CN102381822A - Multi-strain compound microbial high-temperature rapid-digestion sludge harmless treatment method - Google Patents

Multi-strain compound microbial high-temperature rapid-digestion sludge harmless treatment method Download PDF

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Publication number
CN102381822A
CN102381822A CN2011101997428A CN201110199742A CN102381822A CN 102381822 A CN102381822 A CN 102381822A CN 2011101997428 A CN2011101997428 A CN 2011101997428A CN 201110199742 A CN201110199742 A CN 201110199742A CN 102381822 A CN102381822 A CN 102381822A
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accounts
sludge
temperature
bacillus
compound microbial
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刘建伦
张景致
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

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  • Treatment Of Sludge (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

The invention discloses a multi-strain compound microbial high-temperature rapid-digestion sludge harmless treatment process method, and the process comprises the following steps: adding a modifier in to sludge for modification, performing pressure filtration and dehydration to obtain a water content of the sludge of below 40%, adding an edible fungus medium (waste material), eupatorium odoratum, tobacco stem slag, fly ash, lanthanide oxides, and composite microbial strains into a material conversion machine, mixing, stirring, spraying compound microbial high-temperature strains, stacking for fermentation; the odor is eliminated after 30 min; heavy metal is passivated after 2 hours; the fermentation starts quickly; after stacking for 24 hours and 48 hours, the stack temperature is above 70 DEG C and below 85 DEG C, and the temperature is preserved for 3 days. The materials rapidly become thoroughly decomposed; with the application of the high-temperature microbial agent, cellulose substances which are difficult to decompose under natural conditions are decomposed acceleratedly as a result of the strong decomposition function of the agent. Material preparation by the sludge realizes quantitative reduction and harmless treatment, and lays a foundation for subsequent resource utilization. Materials prepared by the sludge can be further processed into biological carbon, and the like.

Description

Many bacterial classifications compound microbial high temperature is cleared up sludge harmless treatment method fast
Technical field
The present invention relates to sludge of sewage treatment plants and clear up fast, subtract the method for appearance, no stink, heavy metal-passivated, harmless treatment process fast at thermophilic fermentation.
Background technology
The sludge of sewage treatment plants treatment and disposal; Take landfill, burning, compost, thermal treatment in the past, add heat drying, add treatment processs such as alkali is stable; The mud landfill is not finally to avoid environmental pollution just to delay the time that environmental pollution produces, so landfill is not the sludge treatment best bet.
The burning facility investment is big, and running cost is higher, and the control obnoxious flavour has certain degree of difficulty.Sludge composting, floor space is big, and the spontaneous fermentation time is long, and probiotics and harmful bacterium are also deposited, and the microbiobacterial agent leavening temperature is no more than 65 ℃ mostly, and it is not thorough to become thoroughly decomposed, and heavy metals exceeding standard is difficult to the soil utilization.Thermal treatment, add heat drying.The heating power mummification.The finding mode is many in the market, for example turns round sleeve mummification, garden dish desiccation machine, low temperature fluidized-bed, paddle drying machine, fume afterheat mummification etc.But which kind of form that don't work all is to remove moisture with heat energy, is with energy replacement, " with hot heat exchange ", and be " little to change greatly ", but this is unallowed on technical concept.Result in real world applications is that efficient is low, investment is big, and running cost is high.Though application is arranged in the market, this is caving-in bash.It is stable to add alkali, handles not thoroughly, and cost is higher relatively, and fund input is relatively large.Because the singularity and the intractability of mud more than are difficult to reach minimizing, the innoxious and recycling that sludge treatment is disposed.
Summary of the invention
The present invention mainly solves be utilize many bacterial classifications compound microbial high temperature to clear up the mud process method fast it can make mud subtract appearance fast; The volume decrement of mud is to original about 1/5; Product is stable, no stink, heavy metal-passivated, pathogen-free domestic, and the sludge product purposes after the biological treatment is many.
Its process method is:
The mud of Sewage Plant carries out modification through adding properties-correcting agent to mud, with pump mud is sent into the elasticity plate-and-frame filter press then; After treating that mud is filled, the beginning filter-press dehydration reaches below 40% moisture percentage in sewage sludge, and mud is transferred pH value about 6; Add culture medium of edible fungus (waste material) 3~8%, Herba Eupatorii Odorati (pulverizing) 2~6%, tobacco rod slag 3~6%, flyash 6~10%, lanthanide oxide 0.5~1%, complex micro organism fungicide 0.3~1% gets into to mix in the material transforming machine and stirs and spray compound microbial high-temperature strain; The fermentation of banking up, stink is eliminated after 30 minutes, 2 hours post-passivation heavy metals; Fermentation starting is fast, piles up after 24 hours, and heap temperature rises 50~60 ℃; The heap temperature reaches more than 70 ℃ after 48 hours, and below 85 ℃, this temperature kept 3 days.Material becomes thoroughly decomposed soon, because after using this high temperature microbial inoculum, strong decomposition function makes difficult under field conditions (factors) material accelerate decompsn of decomposing such as cellulose substances; Material becomes thoroughly decomposed thoroughly simultaneously; Organism is degraded fast, and stink is removed rapidly, and heavy metal obtains effective passivation.Reached harmless treatment, for follow-up recycling is laid a good foundation.Fermenting process is an aerobic fermentation.Bacterial classification is 0.3~1%: 100 with the ratio of material.
The compound microbial microbial inoculum
Actinomycetes (Actinomycete); Bacillus licheniformis (Bacillus Licheniformis); Bacillus pumilus (Bacillus pumilus); Pseudomonas (Pseudomonas Preparation); Fermentation Cytophaga (Cytophaga fermentans); Pseudomonas boreopolis (Photosynthetic bacteria); Photosynthetic bacteria (Photosynthetic bacteria); White-rot fungi (Basidiomycetes); Produce yellowish fiber Zymomonas mobilis (Cellulomonas flavigena); Pantothenic acid props up genus bacillus (Bacillus pantothenticus); Bacillus megaterium (Bacillus magaterium); Thermoactinomyces (Thermophillc actinomycetes); Yeast (Yeast); Germ oligotrophy unit cell (Stenotrophomonas maitophilia); Phanerochaete chrysosporium (Phanerochaete chrysosporium); Lactobacterium acidophilum (Lactobacillus acidophilus); 17 kinds of bacterium of husky thunder bacterium (Serratia) mix to be cultivated
Said cultivation is that Actinomycete accounts for 2~6% by weight; Bacillus Licheniformis accounts for 16~20%; Bacillus pumilus accounts for 3~7%; Pseudomonas Preparation accounts for 1~5%; Cytophaga fermentans accounts for 4~11%; Photosynthetic bacteria accounts for 8~15%; Photosynthetic bacteria accounts for 3~10%; Basidiomycetes accounts for 6~14%; Cellulomonas flavigena accounts for 5~9%; Bacillus pantothenticus accounts for 2.5~5%; Bacillus magaterium accounts for 7~11%; Thermophillc actinomycetes accounts for 11~15%; Yeast accounts for 13~19%; Stenotrophomonas maitophilia accounts for 9~14%; Phanerochaete chrysosporium accounts for 4~10%; Lactobacillus acidophilus accounts for 2.5~6%; Serratia accounts for 3~8%
The explanation of the used addition material of the present invention is following:
Culture medium of edible fungus (waste material) is the dead meal behind the fruiting,
Herba Eupatorii Odorati is the wild grass of the Nature,
The tobacco rod slag is a waste,
Lanthanide oxide is a mineral substance.
Sludge product purposes after the processing according to the invention is many, the ability recycling,
Mud material after treatment; Total nutrient content is high, water ratio be low, organic content is high, pH value 6.5~8; Product is stable, no stink, pathogen-free domestic biology, heavy metal reach agricultural standards, increases soil fertility, and the soil is porous to reach soil; Reduce disease and pest; Contain the multiple beneficial microbial bacteria, can promote even, lasting, the fully absorption of crop, can prepare following product: desert afforestation modifying agent, saline-alkali soil conditioner, the quick-acting modifying agents of acid soil, special-purpose particle, charcoal, carbon rod, the fuel etc. of afforesting of beach saline land nutrition.

Claims (2)

1. clear up sewage sludge harmlessness treatment process method fast with many bacterial classifications compound microbial high temperature, it is characterized in that:
(1), prepares burden by the per-cent of following composition weight: add culture medium of edible fungus (waste material) 3~8%, Herba Eupatorii Odorati (pulverizing) 2~6%, tobacco rod slag 3~6%, flyash 6~10%, lanthanide oxide 0.5~1%, composite microbial bacteria 0.3~1% in the sludge of sewage treatment plants;
(2), mud is carried out modification, with pump mud is sent into the elasticity plate-and-frame filter press then by adding properties-correcting agent in the said sludge of sewage treatment plants, treat that mud is filled after, the beginning filter-press dehydration reaches below 40% moisture percentage in sewage sludge;
(3), the per-cent by said weight sprays many bacterium compound microbial high-temperature strain then, in the material transforming machine, thorough mixing is even, the fermentation of banking up; Stink is eliminated after 30 minutes, 2 hours post-passivation heavy metals, and fermentation starting is fast, piles up after 24 hours; Heap temperature rises 50~60 ℃, and after 48 hours, the heap temperature reaches more than 70 ℃, below 85 ℃; This temperature kept 3 days, and material becomes thoroughly decomposed soon, because after using this high temperature microbial inoculum, strong decomposition function makes difficult under field conditions (factors) material accelerate decompsn of decomposing such as cellulose substances; Material becomes thoroughly decomposed thoroughly simultaneously, and organism is degraded fast, and stink is removed rapidly, and heavy metal obtains effective passivation.
2. clear up sewage sludge harmlessness treatment process method fast according to many bacterial classifications of the said usefulness of claim 1 compound microbial high temperature; It is characterized in that; Said many bacterial classifications compound microbial is that actinomycetes, Bacillus licheniformis, bacillus pumilus, pseudomonas, fermentation Cytophaga, northern city Zymomonas mobilis, photosynthetic bacteria, white-rot fungi, product yellowish fiber Zymomonas mobilis, pantothenic acid prop up genus bacillus, bacillus megaterium, thermoactinomyces, yeast, germ oligotrophy unit cell, Phanerochaete chrysosporium, Lactobacterium acidophilum, 17 kinds of bacterium of husky thunder bacterium and mix and cultivate, and said cultivation is that Actinomycete accounts for 2~6% by weight, Bacillus Licheniformis accounts for 16~20%, Bacillus pumilus accounts for 3~7%, Pseudomonas Preparation accounts for 1~5%, Cytophaga fermentans accounts for 4~11%, Photosynthetic bacteria accounts for 8~15%, Photosynthetic bacteria accounts for 3~10%, Basidiomycetes accounts for 6~14%, Cellulomonas flavigena accounts for 5~9%, Bacillus pantothenticus accounts for 2.5~5%, Bacillus magaterium accounts for 7~11%, Thermophillc actinomycetes accounts for 11~15%, Yeast accounts for 13~19%, Stenotrophomonas maitophilia accounts for 9~14%, Phanerochaete chrysosporium accounts for 4~10%, Lactobacillus acidophilus accounts for 2.5~6%, Serratia accounts for 3~8%.
CN2011101997428A 2011-07-18 2011-07-18 Multi-strain compound microbial high-temperature rapid-digestion sludge harmless treatment method Pending CN102381822A (en)

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Cited By (26)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102643748A (en) * 2012-05-09 2012-08-22 刘建伦 Sludge-reduced microorganism combined dominant population in sewage processing
CN102659296A (en) * 2012-05-31 2012-09-12 北京师范大学 Method for controlling lake plant siltation by white rot fungi
CN103337652A (en) * 2013-06-14 2013-10-02 国家电网公司 Novel fuel cell
CN103337651A (en) * 2013-06-14 2013-10-02 国家电网公司 Biological-agent fuel cell
CN103910476A (en) * 2014-03-25 2014-07-09 山东省科学院能源研究所 Municipal dewatered sludge accessory-free bio-drying method on basis of sodium hydroxide pretreatment
CN104761110A (en) * 2015-04-03 2015-07-08 李文新 Sludge treatment method for sewage plants
CN104773933A (en) * 2015-04-03 2015-07-15 李文新 Treatment system for sewage plant sludge
CN104926052A (en) * 2015-05-15 2015-09-23 刘婷 Recyclable sludge treatment method
CN104926053A (en) * 2015-05-15 2015-09-23 刘婷 Sludge treatment method
CN104945188A (en) * 2015-04-14 2015-09-30 珠海市清宇环保科技有限公司 Compound microbial organic fertilizer for improvement of saline-alkali soil and preparation method thereof
CN105061037A (en) * 2015-08-03 2015-11-18 山东沃科奇实业有限公司 Microbial organic fertilizer containing modified municipal sludge, and preparation method thereof
CN105217912A (en) * 2015-09-14 2016-01-06 广州市净水有限公司 A kind of municipal sludge efficient energy-saving quick biological drying technology
CN105950502A (en) * 2016-05-17 2016-09-21 浙江大学 Complex endophytic bacterial inoculant and application thereof in phytoremediation of heavy metal contaminated soil
CN106047750A (en) * 2016-06-01 2016-10-26 上海汉禹环保科技有限公司 Microbial agent for humus organic matter degradation and preparation method thereof
CN106116069A (en) * 2016-08-01 2016-11-16 鹏鹞环保股份有限公司 A kind of combined method of efficient process municipal sludge
CN107032573A (en) * 2017-05-16 2017-08-11 广州大学 A kind of method of available state copper and mickel in utilization white-rot fungi collaboration compost passivation municipal sludge
CN108636343A (en) * 2018-05-21 2018-10-12 天津城建大学 A kind of reinforcing absorption clinker and preparation method thereof and purposes
CN109588272A (en) * 2018-12-13 2019-04-09 浙江大学 The method of one heavy metal species river bottom mud preparation ecological engineering planting matrix
CN109761672A (en) * 2019-03-12 2019-05-17 珠海聚碳复合材料有限公司 A method of sludge is handled using compound Thermophilic Bacteria
CN109851400A (en) * 2019-03-06 2019-06-07 上海交通大学 The self-heating sludge superhigh temperature aerobic compost method and device of strain temperature control stage by stage
CN110127986A (en) * 2019-05-15 2019-08-16 河北九知农业科技有限公司 A kind of sludge reduction, innoxious, resource utilization method and product line device
CN110316921A (en) * 2018-03-30 2019-10-11 福建鑫盛润环境咨询合伙企业(有限合伙) A method of domestic sludge is disposed using superhigh temperature aerobic microbiological fermentation process
CN110438041A (en) * 2019-07-22 2019-11-12 常德职业技术学院 A kind of Novel compound microbial agent for Treatment of Sludge
CN110526532A (en) * 2019-09-26 2019-12-03 山东大学 Utilize the innoxious method with minimizing processing sludge preparation gardens fertilizer of microorganism
CN110922136A (en) * 2019-12-13 2020-03-27 福州大学 Water permeable brick prepared from dredged mud and preparation method thereof
CN111235052A (en) * 2019-12-10 2020-06-05 北京工商大学 Thermophilic bacillus licheniformis and application thereof

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Cited By (34)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102643748A (en) * 2012-05-09 2012-08-22 刘建伦 Sludge-reduced microorganism combined dominant population in sewage processing
CN102659296A (en) * 2012-05-31 2012-09-12 北京师范大学 Method for controlling lake plant siltation by white rot fungi
CN103337651B (en) * 2013-06-14 2015-08-26 国家电网公司 A kind of Biological-agent fuel cell
CN103337652A (en) * 2013-06-14 2013-10-02 国家电网公司 Novel fuel cell
CN103337651A (en) * 2013-06-14 2013-10-02 国家电网公司 Biological-agent fuel cell
CN103337652B (en) * 2013-06-14 2015-09-02 国家电网公司 A kind of fuel cell
CN103910476A (en) * 2014-03-25 2014-07-09 山东省科学院能源研究所 Municipal dewatered sludge accessory-free bio-drying method on basis of sodium hydroxide pretreatment
CN103910476B (en) * 2014-03-25 2015-11-04 山东省科学院能源研究所 Based on the municipal dewatered sludge of NaOH pretreatment without the biological dewatered method of auxiliary material
CN104773933A (en) * 2015-04-03 2015-07-15 李文新 Treatment system for sewage plant sludge
CN104761110A (en) * 2015-04-03 2015-07-08 李文新 Sludge treatment method for sewage plants
CN104773933B (en) * 2015-04-03 2016-07-06 重庆鼎旺环保园林有限公司 A kind of process system of sewage plant sludge
CN104945188A (en) * 2015-04-14 2015-09-30 珠海市清宇环保科技有限公司 Compound microbial organic fertilizer for improvement of saline-alkali soil and preparation method thereof
CN104926052A (en) * 2015-05-15 2015-09-23 刘婷 Recyclable sludge treatment method
CN104926053A (en) * 2015-05-15 2015-09-23 刘婷 Sludge treatment method
CN104926052B (en) * 2015-05-15 2017-11-17 刘婷 A kind of method for sludge treatment of recoverable
CN105061037A (en) * 2015-08-03 2015-11-18 山东沃科奇实业有限公司 Microbial organic fertilizer containing modified municipal sludge, and preparation method thereof
CN105061037B (en) * 2015-08-03 2018-01-23 山东沃科奇实业有限公司 A kind of microbial organic fertilizer containing modified municipal sludge and preparation method thereof
CN105217912A (en) * 2015-09-14 2016-01-06 广州市净水有限公司 A kind of municipal sludge efficient energy-saving quick biological drying technology
CN105950502A (en) * 2016-05-17 2016-09-21 浙江大学 Complex endophytic bacterial inoculant and application thereof in phytoremediation of heavy metal contaminated soil
CN105950502B (en) * 2016-05-17 2019-09-06 浙江大学 A kind of compound endogenetic bacteria microbial inoculum and its application in heavy-metal contaminated soil phytoremediation
CN106047750A (en) * 2016-06-01 2016-10-26 上海汉禹环保科技有限公司 Microbial agent for humus organic matter degradation and preparation method thereof
CN106116069A (en) * 2016-08-01 2016-11-16 鹏鹞环保股份有限公司 A kind of combined method of efficient process municipal sludge
CN107032573A (en) * 2017-05-16 2017-08-11 广州大学 A kind of method of available state copper and mickel in utilization white-rot fungi collaboration compost passivation municipal sludge
CN110316921A (en) * 2018-03-30 2019-10-11 福建鑫盛润环境咨询合伙企业(有限合伙) A method of domestic sludge is disposed using superhigh temperature aerobic microbiological fermentation process
CN108636343A (en) * 2018-05-21 2018-10-12 天津城建大学 A kind of reinforcing absorption clinker and preparation method thereof and purposes
CN109588272A (en) * 2018-12-13 2019-04-09 浙江大学 The method of one heavy metal species river bottom mud preparation ecological engineering planting matrix
CN109851400A (en) * 2019-03-06 2019-06-07 上海交通大学 The self-heating sludge superhigh temperature aerobic compost method and device of strain temperature control stage by stage
CN109761672A (en) * 2019-03-12 2019-05-17 珠海聚碳复合材料有限公司 A method of sludge is handled using compound Thermophilic Bacteria
CN110127986A (en) * 2019-05-15 2019-08-16 河北九知农业科技有限公司 A kind of sludge reduction, innoxious, resource utilization method and product line device
CN110438041A (en) * 2019-07-22 2019-11-12 常德职业技术学院 A kind of Novel compound microbial agent for Treatment of Sludge
CN110526532A (en) * 2019-09-26 2019-12-03 山东大学 Utilize the innoxious method with minimizing processing sludge preparation gardens fertilizer of microorganism
CN111235052A (en) * 2019-12-10 2020-06-05 北京工商大学 Thermophilic bacillus licheniformis and application thereof
CN110922136A (en) * 2019-12-13 2020-03-27 福州大学 Water permeable brick prepared from dredged mud and preparation method thereof
CN110922136B (en) * 2019-12-13 2021-06-01 福州大学 Water permeable brick prepared from dredged mud and preparation method thereof

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