CN107974315A - It is a kind of to utilize the method that the dregs of a decoction and organic wastewater prepare new fuel slurry of fermenting - Google Patents

It is a kind of to utilize the method that the dregs of a decoction and organic wastewater prepare new fuel slurry of fermenting Download PDF

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Publication number
CN107974315A
CN107974315A CN201810001027.0A CN201810001027A CN107974315A CN 107974315 A CN107974315 A CN 107974315A CN 201810001027 A CN201810001027 A CN 201810001027A CN 107974315 A CN107974315 A CN 107974315A
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China
Prior art keywords
decoction
dregs
organic wastewater
slurry
fuel slurry
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CN201810001027.0A
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CN107974315B (en
Inventor
王明霞
何先标
唐量华
李亚平
赵楚
徐旭明
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Zhejiang Fengdeng green energy environmental protection Co.,Ltd.
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ZHEJIANG FENGDENG CHEMICAL CO Ltd
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    • 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
    • C10L1/00Liquid carbonaceous fuels
    • C10L1/32Liquid carbonaceous fuels consisting of coal-oil suspensions or aqueous emulsions or oil emulsions
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/24Mixing, stirring of fuel components
    • 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
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/28Cutting, disintegrating, shredding or grinding

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  • Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The present invention relates to waste water, waste processing and fuel slurry technology of preparing, it is desirable to provide a kind of to utilize the method that the dregs of a decoction and organic wastewater prepare new fuel slurry of fermenting.Including:The organic wastewater for the dregs of a decoction and the half dosage of fermenting is placed in blade agitators, and forming the dregs of a decoction by shearing pretreatment starches;Pretreated dregs of a decoction slurry and the organic wastewater of remaining dosage are added in grinder, uses wet-grinding technology and relative device that fuel slurry of the viscosity for below 1200mPas is prepared.The present invention is modified pretreatment using high speed shear to the fermentation dregs of a decoction, discharges bound combination water, overcomes that its poor fluidity, water imbibition are strong, are difficult into the shortcomings of starching.Make full use of a variety of dispersants contained in itself using organic wastewater, stabilizer, alkaline matter etc. further to nurse one's health modification to the fermentation dregs of a decoction, save substantial amounts of additive.Preparation process and flow are simple, easy to operate, and cost is low, it is not necessary to carry out complexity, high cost biochemical treatment, have obvious economical and environmentally friendly benefit.

Description

It is a kind of to utilize the method that the dregs of a decoction and organic wastewater prepare new fuel slurry of fermenting
Technical field
The present invention relates to waste water, waste processing and fuel slurry technology of preparing.In particular it relates to a kind of utilize hair The method that the ferment dregs of a decoction and organic wastewater prepare new fuel slurry.
Background technology
In recent years, developing rapidly with China's pharmaceuticals industry, generates the pharmaceutical wastes of a large amount of complicated components, to environmental protection Cause brings immense pressure.Fermentation class pharmacy is one kind of pharmaceutical industry, refer to by the method for fermentation produce antibiotic or its His active ingredient, then produces the process of medicine by the process such as separation, purifying, refined.It can be produced in fermentation pharmacy engineering The raw substantial amounts of fermentation dregs of a decoction, the main component for the dregs of a decoction that ferment is remaining fermentation medium, wherein containing microorganism mycelia residuum, The metabolite of strain, organic solvent and a small amount of medicine and its catabolite.According to statistics, the fermentation medicine that China produces every year The quantity of slag is up to 1,000,000 tons.Fermentation dregs of a decoction viscosity is big, moisture content is high (and being mostly to combine water), can be to ecological ring if mishandling Border and health produce potential threat.Early in 2008, the fermentation dregs of a decoction were just put into Chinese danger wastes register.However, Common fermentation dregs of a decoction disposal means (burning method, landfill method, fodder etc.) or cost are too high, or land occupation area is big, or There are problems that bio-safety, etc., therefore, the innoxious of the dregs of a decoction that ferment, recycling treatment problems demand solve.
Organic wastewater, is exactly the waste water based on organic pollution as its name suggests, wherein often containing substantial amounts of carbon aquation Compound, protein, lipid, cellulose etc..The source of organic wastewater is very wide, including sanitary sewage, dyeing waste water, black liquid, Pharmacy waste water etc..Organic wastewater often has the spies such as organic matter concentration height, complicated component, strong acid and strong base, colourity are high, peculiar smell is big Point, belongs to one of industrial discarded object difficult to deal with.Complex treatment process, long flow path, processing cost height are at this kind of waste water The distinguishing feature of reason process.Thus, a kind of organic wastewater disposal technology of novel environment friendly is developed, it is same that there is reality meaning well Justice.
The content of the invention
The technical problem to be solved in the present invention is overcome deficiency of the prior art, there is provided one kind using ferment the dregs of a decoction and The method that organic wastewater prepares new fuel slurry, solves the fermentation dregs of a decoction and organic wastewater minimizing, innoxious, recycling Problem.
In order to solve technical problem, solution of the invention is:
A kind of method that the dregs of a decoction and organic wastewater prepare fuel slurry of fermenting is provided, is comprised the following steps:
(1) organic wastewater for the dregs of a decoction and the half dosage of fermenting is placed in blade agitators, with turning for 800~1200rpm Fast 20~60min of Stirring, (improves the mobility and paste-forming properties of the fermentation dregs of a decoction with this by shearing pretreatment and forming the dregs of a decoction and starch Can);
(2) pretreated dregs of a decoction slurry and the organic wastewater of remaining dosage are added in grinder, using wet-grinding technology and relative device system It is standby obtain fuel slurry that viscosity is below 1200mPas (a variety of dispersants in itself that contained using organic wastewater, stabilizer, Alkaline matter etc. further nurses one's health modification to the fermentation dregs of a decoction).
In the present invention, the ratio between mass fraction of the fermentation dregs of a decoction and whole organic wastewaters is 70~90: 10~30.
In the present invention, the addition of the control fermentation dregs of a decoction and organic liquid waste, makes the matter that solid in fuel slurry is finally made It is 33~42% to measure percent concentration.
In the present invention, the fermentation dregs of a decoction are to prepare antibiotic, vitamin or amino acids drug mistake using fermentation method The mycelia residue produced in journey, its moisture content are 50~65%.
In the present invention, the organic wastewater is one in pharmacy waste water, black liquid, coal chemical industrial waste water or dyeing waste water Kind.
Inventive principle describes:
(1) pretreatment modification is carried out to the fermentation dregs of a decoction using high speed shear, the flocculent structure in the fermentation dregs of a decoction can be destroyed, made Bound cellular water is transformed into the Free water for promoting lubrication, significantly improves the mobility of the dregs of a decoction;Meanwhile by extruding, touching The comprehensive function hit, sheared, makes the fermentation dregs of a decoction be uniformly dispersed emulsifying, and improves the slurry performance of the fermentation dregs of a decoction.In addition, mistake herein Part organic wastewater is additionally added in journey, the physicochemical property and mobility to the dregs of a decoction further improve, and preliminarily form with one Determine the uniform dregs of a decoction slurry of mobility.
(2) modified dregs of a decoction slurry and remaining organic wastewater are separately added into grinder, viscosity is prepared using wet-grinding technology and relative device For the fermentation dregs of a decoction fuel slurry of below 1200mPa s.This process is added without any additive, but utilizes organic wastewater sheet The fermentation dregs of a decoction are further nursed one's health modification by a variety of dispersants that body contains, stabilizer, alkaline matter etc., meanwhile, with reference to grinder Shearing abrasive action, make in mixture that various composition blending is more preferable, and conditioning is more thorough, and surface modification effect more preferably, is prepared With certain calorific value, mobility and the preferable fuel slurry of stability.
(3) qualified fuel slurry is stored in slurry can, is sent again as needed to gasification furnace and is carried out gasification reaction, or send Combustion reaction is carried out to boiler, can also be sent outside to other users.
Continuous accumulation and ripe, technology with industrialized unit operating experience are improved with the continuous development of gasification technology Gradually strengthen for the adaptability of raw material, it is also increasingly extensive using the scope of raw material.It is rich in view of the finiteness of fossil energy Industrial by-products/discarded object containing carbon hydrogen element become potential coal, oil substitute and be widely used in studying.And send out Often containing certain organic matter (dry base heat value of the fermentation dregs of a decoction may be up to 20MJ/kg), both are made for the ferment dregs of a decoction, organic wastewater Into a kind of fuel slurry used as the raw material or auxiliary material of gasification furnace (gasification mode that raw material is conveyed with slurry form), Using gasification furnace high temperature environment by the complete decomposition and inversion of organic substance therein, become useful component and enter product rough coal Gas, can not only solve the high cost process problem of the fermentation dregs of a decoction and sewage, moreover it is possible to increase the active ingredient and heat in raw gas Value, while the organic matter in waste water is as the Sulfonates in papermaking wastewater, humic acid substance may also function as slurrying additive Effect, disperses solid matter in simultaneously stable slurry, forms the homogeneous (uniform) fluid of good fluidity, reduces gasification slurry manufacturing cost, carries High Business Economic Benefit.
Compared with prior art, advantage of the invention is that:
(1) pretreatment is modified to the fermentation dregs of a decoction using the method for high speed shear, discharges bound combination water, gram Take that its poor fluidity, water imbibition are strong, are difficult into the shortcomings of slurry.
(2) Sulfonates, humic acid substance of the organic wastewater as contained by black liquid, dyeing waste water are taken full advantage of Contained detergent, surfactant, contained phenols, ammonia nitrogen substances etc. in coal chemical industrial waste water, to the dregs of a decoction slurry that ferments Conditioning modification is carried out, has saved substantial amounts of additive.
(3) preparation process and flow are simple, easy to operate, and cost is low, it is not necessary at biochemistry that carry out complexity, high cost Reason.
(4) the fermentation dregs of a decoction and this two class of organic wastewater are converted into burn or gasify compared with the discarded object that difficulty is put Fuel slurry, makes full use of organic matter contained therein, turns waste into wealth, and has obvious economical and environmentally friendly benefit.
Brief description of the drawings
Fig. 1 is the process flow chart of the present invention.
Embodiment
Following embodiment can make the technical staff of this professional skill field more fully understand the present invention, but not to appoint Where formula limitation is of the invention.The number of the fermentation dregs of a decoction and organic wastewater refers both to mass fraction in each embodiment.
Embodiment 1
Selected materials are the antibiotic bacterium dregs and black liquid of moisture content 50% in the present embodiment.
By 80 parts of antibiotic bacterium dregs and 10 parts of Zao Zhi liquid be placed in the blade agitators of 1000rpm and carry out Stirring 60min, realizes the modified pretreatment of the dregs of a decoction, then into grinder and 10 parts of Zao Zhi liquid mixed grinding, obtained viscosity is The antibiotic bacterium dregs waste water fuel slurry of 1168mPas, the mass percent concentration of solid is 42% in fuel slurry.
Embodiment 2
Selected materials are the vitamin dregs of a decoction and coal chemical industrial waste water of moisture content 65% in the present embodiment.
90 parts of vitamin dregs of a decoction and 5 parts of coal chemical industrial waste waters are placed in the blade agitators of 1200rpm and carry out Stirring 20min, realizes the modified pretreatment of the dregs of a decoction, is into grinder and 5 parts of wastewater from chemical industry mixed grindings, obtained viscosity then The vitamin dregs of a decoction fuel slurry of 845mPas, the mass percent concentration of solid is 33% in fuel slurry.
Embodiment 3
Selected materials are the amino acid dregs of a decoction and coal chemical industrial waste water of moisture content 60% in the present embodiment.
86 parts of amino acid dregs of a decoction and 7 parts of coal chemical industrial waste waters are placed in the blade agitators of 800rpm and carry out Stirring 30min, realizes the modified pretreatment of the dregs of a decoction, is into grinder and 7 parts of coal chemical industrial waste water mixed grindings, obtained viscosity then The amino-acid medical slurry fluid fuel of 923mPas, the mass percent concentration of solid is 36% in fuel slurry.
Embodiment 4
Selected materials are the antibiotic bacterium dregs and dyeing waste water of moisture content 50% in the present embodiment.
70 parts of antibiotic bacterium dregs and 15 dyeing waste water parts are placed in the blade agitators of 1000rpm and carry out Stirring 40min, realizes the modified pretreatment of the dregs of a decoction, is into grinder and 15 parts of dyeing waste water mixed grindings, obtained viscosity then The antibiotic bacterium dregs fuel slurry of 1067mPas, the mass percent concentration of solid is 38% in fuel slurry.
Embodiment 5
Selected materials are the antibiotic bacterium dregs and pharmacy waste water of moisture content 56% in the present embodiment.
90 parts of antibiotic bacterium dregs and 5 parts of pharmacy waste waters are placed in the blade agitators of 1000rpm and carry out Stirring 50min, realizes the modified pretreatment of the dregs of a decoction, is into grinder and 5 parts of pharmacy waste water mixed grindings, obtained viscosity then The antibiotic bacterium dregs fuel slurry of 991mPas, the mass percent concentration of solid is 42% in fuel slurry.
Embodiment 6
Selected materials are the antibiotic bacterium dregs and black liquid of moisture content 65% in the present embodiment.
86 parts of antibiotic bacterium dregs and 7 parts of black liquids are placed in the blade agitators of 1000rpm and carry out Stirring 20min, realizes the modified pretreatment of the dregs of a decoction, is into grinder and 7 parts of black liquid mixed grindings, obtained viscosity then The antibiotic bacterium dregs fuel slurry of 877mPas, the mass percent concentration of solid is 33% in fuel slurry.
The application method of fuel slurry:
The fuel slurry prepared in embodiment 1-6 is stored in slurry can, send again as needed to gasification furnace into Row gasification reaction, or give to boiler and carry out combustion reaction, it can also send outside to other users and to be used as fuel.
Fuel slurry is used as auxiliary fuel in practical applications, enters gasification furnace or boiler at the same time with coal or water-coal-slurry, weight The ratio that amount accounts for main fuel is that (fuel slurry is individually to be sent into gasification furnace all the way to 0-20%, is not blended in advance with coal or water-coal-slurry It is re-fed into gasification furnace).
Gasification result is tested:
Fuel slurry in Example 1-6, is respectively used to coal water slurry entrained flow bed gasification stove by the occupation mode and carries out React and produce synthesis gas.Root is it is observed that fuel slurry gasification reaction is stablized, and gasification furnace overall operation is in order.Due to gas Change stove reaction temperature is higher, and fuel slurry is after the process fully to gasify, and there is no high-risk or standard-exceeding components for exhaust gas or residue. Table 1 is the component of caused synthesis gas when adding the fuel slurry of embodiment 1-6 respectively into coal water slurry entrained flow bed gasification stove Information, the data in table are the average value gathered three times a day.
Gas composition content during the slurry gasification of 1 dregs of a decoction of table
As shown in Table 1, the available gas component (CO+H of the dregs of a decoction slurry of each embodiment2) content is between 73.1-76.0% Between, reach the standard of commercial Application, and realize innoxious, the recycling of the dregs of a decoction and waste water.

Claims (5)

  1. A kind of 1. method that the dregs of a decoction and organic wastewater prepare fuel slurry of fermenting, it is characterised in that comprise the following steps:
    (1) organic wastewater for the dregs of a decoction and the half dosage of fermenting is placed in blade agitators, is revolved with the rotating speed of 800~1200rpm Turn 20~60min of stirring, dregs of a decoction slurry is formed by shearing pretreatment;
    (2) pretreated dregs of a decoction slurry and the organic wastewater of remaining dosage are added in grinder, is prepared into using wet-grinding technology and relative device To the fuel slurry that viscosity is below 1200mPas.
  2. 2. the according to the method described in claim 1, it is characterized in that, mass fraction of the fermentation dregs of a decoction and whole organic wastewaters The ratio between be 70~90: 10~30.
  3. 3. according to the method described in claim 1, it is characterized in that, the addition of the control fermentation dregs of a decoction and organic liquid waste, makes most The mass percent concentration of solid is 33~42% in obtained fuel slurry eventually.
  4. 4. according to the method described in claims 1 to 3 any one, it is characterised in that the fermentation dregs of a decoction are using hair Ferment method prepares the mycelia residue produced during antibiotic, vitamin or amino acids drug, its moisture content is 50~65%.
  5. 5. according to the method described in claims 1 to 3 any one, it is characterised in that the organic wastewater is that pharmacy is given up One kind in water, black liquid, coal chemical industrial waste water or dyeing waste water.
CN201810001027.0A 2018-01-02 2018-01-02 Method for preparing novel slurry fuel by utilizing fermented medicine residues and organic wastewater Active CN107974315B (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112226255A (en) * 2020-09-25 2021-01-15 梵境新能源科技(浙江)有限公司 Gasification co-processing method for polymorphic waste
CN112852511A (en) * 2020-12-03 2021-05-28 青岛特利尔环保集团股份有限公司 Composite slurry fuel and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101457165A (en) * 2009-01-14 2009-06-17 李寒旭 Coal water slurry made by combining lincomycin wet bacteria slag and coal
CN101831329A (en) * 2010-03-30 2010-09-15 安徽淮化股份有限公司 High-stability coal water slurry and preparation method thereof
CN103060031A (en) * 2012-12-26 2013-04-24 东南大学 Papermaking black liquor modified sludge-petroleum coke slurry and preparation method thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101457165A (en) * 2009-01-14 2009-06-17 李寒旭 Coal water slurry made by combining lincomycin wet bacteria slag and coal
CN101831329A (en) * 2010-03-30 2010-09-15 安徽淮化股份有限公司 High-stability coal water slurry and preparation method thereof
CN103060031A (en) * 2012-12-26 2013-04-24 东南大学 Papermaking black liquor modified sludge-petroleum coke slurry and preparation method thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
张晔: "抗生素菌渣与煤粉配合成浆性能及燃烧动力学研究", 《万方学位论文》 *
张晔: "淮北矿物煤与抗生素湿菌渣配合制备水煤浆的试验研究", 《选煤技术》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112226255A (en) * 2020-09-25 2021-01-15 梵境新能源科技(浙江)有限公司 Gasification co-processing method for polymorphic waste
CN112226255B (en) * 2020-09-25 2021-05-18 梵境新能源科技(浙江)有限公司 Gasification co-processing method for polymorphic waste
CN112852511A (en) * 2020-12-03 2021-05-28 青岛特利尔环保集团股份有限公司 Composite slurry fuel and preparation method thereof

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