CN106925593A - A kind of method of antibiotic fermentation bacteria residue solidification dehydration - Google Patents

A kind of method of antibiotic fermentation bacteria residue solidification dehydration Download PDF

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Publication number
CN106925593A
CN106925593A CN201511006120.3A CN201511006120A CN106925593A CN 106925593 A CN106925593 A CN 106925593A CN 201511006120 A CN201511006120 A CN 201511006120A CN 106925593 A CN106925593 A CN 106925593A
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antibiotic
bacteria residue
solidification
dehydration
fermentation
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Chinese (zh)
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刘庆芬
周畅
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Institute of Process Engineering of CAS
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Institute of Process Engineering of CAS
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/48Solid fuels essentially based on materials of non-mineral origin on industrial residues and waste materials

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Fertilizers (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention provides a kind of method of antibiotic fermentation bacteria residue solidification dehydration, methods described is:Antibiotic fermentation bacteria residue is mixed with solidification dehydrating agent, curing reaction, the moisture in removing antibiotic fermentation bacteria residue is carried out;Wherein, the solidification dehydrating agent is:Any number of in hydrate, absorbable moisture or the inorganic matter that can be reacted with water and/or organic matter or at least two combination can be formed.The bacteria residue solid mixt that the curing reaction is produced recycling or can carry out burning disposal directly or after being dehydrated.Methods described can be by fast dewatering temperature and complete dehydration temperaturre the reduction 10-90% of the bacteria residue that ferments;Solve the problems, such as that transport difficult, easy secondary fermentation are stored under antibiotic fermentation wet bacteria slag normal temperature produces the treatment process cost such as pollution, dehydration high, be that antibiotic fermentation wet bacteria slag low cost recycling and harmless treatment provide a kind of new method.

Description

A kind of method of antibiotic fermentation bacteria residue solidification dehydration
Technical field
Technical field is utilized the invention belongs to the treatment of antibiotic fermentation bacteria residue and changing waste into resources, is related to a kind of anti- The method of raw element fermentation bacteria residue solidification dehydration, more particularly to one kind is right to process with antibiotic fermentation wet bacteria slag As realizing the side of the dehydration of antibiotic fermentation bacteria residue low-cost solidification and its recycling and harmless treatment Method.
Background technology
China is antibiotics production state maximum in the world, and the 90% of global antibiotic bulk drug carries by China For.The production process of antibiotic bulk drug includes the unit process such as fermentation, extraction, refined.In fermentation process Middle to produce substantial amounts of antibiotic fermentation bacteria residue, China there are about 2,000,000 tons of antibiotic fermentation bacteria residues and urgently locates every year Reason.Antibiotic fermentation bacteria residue is main by fermentation mycelium, residual antibiotic, remaining culture medium and other generations Thank to product.Antibiotic bacterium dregs are mishandling, and residual antibiotic therein may induce generation drug-fast bacteria and super Bacterium, China is listed within 2008《National Hazard waste register》, antibiotic bacterium dregs are by dangerous solid Discarded object is strictly supervised.
The antibiotic fermentation wet bacteria slag content of organic matter is enriched, and has the value of recycling;But wet bacteria slag is normal Warm easily secondary fermentation, self-dissolving is thinning, distributes stench, pollutes environment.Wet bacteria slag moisture content is generally 70-90%, and moisture combined with bacteria residue in colloidal state, in the absence of free water, the mechanical means such as centrifugation is difficult to Dehydration.At present, burn and specification landfill is only antibiotic bacterium dregs processing method for meeting regulation, but There is a problem of high cost and easily cause secondary pollution.
In the research of antibiotic fermentation bacteria residue processing method, Zhang Guangyi et al. have studied hydro-thermal process antibiotic Bacteria residue dehydration prepares solid bio-fuel, and the hydrothermal condition of optimization is 180-200 DEG C for the treatment of 30-60min, institute The solid bio-fuel moisture content of preparation is in 45%-48%.Hydrothermal reaction condition harshness is, it is necessary to high temperature and height Pressure carries out dehydration, and high energy consumption, processing cost is high.
CN 104212840A disclose a kind of processing method of antibiotic fermentation bacteria residue, including can by hydrochloric acid woods The fermentation bacteria residue of mycin and gentamicin is well mixed with water, is configured to suspension;Then suspension is carried out Anaerobic fermentation treatment.Methods described is a kind of efficient hair of the bacteria residue that fermented to Lincomycin Hydrochloride and gentamicin Ferment handling process.But, methods described cannot in time process a large amount of antibiotic bacterium dregs and its secondary fermentation, and And it is relatively costly.CN 102728142A disclose a kind of processing method of antibiotic bacterium dregs high-efficiency dehydration, institute Processing method is stated to comprise the following steps:A bacteria residue by test, is obtained the isoelectric point value of bacteria residue by ();(b) Bacteria residue is added into acid solution or alkali lye, isoelectric point value of its pH value obtained by step (a) is adjusted to;C () will In step (b) products therefrom, flocculant solution, stirring, precipitation, filtering are added, you can.But, institute State the method high cost of antibiotic bacterium dregs dehydration, complex operation.
The content of the invention
For antibiotic fermentation bacteria residue yield at this stage is big, the treatment process cost such as easy secondary fermentation and dehydration Situation high, it is described it is an object of the invention to provide a kind of method of antibiotic fermentation bacteria residue solidification dehydration Method can at normal temperatures realize the solidification dehydration of wet bacteria slag, solve and be difficult under antibiotic fermentation bacteria residue normal temperature Storage, the problem of transport, are that antibiotic fermentation wet bacteria slag low cost recycling and harmless treatment are provided A kind of new method.
It is that, up to this purpose, the present invention uses following technical scheme:
The invention provides a kind of method of antibiotic fermentation bacteria residue solidification dehydration, methods described is:By antibiosis Element fermentation bacteria residue mixes with solidification dehydrating agent, carries out curing reaction, the water in removing antibiotic fermentation bacteria residue Point;Wherein, the solidification dehydrating agent is:Hydrate, absorbable moisture or the nothing that can be reacted with water can be formed Any number of in machine thing and/or organic matter or at least two combination.
It is described solidification dehydrating agent can be:Organic matter that hydrate can be formed, the inorganic matter that hydrate can be formed, The organic matter of absorbable moisture, the inorganic matter of absorbable moisture, the inorganic matter that can be reacted with water or can be anti-with water In the organic matter answered any one or at least two combination.Typical but non-limiting solidification dehydrating agent group It is combined into:The inorganic matter and the inorganic matter that can be reacted with water of hydrate can be formed, the organic matter of hydrate can be formed With the inorganic matter of absorbable moisture, the organic matter that can be reacted with water, the organic matter of absorbable moisture and can be formed The organic matter of hydrate, can be formed hydrate organic matter, can with water react inorganic matter, hydration can be formed The inorganic matter of thing and the organic matter etc. that can be reacted with water.
The solidification dehydrating agent is alternatively and contains the nothing that can form hydrate, absorbable moisture or can be reacted with water Any number of in machine thing and/or organic matter or the mixture of at least two combination.
Those skilled in the art can solidify each component in dehydrating agent according to actual antibiotic bacterium dregs regulation, So as to reach more preferable dehydrating effect.
The antibiotic fermentation bacteria residue with solidification dehydrating agent reaction mechanism be:By solidifying dehydrating agent and bacteria residue Mixing, destroy the colloform texture of bacteria residue, the transformation of moisture existence form in bacteria residue is realized, so as to reduce Dehydration temperaturre, reduces dehydration cost.
The present invention is using the dehydrating agent that solidifies as described above by the moisture removal in antibiotic fermentation bacteria residue.Solidification is anti- The bacteria residue solid mixt biochemical property stabilization that should be produced, will not further secondary fermentation.Solve antibiotic Be difficult to the problem that stores, transport under fermentation bacteria residue normal temperature, and antibiotic bacterium dregs secondary fermentation problem, be Antibiotic fermentation wet bacteria slag low cost recycling and harmless treatment provide a kind of new method.
The antibiotic fermentation bacteria residue derives from beta-lactam antibiotic (such as penicillin), macrolide Class antibiotic (such as erythromycin), aminoglycoside antibiotics (such as streptomysin), Tetracyclines antibiosis Plain (such as terramycin), amphenicols antibiotic (such as chloramphenicol), polypeptide antibiotics are (as through the ages Mycin etc.), act on antibiotic (such as lincomycin, lindamycin, mould through the ages of gram-positive bacteria Element, bacitracin etc.), act on gram- bacteria antibiotic (such as polymyxins, phosphonomycin, ciramycin, Seromycin, rifampin etc.), antimycotic antibiotic (such as griseofulvin), antineoplastic antibiotic (such as Mitomycin, actinomycin D, bleomycin or adriamycin etc.) or antibiotic with immunosuppressive action In (such as cyclosporin) any one or at least two combination.Typical but non-limiting combination For:Beta-lactam antibiotic and macrolide antibiotics, aminoglycoside antibiotics, Tetracyclines resist Raw element and amphenicols antibiotic, polypeptide antibiotics and the antibiotic for acting on gram-positive bacteria, effect Antibiotic, antimycotic antibiotic, antineoplastic antibiotic in gram- bacteria with there is immunosuppressive action Antibiotic, beta-lactam antibiotic, macrolide antibiotics, aminoglycoside antibiotics and Fourth Ring Plain class antibiotic.
The inorganic matter and/or organic matter for forming hydrate is that can form the inorganic salts of hydrate and/or have Machine salt.
Preferably, the inorganic salts for forming hydrate be sulfate, carbonate, ammonium salt, hydrochloride or In sulphite any one or at least two combination.It is typical but non-limiting to be combined as:Sulfate With sulfate, sulfate and carbonate, carbonate and carbonate, carbonate and ammonium salt, hydrochloride, sulfurous Hydrochlorate and sulfate, carbonate, ammonium salt, hydrochloride and sulphite.
Preferably, the inorganic salts for forming hydrate be sodium carbonate, magnesium chloride, ammonium chloride, calcium chloride, In aluminum sulfate, magnesium sulfate, copper sulphate, sodium sulphate or sodium acetate any one or at least two combination. It is typical but non-limiting to be combined as:Sodium carbonate and magnesium chloride, ammonium chloride, calcium chloride and aluminum sulfate, sulfuric acid Magnesium, copper sulphate, sodium sulphate and sodium acetate, sodium carbonate, magnesium chloride, ammonium chloride and calcium chloride etc..
Preferably, the inorganic matter of the absorbable moisture is anhydrous silica gel.
Preferably, the inorganic matter that can be reacted with water is calcium oxide.
The antibiotic fermentation bacteria residue is 1 with the mass ratio of the solidification dehydrating agent:0.2-1:3, such as 1:0.5、 1:0.8、1:1.0、1:1.2、1:1.5、1:1.8、1:2.0、1:2.3、1:2.5 or 1:2.8 etc., consider solid Change the factors, preferably 1 such as dehydrating agent cost, bacteria residue treatment effeciency and treatment effect:1-1:2, both can be with Ensure the effect of bacteria residue solidification dehydration, bacteria residue treatment effeciency and relatively low solidification dehydration higher can be ensured again Cost.
The temperature of the curing reaction be 0-100 DEG C, such as 5 DEG C, 10 DEG C, 15 DEG C, 20 DEG C, 30 DEG C, 40 DEG C, 50 DEG C, 60 DEG C, 70 DEG C, 80 DEG C, 90 DEG C or 95 DEG C etc., preferably 15-50 DEG C.
The time of the curing reaction because choose solidification dehydrating agent and bacteria residue treating capacity it is different and different, Curing reaction terminal is to obtain what dry and comfortable solid mixt determined.
During the antibiotic fermentation bacteria residue is mechanical agitation, stirs or extrude with the mode that mix of solidification dehydrating agent Any one or at least two combination.It is typical but non-limiting to be combined as:Mechanical agitation with stir, Mechanical agitation and extruding, mechanical agitation, stir and extruding.The purpose of the mixing be will solidification dehydrating agent with Antibiotic fermentation bacteria residue is well mixed, so that the uniform curing dehydration of antibiotic fermentation bacteria residue.
Used as preferred technical scheme, methods described also includes:The bacteria residue solid-state that curing reaction is produced mixes Thing carries out dewater treatment, the mode of the dewater treatment be in heating, air-dry or evaporating any one or extremely Lack two kinds of combination, the mode of dewater treatment is as described:Heating is combined with air-dried, heats and evaporation is tied Close, heating, the air-dried mode combined with evaporation are dehydrated.The bacteria residue that the curing reaction is produced is powder Shape or other shapes.The shape of the bacteria residue solid mixt is different according to the degree of its solidification dehydration.
Preferably, the temperature of the dewater treatment be 15-160 DEG C, such as 20 DEG C, 25 DEG C, 30 DEG C, 40 DEG C, 50 DEG C, 60 DEG C, 70 DEG C, 80 DEG C, 100 DEG C, 110 DEG C, 120 DEG C, 130 DEG C or 150 DEG C etc., preferably 40-80℃。
Bacteria residue solid mixt recycling after the bacteria residue solid mixt of curing reaction generation and/or dehydration Or carry out burning disposal.Bacteria residue solid-state mixing after the bacteria residue solid mixt of curing reaction generation and/or dehydration Thing can be used as solid fuel.
Used as preferred technical scheme, methods described is:It is under the conditions of 0-100 DEG C, antibiotic fermentation is wet Bacteria residue is 1 according to mass ratio with solidification dehydrating agent:0.2-1:3 mixing, form bacteria residue solid mixt;By bacteria residue Solid mixt directly or after dehydration recycling or carries out burning disposal, wherein, the temperature of the dehydration It is 15-160 DEG C.
Compared with prior art, beneficial effects of the present invention are:
(1) method of the antibiotic fermentation bacteria residue solidification dehydration that the present invention is provided, can be by the fast of bacteria residue of fermenting Fast dehydration temperaturre and complete dehydration temperaturre reduction 10-90%.By taking penicillin mushroom dregs as an example, process blue or green through the method After mycin fermentation bacteria residue, it is possible to achieve dehydration peak temperature is reduced to 71.9 DEG C, is dehydrated temperature completely by 97.4 DEG C Degree is reduced to 98.5 DEG C by 162.7 DEG C, and fermentation bacteria residue fast dewatering temperature peak reduction by 27% is dehydrated temperature completely Degree reduces by 37%, realizes inexpensive dehydration.
(2) method of the antibiotic fermentation bacteria residue solidification dehydration that the present invention is provided so that antibiotic fermentation bacteria residue Physical behavior there is huge change, dry and comfortable solid-state is changed into by original colloidal state, solve antibiotic hair The problems such as storage transport, easy secondary fermentation pollution environment are difficult under ferment wet bacteria slag normal temperature, is that recycling is carried New basis is supplied, tool is of great significance.
Brief description of the drawings
Fig. 1 is the shape appearance figure before and after the antibiotic fermentation bacteria residue solidification dehydration that embodiment 1 is provided, wherein (a) It is the shape appearance figure before solidification dehydration, (b) is the shape appearance figure after solidification dehydration.
Fig. 2 is the shape appearance figure before and after the antibiotic fermentation bacteria residue solidification dehydration that embodiment 2 is provided, wherein (a) It is the shape appearance figure before solidification dehydration, (b) is the shape appearance figure after solidification dehydration.
Fig. 3 is the shape appearance figure before and after the antibiotic fermentation bacteria residue solidification dehydration that embodiment 3 is provided, wherein (a) It is the shape appearance figure before solidification dehydration, (b) is the shape appearance figure after solidification dehydration.
Fig. 4 is the shape appearance figure before and after the antibiotic fermentation bacteria residue solidification dehydration that embodiment 4 is provided, wherein (a) It is the shape appearance figure before solidification dehydration, (b) is the shape appearance figure after solidification dehydration.
Specific embodiment
Technical scheme, but institute are further illustrated below in conjunction with the accompanying drawings and by specific embodiment There is embodiment not constitute any limitation to the present invention.
Embodiment 1
By abomacetin fermentation bacteria residue and No. 1 solidification dehydrating agent (main component is sodium carbonate) according to mass ratio 1:0.2 Mixing, carries out curing reaction under 0 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Shape appearance figure before and after the solidification dehydration of abomacetin fermentation bacteria residue is as shown in figure 1, as can be seen from the figure bacteria residue By after curing reaction, physical pattern is changed into dry and comfortable solid state powder (b) from colloidal state (a).
Embodiment 2
By penicillin fermentation bacteria residue and No. 2 solidifications dehydrating agent (main component is magnesium sulfate) according to mass ratio 1:3 mix Close, curing reaction is carried out under 100 DEG C, stirring condition, obtain dry and comfortable bacteria residue solid mixt.
Shape appearance figure before and after the solidification dehydration of penicillin fermentation bacteria residue is as shown in Fig. 2 as can be seen from the figure bacteria residue By after curing reaction, physical pattern is changed into dry and comfortable solid state powder (b) from colloidal state (a).
Embodiment 3
By griseofulvin fermentation bacteria residue and No. 3 solidifications dehydrating agent (main component is copper sulphate) according to mass ratio 1:1 Mixing, carries out curing reaction under 15 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Shape appearance figure before and after griseofulvin fermentation bacteria residue solidification dehydration is as shown in figure 3, as can be seen from the figure bacterium Slag is by after curing reaction, physical pattern is changed into dry and comfortable solid state powder (b) from colloidal state (a).
Embodiment 4
By lincomycin fermentation bacteria residue and No. 4 solidifications dehydrating agent (main component is sodium sulphate) according to mass ratio 1:2 Mixing, carries out curing reaction under 50 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Shape appearance figure before and after the solidification dehydration of lincomycin fermentation bacteria residue is as shown in figure 4, as can be seen from the figure bacterium Slag is by after curing reaction, physical pattern is changed into dry and comfortable solid state powder (b) from colloidal state (a).
Embodiment 5
By terramycin fermentation bacteria residue and No. 5 solidifications dehydrating agent (main component is zinc sulfate) according to mass ratio 1:0.8 Mixing, carries out curing reaction under 25 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Embodiment 6
By big mycin fermentation bacteria residue and No. 6 solidifications dehydrating agent (main component is ammonium chloride) according to mass ratio 1:3 mix Close, curing reaction is carried out under 25 DEG C, stirring condition, obtain dry and comfortable bacteria residue solid mixt.
Embodiment 7
By Ferment of DM bacteria residue and No. 7 solidifications dehydrating agent (main component is magnesium chloride) according to mass ratio 1:1.7 Mixing, carries out curing reaction under 45 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Embodiment 8
By streptomycin fermentation bacteria residue and No. 8 solidifications dehydrating agent (main component is calcium chloride) according to mass ratio 1:2.5 Mixing, carries out curing reaction under 50 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid mixt.
Embodiment 9
By cynnematin fermentation bacteria residue and No. 9 solidification dehydrating agents (main component is magnesium chloride, magnesium sulfate) according to matter Amount compares 1:1.5 mixing, carry out curing reaction under 50 DEG C, stirring condition, obtain dry and comfortable bacteria residue solid-state mixing Thing.
Embodiment 10
By vancomycin fermentation bacteria residue with No. 10 solidify dehydrating agent (main component is aluminum sulfate) mixtures according to Mass ratio 1:0.6 mixing, carries out curing reaction under 30 DEG C, stirring condition, obtains dry and comfortable bacteria residue solid-state and mixes Compound.
Embodiment 11
By ciramycin fermentation bacteria residue and No. 11 solidification dehydrating agents (main component is ammonium chloride, sodium sulphate) according to matter Amount compares 1:2.2 mixing, carry out curing reaction under 40 DEG C, stirring condition, obtain dry and comfortable bacteria residue solid-state mixing Thing.
Embodiment 12
Medecamycin fermentation bacteria residue is pressed with No. 12 solidification dehydrating agents (main component is sodium sulfite, sodium sulphate) According to mass ratio 1:3 mixing, carry out curing reaction under 15 DEG C, stirring condition, obtain dry and comfortable bacteria residue solid-state Mixture.
Applicant's statement, the foregoing is only specific embodiment of the invention, but protection scope of the present invention It is not limited thereto, person of ordinary skill in the field is it will be clearly understood that any skill for belonging to the art Art personnel the invention discloses technical scope in, the change or replacement that can be readily occurred in all fall within the present invention Protection domain and it is open within the scope of.

Claims (10)

1. the method for a kind of antibiotic fermentation bacteria residue solidification dehydration, it is characterised in that methods described is:Will Antibiotic fermentation bacteria residue mixes with solidification dehydrating agent, curing reaction is carried out, in removing antibiotic fermentation bacteria residue Moisture;Wherein, the solidification dehydrating agent is:Hydrate, absorbable moisture can be formed or can be reacted with water Any number of in inorganic matter and/or organic matter or at least two combination.
2. method according to claim 1, it is characterised in that the antibiotic fermentation bacteria residue source In beta-lactam antibiotic, macrolide antibiotics, aminoglycoside antibiotics, Tetracyclines antibiosis Element, amphenicols antibiotic, polypeptide antibiotics, the antibiotic for acting on gram-positive bacteria, act on The antibiotic of gram- bacteria, antimycotic antibiotic, antineoplastic antibiotic or with immunosuppressive action In antibiotic any one or at least two combination.
3. method according to claim 1 and 2, it is characterised in that the nothing for forming hydrate Machine thing and/or organic matter are the inorganic salts and/or organic salt that can form hydrate;
Preferably, the inorganic salts for forming hydrate be sulfate, carbonate, ammonium salt, hydrochloride or In sulphite any one or at least two combination;
Preferably, the inorganic salts for forming hydrate be sodium carbonate, magnesium chloride, ammonium chloride, calcium chloride, In aluminum sulfate, magnesium sulfate, copper sulphate, sodium sulphate or sodium acetate any one or at least two combination;
Preferably, the inorganic matter of the absorbable moisture is anhydrous silica gel;
Preferably, the inorganic matter that can be reacted with water is calcium oxide.
4. according to the method that one of claim 1-3 is described, it is characterised in that the antibiotic fermentation bacteria residue Mass ratio with the solidification dehydrating agent is 1:0.2-1:3, preferably 1:1-1:2.
5. according to the method that one of claim 1-4 is described, it is characterised in that the temperature of the curing reaction It is 0-100 DEG C, preferably 15-50 DEG C.
6. method according to claim 1, it is characterised in that the antibiotic fermentation bacteria residue with it is solid Change dehydrating agent mixing mode for mechanical agitation, stir or extrude in any one or at least two group Close.
7. according to the method that one of claim 1-6 is described, it is characterised in that methods described also includes:Will The bacteria residue solid mixt that curing reaction is produced carries out dewater treatment, the mode of the dewater treatment is heating, Air-dry or evaporation in any one or at least two combination.
8. method according to claim 7, it is characterised in that the temperature of the dewater treatment is 15-160 DEG C, preferably 40-80 DEG C.
9. according to the method that one of claim 1-8 is described, it is characterised in that the bacterium produced to curing reaction Bacteria residue solid mixt after slag solid mixt and/or dehydration carries out recycling or carries out at burning Reason.
10. according to the method that one of claim 1-9 is described, it is characterised in that methods described is: It is 1 according to mass ratio by antibiotic fermentation wet bacteria slag and solidification dehydrating agent under the conditions of 0-100 DEG C:0.2-1:3 mix Close, form bacteria residue solid mixt;Bacteria residue solid mixt directly or after dehydration recycling or is carried out Burning disposal, wherein, the temperature of the dehydration is 15-160 DEG C.
CN201511006120.3A 2015-12-29 2015-12-29 A kind of method of antibiotic fermentation bacteria residue solidification dehydration Pending CN106925593A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109266416A (en) * 2018-09-12 2019-01-25 湖南省万木汇生物质燃料有限责任公司 A kind of compound biomass granular fuel and its preparation method and application
CN110342966A (en) * 2019-07-12 2019-10-18 沈阳中科微道生物科技有限公司 A kind of quick, the effective dehydrating method of the useless bacteria residue of vitamin c fermenting
CN110813999A (en) * 2019-11-27 2020-02-21 湖北共同生物科技有限公司 Method for curing and dehydrating steroid compound fermentation fungus residues
CN112815638A (en) * 2020-12-31 2021-05-18 伊犁川宁生物技术股份有限公司 Method for drying erythromycin thiocyanate fungus residues

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101624256A (en) * 2008-07-09 2010-01-13 密西西比国际水务有限公司 Method and device for processing sludge and/or waste residues
CN103664126A (en) * 2012-09-20 2014-03-26 深圳市海川实业股份有限公司 Sludge curing treatment agent and method for treating sludge by use of curing treatment agent

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101624256A (en) * 2008-07-09 2010-01-13 密西西比国际水务有限公司 Method and device for processing sludge and/or waste residues
CN103664126A (en) * 2012-09-20 2014-03-26 深圳市海川实业股份有限公司 Sludge curing treatment agent and method for treating sludge by use of curing treatment agent

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张利民,李如章: "GB一青霉素菌渣的脱水处理和含糖量的测定", 《张 家 口 医 学 院 学报》 *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109266416A (en) * 2018-09-12 2019-01-25 湖南省万木汇生物质燃料有限责任公司 A kind of compound biomass granular fuel and its preparation method and application
CN110342966A (en) * 2019-07-12 2019-10-18 沈阳中科微道生物科技有限公司 A kind of quick, the effective dehydrating method of the useless bacteria residue of vitamin c fermenting
CN110813999A (en) * 2019-11-27 2020-02-21 湖北共同生物科技有限公司 Method for curing and dehydrating steroid compound fermentation fungus residues
CN112815638A (en) * 2020-12-31 2021-05-18 伊犁川宁生物技术股份有限公司 Method for drying erythromycin thiocyanate fungus residues

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