CN102887749A - Innocent static aerobic composting treatment method for silkworm excrement - Google Patents
Innocent static aerobic composting treatment method for silkworm excrement Download PDFInfo
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- CN102887749A CN102887749A CN2012103389741A CN201210338974A CN102887749A CN 102887749 A CN102887749 A CN 102887749A CN 2012103389741 A CN2012103389741 A CN 2012103389741A CN 201210338974 A CN201210338974 A CN 201210338974A CN 102887749 A CN102887749 A CN 102887749A
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- silkworm excrement
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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
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Abstract
The invention discloses an innocent static aerobic composting treatment method for silkworm excrement. The method comprises the following steps of: 1) putting up an open floor on the bottom of a treatment tank; 2) spreading a layer of conditioner on the open floor; 3) pouring mixture of the silkworm excrement and the conditioner on the layer of the conditioner and spreading, or alternately poring the silkworm excrement and the conditioner to obtain a plurality of composite layer piles and then spreading; and 4) finally covering a layer of conditioner on the surfaces of the piles in the treatment tank. A layer of mushroom residues is coated on the bottom of a silkworm excrement tank and the surface of the silkworm excrement respectively, so that the direct contact between the silkworm excrement and natural environment can be avoided, the function of heat preservation can be exerted, and different parts of silkworm excrement have the high enough temperature; and therefore, the whole high-temperature aerobic fermentation effect of the silkworm excrement tank can be guaranteed, the fermentation and composting speed of the silkworm excrement is accelerated, and the effect of killing pathogens in the silkworm excrement can be improved.
Description
Technical field
The present invention relates to a kind of silkworm excrement refuse processing method, especially relate to the innoxious static aerobic composting treatment method of a kind of silkworm excrement.
Background technology
Silkworm excrement is the important waste in breed silkworms producing, and except refering in particular to the solid manure that silkworm larva discharges, also comprises residual mulberry, the bedding and padding in the silkworm rearing bed and silkworm body and seat sterilizing agent etc. and some die of illness silkworm and small and weak silkworm corpse that food is surplus on producing.Because the inevitable various infectivity flacherie cause of diseases that exist are processed without safe in the silkworm excrement, very likely production are caused a significant threat.Especially can breed silkworms in 1 year in south China silkworm district in 8-9 month, silkworm is criticized and joins end to end, and the quantity of silkworm excrement constantly increases, and it is serious arbitrarily to abandon phenomenon, has become new rural area public hazards in part silkworm district.Because silkworm and mulberry production has significant dispersed petty-farmer management feature, measure large, wide, dispersion, huge numbers of families' silkworm excrement is difficult to carry out batch production and processes and fully utilize.Therefore, research and development practical innoxious process for treating simple, strong operability has important realistic meaning.
According to being processed on-site investigation, south China silkworm district silkworm excrement finds, except most silkworm excrements are arbitrarily abandoned, also there is part silkworm family silkworm excrement can be carried out doing Fertilizer application after stack retting is processed, but most processing modes are simple, it is the not turning of simple stack retting, therefore silkworm excrement surface and bottom can't form the aerobic composting fermentation condition and cause ferments insufficiently, and can not produce enough high temperature and kills cause of disease, and sterilization is not thorough.
At present, research there is not yet the research report about silkworm excrement cause of disease compost hazard-free, present method is namely for rural production present situation nowadays, and it is innoxious and reduce a kind of summary silkworm excrement static compost method of environmental pollution to carry out the pollution, the flacherie that are intended to solve on the spot silkworm district silkworm excrement waste.
Summary of the invention
The object of the present invention is to provide the innoxious static aerobic compost method of a kind of silkworm excrement, the method less investment operates simple and easyly, and effect is remarkable.
For realizing the object of the invention, the present invention realizes by following technical measures: the innoxious static aerobic composting treatment method of a kind of silkworm excrement, may further comprise the steps,
(1) the bottom built with treating pond forms Stilt layer;
(2) at frame tiling one deck amendment;
(3) after the amendment layer is poured the mixture of silkworm excrement and amendment into, pave, or pour silkworm excrement in turn, amendment forms and paves after a plurality of composite beds are piled up;
(4) cover again at last one deck amendment on the top layer for the treatment of pond stores.
Built on stilts floor height 8-11cm of the present invention; The amendment thickness that tiles at frame is 5-10cm.
The weight ratio of silkworm excrement and amendment is 7～9:1～3 in the silkworm excrement amendment mixture of the present invention, and piling height is 80-90cm, and adopting the carbon-nitrogen ratio (C/N) of silkworm excrement is 10～30:1.
Silkworm excrement amendment composite bed of the present invention is pressed the compound accumulation of silkworm excrement-amendment-silkworm excrement successively, and the weight ratio of layering silkworm excrement and amendment is 8:2; Piling height is 80-90cm, and adopting the carbon-nitrogen ratio (C/N) of silkworm excrement is 10～30:1.
It is 5-10cm that top layer of the present invention covers one deck amendment thickness at last.
Amendment of the present invention is selected the materials such as bacterium chaff or husk.
The present invention has following beneficial effect:
(1) owing to adds one deck bacterium chaff in bottom, silkworm excrement pond and silkworm excrement surface, can avoid silkworm excrement directly to contact with physical environment, play the effect of insulation, guarantee that the silkworm excrement different sites all produces enough high temperature, thereby ensure the high-temperature aerobic fermentation effect of silkworm excrement pond integral body, both accelerate the speed of silkworm excrement fermentation maturity, also improved the killing effect to cause of disease in the silkworm excrement.
(2) in accumulation, add a certain proportion of amendment, can play the C/N ratio that improves windrow on the one hand, added on the other hand dry amendment and can make the suitable water cut of silkworm excrement, reached suitable water ratio scope.The part unpleasant odor that simultaneously adsorbable silkworm excrement fermentation produces has improved the pollution of compost fermentation to air.
(3) the treating pond bottom is built on stilts, makes silkworm excrement bottom well-ventilated, oxygen supply abundance, improves the effect of fermentation.
Embodiment
Embodiment 1
(1) the cement pit bottom is blank, with about the built on stilts 10cm of common brick, spread straight bamboo cane, the bamboo cane gap is little, prevents that composting material from spilling from gap location, and the bottom, pond is natural ventilating status, clog-free thing.
(2) at bamboo cane tiling thick layer approximately with the drying and crushing bacterium chaff of 5cm, then be that 12.5:1 silkworm excrement and bacterium chaff are poured in the silkworm excrement pond by the mixed silkworm excrement bacterium of 8:2 weight ratio chaff mixture with C/N, heap up to 90cm till, pave, then be the about 5cm bacterium of surface coverage thick layer chaff.
(3) at the different positions in the silkworm excrement pond thermometric of setting up an office.Determine turning according to the warm changing conditions of heap.
(4) the sick silkworm of infected silkworm pebrine is put into compost, interval 24h sampling, to sample grind, centrifugal, purify, purifying cause of disease artificial inoculation silkworm is played silkworm 4h 3 ages, investigation is judged killing effect to the infection rate of silkworm.
(5) investigation result: the time of silkworm excrement upper, middle and lower section heap temperature 〉=50 ℃ is respectively 18-20d, and the time of the middle part of compost and bottom temp 〉=60 ℃ is between 11-23 days.60 ℃ of high temperature has obvious elimination effect to the activity of nosema bombycis protozoon, and the nosema bombycis protozoon loses virulence fully processing 96h.
Embodiment 2
(1) the cement pit bottom is blank, with about the built on stilts 10cm of common brick, spread straight bamboo cane, the bamboo cane gap is little, prevents that composting material from spilling from gap location, and the bottom, pond is natural ventilating status, clog-free thing.
(2) at bamboo cane tiling thick layer approximately with the drying and crushing bacterium chaff of 5cm, then pouring 80 jin of C/N into is the 15:1 silkworm excrement, auxiliary flat, put into again 20 jin of bacterium chaffs, auxiliary flat, be sequentially added into one by one in this manner silkworm excrement-bacterium chaff-silkworm excrement and pile up, heap is up to till the 90cm, pave, then be the about 5cm bacterium of surface coverage thick layer chaff.
(3) at the different positions in the silkworm excrement pond thermometric of setting up an office.Determine turning according to the warm changing conditions of heap.
The sick silkworm that (4) will infect nuclear polyhedrosis virus is put into compost, interval 24h sampling, to sample grind, centrifugal, purify, purifying cause of disease artificial inoculation silkworm is played silkworm 4h 3 ages, investigation is judged killing effect to the infection rate of silkworm.
(5) investigation result: the time of silkworm excrement different piece heap temperature 〉=50 ℃ is at 12-24d, and the time of the middle part of compost and bottom temp 〉=60 ℃ is between 14-16 days.60 ℃ of high temperature has obvious elimination effect to the activity of Bombyx mori nuclear polyhydrosis virus, and cause of disease loses virulence fully processing 48h.
Embodiment 3
(1) the cement pit bottom is blank, with about the built on stilts 8cm of common brick, spread straight bamboo cane, the bamboo cane gap is little, prevents that composting material from spilling from gap location, and the clog-free thing in bottom, pond is natural ventilating status.
(2) at bamboo cane tiling thick layer approximately with the husk of 5cm, then the silkworm excrement and the bacterium chaff that with C/N are 10:1 are poured in the silkworm excrement pond by the mixed silkworm excrement bacterium of 7:3 weight ratio chaff mixture, heap up to 90cm till, pave, then be the about 5cm bacterium of surface coverage thick layer chaff.
(3) at the different positions in the silkworm excrement pond thermometric of setting up an office.Determine turning according to the warm changing conditions of heap.
(4) the sick silkworm of infected silkworm pebrine is put into compost, interval 24h sampling, to sample grind, centrifugal, purify, purifying cause of disease artificial inoculation silkworm is played silkworm 4h 3 ages, investigation is judged killing effect to the infection rate of silkworm.
(5) investigation result: the time of silkworm excrement upper, middle and lower section heap temperature 〉=50 ℃ is respectively 18-20d, and the time of the middle part of compost and bottom temp 〉=60 ℃ is between 10-25 days.60 ℃ of high temperature has obvious elimination effect to the activity of nosema bombycis protozoon, and the nosema bombycis protozoon loses virulence fully processing 96h.
Above embodiment only is used for setting forth the present invention, and protection scope of the present invention is not only to be confined to following examples.The those of ordinary skill of described technical field all can be realized purpose of the present invention according to above content disclosed by the invention and scope that each parameter is got.
Claims (6)
1. the innoxious static aerobic composting treatment method of silkworm excrement is characterized in that may further comprise the steps,
(1) the bottom built with treating pond forms Stilt layer;
(2) at frame tiling one deck amendment;
(3) after the amendment layer is poured the mixture of silkworm excrement and amendment into, pave, or pour silkworm excrement in turn, amendment forms a plurality of composite beds and piles up;
(4) cover again at last one deck amendment on the top layer for the treatment of pond stores.
2. the innoxious static aerobic composting treatment method of silkworm excrement according to claim 1 is characterized in that described built on stilts floor height 8-11cm; The amendment thickness that tiles at frame is 5-10cm.
3. the innoxious static aerobic composting treatment method of silkworm excrement according to claim 1, it is characterized in that the weight ratio of silkworm excrement and amendment is 7～9:1～3 in the described silkworm excrement amendment mixture, piling height is 80-90cm, and adopting the carbon-nitrogen ratio (C/N) of silkworm excrement is 10～30:1.
4. the innoxious static aerobic composting treatment method of silkworm excrement according to claim 1 is characterized in that described silkworm excrement amendment composite bed presses the compound accumulation of silkworm excrement-amendment-silkworm excrement successively, and the weight ratio of layering silkworm excrement and amendment is 8:2; Total piling height is 80-90cm, and adopting the carbon-nitrogen ratio (C/N) of silkworm excrement is 10～30:1.
5. the innoxious static aerobic composting treatment method of silkworm excrement according to claim 1 is characterized in that it is 5-10cm that described top layer covers one deck amendment thickness at last.
6. the innoxious static aerobic composting treatment method of each described silkworm excrement according to claim 1-5 is characterized in that described amendment selects bacterium chaff or husk.
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| CN201210338974.1A CN102887749B (en) | 2012-09-13 | 2012-09-13 | Innocent static aerobic composting treatment method for silkworm excrement |
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Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104193435A (en) * | 2014-09-19 | 2014-12-10 | 广西地源之本肥业有限公司 | Biological organic fertilizer additive and preparation method thereof |
| CN104193456A (en) * | 2014-09-19 | 2014-12-10 | 广西地源之本肥业有限公司 | Organic silkworm excrement fertilizer and preparation method thereof |
| CN104230442A (en) * | 2014-09-19 | 2014-12-24 | 广西地源之本肥业有限公司 | Organic fertilizer containing silkworm excrement and preparation method thereof |
| CN104355863A (en) * | 2014-11-12 | 2015-02-18 | 四川省农业科学院蚕业研究所 | Bio-organic fertilizer and preparation method thereof |
| CN105237247A (en) * | 2015-11-20 | 2016-01-13 | 广东省农业科学院蚕业与农产品加工研究所 | Silkworm excrement compound bacterial manure and preparing method thereof |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101209943A (en) * | 2007-12-24 | 2008-07-02 | 安徽省农业科学院土壤肥料研究所 | Long-acting flower fertilizer and producing method thereof |
| CN201109760Y (en) * | 2007-02-01 | 2008-09-03 | 宜州市科学技术局 | Pool for processing silkworm excrement |
| CN201648256U (en) * | 2009-12-08 | 2010-11-24 | 广东省农业科学院蚕业与农产品加工研究所 | Device for hazard-free aerobic static silkworm dung composting treatment method |
| CN102432356A (en) * | 2011-09-16 | 2012-05-02 | 浙江大学 | Method for producing specialized organic fertilizer for protected cultivation by silkworm excrement fermentation |
-
2012
- 2012-09-13 CN CN201210338974.1A patent/CN102887749B/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201109760Y (en) * | 2007-02-01 | 2008-09-03 | 宜州市科学技术局 | Pool for processing silkworm excrement |
| CN101209943A (en) * | 2007-12-24 | 2008-07-02 | 安徽省农业科学院土壤肥料研究所 | Long-acting flower fertilizer and producing method thereof |
| CN201648256U (en) * | 2009-12-08 | 2010-11-24 | 广东省农业科学院蚕业与农产品加工研究所 | Device for hazard-free aerobic static silkworm dung composting treatment method |
| CN102432356A (en) * | 2011-09-16 | 2012-05-02 | 浙江大学 | Method for producing specialized organic fertilizer for protected cultivation by silkworm excrement fermentation |
Non-Patent Citations (2)
| Title |
|---|
| 《蚕业科学》 20111231 廖森泰等 "华南蚕区蚕沙产地无害化和肥料化处理技术体系构建思路" 第1086－1088页 1－6 第37卷, 第6期 * |
| 廖森泰等: ""华南蚕区蚕沙产地无害化和肥料化处理技术体系构建思路"", 《蚕业科学》 * |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104193435A (en) * | 2014-09-19 | 2014-12-10 | 广西地源之本肥业有限公司 | Biological organic fertilizer additive and preparation method thereof |
| CN104193456A (en) * | 2014-09-19 | 2014-12-10 | 广西地源之本肥业有限公司 | Organic silkworm excrement fertilizer and preparation method thereof |
| CN104230442A (en) * | 2014-09-19 | 2014-12-24 | 广西地源之本肥业有限公司 | Organic fertilizer containing silkworm excrement and preparation method thereof |
| CN104355863A (en) * | 2014-11-12 | 2015-02-18 | 四川省农业科学院蚕业研究所 | Bio-organic fertilizer and preparation method thereof |
| CN105237247A (en) * | 2015-11-20 | 2016-01-13 | 广东省农业科学院蚕业与农产品加工研究所 | Silkworm excrement compound bacterial manure and preparing method thereof |
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