recycle of countryside wastes and the Sustainable development of agricultural.Rural organic wastes of the present invention piles rotten fermentation process as a kind of green technology, has Ecological Sustainability.The present invention adopts heap rotten zymotechnique that rural organic wastes is carried out recycling, both protects ecotope, and turn improves economic benefit, and had great practical value.
Embodiment
Below in conjunction with embodiment, the present invention is further described in detail, the embodiment provided only in order to illustrate the present invention, instead of in order to limit the scope of the invention.Experimental technique in following embodiment, if no special instructions, is ordinary method.Material used in following embodiment, reagent etc., if no special instructions, all can obtain from commercial channels.
Viride (Trichodermaviride) ACCC30206 used in following embodiment and yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 was all concealed in China Committee for Culture Collection of Microorganisms's agricultural microorganism center and (is called for short ACCC before the applying date of the application, address: No.12 ,zhongguancun south street,Haidian District, Beijing, INST OF AGRICULTURAL RESOURCES, postcode 100081), viride (Trichodermaviride) ACCC30206 and yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 are July 26 nineteen ninety collection day, from collection, the public can obtain this two bacterial strains from China Committee for Culture Collection of Microorganisms's agricultural microorganism center.
In following embodiment, full nitrogen, full phosphorus, the full nutrient content such as potassium, organic matter of all samples detects according to organic fertilizer standard NY525-2012, and total nutrient content refers to full nitrogen, full phosphorus, full potassium content sum.
Cucumber variety in following embodiment is match storehouse, and green pepper kind is red Susan (Li Shigui, Wang Fei, Gu Jingang, Zhu Changxiong.The application of microbiobacterial agent in agricultural wastes compost maturity process and field test effect thereof.JOURNAL OF MICROBIOLOGY, 2011,31(6): 62-65.), provide by Vegetable & Flower Inst., Chinese Academy of Agriculture Science, the public can obtain from Chinese Academy of Agricultural Sciences's agricultural resource and agricultural regionalization institute, and this biomaterial related experiment of the present invention of only attaching most importance to again is used, not can be used as other purposes and uses.
The preparation of embodiment 1, organic material composting microbial inoculum
Viride (Trichodermaviride) ACCC30206 is seeded in PDA medium slant, yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 is seeded in GPYA medium slant, be placed in 28 DEG C of incubator activation culture 2-3 days, obtain yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 of viride (Trichodermaviride) ACCC30206 and the activation activated.
Viride (Trichodermaviride) ACCC30206 of activation is accessed yeast saccharomyces cerevisiae (Saccharomycescerevisiae) the ACCC20065 access GPY substratum of PD substratum, activation, all at 28 DEG C, 200r/min shaking culture 3 days, obtains viride (Trichodermaviride) ACCC30206 fermented liquid (5 × 10 respectively
9and yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 fermented liquid (5 × 10 cfu/ml)
9cfu/ml).Viride (Trichodermaviride) ACCC30206 fermented liquid and yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 fermented liquid are carried out being mixed to get organic material composting microbial inoculum according to colony-forming unit (cfu) the number ratio of 1:1.In this organic material composting microbial inoculum, the content of viride (Trichodermaviride) ACCC30206 is 2.5 × 10
9the content of cfu/ml, yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 is 2.5 × 10
9cfu/ml.
Wherein, the preparation method of substratum is as follows:
PD substratum: the potato that potato 200g(removes the peel is cut into small pieces, boiled and crossed elimination filtrate in 30 minutes), glucose 20g, be settled to 1000ml with distilled water, 121 DEG C of vapor sterilization 20min.
PDA substratum: the potato that potato 200g(removes the peel is cut into small pieces, boiled and crossed elimination filtrate in 30 minutes), glucose 20g, agar 18-20g, is settled to 1000ml with distilled water, 121 DEG C of vapor sterilization 20min.
GPY substratum: glucose 40g, peptone 5g, yeast extract paste 5g, be settled to 1000ml with distilled water, 121 DEG C of vapor sterilization 20min.
GPYA substratum: glucose 40g, peptone 5g, yeast extract paste 5g, agar 18-20g, be settled to 1000ml with distilled water, 121 DEG C of vapor sterilization 20min.
Embodiment 2, utilizing the organic material composting microbial inoculum of embodiment 1, with the organic composition that becomes thoroughly decomposed in agricultural crop straw, livestock and poultry cultivation ight soil and rural area solid life refuse for piling rotten fermentation raw material, adopting three forms to pile rotten fermentation for organic fertilizer
1, the preparation of rotten fermentation raw material is piled
Organic composition that becomes thoroughly decomposed in the rural area solid life refuse adopted in this step is mixed according to the mass ratio of 1:2:2 by the residual body of vegetables, melon and fruit peel and rubbish from cooking.Wherein, the residual body of vegetables is Collina and discarded Chinese cabbage leaf, and melon and fruit peel is Watermelon rind, and rubbish from cooking is leftovers and leftovers; The quality of the residual body of vegetables, melon and fruit peel and rubbish from cooking with 45% water content meter.
This step maize straw and organic in the solid life refuse of rural area are become thoroughly decomposed into cut into length be the fritter of 2.0cm after and cow dung be mixed with three kinds of rotten fermentation raw materials of heap according to different ratio: pile rotten fermentation raw material A, pile rotten fermentation raw material B and pile rotten fermentation raw material C.These three kinds are piled rotten fermentation raw material maize straw used, cow dung is all identical with the organic composition that becomes thoroughly decomposed in the solid life refuse of rural area.Wherein, pile rotten fermentation raw material A the organic composition that becomes thoroughly decomposed in maize straw, cow dung and rural area solid life refuse is mixed to get according to the mass ratio of 1:2.5:1.5.Pile rotten fermentation raw material B the organic composition that becomes thoroughly decomposed in maize straw, cow dung and rural area solid life refuse is mixed to get according to the mass ratio of 3:5:2.Pile rotten fermentation raw material C the organic composition that becomes thoroughly decomposed in maize straw, cow dung and rural area solid life refuse is mixed to get according to the mass ratio of 1:1.5:2.5.
Wherein, the water content of above-mentioned maize straw is 15%, and the water content of cow dung is 30%, and the water content of the organic composition that becomes thoroughly decomposed in the solid life refuse of rural area is 45%.The nutrient content of three kinds of rotten raw materials of heap is as shown in table 1.
The nutrient content (in butt) of table 1, three kinds of rotten raw materials of heap
2, the preparation of body material is piled
By rotten for heap fermentation raw material A, pile rotten fermentation raw material B and pile rotten fermentation raw material C and make heap body material simultaneously.
The preparation of 2.1 heap body material A
Adding total thalline content according to every kilogram of rotten fermentation raw material A of heap is 5 × 10
9the thalline content of cfu(and viride (Trichodermaviride) ACCC30206 and the thalline content of yeast saccharomyces cerevisiae (Saccharomycescerevisiae) ACCC20065 are respectively 2.5 × 10
9the proportioning of the organic material composting microbial inoculum of embodiment 1 cfu), the organic material composting microbial inoculum adding embodiment 1 in the rotten fermentation raw material A of heap obtains heap body material A.
The preparation of 2.2 heap body material B
Replace with except the rotten fermentation raw material B of heap except by rotten for the heap of 2.1 fermentation raw material A, all the other are identical.
The preparation of 2.3 heap body material C
Replace with except the rotten fermentation raw material C of heap except by rotten for the heap of 2.1 fermentation raw material A, all the other are identical.
3, heap body material is made heap body to carry out the rotten fermentation of three forms heaps and obtain organic fertilizer
The rotten fermentation of heap is carried out in fermentation cabin, this fermentation cabin comprises Cang Ding, at the bottom of bulkhead and storehouse, perpendicular to arranging multiple lattice wall at the bottom of storehouse at the bottom of storehouse, fermentation cabin lattice wall is divided into 9 lattice by volume, namely described fermentation cabin is divided into 3 three lattice groups by lattice wall, each three lattice groups are made up of adjacent three lattice, the ventilation slot of twice length × wide × height=6m × 0.15m × 0.13m is longitudinally evenly distributed under the storehouse of every lattice, per pass ventilation slot is laid stainless-steel sheet with holes a piece, length × wide × thick=6m × 0.19m × 0.003m of every block stainless-steel sheet, it is that the ventilating pit of 0.012m is beneficial to ventilated that every block stainless-steel sheet is evenly distributed 400 diameters, after stainless-steel sheet completed by ventilation slot, steel plate top is just concordant with at the bottom of storehouse.Three adjacent lattice are three lattice groups, and this fermentation cabin is divided into 3 three lattice groups, are respectively three lattice group A, three lattice group B and three lattice group C.
Prepare organic fertilizer A, organic fertilizer B and organic fertilizer C by the following method simultaneously.
The preparation of 3.1 organic fertilizer A
Add water in the heap body material A of 2.1 preparations and the water content of heap body material A is all adjusted to 60%, heap body material A is made the heap body of length × wide × height=6m × 3m × 1.5m at first lattice of three lattice group A, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain first time fermentation heap body material A, the second lattice first time fermentation heap body material A overturning being entered three lattice group A make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain second time fermentation heap body material A, the 3rd lattice overturning of second time fermentation heap body material A being entered three lattice group A make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain organic fertilizer A.
The preparation of 3.2 organic fertilizer B
Replace with except B except by A, all the other are completely with 3.1.Concrete grammar is as follows: adding water in the heap body material B of 2.2 preparations is all adjusted to 60% by the water content of heap body material B, heap body material B is made the heap body of length × wide × height=6m × 3m × 1.5m at first lattice of three lattice group B, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain first time fermentation heap body material B, the second lattice first time fermentation heap body material B overturning being entered three lattice group B make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain second time fermentation heap body material B, the 3rd lattice second time fermentation heap body material B overturning being entered three lattice group B make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is that in the environment of 60%, standing for fermentation obtains organic fertilizer B in 7 days.
The preparation of 3.3 organic fertilizer C
Replace with except C except by A, all the other are completely with 3.1.Concrete grammar is as follows: adding water in the heap body material C of 2.3 preparations is all adjusted to 60% by the water content of heap body material C, heap body material C is made the heap body of length × wide × height=6m × 3m × 1.5m at first lattice of three lattice group C, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain first time fermentation heap body material C, the second lattice first time fermentation heap body material C overturning being entered three lattice group C make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain second time fermentation heap body material C, the 3rd lattice second time fermentation heap body material C overturning being entered three lattice group C make the heap body of length × wide × height=6m × 3m × 1.5m, be 30-35 DEG C in temperature, relative humidity is standing for fermentation 7 days in the environment of 60%, obtain organic fertilizer C.
4, results and analysis
The nutrient content of sample before and after 4.1 heap corruption fermentations
As shown in table 2, organic fertilizer A is compared with heap body material A, and content of tatal phosphorus significantly increases, and amplification is 6.79%; And organic, full nitrogen and full potassium content decrease, the range of decrease is respectively 6.26%, 4.35% and 5.23%; But total nutrient content then increases to some extent.Organic fertilizer B is compared with heap body material B, and content of tatal phosphorus also significantly increases, and amplification is 5.41%; And organic, full nitrogen and full potassium content decrease, the range of decrease is respectively 4.95%, 4.85% and 4.38%; But total nutrient content has increased slightly.Organic fertilizer C is compared with heap body material C, and content of tatal phosphorus also significantly increases, and amplification is 5.34%; And organic, full nitrogen and full potassium content decrease, the range of decrease is respectively 4.20%, 4.40% and 4.61%; But total nutrient content slightly increases.Result shows, heap body material is conducive to saving from damage of nutrient after the rotten fermentation of three form heaps.
The nutrient content (in butt) of sample before and after the rotten fermentation of table 2, heap
| Sample | Organic % | Full nitrogen (N) % | Full phosphorus (P) % | Full potassium (K) % | Total nutrient % |
| Heap body material A | 52.6 | 1.84 | 3.24 | 1.53 | 6.61 |
| Organic fertilizer A | 49.5 | 1.76 | 3.46 | 1.45 | 6.67 |
| Heap body material B | 50.9 | 1.73 | 3.14 | 1.43 | 6.30 |
| Organic fertilizer B | 48.5 | 1.65 | 3.31 | 1.37 | 6.33 |
| Heap body material C | 47.1 | 1.66 | 2.81 | 1.59 | 6.06 |
| Organic fertilizer C | 45.2 | 1.59 | 2.96 | 1.52 | 6.07 |
The field fertilizer efficiency experiment of 4.2 organic fertilizer
Field test is carried out at Chinese Academy of Agricultural Sciences's Langfang Experimental Base, and the cucumber variety of cultivation is match storehouse, and green pepper kind is red Susan.
Cucumber cultivation experiment is identical with the experimental design method of green pepper cultivation experiments, all as follows: experiment adopts randomized block design, 3 iterons are set, each iteron arranges 4 communities at random, is respectively CK treatment zone, organic fertilizer A treatment zone, organic fertilizer B treatment zone, organic fertilizer C treatment zone.The area of each community is 30m
2.
Except spreading manuer in holes except the kind difference of fertilizer in soil, other field management of each process is all identical.Contrast organic fertilizer is for being 30-35 DEG C by heap body material A in temperature, relative humidity is leave standstill spontaneous fermentation turning after 7 days in the environment of 60%, be 30-35 DEG C in temperature again, relative humidity is leave standstill spontaneous fermentation turning after 7 days in the environment of 60%, be 30-35 DEG C in temperature again, relative humidity is leave standstill the organic fertilizer that spontaneous fermentation obtains after 7 days in the environment of 60%.In each community respectively when transplanting, earthing field planting again after fertilizer 10 grams of spreading manuer in holes around every vegetable seedling rhizosphere.Wherein, CK treatment zone is contrast, and the fertilizer executed is contrast organic fertilizer; The fertilizer that organic fertilizer A executes treatment zone is organic fertilizer A; The fertilizer that organic fertilizer B executes treatment zone is organic fertilizer B; The fertilizer that organic fertilizer C executes treatment zone is organic fertilizer C.Investigate the output (abbreviation cucumber yield) of cucumber fruits in the harvesting time of cucumber, investigate the output (abbreviation yield of hot pepper) of pepper fruit in the harvesting time of capsicum.Significance of difference analysis is carried out with t-Test.
Result shows that organic fertilizer A, organic fertilizer B and organic fertilizer C are to the obvious effect of increasing production of cucumber and green pepper, and organic fertilizer A is 21.98%(table 3 to the effect of increasing production of cucumber compared with contrast organic fertilizer), be 19.71%(table 4 to the effect of increasing production of green pepper); Organic fertilizer B is 16.34%(table 3 to the effect of increasing production of cucumber), be 14.15%(table 4 to the effect of increasing production of green pepper); Organic fertilizer C is 15.42%(table 3 to the effect of increasing production of cucumber), be 13.35%(table 4 to the effect of increasing production of green pepper).Organic fertilizer A to the obvious effect of increasing production of cucumber and green pepper higher than organic fertilizer B and organic fertilizer C, organic fertilizer B and organic fertilizer C to the effect of increasing production of cucumber and green pepper without significant difference.
Effect of increasing production to cucumber after the rotten fermentation of table 3, countryside wastes heap
| Process | Cell production (kg/ community) | Effect of increasing production (%) | The significance of difference |
| Organic fertilizer A | 106.0 | 21.98 | C |
| Organic fertilizer B | 101.1 | 16.34 | B |
| Organic fertilizer C | 100.3 | 15.42 | B |
| CK | 86.9 | / | A |
Note: in table, data are mean value, between the process that in the significance of difference, letter is different, there were significant differences (P < 0.05), without significant difference (P > 0.05) between the process that in the significance of difference, letter is identical.
After the rotten fermentation of table 4, countryside wastes heap, sample is to the effect of increasing production of green pepper
| Process | Cell production (kg/ community) | Effect of increasing production (%) | The significance of difference |
| Organic fertilizer A | 75.3 | 19.71 | C |
| Organic fertilizer B | 71.8 | 14.15 | B |
| Organic fertilizer C | 71.3 | 13.35 | B |
| CK | 62.9 | / | A |
Note: in table, data are mean value, between the process that in the significance of difference, letter is different, there were significant differences (P < 0.05), without significant difference (P > 0.05) between the process that in the significance of difference, letter is identical.
Claims (7)
1. rural organic wastes piles rotten fermentation process, comprise agricultural crop straw, organic composition that becomes thoroughly decomposed in livestock and poultry cultivation ight soil and rural area solid life refuse carries out being mixed to get the rotten fermentation raw material of heap, in the rotten fermentation raw material of described heap, add organic material composting microbial inoculum obtain heap body material, described heap body material is made heap body to carry out first time fermentation and obtain for the first time fermentation heap body material, second time fermentation heap body material is obtained by carrying out second time fermentation after described first time fermentation heap body material turning, fertilizer is obtained by carrying out third time fermentation after the turning of described second time fermentation heap body material,
The activeconstituents of described organic material composting microbial inoculum is made up of viride and yeast saccharomyces cerevisiae;
Described viride is numbered ACCC30206 China Committee for Culture Collection of Microorganisms's agricultural microorganism center, and described yeast saccharomyces cerevisiae is numbered ACCC20065 China Committee for Culture Collection of Microorganisms's agricultural microorganism center; The mass ratio of the organic composition that becomes thoroughly decomposed in described agricultural crop straw, described livestock and poultry cultivation ight soil and described rural area solid life refuse is 1:(1.5-2.5): (0.7-2.5), wherein, the quality of described agricultural crop straw in water content for 15%, the quality of described livestock and poultry cultivation ight soil in water content 30%, the quality of the organic composition that becomes thoroughly decomposed in the solid life refuse of described rural area in water content for 45%;
Colony-forming unit (cfu) number of described viride and described yeast saccharomyces cerevisiae is than being (1-2): (1-2).
2. rural organic wastes according to claim 1 piles rotten fermentation process, it is characterized in that: the mass ratio of the organic composition that becomes thoroughly decomposed in described agricultural crop straw, described livestock and poultry cultivation ight soil and described rural area solid life refuse is 1:2.5:1.5 or 1:1.5:2.5.
3. method according to claim 1 and 2, is characterized in that: described heap body is rectangular parallelepiped, and the length of described heap body is 6 meters, and wide is 3 meters, and height is 1.4 meters-1.6 meters; And/or,
The fermentation of described first time, the fermentation of described second time, the fermentation of described third time all temperature be 20-35 DEG C, relative humidity is carry out fermentation in the environment of 50%-80% 7 days.
4. method according to claim 1 and 2, is characterized in that: in described organic material composting microbial inoculum, and the number of colony forming units of described viride and described yeast saccharomyces cerevisiae is than being 1:1.
5. method according to claim 1 and 2, is characterized in that: the proportioning of the rotten fermentation raw material of described heap and described organic material composting microbial inoculum is that to add total thalline content in every kilogram of rotten fermentation raw material of described heap be 5 × 10
9the described organic material composting microbial inoculum of cfu.
6. in claim 1-5, arbitrary described rural organic wastes piles fertilizer prepared by rotten fermentation process.
7. improve the method for cultivated plant output, comprise and apply fertilizer according to claim 6 in the soil of described cultivated plant, improve the output of described cultivated plant.
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| CN105646035A (en) * | 2015-12-22 | 2016-06-08 | 成都新柯力化工科技有限公司 | Method for preparing water-soluble ecological organic carbon fertilizer by using plant stalks |
| CN105753524A (en) * | 2016-01-25 | 2016-07-13 | 南江县万事康生物科技有限公司 | Organic fertilizer and preparation method thereof |
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| CN106631212A (en) * | 2017-01-03 | 2017-05-10 | 西北民族大学 | Method of using planting and breeding wastes in vegetable production areas to produce organic fertilizers |
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