CN101869906A - Biological in-situ pretreatment method of solid organic wastes - Google Patents

Biological in-situ pretreatment method of solid organic wastes Download PDF

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Publication number
CN101869906A
CN101869906A CN201010208055.3A CN201010208055A CN101869906A CN 101869906 A CN101869906 A CN 101869906A CN 201010208055 A CN201010208055 A CN 201010208055A CN 101869906 A CN101869906 A CN 101869906A
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solid organic
bacillus
organic castoff
wastes
castoff
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CN201010208055.3A
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CN101869906B (en
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乔长晟
钟堃
蒋磊
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Tianjin Peiyang Biotrans Biotech Co Ltd
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Tianjin Peiyang Biotrans Biotech Co Ltd
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Abstract

The invention relates to an ins-situ pretreatment method of solid organic waste resources (catering wastes, domestic garbage, garbage in vegetable markets, brewer grains, distiller grains, stevia rebaudiana waste residues, traditional Chinese dregs, wastes in slaughter houses, wastes in culturing farms and the like). Mixed bacterial are added into the organic wastes at temporary storage places of the solid organic wastes (garbage cans, sewer manholes, scrapyards and the like) and stood and treated in a natural state. The invention discloses a method for effectively solving the treatment on the solid organic wastes from the generation to the treatment, which thoroughly controls the hazards brought by the solid organic wastes, such as mosquito breeding, stink, pathogenic microorganism infection and the like and provides prerequisite conditions for post treatment of the solid organic wastes and realization of hazard-free treatment, reclamation and reduction of waste resources.

Description

A kind of biological in-situ pretreatment method of solid organic wastes
Technical field
The present invention relates to a kind of solid organic castoff preprocess method, particularly, be by mixed microorganism in the solid organic castoff storing containers or the storing place it is handled, thereby controlled from the source that solid organic castoff brought such as mosquito grow, harm such as stench, cause pathogeny imcrobe infection, be the post processing of solid organic castoff simultaneously, realized that the recycling and minimizing of waste resource provides prerequisite.
Background technology
At present, along with the continuous growth of population, growth in the living standard and industry, agricultural economy are more and more flourishing, produced a large amount of solid organic castoffs every day, if these solid organic castoffs adopt landfill or burning disposal, both wasted a large amount of resources, take a large amount of soils again.In the rubbish that is produced, great majority are organic matter in food garbage, house refuse and the food market rubbish, can roughly these organic matters be divided into protein-based, starch based, fats and cellulose family, these materials all are natural organic matters, comply with the call of national conservation-minded society, these benefit materials ought to be recycled.Simultaneously, also can produce certain solid waste in the industry, in the stevioside production process, extract stevioside after, remaining a large amount of stevia rebaudiana dregs, these stevia rebaudiana dregs can be delivered to the refuse depot, invisible like this increase the workload of garbage disposal; The extraction of medicinal herb components also can bring the generation of a large amount of medium-height grass dregs of a decoction, and this part medium-height grass dregs of a decoction will be dropped.The needs of urban development, needs of economic development can find a kind of method of handling solid organic castoff so need badly, realizes the minimizing of rubbish on the one hand, on the other hand organic waste can be utilized again.The present invention provides strong prerequisite for the realization of these targets, with of the generation of these solid waste by certain means control mosquito, harmful microbe breeding and stench, for sufficient the preparation carried out in the processing of next step solid organic castoff, thereby alleviate the pressure that environment is caused, environment purification improves the appearance of the city, and reduces the use in landfill soil, realize the cleaner production of industry and agricultural, reduce purpose simultaneously the pollution of environment.
Summary of the invention
Controlled from the source that solid organic castoff brought such as mosquito grow, harm such as stench, cause pathogeny imcrobe infection, be the post processing of solid organic castoff simultaneously, realized that the recycling and minimizing of waste resource provides prerequisite.
The present invention realizes that the technical scheme of above-mentioned purpose is: will mix bacterium and mixing enzyme preparation and join in the container that has solid organic castoff, and leave standstill cultivation under the condition of (15~50 ℃) under field conditions (factors).
And described solid organic castoff comprises castoff of food and drink, house refuse and food market rubbish, brewex's grains, distillers ' grains, STEVIA REBAUDIANA waste residue, the medium-height grass dregs of a decoction, slaughterhouse discarded object, plant's discarded object etc.
And, described mixed bacterium is Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis) natto bacillus (Bacillus natto), bacillus pumilus (Bacilluspumilus), bacillus subtilis (Bacillus subtilis) and lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b), bacillus stearothermophilus (Bacillus stearothermophilus), each bacterium is cultured to the exponential phase later stage separately, difference is (0.8-1.2: 1.0-1.2: 0.8-1.0: 1.0-1.4: 0.8-1.2: 0.6-0.8 by a certain percentage, v/v) mix, the addition of Mixed Microbes is 1~5% (v/v).
And described enzyme preparation is amylase, protease, cellulase, and the ratio between the various enzymes is 1-1.5: 1-2: 0.5-2, and v/v, mixing enzyme preparation addition are 0.2%-1% (v/v).
Mixed bacterium can be in 15~50 ℃ temperature range normal growth, need not stirring and evenly mixing.
Advantage of the present invention and good effect are:
The present invention has found and a kind ofly can effectively carry out the pretreated technology of solid organic castoff original position, for the subsequent treatment of solid organic castoff provides prerequisite guarantee.
The microorganism that the present invention selects for use is people and animals and environmentally friendly safe bacterial strain, can suppress on the one hand growing of harmful microbe growth and mosquito, on the other hand, can not produce the secondary pollution such as stench etc. in its growth course.
The specific embodiment
The present invention is further described below in conjunction with four embodiment; Following embodiment is illustrative, is not determinate, can not limit protection scope of the present invention with following embodiment.
Embodiment 1:
In the dustbin that stores food garbage, add Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis), bafillus natto (Bacillus natto), bacillus pumilus (Bacilluspumilus), bacillus subtilis (Bacillus subtilis), lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b) and bacillus stearothermophilus (Bacillus stearothermophilus), adding proportion is 0.8: 1.0: 0.8 between each bacterial strain: 1.0: 0.8: 0.6: 1.0, v/v, total addition level is 1% (v/v) of food garbage discarded object, simultaneously, in the dustbin that stores food garbage, add amylase, protease, cellulase, ratio between the various enzymes is 1: 2: 0.5, v/v, the mixing enzyme preparation addition is 0.2% (v/v), environment temperature is 50 ℃, behind the in-situ treatment 8h, ordorless in the dustbin, fly maggot produces, and does not have mouldy phenomenon.
Embodiment 2:
In being mixed with the house refuse storing containers of organic waste, add Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis) natto bacillus (Bacillus natto), bacillus pumilus (Bacillus pumilus), bacillus subtilis (Bacillus subtilis) and lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b), bacillus stearothermophilus (Bacillus stearothermophilus), adding proportion is 1.0: 1.1: 0.9 between each bacterial strain: 1.3: 1.0: 0.7: 1.2, v/v, addition is 3% (v/v) of organic waste, simultaneously, in the dustbin that stores food garbage, add amylase, protease, cellulase, the ratio between the various enzymes are 1.2: 1: 1, v/v, the mixing enzyme preparation addition is 0.5% (v/v), and environment temperature is 30 ℃, behind the in-situ treatment 6h, ordorless in the container, fly maggot produces, and does not have mouldy phenomenon.
Embodiment 3:
In the waste deposit container of food market, add Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis) natto bacillus (Bacillus natto), bacillus pumilus (Bacillus pumilus, bacillus subtilis (Bacillus subtilis)) and lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b), adding proportion is 1.2: 1.2: 1.0 between each bacterial strain of bacillus stearothermophilus (Bacillus stearothermophilus): 1.4: 1.2: 0.7: 1.2, v/v, addition is 5% (v/v) of organic waste, simultaneously, in the dustbin that stores food garbage, add amylase, protease, cellulase, ratio between the various enzymes is 1.5: 1.0: 2, and v/v, mixing enzyme preparation addition are 1.0% (v/v), environment temperature is 15 ℃, behind the in-situ treatment 12h, interior ordorless in the container, fly maggot produces, and does not have mouldy phenomenon.
Embodiment 4:
To handle raw material and change brewex's grains into, processing procedure and condition and embodiment 1 are together.
Embodiment 5:
To handle raw material and change distillers ' grains into, processing procedure and condition and embodiment 1 are together.
Embodiment 6:
To handle raw material and change the STEVIA REBAUDIANA waste residue into, processing procedure and condition and embodiment 1 are together.
Embodiment 7:
To handle raw material and change the medium-height grass dregs of a decoction into, processing procedure and condition and embodiment 1 are together.
Embodiment 8:
To handle raw material and change the slaughterhouse organic waste into, processing procedure and condition and embodiment 1 are together.
Embodiment 9:
To handle raw material and change plant's organic waste into, processing procedure and condition and embodiment 1 are together.

Claims (7)

  1. One kind effectively solve solid organic castoff after generation before handle the method for disposal during this, it is characterized in that: with Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis) bafillus natto (Bacillus natto), bacillus subtilis (Bacillus subtilis), bacillus pumilus (Bacillus pumilus) and lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b), bacillus stearothermophilus (Bacillus stearothermophilus), amylase, protease, during cellulase joins in the container of depositing waste of organic matter, (15~50 ℃) leave standstill cultivation under the natural conditions, and the mosquito that can avoid solid organic castoff to produce grows, stench, harm such as cause pathogeny imcrobe infection.
  2. 2. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: described solid organic castoff comprises castoff of food and drink, house refuse and food market rubbish, brewex's grains, distillers ' grains, STEVIA REBAUDIANA waste residue, the medium-height grass dregs of a decoction, slaughterhouse discarded object, plant's discarded object etc., and may be mixed with bottle, polybag, the plastic bottle the like waste.
  3. 3. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: described mixed bacterium is Lactobacillus plantarum (Lactobacillus plantarum), streptococcus thermophilus (Str.thermophilus), streptococcus lactis (Str.lactis) bafillus natto (Bacillus natto), bacillus pumilus (Bacillus pumilus), bacillus subtilis (Bacillus subtilis) and lactobacillus bulgaricus (Lactobacillusbulgaricus, L.b), bacillus stearothermophilus (Bacillus stearothermophilus), each bacterium is cultured to the exponential phase later stage separately, difference is (0.8-1.2: 1.0-1.2: 0.8-1.0: 1.0-1.4: 0.8-1.2: 0.6-0.8 by a certain percentage, v/v) mix, the addition that mixes bacterium is 1~5% (v/v).
  4. 4. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: described enzyme is amylase, protease, cellulase, ratio between the various enzymes is 1-1.5: 1-2: 0.5-2, and v/v, mixing enzyme preparation addition are 0.2%-1% (v/v).
  5. 5. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: the auxiliary material that does not need to add each Mixed Microbes growth of any promotion.
  6. 6. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: the temperature conditions of Mixed Microbes growth is 15~50 ℃.
  7. 7. according to the pretreated technology of claims 1 described a kind of solid organic castoff original position, it is characterized in that: be the subsequent treatment of solid organic castoff simultaneously, realize that innoxious, the resource of waste resource and minimizing provide prerequisite.
CN201010208055.3A 2010-06-24 2010-06-24 Biological in-situ pretreatment method of solid organic wastes Active CN101869906B (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102381891A (en) * 2011-07-23 2012-03-21 天津北洋百川生物技术有限公司 Method for producing organic fertilizer by using activated sludge
CN102515894A (en) * 2011-11-29 2012-06-27 王丽希 Organic fertilizer chemical fertilizer and processing technology thereof
CN102941210A (en) * 2012-11-12 2013-02-27 熊鹏 Method for processing plant-based waste residue by utilizing cellulose and combining mechanical expression
CN103626533A (en) * 2013-09-12 2014-03-12 盐城工学院 Biological organic fertilizer and preparation method thereof
CN103664327A (en) * 2013-09-12 2014-03-26 盐城工学院 Compound fertilizer and preparation method thereof
CN110447765A (en) * 2019-08-23 2019-11-15 华中农业大学 A kind of method and its application preparing bafillus natto culture using distillers ' grains
CN110923155A (en) * 2020-02-19 2020-03-27 广州赛太特生物医学科技有限公司 Method for rapidly treating solid waste by using biological agent

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JP2002361215A (en) * 2001-06-06 2002-12-17 Fumitaka Hashimoto Method and device for microbial decomposition of organic waste
JP2004224682A (en) * 2003-01-27 2004-08-12 Toshiro Sekine Method of composting organic waste such as domestic animal dung or garbage
JP2007289879A (en) * 2006-04-26 2007-11-08 Jos-Knot:Kk Food waste recycling method
JP2008189511A (en) * 2007-02-05 2008-08-21 Takashi Nakashita Low-odor composting method
JP4386933B2 (en) * 2007-09-03 2009-12-16 定恒 福田 Organic waste treatment system
CN101709006A (en) * 2009-11-16 2010-05-19 天津科技大学 Method for treating solid organic wastes by biological method

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Publication number Priority date Publication date Assignee Title
DE4312923A1 (en) * 1993-04-15 1994-10-20 Looks Nahrungsmittel Recycling Process for the treatment of waste products made from vegetable substances and products made from vegetable substances, in particular food waste, that are reusable as bio-valuable substances
US6365384B1 (en) * 1999-05-05 2002-04-02 Ryusuke Iijima Method for disposing waste
JP2002361215A (en) * 2001-06-06 2002-12-17 Fumitaka Hashimoto Method and device for microbial decomposition of organic waste
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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102381891A (en) * 2011-07-23 2012-03-21 天津北洋百川生物技术有限公司 Method for producing organic fertilizer by using activated sludge
CN102515894A (en) * 2011-11-29 2012-06-27 王丽希 Organic fertilizer chemical fertilizer and processing technology thereof
CN102941210A (en) * 2012-11-12 2013-02-27 熊鹏 Method for processing plant-based waste residue by utilizing cellulose and combining mechanical expression
CN103626533A (en) * 2013-09-12 2014-03-12 盐城工学院 Biological organic fertilizer and preparation method thereof
CN103664327A (en) * 2013-09-12 2014-03-26 盐城工学院 Compound fertilizer and preparation method thereof
CN103626533B (en) * 2013-09-12 2015-12-02 济南禾依佳农业科技有限公司 Bio-organic fertilizer and preparation method thereof
CN103664327B (en) * 2013-09-12 2016-03-30 青岛金智高新技术有限公司 Compound manure and preparation method thereof
CN105541497A (en) * 2013-09-12 2016-05-04 蒋盘君 Safe pollution-free compound fertilizer and preparation method thereof
CN110447765A (en) * 2019-08-23 2019-11-15 华中农业大学 A kind of method and its application preparing bafillus natto culture using distillers ' grains
CN110447765B (en) * 2019-08-23 2021-03-23 华中农业大学 Method for preparing bacillus natto culture by using distiller's grains and application of bacillus natto culture
CN110923155A (en) * 2020-02-19 2020-03-27 广州赛太特生物医学科技有限公司 Method for rapidly treating solid waste by using biological agent

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