CN101486601A - Composting method for vegetable wastes efficient organic fertilizer - Google Patents
Composting method for vegetable wastes efficient organic fertilizer Download PDFInfo
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- CN101486601A CN101486601A CNA200910021263XA CN200910021263A CN101486601A CN 101486601 A CN101486601 A CN 101486601A CN A200910021263X A CNA200910021263X A CN A200910021263XA CN 200910021263 A CN200910021263 A CN 200910021263A CN 101486601 A CN101486601 A CN 101486601A
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- organic fertilizer
- composting method
- vegetable wastes
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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 an effective composting method of an organic fertilizer of vegetable wastes. The method comprises the following steps of: (1) confirming a field; (2) processing the vegetable wastes; (3) covering dry soil on the selected field; (4) placing the processed vegetable wastes; (5) covering fine dry soil with a thickness of 5 to 7 cm after uniformly spreading highly effective decomposed bacteria liquid, urea, and phosphate fertilizer into the wastes in sequence; (6) arranging vent pipes in a groined type; (7) piling and shaping; (8) pile-turning; and (9) decomposing. The effective composting method of organic fertilizer of vegetable wastes is simple and easy to be carried out, and has low cost; the vegetable wastes processed by composing can be widely applied to the fields of agricultural industry, flower culture, and the like.
Description
Technical field
The present invention relates to the composting method of fertilizer, relate in particular to composting method for vegetable wastes efficient organic fertilizer.
Background technology
Along with the Chinese society rapid economy development, people's living standard constantly improves and improves, and vegetables are as the requisite consumer's goods of people's daily life, and consumption continues to increase, and the consumption growth to the elaboration dish is more rapid, and demand is increasing.Because the centrality of vegetables production distribution and market are to the needs of elaboration dish, so the amount of vegetable castoff is also increasing, do not abandon and do not add for a long time arbitrarily to stack with handling, cause the river course to block again, the overslaugh traffic, thus taken a large amount of land resources.Foul smell that is produced in the vegetable castoff decay process and smelly water easily attract mosquitos and flies, very easily cause environmental pollution; Simultaneously vegetable castoff with pathogeny, become the contagium of disease and pest in the vegetables production process, cause the afterculture vegetable morbidity, produce a series of vicious cycle then, big the increasing that have high input that vegetables are produced influences the vegetables productivity effect.
Owing to contain a large amount of nutritive elements in the vegetable castoff, have the basis of resource utilization recycle, thus it has been carried out the research of vegetable wastes efficient composting technology, for approach is explored in the utilization of vegetable castoff harmless resource utilization.
Summary of the invention
Technical problem to be solved by this invention provides a kind of composting method for vegetable wastes efficient organic fertilizer easy to implement, with low cost.
For addressing the above problem, a kind of composting method for vegetable wastes efficient organic fertilizer of the present invention may further comprise the steps:
(1) determine the place: select to ventilate, on the sunny side, convenient transportation, high-land and esplanade;
(2) processing of vegetable castoff: vegetable castoff is broken to≤section of 5cm, and its water ratio is 65～70%;
(3) on selected place, cover the thick dry ground of 10～15cm;
(4) evenly placing thickness is vegetable castoff after 15～20cm segment;
(5) cover the thick thin dry ground of 5～7cm after in this waste, being sprinkled into efficient decomposition bacterium liquid, urea, phosphate fertilizer successively equably; Wherein said efficient decomposition bacterium liquid, urea, phosphate fertilizer are respectively 0.04～0.1%, 0.1～0.5%, 1～2% of vegetable castoff weight;
(6) vent-pipe is placed on the vegetable castoff in the step (5) by groined type;
(7) repeating step (4), (5) and make it be coniform or trapezoidal heap body; After covering 10～13cm dry ground, the heap surface seals coated with plastic film;
(8) turning when the compost internal temperature drops to below 45 ℃, each layer of uniform mixing, and keep original composting shape;
(9) temperature is 55～65 ℃ in heap, keeps turning after 10～15 days, does not put vent-pipe, gets final product until becoming thoroughly decomposed fully.
Thin dry ground in the described step (5) is soil particle diameter≤1cm, the soil of 10%≤water content≤20%.
Heap body base diameter in the described step (7) is that 250～300cm, height are 200～250cm.
Bottom width was 250～300cm under heap body in the described step (7) was, and last bottom width is 100～150cm, and height is the trapezoidal heap of 200～250cm.
The intersection point of the groined type vent-pipe in the described step (6) is 150～200cm apart from the distance in the center of circle, place.
The present invention compared with prior art has the following advantages:
1, because the present invention adopts the efficient decomposition bacterium liquid that can quicken decomposition, and urea and phosphate fertilizer have been added simultaneously, therefore not only quickened becoming thoroughly decomposed of vegetable castoff, make it become efficient organic fertilizer, and improved the content of main nutrient in the composting production, and reduced the foul smell discharging significantly, prevented the propagation of environmental pollution and disease and pest effectively.Its main fertility index is referring to table 1 and table 2:
Table 1: compost organic content and land for growing field crops, compost soil sample are relatively
| The sample title | Organic average content (g/kg) | Increase (%) than land for growing field crops soil sample | Increase (%) than compost soil sample |
| Compost | 22.01 | 180.38 | 376.4 |
| The compost soil sample | 4.62 | -41.15 | — |
| The land for growing field crops soil sample | 7.85 | — | 322.9 |
Table 2: compost N, P, K content and land for growing field crops, compost soil sample are relatively
| The sample title | Available P (g/kg) | Increase (%) than compost soil sample | Increase (%) than land for growing field crops soil sample | Quick-acting K (g/kg) | Increase (%) than compost soil sample | Increase (%) than land for growing field crops soil sample | Full N (g/kg) | Increase (%) than compost soil sample | Increase (%) than land for growing field crops soil sample |
| Compost | 72.92 | 221.52 | 104.54 | 17.49 | 160.66 | 89.28 | 6.10 | 395.93 | 286.08 |
| The compost soil sample | 22.68 | — | -36.38 | 6.71 | — | -27.38 | 1.23 | — | -22.15 |
| The land for growing field crops soil sample | 35.65 | 57.19 | — | 9.24 | 37.71 | — | 1.58 | 28.46 | — |
Annotate: N is a nitrogen, and P is a Vanadium Pentoxide in FLAKES, and K is a potassium oxide.
2, the present invention is simple and easy to do, with low cost, and the vegetable castoff after compost treatment can be widely used in fields such as agriculture production, flower culture.
Embodiment
A kind of composting method for vegetable wastes efficient organic fertilizer may further comprise the steps:
(1) determine the place: select to ventilate, on the sunny side, convenient transportation, high-land and esplanade.
(2) processing of vegetable castoff: with vegetable castoff hand hay cutter or mince section to≤5cm, and its water ratio is 65～70%.
(3) on selected place, be standardized the circle of 250～300cm, in circle, cover the thick dry ground of 10～15cm and under in the absorption composting process, ooze solution with diameter.
(4) evenly placing thickness is vegetable castoff 500～600kg after 15～20cm segment.
(5) nitrogenous 46% urea, the Yunnan Gejiushi Chemical Fertilizer Plant that is sprinkled into equably successively in this waste that efficient decomposition bacterium liquid, limited liability company of Gansu Liuization group that Gansu Agriculture University, produces produce produces contains P
2O
5Cover the thin dry ground of the thick soil particle diameter≤1cm of 5～7cm, 10%≤water content≤20% behind the phosphate fertilizer of 12% normal superphosphate.
(6) be the aperture of beating diameter 1～1.5cm on the tube wall of 50～100mm hard polyethylene chloride tube every 10cm at the caliber that Wujiang Shu Leshe building material company limited produces, make it become vent-pipe; Be placed in 4 vent-pipes on the vegetable castoff in the step (5) and be groined type, the intersection point that makes groined type is 150～200cm apart from the distance in the center of circle, place, and outside two ends are exposed to.
(7) repeating step (4), (5) 5～6 times, and make it be the spire body that height is 200～250cm; Preserving moisture coated with plastic film sealing after 10～13cm dry ground is covered in the heap surface heats, and prevents volatile component loss in the composting process.The distance that will keep 300cm simultaneously between the heap is with handled easily; And the heap that will stagger between parallel heap and the heap, to keep good ventilation effect.
Bottom width was 250～300cm under the heap body also can be, and last bottom width is 100～150cm, and height is the trapezoidal heap of 200～250cm.The same step of compost method (4), (5), length is decided on what and place of composting material.
(8) when dropping to below 45 ℃, the compost internal temperature carries out turning, each layer of uniform mixing immediately; Put vent-pipe then well, and keep original composting shape, film is covered.Pile in the body this moment and dry ground is not covered on the surface, and do not add efficient decomposition bacterium liquid and urea, phosphate fertilizer.
(9) temperature is 55～65 ℃ in heap, keeps turning after 10～15 days, does not put vent-pipe, overlay film, until the form of not seeing original vegetable castoff in appearance, rotten fully, chocolate, ordorless flavor has spoiled flavour, with its vat liquor wheat seed is carried out germination test, with distilled water is contrast, and both differ and are no more than 3%, do not attract mosquitos and flies, water content is 16～25%, and heap temperature no longer raises and promptly shows fully and become thoroughly decomposed.Pile body intermediary compost color and be chocolate or black this moment, and quality is loose, and white or canescence mycelia appear in many crumb structure, slightly organism mouldy and corrupe, and non-stimulated and unpleasant stench.
Claims (5)
1, a kind of composting method for vegetable wastes efficient organic fertilizer may further comprise the steps:
(1) determine the place: select to ventilate, on the sunny side, convenient transportation, high-land and esplanade;
(2) processing of vegetable castoff: vegetable castoff is broken to≤section of 5cm, and its water ratio is 65～70%;
(3) on selected place, cover the thick dry ground of 10～15cm;
(4) evenly placing thickness is vegetable castoff after 15～20cm segment;
(5) cover the thick thin dry ground of 5～7cm after in this waste, being sprinkled into efficient decomposition bacterium liquid, urea, phosphate fertilizer successively equably; Wherein said efficient decomposition bacterium liquid, urea, phosphate fertilizer are respectively 0.04～0.1%, 0.1～0.5%, 1～2% of vegetable castoff weight;
(6) vent-pipe is placed on the vegetable castoff in the step (5) by groined type;
(7) repeating step (4), (5) and make it be coniform or trapezoidal heap body; After covering 10～13cm dry ground, the heap surface seals coated with plastic film;
(8) turning when the compost internal temperature drops to below 45 ℃, each layer of uniform mixing, and keep original composting shape;
(9) temperature is 55～65 ℃ in heap, keeps turning after 10～15 days, does not put vent-pipe, gets final product until becoming thoroughly decomposed fully.
2, composting method for vegetable wastes efficient organic fertilizer as claimed in claim 1 is characterized in that: the thin dry ground in the described step (5) is soil particle diameter≤1cm, the soil of 10%≤water content≤20%.
3, composting method for vegetable wastes efficient organic fertilizer as claimed in claim 1 is characterized in that: the heap body base diameter in the described step (7) is that 250～300cm, height are 200～250cm.
4, composting method for vegetable wastes efficient organic fertilizer as claimed in claim 1 is characterized in that: bottom width was 250～300cm under the heap body in the described step (7) was, and last bottom width is 100～150cm, and height is the trapezoidal heap of 200～250cm.
5, composting method for vegetable wastes efficient organic fertilizer as claimed in claim 1 is characterized in that: the intersection point of the groined type vent-pipe in the described step (6) is 150～200cm apart from the distance in the center of circle, place.
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| CN200910021263A CN101486601B (en) | 2009-02-19 | 2009-02-19 | Composting method for vegetable wastes efficient organic fertilizer |
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| CN200910021263A CN101486601B (en) | 2009-02-19 | 2009-02-19 | Composting method for vegetable wastes efficient organic fertilizer |
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| CN101486601B CN101486601B (en) | 2012-10-03 |
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Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102173884A (en) * | 2011-02-28 | 2011-09-07 | 湖北省农业科学院经济作物研究所 | High-mountain vegetable waste microbiological treatment method |
| CN102584357A (en) * | 2012-02-03 | 2012-07-18 | 刘文治 | Treatment method for realizing rapid resource treatment and zero emission of vegetable waste |
| CN103360131A (en) * | 2013-07-18 | 2013-10-23 | 句容市和春园农业机械专业合作社 | Vegetable waste composting technology |
| CN104829309A (en) * | 2015-04-13 | 2015-08-12 | 中国烟草总公司重庆市公司彭水分公司 | Environmental-protection organic fertilizer and production method thereof |
| CN105693305A (en) * | 2014-11-24 | 2016-06-22 | 晋小军 | Method for preparing efficient organic fertilizer through composting livestock and poultry night soil and crop straws |
| CN108129233A (en) * | 2017-12-27 | 2018-06-08 | 重庆千月农业科技开发有限公司 | A kind of preparation method using EM fermentation organic fertilizers |
| CN108164346A (en) * | 2018-03-02 | 2018-06-15 | 奥为（天津）环保科技有限公司 | A kind of method using biomass castoff production organic fertilizer |
| CN108752136A (en) * | 2018-07-04 | 2018-11-06 | 宁夏农林科学院固原分院 | A kind of vegetables waste dish passes through composting method and carries out Fertilizer Transformed reutilization technology |
| RU2751178C1 (en) * | 2020-02-25 | 2021-07-09 | Игорь Викторович Торопов | Solid waste composting method and climate chamber for its implementation |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN101165008A (en) * | 2007-10-10 | 2008-04-23 | 中国农业科学院蔬菜花卉研究所 | Vegetable residual strain microorganism-earthworm multiple step inoculation conversion method |
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- 2009-02-19 CN CN200910021263A patent/CN101486601B/en not_active Expired - Fee Related
Patent Citations (1)
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| CN101165008A (en) * | 2007-10-10 | 2008-04-23 | 中国农业科学院蔬菜花卉研究所 | Vegetable residual strain microorganism-earthworm multiple step inoculation conversion method |
Non-Patent Citations (3)
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| 刘淑霞等: "几种纤维素分解菌在有机质转化中的作用", 《农业环境科学学报》 * |
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Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102173884A (en) * | 2011-02-28 | 2011-09-07 | 湖北省农业科学院经济作物研究所 | High-mountain vegetable waste microbiological treatment method |
| CN102173884B (en) * | 2011-02-28 | 2013-01-09 | 湖北省农业科学院经济作物研究所 | High-mountain vegetable waste microbiological treatment method |
| CN102584357A (en) * | 2012-02-03 | 2012-07-18 | 刘文治 | Treatment method for realizing rapid resource treatment and zero emission of vegetable waste |
| CN102584357B (en) * | 2012-02-03 | 2014-03-05 | 刘文治 | Treatment method for realizing rapid resource treatment and zero emission of vegetable waste |
| CN103360131A (en) * | 2013-07-18 | 2013-10-23 | 句容市和春园农业机械专业合作社 | Vegetable waste composting technology |
| CN103360131B (en) * | 2013-07-18 | 2015-08-05 | 句容市和春园农业机械专业合作社 | A kind of composting process of vegetable castoff |
| CN105693305A (en) * | 2014-11-24 | 2016-06-22 | 晋小军 | Method for preparing efficient organic fertilizer through composting livestock and poultry night soil and crop straws |
| CN104829309A (en) * | 2015-04-13 | 2015-08-12 | 中国烟草总公司重庆市公司彭水分公司 | Environmental-protection organic fertilizer and production method thereof |
| CN108129233A (en) * | 2017-12-27 | 2018-06-08 | 重庆千月农业科技开发有限公司 | A kind of preparation method using EM fermentation organic fertilizers |
| CN108164346A (en) * | 2018-03-02 | 2018-06-15 | 奥为（天津）环保科技有限公司 | A kind of method using biomass castoff production organic fertilizer |
| CN108752136A (en) * | 2018-07-04 | 2018-11-06 | 宁夏农林科学院固原分院 | A kind of vegetables waste dish passes through composting method and carries out Fertilizer Transformed reutilization technology |
| RU2751178C1 (en) * | 2020-02-25 | 2021-07-09 | Игорь Викторович Торопов | Solid waste composting method and climate chamber for its implementation |
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| CN101486601B (en) | 2012-10-03 |
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