CN104030745A - Preparation method of ginkgo residual leaf biological organic fertilizer - Google Patents
Preparation method of ginkgo residual leaf biological organic fertilizer Download PDFInfo
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Abstract
The invention relates to a preparation method of a ginkgo residual leaf biological organic fertilizer, which comprises the following steps: a. preparation of ginkgo residual leaf biological organic fertilizer: a1. selecting poultry and livestock manure, and naturally dehydrating, wherein the water content of the poultry and livestock manure is greater than 60%, and the water content after dehydration is 50%; a2. mixing the manure prepared in the step a1 with 30 wt% of ginkgo residual leaf and 0.1 wt% of microbial inoculant; a3. fermenting the mixture in the step a2, turning over the mixture, aging, drying, pulverizing and packaging to obtain the biological organic fertilizer; and b. applying 2.5kg of the fertilizer to every m<2> of field, and uniformly mixing the prepared biological organic fertilizer with the soil. The organic fertilizer with the ginkgo leaf and microbial inoculant are obviously beneficial to the plant growth and soil improvement.
Description
Technical field
The present invention relates to organic fertilizer field, relate in particular to the preparation method of the residual leaf biological organic fertilizer of a kind of ginkgo.
Background technology
Ginkgo is one of the most ancient existing plant, the distinctive plant of Ye Shi China, and the whole world utilizes the beneficiating ingredient in Ginkgo Leaf to be widely used in the fields such as medical treatment, food antiseptic, plant protection, livestock and poultry and aquaculture.But Ginkgo Leaf extracted and will abandon it at extract, become waste, caused very large waste for this reason, again may be to environment.
The preparation that in prior art, residual ginkgo leaf is applied to organic fertilizer does not also exist.
In view of above-mentioned defect, creator of the present invention has obtained this creation finally through long research and practice.
Summary of the invention
The object of the present invention is to provide the preparation method of the residual leaf biological organic fertilizer of a kind of ginkgo, in order to overcome above-mentioned technological deficiency.
For achieving the above object, the invention provides the preparation method of the residual leaf biological organic fertilizer of a kind of ginkgo, this detailed process is:
Step a, the residual leaf biological organic fertilizer of ginkgo is made;
Step a1, chooses fowl and animal excrement, and natural-dehydration; Fowl and animal excrement water content is greater than 60% in the present invention, and after dehydration, water content is 50%;
Step a2, the residual leaf of ginkgo that the ight soil that above-mentioned steps a1 is made is 30% with mass ratio, 1 ‰ microbiobacterial agent mix;
Step a3, by the fermented mixture of above-mentioned steps a2, stirring, slaking, carries out crushing packing after being dried, and makes biological organic fertilizer;
Step b, at field fertilization 2.5kg/m
2, by even to the biological organic fertilizer making and mixing with soil.
Further, in above-mentioned steps a2, be fermentation reactor system under the condition of 60 DEG C of left and right in temperature.
Further, in above-mentioned steps a2, described microbiobacterial agent is that bacterium is strong; The 60d that ferments in this step, and timing moisturizing.
Beneficial effect of the present invention is compared with prior art: in the present invention, the residual leaf of 30% ginkgo is that to add in the compost of raw material effect the most obvious, and the interpolation of microbiobacterial agent also has obvious effect for becoming thoroughly decomposed of compost.
The compost treatment of adding the residual leaf of 30% ginkgo, heat-up rate is fast, and the continuous high temperature time is long, and the time of becoming thoroughly decomposed is short.Add each processing of microbiobacterial agent, heat up very fast, the time of becoming thoroughly decomposed is short, but the continuous high temperature time is also shorter; The heap body total nitrogen content that adds 1 ‰ microbial inoculums and the residual leaf of 30% ginkgo is the highest, the large effect of microbiobacterial agent in addition of its Decomposition that promotes organonitrogen is described, the speed of response of its heap body is accelerated, accelerated the speed of becoming thoroughly decomposed, and 1 ‰ microbial bacteria dose effect is the most obvious simultaneously.
The fertilizer that adds Ginkgo Leaf and microbial inoculum has obvious benefit to the improvement of plant growth and soil.
Brief description of the drawings
Fig. 1 is the preparation method's of the residual leaf biological organic fertilizer of ginkgo of the present invention schema;
Fig. 2 is the dynamic change figure that the present invention does not add microbial inoculum heap temperature;
Fig. 3 is the dynamic change figure that the present invention adds microbial inoculum heap temperature;
Fig. 4 is the dynamic change figure that the present invention adds microbial inoculum heap body organic content;
Fig. 5 is the dynamic change that the present invention adds full N in the different treatment composting process of microbial inoculum;
Fig. 6 is the dynamic change figure that the present invention adds microbial inoculum heap body seed germination index (GI);
Fig. 7 is the affect figure of different fertilizer Different Fertilization amount of the present invention on field Aboveground Biomass of Young;
Fig. 8 a contains spirogram to the full N of plant after the present invention applies C fertilizer;
Fig. 8 b is the figure that affects that the present invention applies the full N of plant and absorbed dose after C fertilizer.
Embodiment
Below in conjunction with accompanying drawing, technical characterictic and the advantage with other above-mentioned to the present invention are described in more detail.
The making processes of the residual leaf biological organic fertilizer of ginkgo of the present invention is:
Step a, the residual leaf biological organic fertilizer of ginkgo is made;
Step a1, chooses fowl and animal excrement, and natural-dehydration; Fowl and animal excrement water content is greater than 60% in the present invention, and after dehydration, water content is 50%;
Step a2, the residual leaf of ginkgo that the ight soil that above-mentioned steps a1 is made is 30% with mass ratio, 1 ‰ microbiobacterial agent mix, and are fermentation reactor system under the condition of 60 DEG C of left and right in temperature; Wherein, described microbiobacterial agent is that bacterium is strong; The 60d that ferments in this step, and timing moisturizing;
Step a3, by the fermented mixture of above-mentioned steps a2, stirring, slaking, carries out crushing packing after being dried, and makes biological organic fertilizer.
Step b, at field fertilization 2.5kg/m
2, by even to the biological organic fertilizer making and mixing with soil.
Below by specific embodiment, said process is described.
In the present embodiment, the residual leaf of ginkgo and stalk are from Pizhou City, and the residual leaf of ginkgo is that factory extracts posterior lobe slag.Pig manure is from pig farm, farm, Sihong.Microbiobacterial agent title is that bacterium is strong.
Starting material character is as shown in table 1:
Table 1 composting material characteristic
Make according to the method described above after fertilizer compost treatment design:
(1) do not add the residual leaf compost of ginkgo of microbial inoculum:
2 processing are established in this test, the equal pig manure of bed material and stalk and a small amount of inorganic materials, and each processing all piled for the high 1.5m cone shape heap of radius 1m body (Ginkgo Leaf adds the total mass ratio of the dry weight that per-cent is bed material).
Process 1 (code GP) and add the residual leaf+pig manure+stalk of 30% ginkgo at the test initial stage
Process 2 (code P) and add stalk+pig manure (without residual leaf) at the test initial stage
(2) the residual leaf compost of ginkgo of interpolation microbial inoculum
6 processing are established in this test, the equal pig manure of bed material and stalk and a small amount of inorganic materials, each processing all piled for the high 1.5m right cylinder buttress of radius 1m shape heap body, and (Ginkgo Leaf adds the total mass ratio of the dry weight that per-cent is bed material, it is strong that microbial inoculum is elected bacterium as, the total mass ratio that microbial inoculum amount is bed material)
Process 1 (MGP1) and add 30% ginkgo residual leaf+pig manure+stalk+0.5 ‰ microbial inoculum at the test initial stage
Process 2 (MGP2) and add 30% ginkgo residual leaf+pig manure+stalk+1 ‰ microbial inoculum at the test initial stage
Process 3 (MGP3) and add 30% ginkgo residual leaf+pig manure+stalk+2 ‰ microbial inoculum at the test initial stage
Process 4 (MP1) and add stalk+pig manure+0.5 ‰ microbial inoculum at the test initial stage
Process 5 (MP2) and add stalk+pig manure+1 ‰ microbial inoculum at the test initial stage
Process 6 (MP3) and add stalk+pig manure+2 ‰ microbial inoculum at the test initial stage
The compost time, since on April 1st, 2012, finishes after reaction 60d.Unified artificial turning and timing moisturizing, guarantee air flow and the water ratio of adopting in composting process.Then average respectively at every morning 9:00 and temperature that afternoon, 4:00 measured heap body inside with mercurythermometer, and record envrionment temperature with mercurythermometer.Be 3d, 7d, 14d, 21d, 28d, 35d, 42d, 50d, 60d sample time, and sample is used for measuring the dynamic indicators such as physico-chemical property.
Field test
Experimental field and basic physical and chemical: be experimental field located at Chen Xu forest farm, Sihong County, physiochemical properties of soil is as shown in table 2.
Table 2 is studied the basic physical and chemical (0-20cm) of sample ground soil
Physico-chemical property in composting process:
1) do not add the dynamic change of microbial inoculum heap temperature
As shown in Figure 2, in composting process, different treatment compost temperature changed unanimously, all presents the trend of falling after rising, and owing to working as, ground temperature is lower, and heap body is less, and temperature rise is slow, and the time of carrying out is long, and heap body reached respectively greatly top temperature about 10-13 days.Then entered the continuous high temperature stage, then slowly reducing final sum envrionment temperature does not have difference.
For static aerobic compost, 55 DEG C of left and right of heap temperature just can reach the effect of sterilizing at least three days.As seen from the figure, it is 6 days that the processing GP that adds ginkgo residual leaf reaches time of 55 DEG C, and the processing P that does not add the residual leaf of ginkgo does not reach 55 DEG C, still, by the dynamic indicator of organic matter, pH, N, P, K, has illustrated that this processing has finally reached the state becoming thoroughly decomposed; Add the residual leaf of ginkgo and can further accelerate compost fermentation speed, shorten the fermented manure time.
2) dynamic change of interpolation microbial inoculum heap temperature
As shown in Figure 3, add in the situation of microbiobacterial agent of different ratios, in the composting process of compost, the dynamic law of temperature is consistent with the conventional compost that does not add microbial inoculum, but also there are differences.At the composting initial stage, organism in material is fast decoupled under the effect of aerobe, and discharge amount of heat, cause heap temperature to rise rapidly, and owing to adding microbiobacterial agent, local temperature is lower, and heap body is smaller, the reasons such as turning, the heap body of 6 kinds of processing reaches respectively top temperature at 13d.Then enter the continuous high temperature stage, last slowly reduction, final sum envrionment temperature is roughly suitable.
In the situation that not adding microbial inoculum, the interpolation of Ginkgo Leaf is to have played promoter action to increasing sharply of compost temperature, and in the situation that adding microbial inoculum, the alternating temperature successful of the pig manure of Ginkgo Leaf is higher than the pig manure that does not add Ginkgo Leaf.Meanwhile, through Fig. 1 and Fig. 2 comparison, on the basis of the pig manure of the residual leaf of ginkgo and do not add on the pig manure basis of the residual leaf of ginkgo, the compost treatment of the residual leaf of interpolation 30% ginkgo, heat-up rate is fast, and the continuous high temperature time is long, and the time of becoming thoroughly decomposed is short.Add each processing of microbiobacterial agent, heat up very fast, the time of becoming thoroughly decomposed is short, but the continuous high temperature time is also shorter.
3) dynamic change of interpolation microbial inoculum heap body organic content
As shown in Figure 4, respectively process in composting process generally, the organic content of heap body presents downtrending, the variation of 3 days to 21 days is not obvious, because local temperature is lower, and turning in addition, the organic content of the heap body of outdoor compost does not obviously rise, microbial activities is less, and organic consumption is lower, so downtrending is not obvious.At 21 days to 42 days, when ground temperature raises, microbial activities strengthened, organic consumption is large, and downtrending is obvious, has a trend raising in 50 days, owing to working as, ground temperature is suddenly low, microbial activities reduces, in the situation that in the residual leaf of ginkgo and pig manure, some organic matter is not consumed, through turning, make organic rising, but along with time of compost with become thoroughly decomposed, there is downward trend, the state that each processing tends towards stability subsequently.
To sum up, in the situation that not adding microbial inoculum, the organic content of the pig manure of the residual leaf of ginkgo, higher than the organic content 1.12% of pig manure, illustrates under the state of becoming thoroughly decomposed, the pig manure successful of the residual leaf of ginkgo.Each processing (GP, MGP1, MGP2, MGP3) organic content of adding the residual leaf of 30% ginkgo all exceedes organic compost organic content and is not less than 30% general standard, shows that the residual leaf of ginkgo can be for the composting of biological organic fertilizer.The interpolation of microbiobacterial agent has obvious impact to compost organic content.Compost treatment (MP1, MP2 and the MP3) organic content of adding microbial inoculum and do not add the residual leaf of ginkgo, only the organic content of MP1 processing (microbial inoculum addition is 0.5 ‰) exceedes 30%, though this shows that microbiobacterial agent interpolation has effect to the quick composting of compost, but may reduce the organic content of compost, especially in the time that the interpolation of microbial inoculum amount is higher.
4) dynamic change of full N in the different treatment composting process of interpolation microbial inoculum
As shown in Figure 5, in the compost of interpolation microbiobacterial agent, in each processing heap body, TN content is unanimous on the whole with dynamic law and the common compost of the time of composting.Different, owing to having added microbiobacterial agent in the material of banking up, accelerate the reaction process of compost, therefore, dynamic law performance is obviously.
In whole composting process, respectively process in the time that composting starts and no significant difference, on the low side due to envrionment temperature, not reaction inviolent, turning unstable, had individual ascendant trend in from 3 to 7 days, start sharply to decline since the 7th day total nitrogen and respectively process, this is the rising due to envrionment temperature, and the rising of heap temperature adds again a large amount of microorganisms, in heap body, easily degradation material is abundant, make microbial activities frequent, a large amount of organonitrogen fast decoupleds forms NH3, so a large amount of ammonias is overflowed.Because reaction is fast, there is no timely turning, the local anoxic condition of heap body, denitrification aggravation, a large amount of nitric nitrogens are converted into nitrogen volatilization.After 21 days, enter the rising stage, a large amount of pig manures and Ginkgo Leaf be by microbial consumption, cause piling body by a large amount of dry-matteies hour, so the content of TN constantly rose in the later stage.
To sum up, in the situation that not adding microbial inoculum, the GP total nitrogen content that adds the residual leaf of ginkgo is higher than processing P after compost finishes, and exceeds 1.32%.In the situation that adding microbial inoculum, the full N amount of MGP1, MGP2 of processing is higher than processing GP and P, all the other are processed all lower than GP and P, explanation, add microbial inoculum amount and be 0.5 ‰ and 1 ‰ effect higher than the processing compost that does not add microbial inoculum, and process MGP1 apparently higher than MGP2, this shows to add 0.5 ‰ microbial inoculum amount, and the pig manure that adds the residual leaf of 30% ginkgo has been accelerated speed of response and the speed of becoming thoroughly decomposed of heap body, has improved heap weight.
Seed germination experiment is considered to evaluate the method for the tool cogency of compost maturity.There are some researches show, the compost extraction becoming thoroughly decomposed completely can promote the germination of seed.The unified corn seed that adopts seed shop to buy of this test seed.It is fast that corn seed has germination, the advantage of easily measuring.Test is front by a few hours in seed submergence warm water.Time to be tested, take out and put into the culture dish that vat liquor is housed.Then put into 25 DEG C of incubators and cultivate 48h.After finishing, add up the number of shoots of corn in each culture dish, and measure the germination length of each corn.
5) dynamic change of the seed germination index (GI) of interpolation microbial inoculum heap body
Fig. 6 is for adding the dynamic change figure of microbial inoculum heap body seed germination index (GI), and each processing (GP, MGP1, MGP2, MGP3) GI value of adding the residual leaf of 30% ginkgo is respectively 96%, 89%, 90%, 87%.Compost treatment (P, MP1, MP2 and MP3) the compost GI value of adding microbial inoculum and do not add the residual leaf of ginkgo is respectively 95%, 86%, 91% and 85%, and this shows the more than 80% nontoxic requirement that each processing all reaches.In the process of composting, the 35th day time, the GI value of processing GP, MGP2, MP2 has all reached 80%, and this shows, the interpolation of microbial bacteria dosage has promoter action for the heap body that whether adds the residual leaf of ginkgo, and 1 ‰ microbial bacteria dose effect is the most obvious.
6) impact of different treatment compost on Aboveground Biomass of Young
Fig. 7 is the affect figure of different fertilizer Different Fertilization amount on field Aboveground Biomass of Young, A: Shandong Mei Beier fertilizer; B: the pig manure that adds the residual leaf of ginkgo; C: the residual leaf pig manure of ginkgo that adds microbial inoculum; D: the pig manure that adds microbial inoculum; E: pig manure; In the time that rate of fertilizer application is 2.5kg/m2, the biomass of processing A2, B2, C2 is apparently higher than community D2 and E2 biomass, and this shows to apply the residual leaf compost of ginkgo that adds the pig manure of the residual leaf of ginkgo and add microbial inoculum to promoting the effect of plant growth.
7) the full N content of different treatment compost on plant and the impact of absorbed dose
Fig. 8 a, b are depicted as and apply the figure that affects on the full N content of plant and absorbed dose after C fertilizer, apply its nitrogen content of crop after the pig manure that adds microbial inoculum and the residual leaf of ginkgo and be 0.49kg/m2,0.44kg/m2 and 0.39kg/m2 apparently higher than the plant nitrogen content that does not apply fertilizer.Along with the increase of rate of fertilizer application, the total nitrogen content of crop decreases.The community crop nitrogen absorbing amount that does not apply fertilizer is 0.47g/m2 left and right, and the community crop nitrogen absorbing amount that applies fertilizer is that 0.82g/m2,0.66g/m2,0.64g/m2 are apparently higher than the community crop nitrogen absorbing amount that does not apply fertilizer.Along with the increase of rate of fertilizer application, the Crop amount of community decreases, and the rate of fertilizer application of rate of fertilizer application higher than minimum rate of fertilizer application processing 1.5kg/m2 is described, the pig manure of microbial inoculum and Ginkgo Leaf has the growth that suppresses crop.Nitrogen content difference between the processing of Different Fertilization amount is not remarkable, and between the nitrogen absorbing amount of community crop Different Fertilization amount processing, difference is not remarkable.
Different fertilizer, along with the increase of rate of fertilizer application, total nitrogen content and absorbed dose are to have certain rule, and this shows, and the compost that adds the pig manure of the residual leaf of 30% ginkgo and add on this basis microbial inoculum has the effect of promotion to the growth of crop.In the time that rate of fertilizer application is 2.5kg/m2, the total nitrogen content of community A2, B2, C2 and nitrogen absorbing amount are again higher than total nitrogen content and the nitrogen absorbing amount of community D2, E2, this shows, between different fertilizer, be conducive to plant growth to using the compost that adds the pig manure of the residual leaf of 30% ginkgo and add on this basis microbial inoculum under same rate of fertilizer application condition.
And, different fertilizer, along with the increase of rate of fertilizer application, the content of tatal phosphorus of community crop and phosphorus absorbed dose are to have certain variation.The content of tatal phosphorus of the crop of A, B, C community and phosphorus absorbed dose are higher than the content of tatal phosphorus of D, E community crop and absorbed dose, and this shows that the pig manure that adds the pig manure of the residual leaf of ginkgo and add the residual leaf of microbial inoculum ginkgo has promoter action to the growth of crop.Simultaneously, in the time that rate of fertilizer application is 2.5kg/m2, process the crop content of tatal phosphorus of A2, B2, C2 apparently higher than processing C2, D2, this all shows, the pig manure that adds the residual leaf of ginkgo under same rate of fertilizer application condition is conducive to plant growth with the pig manure that adds the residual leaf of microbial inoculum ginkgo.
And in the time that rate of fertilizer application is 2.5kg/m2, the content of tatal phosphorus of the crop of A2, B2, C2 community and potassium absorbed dose are higher than the full potassium content of crop of D2, E2 community and absorbed dose.Simultaneously, different fertilizer is in the case of different rates of fertilizer application, the highest full potassium content of crop of community A, B, C and absorbed dose are all higher than D, E community, this shows in the time of same rate of fertilizer application, adds the growth that the pig manure of the residual leaf of 30% ginkgo and the pig manure of the residual leaf of interpolation microbial inoculum ginkgo are conducive to crop
Rate of fertilizer application 1.5kg/m2,2.5kg/m2,3.5kg/m2 that different fertilizer is different, after being manured into soil, the full potassium content of total nitrogen and total phosphor phosphorus in soil is with its increase, because the phosphorus element major part in soil is to exist with late effect property state, therefore total Phosphorus In Soil content can not be served as the index of soil phosphorus supply, when content of tatal phosphorus is high and do not mean that phosphorus element is in liberal supply, and content of tatal phosphorus is during lower than certain level, but may mean that phosphorus element is under-supply, so content trend is not enough to describe the nutrient situation of soil.Full potassium content has made up again this index, but available phosphorus more can illustrate soil nutrient status, and along with the increase of rate of fertilizer application, its content of soil is also the trend increasing.The soil weight is that the rate of fertilizer application that applies 2.5g/m2 has reached the effect that improves soil.Different rates of fertilizer application, especially, in the time of rate of fertilizer application 2.5kg/m2, applies the full potassium of total soil nitrogen, available phosphorus and the hydrolyzable nitrogen content of the fertile B fertilizer of A and C fertilizer all apparently higher than the soil content that applies D fertilizer and E fertilizer, and the soil phosphorus content that applies B fertilizer is processed higher than other.More than show under same rate of fertilizer application condition, apply the residual leaf pig manure of ginkgo that adds the pig manure of the residual leaf of 30% ginkgo and add microbial inoculum obvious to the improved effect of soil.
In the present invention, along with the increase of rate of fertilizer application, applying of different fertilizer reflects the average light absorption value (D of Functional diversity of soil microbial community in the time of 168h
aWC) be CK > A1 > A2 > A3, B2 > B3 > CK > B1, C2 > CK > C1 > C3, CK > D3 > D1 > D2, CK > E1 > E2 > E3, and be all that the trend that the increase light absorption value along with the time also increases thereupon after 24 hours tends towards stability after 168h, more than show, add 30% the compost of the residual leaf of ginkgo and the residual leaf compost of ginkgo of interpolation microbial inoculum, especially be 2.5kg/m in rate of fertilizer application
2time, the microbial activities of soil is had to the effect of promotion, when soil microbial biomass is declined, provide the energy that microbial respiratory amount is significantly increased, thereby impel Soil microbial respiration activity significantly to rise.In the principal constituent coordinate-system that different fertilizer forms in biolog data analysis at soil between different processing, all exist obvious differentiation, the compost of the residual leaf of ginkgo that adds 30% and the residual leaf compost of ginkgo of interpolation microbial inoculum are described, soil microorganisms reduces utilization of carbon source rate decline Microbial Community Diversity, and soil microorganisms selects to utilize pig manure and pig manure processing from adding microbial inoculum to exist obviously different to carbon source.
The compost of above-mentioned 8 kinds of different treatment, the performance analysis of not adding the residual leaf of 30% ginkgo, add the pig manure of 30% ginkgo residual leaf and adding temperature, the pH of different microbial bacteria dosage, full nitrogen, full phosphorus, full potassium shows, the most obvious taking the residual leaf of 30% ginkgo effect in the compost of interpolation raw material, the interpolation of microbiobacterial agent also has obvious effect for becoming thoroughly decomposed of compost.
The compost treatment of adding the residual leaf of 30% ginkgo, heat-up rate is fast, and the continuous high temperature time is long, and the time of becoming thoroughly decomposed is short.Add each processing of microbiobacterial agent, heat up very fast, the time of becoming thoroughly decomposed is short, but the continuous high temperature time is also shorter; The heap body total nitrogen content that adds 1 ‰ microbial inoculums and the residual leaf of 30% ginkgo is the highest, the large effect of microbiobacterial agent in addition of its Decomposition that promotes organonitrogen is described, the speed of response of its heap body is accelerated, accelerated the speed of becoming thoroughly decomposed, and 1 ‰ microbial bacteria dose effect is the most obvious simultaneously.
The fertilizer that adds Ginkgo Leaf has obvious benefit to the improvement of plant growth and soil.
The foregoing is only preferred embodiment of the present invention, is only illustrative for invention, and nonrestrictive.Those skilled in the art is understood, and in the spirit and scope that limit, can carry out many changes to it in invention claim, amendment, and even equivalence, but all will fall within the scope of protection of the present invention.
Claims (3)
1. a preparation method for the residual leaf biological organic fertilizer of ginkgo, is characterized in that, this detailed process is:
Step a, the residual leaf biological organic fertilizer of ginkgo is made;
Step a1, chooses fowl and animal excrement, and natural-dehydration; Fowl and animal excrement water content is greater than 60% in the present invention, and after dehydration, water content is 50%;
Step a2, the residual leaf of ginkgo that the ight soil that above-mentioned steps a1 is made is 30% with mass ratio, 1 ‰ microbiobacterial agent mix;
Step a3, by the fermented mixture of above-mentioned steps a2, stirring, slaking, carries out crushing packing after being dried, and makes biological organic fertilizer;
Step b, at field fertilization 2.5kg/m
2, by even to the biological organic fertilizer making and mixing with soil.
2. the preparation method of the residual leaf biological organic fertilizer of ginkgo according to claim 1, is characterized in that, in above-mentioned steps a2, is fermentation reactor system under the condition of 60 DEG C of left and right in temperature.
3. the preparation method of the residual leaf biological organic fertilizer of ginkgo according to claim 2, is characterized in that, in above-mentioned steps a2, described microbiobacterial agent is that bacterium is strong; The 60d that ferments in this step, and timing moisturizing.
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106883051A (en) * | 2017-04-12 | 2017-06-23 | 临沂大学 | A kind of insecticidal organic fertilizer and preparation method thereof |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102910988A (en) * | 2012-11-18 | 2013-02-06 | 蒋常德 | Compound microorganism liquid bacterial fertilizer for preventing plant diseases and insect pests and preparation method of compound microorganism liquid bacterial fertilizer |
-
2014
- 2014-06-14 CN CN201410273909.4A patent/CN104030745A/en active Pending
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102910988A (en) * | 2012-11-18 | 2013-02-06 | 蒋常德 | Compound microorganism liquid bacterial fertilizer for preventing plant diseases and insect pests and preparation method of compound microorganism liquid bacterial fertilizer |
Non-Patent Citations (1)
| Title |
|---|
| 沈家禾: ""银杏残叶堆肥研究与应用"", 《中国优秀硕士学位论文全文数据库（电子期刊）农业科技辑》, 31 December 2012 (2012-12-31), pages 043 - 3 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106883051A (en) * | 2017-04-12 | 2017-06-23 | 临沂大学 | A kind of insecticidal organic fertilizer and preparation method thereof |
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