CN109824391A - A kind of tylosin dreg compost method of resource - Google Patents

A kind of tylosin dreg compost method of resource Download PDF

Info

Publication number
CN109824391A
CN109824391A CN201910233636.3A CN201910233636A CN109824391A CN 109824391 A CN109824391 A CN 109824391A CN 201910233636 A CN201910233636 A CN 201910233636A CN 109824391 A CN109824391 A CN 109824391A
Authority
CN
China
Prior art keywords
tylosin
dreg
compost
resource according
compost method
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201910233636.3A
Other languages
Chinese (zh)
Other versions
CN109824391B (en
Inventor
汪群慧
杨民
吴川福
谢栋
高明
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
University of Science and Technology Beijing USTB
Original Assignee
University of Science and Technology Beijing USTB
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by University of Science and Technology Beijing USTB filed Critical University of Science and Technology Beijing USTB
Priority to CN201910233636.3A priority Critical patent/CN109824391B/en
Publication of CN109824391A publication Critical patent/CN109824391A/en
Application granted granted Critical
Publication of CN109824391B publication Critical patent/CN109824391B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The present invention provides a kind of tylosin dreg compost method of resource, belongs to hazardous waste recycling field.Comprise the concrete steps that: tylosin dreg handles 0.5~3h first at 90~170 DEG C, and 5%~30%H is added by solid-to-liquid ratio 1:1~4:1 later2O2Continue to handle 1.5~4h at 90~170 DEG C until moisture content is reduced to 20~40%;Tylosin dreg uses sawdust, mushroom bran, rubbish from cooking as auxiliary material after pretreatment, and is inoculated with hot fermentation microbial inoculum and carries out compost, and heap body hot stage heap body core temperature is greater than 55 DEG C and holding 8 days or more;Material handles 1~4h at 100~170 DEG C after compost.Operation of the present invention is simple, easy, and tylosin removal effect is good in tylosin dreg, while meeting organic fertilizer standard, high-quality can be made and without environmental risk organic fertilizer.

Description

A kind of tylosin dreg compost method of resource
Technical field
The present invention relates to solid waste disposals and resource technology field, refer in particular to a kind of tylosin dreg heap fertile resource Change method.
Background technique
A kind of tylosin, macrolide antibiotics by Microbe synthesis, is made an addition to feed addictive extensively, is used Livestock disease is caused simultaneously by bacterium (such as gram-positive bacterium) in prevention and treatment, tylosin can also play certain Promote the effect of the growth and development of domestic animal.However, will inevitably generate a kind of organic solid in tylosin production process Waste-tylosin dreg.Its nutritional ingredient rich in, microorganism catabolite and a small amount of remaining antibiotic, It such as deals with improperly, will lead to remaining antibiotic and spread in the environment such as soil, surface water even underground water, while antibiotic is anti- Property bacterium will cause the environmental risk of antibiotics resistance gene.
As the byproduct of tylosin production process, tylosin dreg yield is huge.According to investigations, the safe happy bacterium in Shandong 1 ton of tylosin of the plain every production of factory will generate 12 tons of tylosin dregs.In China, from 2008, antibiotic bacterium dregs By for hazardous solid waste, disposition must comply with biomass pyrolytic, burning, landfill and relevant hazardous waste processing side Formula.Wherein, the main method as processing antibiotic bacterium dregs is burned, residual antibiotic can be quickly converted to carbon dioxide and nitrogen Oxide etc..But antibiotic burning disposal is costly at present (it is estimated that being 4000 yuan/ton), causes 1 ton of every production safe happy Rhzomorph production cost will increase nearly 50000 yuan.Therefore, from the viewpoint of sustainable, safe pleasure can be effectively treated by finding one kind Rhzomorph bacteria residue residual antibiotic, and the method that can realize tylosin dreg resource utilization, have important practical significance.
Compost is a kind of tradition and economic and environment-friendly method, can convert debirs to valuable organic soil and change Good dose.In this process, organic matter is degraded to stable humus, is a kind of to clean cheap product.In addition, research table Bright compost can also effectively remove remaining antibiotic in matrix, be more than 70% to most antibiotic removal rates, part antibiotic (macrolides) can be more than 95%, therefore the present invention is directed to develop 1 set of processing tylosin dreg compost method of resource, weight Removal of the point for tylosin in tylosin dreg.
Summary of the invention
The present invention provides a kind of tylosin dreg compost method of resource, can by hazardous waste tylosin dreg into Row recycling forms organic fertilizer, provides certain reference for antibiotic bacterium dregs method of resource from now on.
A kind of tylosin dreg compost method of resource, it is characterised in that:
(1) tylosin dreg need to be pre-processed, i.e., 0.5~3h is handled at 90~170 DEG C, press solid-to-liquid ratio 1 later: 5%~30%H is added in 1~4:12O2Continue to handle 1.5~4h at 90~170 DEG C until moisture content is reduced to 20~40%;
(2) tylosin dreg should use sawdust, mushroom bran, rubbish from cooking as auxiliary material after pre-processing, and be inoculated with high temperature hair Yeast-like fungi agent carries out compost, and heap body hot stage heap body core temperature is greater than 55 DEG C and holding 8 days or more;
(3) material handles 1~4h at 100~170 DEG C after compost.
Further, it to divulge information in the preprocessing process, ventilation is carried out by time relay control air blower, work week Phase is to open 15min, closes 15min, and ventilation quantity is 0.1~0.2m3/h。
Further, the material proportion of the compost is tylosin dreg after pretreatment: sawdust: mushroom bran: rubbish from cooking =5:3:2:1.
Further, the During High-Temperature Composting microbial inoculum additive amount is 0.3%~2%, and microbial inoculum dosing method is first and part heap Fertile material mixes activation, then mixes with all materials.
Further, it needs that moisture is replenished in time according to material water ratio in the composting process, guarantees that hot stage is aqueous Rate is maintained at 40%~70%, and total rate of water make-up control is in 1~50L/m3Windrow d.
Further, turning is needed daily in the composting process, using mechanical stirring turning or manual turning.
Further, the final gained more initial windrow loss of weight 30~50% of fertilizer of step (3).
Further, pretreatment mode can also first be leached using clear water using tylosin dreg, reused alkali and adjusted pH To 10~12,5%~30%H is added2O2, handled 1~4 hour at 60~100 DEG C.
Further, after tylosin dreg is preprocessed and compost recycling treatment, wherein tylosin concentration by 8~ 15g/kg (dry weight) is reduced to detection limit or less (< 1mg/kg).
Further, tylosin dreg is preprocessed, after compost recycling and high-temperature process, and gained fertilizer meets organic The requirements of fertile standard (NY525-2011).
The method of the present invention is easy to operate, easy, and tylosin removal effect is good in tylosin dreg, while satisfaction has The high-quality organic fertilizer of no environmental risk can be made in machine fertilizer standard, and can realize that tylosin zero remains.
Specific embodiment
Experimental comparison has investigated using this method and unused this method in tylosin dreg aerobic composting process Tylosin residual and removal rate, and the indices of production fertilizer.
Embodiment 1 (present invention)
Tylosin dreg handles 1h at 130 DEG C, and 15%H is added by solid-to-liquid ratio 2:1 later2O2Continue at 130 DEG C 2.5h is managed, tylosin dreg uses sawdust, mushroom bran, rubbish from cooking as auxiliary material after pretreatment, tylosin dreg: sawdust: Mushroom bran: rubbish from cooking=5:3:2:1, using clear water adjust initial aqueous rate be 60%, and be inoculated with 0.5% hot fermentation microbial inoculum into Row compost, time are 15 days, carry out artificial turning daily, are aerated using time relay control air blower, the duty cycle To open 15min, 15min, ventilation quantity 0.15m are closed3/ h, heap body hot stage heap body core temperature are greater than 55 DEG C and keep 8 days, material handled 2h at 130 DEG C after compost.(< 1mg/ is not detected in tylosin residual in the obtained composting production of the present embodiment Kg), tylosin removal rate is 100%, and gained fertilizer percentage of seedgermination is 98.5%.
Embodiment 2 (comparative example)
Using tylosin dreg same as Example 1, (1) is not preprocessed unlike embodiment;(2) and bacterium Chaff carries out mixing compost in the ratio of 1:2;(3) the air blower ventilation operation period is to open 1h, closes 1h, ventilation quantity 0.1m3/ H, heap body core temperature are greater than 55 DEG C and only maintain 4 days;(4) During High-Temperature Composting terminates material and is not heat-treated.The present embodiment institute Obtaining tylosin residual in composting production is 1.5g/kg, and tylosin removal rate is 54%, percentage of seedgermination 58%.
Experimental result comparative analysis:
Compared with comparative example, the present invention mainly has some different (1) first to be pre-processed, and makes in tylosin dreg Most of tylosin remains to have obtained effective removal, and the tylosin concentration into composting system has obtained significantly It reduces, at the same time, tylosin mitigates the inhibiting effect of microorganism, and the stability for the entire composting system for being has obtained pole The earth improves;(2) auxiliary material that joined this high C/N of sawdust in mixing improves the C/N of entire composting system, high C/N Carbon is utilized conducive to microorganism, the activity of microorganism is strengthened, so that heap body either maximum temperature or hot stage continue Time has all obtained great promotion;(3) by reducing ventilation interval time, increasing ventilatory capacity the oxygen supply of composting system is filled Foot, conducive to well support microorganism activity, conducive to tylosin removal and windrow it is decomposed;(4) During High-Temperature Composting terminate material into Row heat treatment, can be made high-quality and the organic fertilizer without environmental risk.
These differences directly result in comparative example tylosin residual it is excessively high, fertilizer rotten degree is inadequate, and percentage of seedgermination is too low, It is unsatisfactory for organic fertilizer standard, and the present invention can effectively remove tylosin, the decomposed degree of fertilizer is good, meets organic fertilizer mark It is quasi-.(NY525-2011).Embodiment described above 1 is the preferred embodiment of the present invention, it is noted that for the art Those of ordinary skill for, without departing from the principles of the present invention, several improvements and modifications can also be made, this A little improvements and modifications also should be regarded as protection scope of the present invention.

Claims (10)

1. a kind of tylosin dreg compost method of resource, it is characterised in that:
(1) tylosin dreg need to be pre-processed, i.e., at 90~170 DEG C handle 0.5~3h, later by solid-to-liquid ratio 1:1~ 5%~30%H is added in 4:12O2Continue to handle 1.5~4h at 90~170 DEG C until moisture content is reduced to 20~40%;
(2) tylosin dreg should use sawdust, mushroom bran, rubbish from cooking as auxiliary material after pre-processing, and be inoculated with hot fermentation bacterium Agent carries out compost, and heap body hot stage heap body core temperature is greater than 55 DEG C and holding 8 days or more;
(3) material handles 1~4h at 100~170 DEG C after compost.
2. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: the pretreatment It to divulge information in the process, ventilation is carried out by time relay control air blower, and the duty cycle is to open 15min, closes 15min, is led to Air quantity is 0.1~0.2m3/h。
3. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: the material of compost Proportion is tylosin dreg after pretreatment: sawdust: mushroom bran: rubbish from cooking=5:3:2:1.
4. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: During High-Temperature Composting bacterium Agent additive amount is 0.3%~2%, and microbial inoculum dosing method is first to mix to activate with part compost material, then mix with all materials.
5. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: in composting process Moisture need to be replenished in time according to material water ratio, guarantee that hot stage moisture content is maintained at 40%~70%, total rate of water make-up control In 1~50L/m3Windrow d.
6. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: in composting process Turning is needed daily, using mechanical stirring turning or manual turning.
7. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: final gained fertilizer Expect more initial windrow loss of weight 30~50%.
8. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: pretreatment mode It can also first be leached using clear water using tylosin dreg, reuse alkali and adjust pH to 10~12,5%~30%H is added2O2, It is handled 1~4 hour at 60~100 DEG C.
9. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: tylosin bacterium After slag is preprocessed and compost recycling treatment, wherein tylosin concentration by 8~15g/kg (dry weight) be reduced to detection limit with Under (< 1mg/kg).
10. a kind of tylosin dreg compost method of resource according to claim 1, it is characterised in that: tylosin Bacteria residue is preprocessed, after compost recycling and high-temperature process, and gained fertilizer meets the items of organic fertilizer standard (NY525-2011) It is required that.
CN201910233636.3A 2019-03-26 2019-03-26 Tylosin fungus dreg compost recycling method Active CN109824391B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910233636.3A CN109824391B (en) 2019-03-26 2019-03-26 Tylosin fungus dreg compost recycling method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910233636.3A CN109824391B (en) 2019-03-26 2019-03-26 Tylosin fungus dreg compost recycling method

Publications (2)

Publication Number Publication Date
CN109824391A true CN109824391A (en) 2019-05-31
CN109824391B CN109824391B (en) 2021-01-26

Family

ID=66872229

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910233636.3A Active CN109824391B (en) 2019-03-26 2019-03-26 Tylosin fungus dreg compost recycling method

Country Status (1)

Country Link
CN (1) CN109824391B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111410567A (en) * 2020-03-27 2020-07-14 山东鲁抗中和环保科技有限公司 Circulating type antibiotic bacterium residue compost and waste gas treatment method
CN114455988A (en) * 2022-02-11 2022-05-10 山东鲁抗中和环保科技有限公司 Tylosin fungus dreg compost fermentation process

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103641529A (en) * 2013-11-18 2014-03-19 宁夏泰瑞制药股份有限公司 Biological organic fertilizer and preparation method thereof
CN104086244A (en) * 2014-06-26 2014-10-08 北京质智天成环境科技有限公司 Method for converting humus by biologically fermenting antibiotic mushroom dregs
CN105418195A (en) * 2015-12-29 2016-03-23 哈尔滨工业大学 Method of preparing composite organic fertilizer from biological pharmacy mycelium sludge
CN106110562A (en) * 2016-06-29 2016-11-16 上海化工研究院 A kind of for removing the method for griseofulvin in biological medicine waste residue
CN106588386A (en) * 2016-12-29 2017-04-26 华北制药河北华民药业有限责任公司 Harmless treatment method of antibiotic fermented mushroom residues for manufacturing organic fertilizer
CN107337496A (en) * 2017-08-09 2017-11-10 哈尔滨工业大学 A kind of method that organic fertilizer is produced using tylosin dreg
CN107337497A (en) * 2017-08-11 2017-11-10 哈尔滨工业大学 A kind of method that organic fertilizer is produced using aminoglycoside antibiotics bacteria residue
CN108500034A (en) * 2018-03-27 2018-09-07 中广核达胜加速器技术有限公司 A kind of antibiotic bacterium residues processing technique
CN108653971A (en) * 2018-03-27 2018-10-16 上海化工研究院有限公司 A method of remaining penicillin antibiotics in removal biological medicine waste residue
CN109160841A (en) * 2018-11-20 2019-01-08 贵州兴源利民农业发展有限公司 A kind of gardens flowers and trees matrix fertilizer using antibiotic bacterium dregs production

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103641529A (en) * 2013-11-18 2014-03-19 宁夏泰瑞制药股份有限公司 Biological organic fertilizer and preparation method thereof
CN104086244A (en) * 2014-06-26 2014-10-08 北京质智天成环境科技有限公司 Method for converting humus by biologically fermenting antibiotic mushroom dregs
CN105418195A (en) * 2015-12-29 2016-03-23 哈尔滨工业大学 Method of preparing composite organic fertilizer from biological pharmacy mycelium sludge
CN106110562A (en) * 2016-06-29 2016-11-16 上海化工研究院 A kind of for removing the method for griseofulvin in biological medicine waste residue
CN106588386A (en) * 2016-12-29 2017-04-26 华北制药河北华民药业有限责任公司 Harmless treatment method of antibiotic fermented mushroom residues for manufacturing organic fertilizer
CN107337496A (en) * 2017-08-09 2017-11-10 哈尔滨工业大学 A kind of method that organic fertilizer is produced using tylosin dreg
CN107337497A (en) * 2017-08-11 2017-11-10 哈尔滨工业大学 A kind of method that organic fertilizer is produced using aminoglycoside antibiotics bacteria residue
CN108500034A (en) * 2018-03-27 2018-09-07 中广核达胜加速器技术有限公司 A kind of antibiotic bacterium residues processing technique
CN108653971A (en) * 2018-03-27 2018-10-16 上海化工研究院有限公司 A method of remaining penicillin antibiotics in removal biological medicine waste residue
CN109160841A (en) * 2018-11-20 2019-01-08 贵州兴源利民农业发展有限公司 A kind of gardens flowers and trees matrix fertilizer using antibiotic bacterium dregs production

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
公丕成,等: "我国抗生素菌渣资源化研究新进展", 《环境工程》 *
卢啸旸,等: "灰黄霉素医药残渣氧化处理技术及其在农业施肥领域的应用前景", 《化肥工业》 *
武深树: "《畜禽粪便污染防治技术》", 31 December 2014, 湖南科学技术出版社 *
王琪等: "《国内外危险废物豁免管理实践》", 31 July 2012, 中国环境科学出版社 *
耿晓玲: "基于"强化碱解+H2O2氧化"土霉素菌渣物化减量化技术研究", 《河北科技大学硕士学位论文》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111410567A (en) * 2020-03-27 2020-07-14 山东鲁抗中和环保科技有限公司 Circulating type antibiotic bacterium residue compost and waste gas treatment method
CN114455988A (en) * 2022-02-11 2022-05-10 山东鲁抗中和环保科技有限公司 Tylosin fungus dreg compost fermentation process

Also Published As

Publication number Publication date
CN109824391B (en) 2021-01-26

Similar Documents

Publication Publication Date Title
Taiwo et al. Influence of composting techniques on microbial succession, temperature and pH in a composting municipal solid waste
CN102775201B (en) Carbon-sequestering high-activity microbial organic fertilizer and preparation method thereof
CN102942395B (en) Preparation method of aerobic high-temperature static compost by using corrosion-promoting compost composite fermentation bacteria agent
CN108002871A (en) A kind of method that rubbish from cooking makes green fertilizer material
CN104370582B (en) A kind of organic waste odorless aerobic compost method
CN107986828A (en) A kind of agricultural organic waste highly effective compost method
CN103708967A (en) Method for producing organic fertilizer by using pig manures
CN106220259B (en) A kind of organic waste deodorant based on wormcast and complex microorganism
CN104892096B (en) A kind of method of livestock waste rapid draing Composting
CN106746428A (en) A kind of high-temperature aerobic fermentation method for sludge treatment and device
CN108558471A (en) A kind of organic treatment method changing rejected material to useful resource of rural area mixing
CN106242830A (en) A kind of acceleration biodegradable adjuvant of garden garbage and application thereof
CN102850098A (en) Production method of efficient odorless organic fertilizer
CN109824391A (en) A kind of tylosin dreg compost method of resource
CN107011002A (en) A kind of biological integrated treatment technology of organic domestic waste
CN109650957A (en) A kind of superhigh temperature pretreatment compost method reducing nitrogen gas loss
CN206417986U (en) A kind of high-temperature aerobic fermentation sludge treatment equipment
CN105087413A (en) Preparation and application of complex microbial inoculants capable of fermenting livestock and poultry excrement effectively and quickly
CN101624300A (en) Method for removing heavy metal in solid organic waste compost
CN106916766A (en) Microorganism hybrid solid fermentation method degraded antibiotic bacterium dregs formula and technique
WO2014032314A1 (en) Palm oil byproduct biological humic acid, production method thereof and biological humic acid conversion agent used in the method
CN104419654A (en) Organic fertilizer microbial agent produced by rapid fermentation of edible fungus residue and method for producing organic fertilizer by same
CN110819554B (en) Extreme thermophilic bacteria and application thereof in high-temperature compost fermentation
CN102732465A (en) Thermophilic facultative aerobic bacteria UTM601 and application thereof
CN107759417A (en) A kind of mushroom slag biological fertilizer and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant