CN104366010A - Ecological comprehensive treatment process of waste vegetable leaves - Google Patents
Ecological comprehensive treatment process of waste vegetable leaves Download PDFInfo
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- CN104366010A CN104366010A CN201410539474.3A CN201410539474A CN104366010A CN 104366010 A CN104366010 A CN 104366010A CN 201410539474 A CN201410539474 A CN 201410539474A CN 104366010 A CN104366010 A CN 104366010A
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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 belongs to the technical field of organic waste cycle comprehensive utilization, and discloses an ecological comprehensive treatment process of waste vegetable leaves. The process comprises the steps: firstly, the waste vegetable leaves are artificially sorted to excellent, good and inferior categories according to a rotting condition, and then the excellent vegetable leaves are made into a ferment silage rich in lactic acid bacteria; the good vegetable leaves are made into a liquid probiotic biological feed additive; and the inferior vegetable leaves are made into a liquid probiotic biological organic fertilizer. The whole treatment process has no need of extrusion and dry dehydration treatment on the vegetable leaves, is low in energy consumption, has no sewage generated, has no need of arrangement of a sewage treatment system, is easy to industrialize, is economic and environmentally friendly, and achieves maximization of the waste utilization value.
Description
Technical field
The invention belongs to organic waste circulation comprehensive and utilize technical field, be specifically related to a kind of waste vegetable leaves ecology synthesis treatment process.
Background technology
There are many growing vegetables and distribution centre in China.Complete whole fresh vegetable often when operator returns from vegetable grower's purchase, they leave the delicate part of dish (as cabbage, baby cabbage etc.) to be packaged into freezer, and the remainder of dish then abandons becomes dish leaf rubbish, from every number of days ton to 2000 tons! But because the water content of fresh vegetable leaf is easily rotted up to more than 90%, as unprocessed can be liable to illness with regard to Direct-fed poultry; Conventional processing method often produces the high concentrated organic wastewater being difficult in a large number dispose, up to the present, way is well disposed in various places also neither one, mostly as organic waste fall toward mountain hole topple over field leave nature rot, both contaminated air, polluted source again, has a strong impact on living environment and the health of people.
A kind of recycling production process of discarded vegetable leaves is disclosed in patent 201110058132.6, it mainly comprises sorting, the process of not corrupt dish leaf, addle the process of dish leaf and sewage disposal four steps, but this technique first will carry out fragmentation, extruding and drying and dehydrating process to dish leaf, but moisture is high in dish leaf, generally reach 80% ~ 90%, therefore dehydration energy consumption is very big, and subsequent technique also will carry out sewage disposal to the moisture removed, need supporting huge sewage-treatment plant, processing cost is high.
Summary of the invention
In order to solve the shortcoming and defect part of prior art, the object of the present invention is to provide a kind of waste vegetable leaves ecology synthesis treatment process.
The object of the invention is achieved through the following technical solutions:
A kind of waste vegetable leaves ecology synthesis treatment process, comprises following operational sequence:
(1) be excellent, good and inferior three classifications by waste vegetable leaves according to the situation artificial separation of addling;
(2) the excellent dish leaf vegetable-chopper sorted out is chopped into 0.5 ~ 3cm long fragment dish grain, then with conveying worm feeding to the silage silo that ferments, conveying worm add in feeding process the righting agent of dish leaf quality 1% ~ 3%, the bio-carrier of 2% ~ 3% and 3% ~ 6% the prebiotic engineered microbes biologic product 1 of compound, make it fully to be uniformly mixed with dish grain, the dish grain sending into fermentation silage silo is degraded at normal temperatures, is activated, fermentation, through 5 ~ 7 days, obtain rich lactobacteria-containing ferment ensilage;
(3) the good dish leaf will sorted out, carry out size degradation with dish leaf disintegrator and become puree, add simultaneously the righting agent of dish leaf quality 1% ~ 3%, 2% ~ 3% nutritional agents, the bio-carrier of 2% ~ 5%, the biological deodorant of 0.5% ~ 1% and 3% ~ 6% biologic product 2 obtain mix puree, then mixing puree liquid is sent into and carry out degrading, activating and fermentation with in the retort stirred, react 5 ~ 7 days under normal temperature, obtain liquid probiotics feed addictive;
(4) inferior dish leaf will be sorted out, carry out size degradation with dish leaf disintegrator and become puree, add simultaneously the righting agent of dish leaf quality 0.5% ~ 2%, 1% ~ 3% nutritional agents, the bio-carrier of 3% ~ 6%, the biological deodorant of 0.5% ~ 1% and 3% ~ 5% biologic product 3, then mixing puree is sent into and carry out degrading, activating and fermentation with in the retort stirred, react 5 ~ 7 days under normal temperature, obtain liquid probiotics fertilizer.
Operation (2), (3) and the righting agent prescription described in (4) and technique as follows: by mass parts, hawthorn 1 ~ 2 part, rice sprout 2 ~ 3 parts, 2 ~ 3 parts, Fructus Hordei Germinatus, Momordica grosvenori 1 ~ 2 part, chrysanthemum 1 ~ 2 part, 2 ~ 3 parts, brown sugar and 185 ~ 191 parts, clear water are mixed, boil and obtain for fried 30 ~ 60 minutes.
Operation (2), (3) and the bio-carrier described in (4) refer to specific area >=500m2/g, and granularity is 100 ~ 150 object honeycomb stone or zeolite powders.
Operation (3) and the nutritional agents described in (4) refer to that length is the wax gourd grain of 1 ~ 5cm.
Biologic product 1 described in operation (2) refers to the compound probiotic microorganisms containing photosynthetic bacteria, lactic acid bacteria, ferment and Bifidobacterium.
Operation (3) and the biological deodorant described in (4) refer to the compound probiotic microorganisms containing EM bacterium.
Biologic product 2 described in operation (3) refers to the compound probiotic microorganisms containing photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, ferment and lactic acid bacteria.
Biologic product 3 described in operation (4) refers to the compound probiotic microorganisms containing soil improvement bacterium, depollution of environment bacterium, photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, ferment and lactic acid bacteria.
Above-mentioned ecology synthesis treatment process also can be applicable to other organic wastes as organic matters such as stalks, the preferred cornstalk of described stalk and sorghum stalk.
Technique tool of the present invention has the following advantages and beneficial effect:
(1) technique of the present invention is without the need to extruding and drying and dehydrating process dish leaf, and energy consumption is low, generate without sewage, without the need to arranging supporting sewage disposal system, is easy to industrialization;
(2) technique of the present invention is substantially by the comprehensive utilization of all parts of waste vegetable leaves, and excellent dish leaf is prepared into rich lactobacteria-containing ferment ensilage, can be widely used in feeding or mix and feeding of ox, sheep, pig, goose, chicken etc.; Good dish leaf is prepared into liquid probiotics feed addictive, and the feed that can be widely used in poultry and aquaculture is mixed and fed; Inferior dish leaf is prepared into liquid probiotics fertilizer, vegetables and fruits, tealeaves, tobacco leaf and landscape flower can be widely used in and make organic fertilizer application, and the sorting ratio of described excellent dish leaf, good dish leaf and inferior dish leaf also suitably can adjust according to the conditions of demand of product and production capacity situation, realizes maximum twice laid;
(3) biologic product used in technique of the present invention is probiotic microorganisms, nontoxic corrosion-free to people and animals, can not produce secondary pollution.
Detailed description of the invention
Below in conjunction with embodiment, the present invention is described in further detail, but embodiments of the present invention are not limited thereto.
Embodiment 1
A kind of waste vegetable leaves ecology synthesis treatment process of the present embodiment, concrete operations operation is as follows:
(1) be excellent, good and inferior three classifications by waste vegetable leaves according to the situation artificial separation of addling;
(2) the excellent dish leaf vegetable-chopper sorted out is chopped into 0.5 ~ 3cm long fragment dish grain, then with conveying worm feeding to the silage silo that ferments, conveying worm adds the righting agent of dish leaf quality 2% in feeding process, the bio-carrier of 2.5% and 4% containing photosynthetic bacteria, lactic acid bacteria, the compound probiotic microorganisms of ferment and Bifidobacterium, make it fully to be uniformly mixed with dish grain, the dish grain sending into fermentation silage silo is degraded at normal temperatures, activation, fermentation, through 5 days, obtain rich lactobacteria-containing ferment silage production, for ox after the packing of product, sheep, pig, goose, feeding or mixing of chicken etc. is fed,
(3) the good dish leaf will sorted out, carry out size degradation with dish leaf disintegrator and become puree, it is 90% that puree adds clear water to moisture content according to actual conditions, add the righting agent of dish leaf quality 1.5% simultaneously, the length of 2% is the wax gourd grain of 1 ~ 5cm, the bio-carrier of 3%, the compound probiotic microorganisms containing EM bacterium of 0.8% and 4.5% containing photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, the compound probiotic microorganisms of ferment and lactic acid bacteria obtains mixing puree, then mixing puree liquid is sent into and degrade with in the retort stirred, activation and fermentation, react 6 days under normal temperature, obtain liquid probiotics feedstuff additive product, product pump is stored to groove tank, then mix with tank car outward transport or the filling feed for poultry and aquaculture and feed,
(4) inferior dish leaf will be sorted out, carry out size degradation with dish leaf disintegrator and become puree, it is 90% that puree adds clear water to moisture content according to actual conditions, add the righting agent of dish leaf quality 1.2% simultaneously, the length of 3% is the wax gourd grain of 1 ~ 5cm, the bio-carrier of 6%, the compound probiotic microorganisms containing EM bacterium of 1% and 5% containing soil improvement bacterium, depollution of environment bacterium, photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, the compound probiotic microorganisms of ferment and lactic acid bacteria, then mixing puree is sent into and degrade with in the retort stirred, activation and fermentation, react 7 days under normal temperature, obtain liquid probiotics organic fertilizer product, product pump is stored to groove tank, then with tank car outward transport or filling for vegetables and fruits, tealeaves, tobacco leaf and landscape flower make organic fertilizer application.
In the present embodiment operation (2), (3) and the righting agent prescription described in (4) and technique as follows: by mass parts, hawthorn 1 part, rice sprout 2 parts, 2 parts, Fructus Hordei Germinatus, Momordica grosvenori 1 part, chrysanthemum 1 part, 2 parts, brown sugar and 191 parts, clear water are mixed, boil and obtain for fried 60 minutes.
Operation (2), (3) and the bio-carrier described in (4) refer to that specific area is 500m2/g, and granularity is 100 object honeycomb stones.
Embodiment 2
A kind of waste vegetable leaves ecology synthesis treatment process of the present embodiment, concrete operations operation is as follows:
(1) be excellent, good and inferior three classifications by waste vegetable leaves according to the situation artificial separation of addling;
(2) the excellent dish leaf vegetable-chopper sorted out is chopped into 0.5 ~ 3cm long fragment dish grain, then with conveying worm feeding to the silage silo that ferments, conveying worm adds the righting agent of dish leaf quality 3% in feeding process, the bio-carrier of 3% and 6% containing photosynthetic bacteria, lactic acid bacteria, the compound probiotic microorganisms of ferment and Bifidobacterium, make it fully to be uniformly mixed with dish grain, the dish grain sending into fermentation silage silo is degraded at normal temperatures, activation, fermentation, through 7 days, obtain rich lactobacteria-containing ferment silage production, for ox after the packing of product, sheep, pig, goose, feeding or mixing of chicken etc. is fed,
(3) the good dish leaf will sorted out, carry out size degradation with dish leaf disintegrator and become puree, it is 90% that puree adds clear water to moisture content according to actual conditions, add the righting agent of dish leaf quality 2% simultaneously, the length of 3% is the wax gourd grain of 1 ~ 5cm, the bio-carrier of 5%, the compound probiotic microorganisms containing EM bacterium of 0.5% and 3% containing photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, the compound probiotic microorganisms of ferment and lactic acid bacteria obtains mixing puree, then mixing puree liquid is sent into and degrade with in the retort stirred, activation and fermentation, react 6 days under normal temperature, obtain liquid probiotics feedstuff additive product, product pump is stored to groove tank, then mix with tank car outward transport or the filling feed for poultry and aquaculture and feed,
(4) inferior dish leaf will be sorted out, carry out size degradation with dish leaf disintegrator and become puree, it is 90% that puree adds clear water to moisture content according to actual conditions, add the righting agent of dish leaf quality 0.5% simultaneously, the length of 1% is the wax gourd grain of 1 ~ 5cm, the bio-carrier of 3%, the compound probiotic microorganisms containing EM bacterium of 0.5% and 3% containing soil improvement bacterium, depollution of environment bacterium, photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, the compound probiotic microorganisms of ferment and lactic acid bacteria, then mixing puree is sent into and degrade with in the retort stirred, activation and fermentation, react 5 days under normal temperature, obtain liquid probiotics organic fertilizer product, product pump is stored to groove tank, then with tank car outward transport or filling for vegetables and fruits, tealeaves, tobacco leaf and landscape flower make organic fertilizer application.
In the present embodiment operation (2), (3) and the righting agent prescription described in (4) and technique as follows: by mass parts, hawthorn 2 parts, rice sprout 3 parts, 3 parts, Fructus Hordei Germinatus, Momordica grosvenori 2 parts, chrysanthemum 2 parts, 3 parts, brown sugar and 185 parts, clear water are mixed, boil and obtain for fried 30 minutes.
Operation (2), (3) and the bio-carrier described in (4) refer to that granularity is 150 object zeolite powders.
Above-described embodiment is the present invention's preferably embodiment; but embodiments of the present invention are not restricted to the described embodiments; change, the modification done under other any does not deviate from Spirit Essence of the present invention and principle, substitute, combine, simplify; all should be the substitute mode of equivalence, be included within protection scope of the present invention.
Claims (10)
1. a waste vegetable leaves ecology synthesis treatment process, is characterized in that: described technique comprises following operational sequence:
(1) be excellent, good and inferior three classifications by waste vegetable leaves according to the situation artificial separation of addling;
(2) the excellent dish leaf vegetable-chopper sorted out is chopped into 0.5 ~ 3cm long fragment dish grain, then with conveying worm feeding to the silage silo that ferments, conveying worm add in feeding process the righting agent of dish leaf quality 1% ~ 3%, the bio-carrier of 2% ~ 3% and 3% ~ 6% the prebiotic engineered microbes biologic product 1 of compound, make it fully to be uniformly mixed with dish grain, the dish grain sending into fermentation silage silo is degraded at normal temperatures, is activated, fermentation, through 5 ~ 7 days, obtain rich lactobacteria-containing ferment ensilage;
(3) the good dish leaf will sorted out, carry out size degradation with dish leaf disintegrator and become puree, add simultaneously the righting agent of dish leaf quality 1% ~ 3%, 2% ~ 3% nutritional agents, the bio-carrier of 2% ~ 5%, the biological deodorant of 0.5% ~ 1% and 3% ~ 6% biologic product 2 obtain mix puree, then mixing puree liquid is sent into and carry out degrading, activating and fermentation with in the retort stirred, react 5 ~ 7 days under normal temperature, obtain liquid probiotics feed addictive;
(4) inferior dish leaf will be sorted out, carry out size degradation with dish leaf disintegrator and become puree, add simultaneously the righting agent of dish leaf quality 0.5% ~ 2%, 1% ~ 3% nutritional agents, the bio-carrier of 3% ~ 6%, the biological deodorant of 0.5% ~ 1% and 3% ~ 5% biologic product 3, then mixing puree is sent into and carry out degrading, activating and fermentation with in the retort stirred, react 5 ~ 7 days under normal temperature, obtain liquid probiotics fertilizer.
2. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, it is characterized in that: operation (2), (3) and the righting agent prescription described in (4) and preparation technology as follows: by mass parts, hawthorn 1 ~ 2 part, rice sprout 2 ~ 3 parts, 2 ~ 3 parts, Fructus Hordei Germinatus, Momordica grosvenori 1 ~ 2 part, chrysanthemum 1 ~ 2 part, 2 ~ 3 parts, brown sugar and 185 ~ 191 parts, clear water are mixed, boil and obtain for fried 30 ~ 60 minutes.
3. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: operation (2), (3) and the bio-carrier described in (4) refer to specific area>=500m
2/ g, granularity is 100 ~ 150 object honeycomb stone or zeolite powders.
4. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: operation (3) and the nutritional agents described in (4) refer to that length is the wax gourd grain of 1 ~ 5cm.
5. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: the biologic product 1 described in operation (2) refers to the compound probiotic microorganisms containing photosynthetic bacteria, lactic acid bacteria, ferment and Bifidobacterium.
6. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: operation (3) and the biological deodorant described in (4) refer to the compound probiotic microorganisms containing EM bacterium.
7. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: the biologic product 2 described in operation (3) refers to the compound probiotic microorganisms containing photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, ferment and lactic acid bacteria.
8. a kind of waste vegetable leaves ecology synthesis treatment process according to claim 1, is characterized in that: the biologic product 3 described in operation (4) refers to the compound probiotic microorganisms containing soil improvement bacterium, depollution of environment bacterium, photosynthetic bacteria, cellulase, hemicellulase, lignoenzyme, ferment and lactic acid bacteria.
9. the application of the technique described in any one of claim 1 ~ 8 in other organic waste treatments.
10. application according to claim 9, is characterized in that: described organic waste refers to cornstalk and sorghum stalk.
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Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104803724A (en) * | 2015-05-22 | 2015-07-29 | 浦北县科学技术开发中心 | Method for treating processing waste liquid and waste residues of banana leaf sheathes for knotting artwork |
| CN104892040A (en) * | 2015-05-22 | 2015-09-09 | 浦北县科学技术开发中心 | Treatment method of banana leaf sheath processing waste liquor and waste slag |
| CN105130520A (en) * | 2015-09-02 | 2015-12-09 | 李而宏 | Treatment method and equipment for vegetable and fruit waste |
| CN106721050A (en) * | 2016-12-11 | 2017-05-31 | 钱树青 | A kind of method that utilization waste vegetable leaves produce ensilage |
| CN107445657A (en) * | 2017-09-25 | 2017-12-08 | 中南民族大学 | A kind of method that organic fertilizer is prepared using vegetables waste dish |
| CN107788224A (en) * | 2017-10-15 | 2018-03-13 | 河北圆成环保科技有限公司 | A kind of agricultural fertilizer or livestock fodder additives and preparation method thereof |
| CN110759761A (en) * | 2019-11-07 | 2020-02-07 | 云南嘉谷环保有限公司 | Biological treatment method for waste vegetable leaves |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1699297A (en) * | 2004-09-09 | 2005-11-23 | 珠海市绿色世界生物科技有限公司 | Process for preparing organic liquid fertilizer and organic solid fertilizer |
| CN101117302A (en) * | 2007-07-12 | 2008-02-06 | 谢忠贤 | Method for preparing biological organic-inorganic polyvalent environment protective composite fertilizer |
| CN101990982A (en) * | 2009-08-25 | 2011-03-30 | 张伟 | Additive for mutton sheep fattening silage |
| CN102172260A (en) * | 2011-03-11 | 2011-09-07 | 通海县福慧科技有限公司 | Recycling production process of discarded vegetable leaves |
| CN102951939A (en) * | 2012-11-02 | 2013-03-06 | 湖南回龙湖现代农业科技有限公司 | Rapid harmless plant organic residue treatment and fertilizer utilization process and equipment thereof |
-
2014
- 2014-10-13 CN CN201410539474.3A patent/CN104366010A/en active Pending
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1699297A (en) * | 2004-09-09 | 2005-11-23 | 珠海市绿色世界生物科技有限公司 | Process for preparing organic liquid fertilizer and organic solid fertilizer |
| CN101117302A (en) * | 2007-07-12 | 2008-02-06 | 谢忠贤 | Method for preparing biological organic-inorganic polyvalent environment protective composite fertilizer |
| CN101990982A (en) * | 2009-08-25 | 2011-03-30 | 张伟 | Additive for mutton sheep fattening silage |
| CN102172260A (en) * | 2011-03-11 | 2011-09-07 | 通海县福慧科技有限公司 | Recycling production process of discarded vegetable leaves |
| CN102951939A (en) * | 2012-11-02 | 2013-03-06 | 湖南回龙湖现代农业科技有限公司 | Rapid harmless plant organic residue treatment and fertilizer utilization process and equipment thereof |
Non-Patent Citations (5)
| Title |
|---|
| 中国人民解放军第一八一医院: "长贮发酵饲料的制作和使用", 《微生物学通报》 * |
| 方栋: "厨房弃物可制不臭肥土", 《花木盆景》 * |
| 曾伟: "菜叶青贮是猪鸡的好饲料", 《新农业》 * |
| 连新: "青菜叶的青贮", 《中国畜牧杂志》 * |
| 郑霞林等: "家庭自制有机肥4法及简易去臭9法", 《农村新技术》 * |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104803724A (en) * | 2015-05-22 | 2015-07-29 | 浦北县科学技术开发中心 | Method for treating processing waste liquid and waste residues of banana leaf sheathes for knotting artwork |
| CN104892040A (en) * | 2015-05-22 | 2015-09-09 | 浦北县科学技术开发中心 | Treatment method of banana leaf sheath processing waste liquor and waste slag |
| CN105130520A (en) * | 2015-09-02 | 2015-12-09 | 李而宏 | Treatment method and equipment for vegetable and fruit waste |
| CN105130520B (en) * | 2015-09-02 | 2018-11-06 | 李而宏 | The processing method and equipment of vegetables and fruit waste |
| CN106721050A (en) * | 2016-12-11 | 2017-05-31 | 钱树青 | A kind of method that utilization waste vegetable leaves produce ensilage |
| CN107445657A (en) * | 2017-09-25 | 2017-12-08 | 中南民族大学 | A kind of method that organic fertilizer is prepared using vegetables waste dish |
| CN107788224A (en) * | 2017-10-15 | 2018-03-13 | 河北圆成环保科技有限公司 | A kind of agricultural fertilizer or livestock fodder additives and preparation method thereof |
| CN110759761A (en) * | 2019-11-07 | 2020-02-07 | 云南嘉谷环保有限公司 | Biological treatment method for waste vegetable leaves |
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