CN110496486A - A kind of purification method of fermented feed production tail gas - Google Patents

A kind of purification method of fermented feed production tail gas Download PDF

Info

Publication number
CN110496486A
CN110496486A CN201910870552.0A CN201910870552A CN110496486A CN 110496486 A CN110496486 A CN 110496486A CN 201910870552 A CN201910870552 A CN 201910870552A CN 110496486 A CN110496486 A CN 110496486A
Authority
CN
China
Prior art keywords
lye
tail gas
weight
water
culture
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
CN201910870552.0A
Other languages
Chinese (zh)
Other versions
CN110496486B (en
Inventor
辛旭峰
杜祖波
徐会茹
李卫青
李秋
王珊珊
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.)
Laiyang Luhua Biological Protein Co ltd
SHANDONG LUHUA GROUP CO Ltd
Original Assignee
Laiyang Luhua Biological Protein Co Ltd
LUHUA GROUP CO Ltd SHANDONG
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 Laiyang Luhua Biological Protein Co Ltd, LUHUA GROUP CO Ltd SHANDONG filed Critical Laiyang Luhua Biological Protein Co Ltd
Priority to CN201910870552.0A priority Critical patent/CN110496486B/en
Publication of CN110496486A publication Critical patent/CN110496486A/en
Application granted granted Critical
Publication of CN110496486B publication Critical patent/CN110496486B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D50/00Combinations of methods or devices for separating particles from gases or vapours
    • B01D50/60Combinations of devices covered by groups B01D46/00 and B01D47/00
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1487Removing organic compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1493Selection of liquid materials for use as absorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/38Removing components of undefined structure
    • B01D53/40Acidic components
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/38Removing components of undefined structure
    • B01D53/44Organic components
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/75Multi-step processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/79Injecting reactants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/84Biological processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/96Regeneration, reactivation or recycling of reactants
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/304Alkali metal compounds of sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/306Alkali metal compounds of potassium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/404Alkaline earth metal or magnesium compounds of calcium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/602Oxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/604Hydroxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/606Carbonates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/95Specific microorganisms
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2252/00Absorbents, i.e. solvents and liquid materials for gas absorption
    • B01D2252/20Organic absorbents
    • B01D2252/205Other organic compounds not covered by B01D2252/00 - B01D2252/20494
    • B01D2252/2053Other nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/304Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/708Volatile organic compounds V.O.C.'s
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Molecular Biology (AREA)
  • Sustainable Development (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)

Abstract

本发明属于尾气处理技术领域,尤其涉及一种发酵饲料生产尾气的净化方法。本发明采用四步连续处理方法,即采用布袋除尘、碱液吸收、高压喷雾吸附、生物液喷淋分别对粉尘、挥发性有机酸、硫化氢气体、醇、酯等异味气体等进行净化处理。本发明工艺对尾气的异味去除率高、成本低、高效环保无二次污染,适合在发酵饲料行业大规模推广应用。The invention belongs to the technical field of tail gas treatment, in particular to a method for purifying tail gas from fermented feed production. The present invention adopts a four-step continuous treatment method, that is, dust, volatile organic acids, hydrogen sulfide gas, alcohol, ester and other odorous gases are respectively purified by bag dust removal, lye absorption, high-pressure spray adsorption, and biological liquid spray. The process of the invention has high tail gas odor removal rate, low cost, high efficiency, environmental protection and no secondary pollution, and is suitable for large-scale popularization and application in the fermented feed industry.

Description

一种发酵饲料生产尾气的净化方法A method for purifying tail gas from fermented feed production

技术领域technical field

本发明属于尾气处理技术领域,尤其涉及一种发酵饲料生产尾气的净化方法。The invention belongs to the technical field of tail gas treatment, in particular to a method for purifying tail gas from fermented feed production.

背景技术Background technique

饲料发酵过程中会产生大量醋酸、乳酸等有机酸,以及硫化氢、硫醇、氨气等挥发性异味气体。尤其是发酵饲料在烘干过程中,大量挥发性物质随水蒸气及粉尘排放出来,若处理不当会对环境造成一定污染,并严重影响周边居民环境。随着人们环境保护意识的逐渐增强,关于工业尾气排放标准以及监管力度愈加严格。发酵饲料生产尾气不经处理直接排放会被相关监管部门禁止和处罚。During the feed fermentation process, a large amount of organic acids such as acetic acid and lactic acid, as well as volatile odor gases such as hydrogen sulfide, mercaptan and ammonia will be produced. Especially during the drying process of fermented feed, a large amount of volatile substances are emitted along with water vapor and dust. If not handled properly, it will cause certain pollution to the environment and seriously affect the environment of surrounding residents. With the gradual enhancement of people's awareness of environmental protection, the standards and supervision of industrial exhaust emissions have become more stringent. Direct discharge of fermented feed production tail gas without treatment will be prohibited and punished by relevant regulatory authorities.

目前常用的发酵饲料尾气净化方法主要采用碱液吸收,再经水洗喷淋后排放。这种简单的处理方式很难将发酵饲料尾气中的异味物质处理完全,并且烘干过程尾气排放量非常大,只经过一次碱洗、一次喷淋无法满足安全排放的需求。At present, the commonly used method of purifying the tail gas of fermented feed mainly adopts alkali solution absorption, and then discharges after washing and spraying. This simple treatment method is difficult to completely treat the odorous substances in the tail gas of fermented feed, and the exhaust gas emission during the drying process is very large, and only one alkali washing and one spraying cannot meet the needs of safe discharge.

发明内容Contents of the invention

本发明针对上述现有技术存在的不足,提供一种发酵饲料生产尾气的净化方法。The present invention aims at the deficiencies in the above-mentioned prior art, and provides a method for purifying the tail gas produced by fermented feed.

本发明解决上述技术问题的技术方案如下:The technical scheme that the present invention solves the problems of the technologies described above is as follows:

一种发酵饲料生产尾气的净化方法,步骤如下:A method for purifying tail gas from fermented feed production, the steps are as follows:

(1)布袋除尘器除尘:在发酵饲料烘干过程中,沸腾干燥机烘干的尾气在抽风机作用下,经过布袋除尘器进行一级除尘;(1) Dust removal by bag filter: During the drying process of fermented feed, the tail gas dried by the boiling dryer is subjected to primary dust removal through the bag filter under the action of the exhaust fan;

(2)碱液吸收:经步骤(1)处理后的尾气通入碱液喷淋室,碱液喷淋室顶部装有雾化喷头,下层为碱液循环池,碱液循环池通过碱液添加泵连通至碱液储箱;尾气从碱液喷淋室侧方进入,经过顶部密集排列的雾化喷头喷淋吸收,去除刺激性气体,同时进行二级除尘;(2) Alkali absorption: The tail gas treated in step (1) is passed into the lye spray room, the top of the lye spray room is equipped with an atomizing nozzle, the lower layer is the lye circulation pool, and the lye circulation pool passes through the lye The adding pump is connected to the lye storage tank; the tail gas enters from the side of the lye spray room, and is sprayed and absorbed by the densely arranged atomizing nozzles on the top to remove the irritating gas and perform secondary dust removal at the same time;

(3)高压喷雾吸附:经步骤(2)处理后的尾气进入排气管道,在排气管道内安装高压喷雾嘴,除味吸附剂被加压至高压喷雾嘴雾化,形成雾滴,对尾气进行除味、降温;(3) High-pressure spray adsorption: the tail gas processed in step (2) enters the exhaust pipe, and a high-pressure spray nozzle is installed in the exhaust pipe, and the deodorizing adsorbent is pressurized to the high-pressure spray nozzle to atomize to form droplets, The tail gas is deodorized and cooled;

(4)生物液喷淋:经步骤(3)处理后的尾气在引风机作用下、从生物液喷淋塔底部进入,生物液喷淋塔内的生物吸收液从上向下分多层喷淋,尾气经喷淋处理后高空排放。(4) Biological liquid spraying: The tail gas treated in step (3) enters from the bottom of the biological liquid spray tower under the action of the induced draft fan, and the biological absorption liquid in the biological liquid spray tower is sprayed in multiple layers from top to bottom. Spraying, the tail gas is discharged at high altitude after spraying treatment.

进一步,步骤(2)中,碱液储箱内的碱液通过碱液添加泵按照100-200mL/min的流速向碱液循环池内补充高浓度碱液,保证碱液循环池内的碱液pH值控制在8-10。Further, in step (2), the lye in the lye storage tank is supplemented with high-concentration lye in the lye circulation pool by the lye addition pump according to the flow rate of 100-200mL/min, so as to ensure the pH value of the lye in the lye circulation pool Control it at 8-10.

更进一步,所述碱液中的溶质物质为氢氧化钠、氢氧化钾、生石灰、碳酸钠或碳酸氢钠;所述碱液储箱内的碱液配制为:向1L水中加入400-500g的溶质物质。Furthermore, the solute substance in the lye is sodium hydroxide, potassium hydroxide, quicklime, sodium carbonate or sodium bicarbonate; the lye in the lye storage tank is prepared as follows: add 400-500g of solute substance.

采用上述进一步方案的有益效果是,尾气经碱液喷淋吸收、去除硫化氢、有机酸等刺激性酸性气体后,会导致碱液循环池内的碱液浓度和碱液pH值降低,因此不断向碱液循环池内补充高浓度碱液,以保证碱液喷淋吸收效果。The beneficial effect of adopting the above-mentioned further scheme is that after the tail gas is sprayed and absorbed by the lye, and the irritating acid gases such as hydrogen sulfide and organic acid are removed, the lye concentration and lye pH value in the lye circulation pool will be reduced, so it will continue to The lye circulating pool is supplemented with high-concentration lye to ensure the effect of lye spraying and absorption.

进一步,步骤(3)中,排气管道直径1米,长10米,每相隔5米设置一个高压喷雾嘴;利用高压泵将储罐中的除味吸附剂加压至0.4MPa,除味吸附剂通过高压喷雾嘴雾化,形成直径3-10μm的雾滴。Further, in step (3), the exhaust pipe has a diameter of 1 meter and a length of 10 meters, and a high-pressure spray nozzle is set every 5 meters apart; the deodorizing adsorbent in the storage tank is pressurized to 0.4 MPa by using a high-pressure pump, and the deodorizing adsorption The agent is atomized through a high-pressure spray nozzle to form droplets with a diameter of 3-10 μm.

进一步,步骤(3)中,所述除味吸附剂由阳离子表面活性剂3-9重量份、纳米二氧化硅1-3重量份和水500-1000重量份组成。Further, in step (3), the deodorizing adsorbent is composed of 3-9 parts by weight of cationic surfactant, 1-3 parts by weight of nano silicon dioxide and 500-1000 parts by weight of water.

更进一步,所述的阳离子表面活性剂为十六烷基三甲基溴化铵、十八烷基三甲基溴化铵或十八烷基二甲基氯化铵。Furthermore, the cationic surfactant is cetyltrimethylammonium bromide, octadecyltrimethylammonium bromide or octadecyldimethylammonium chloride.

采用上述进一步方案的有益效果是,阳离子表面活性剂在水溶液中呈正电性,有很强的吸附力,纳米二氧化硅具有粒径小、分散性好、比表面积大等特点,二者结合使用,经高压喷雾嘴雾化后与异味气体分子充分接触、迅速捕获,达到尾气净化效果。The beneficial effect of adopting the above-mentioned further scheme is that the cationic surfactant is positively charged in aqueous solution and has a strong adsorption force, and the nano-silica has the characteristics of small particle size, good dispersibility, and large specific surface area. After being atomized by the high-pressure spray nozzle, it fully contacts with the odor gas molecules and captures them quickly to achieve the effect of exhaust gas purification.

进一步,步骤(4)中,生物吸收液的制备方法如下:Further, in step (4), the preparation method of the biological absorption liquid is as follows:

(1)将光合细菌培养液、酵母菌培养液、乳酸菌培养液、放线菌培养液、丝状菌培养液、醋酸菌培养液按照重量比2:2:2:1:1:1混合,得混合液;(1) Mix photosynthetic bacteria culture fluid, yeast culture fluid, lactic acid bacteria culture fluid, actinomycetes culture fluid, filamentous bacteria culture fluid, and acetic acid bacteria culture fluid in a weight ratio of 2:2:2:1:1:1, get the mixture;

(2)取步骤(1)的混合液,接入灭菌培养基中,每隔12h通气1h,培养60天后,用水稀释1000-2000倍作为生物吸收液。(2) Take the mixed solution of step (1), insert it into the sterilized medium, ventilate it for 1 hour every 12 hours, and after culturing for 60 days, dilute it with water 1000-2000 times as a bioabsorption solution.

更进一步,步骤(1)中,所述光合细菌培养液按重量百分比计,由0.2%氯化铵、0.02%磷酸氢二钾、0.4%乙酸钠、0.2%碳酸氢钠、0.1%氯化钠、0.015%酵母膏、0.02%硫酸镁、99.045%水组成,经121℃高压灭菌,按照光合细菌培养液重量的5%接种量接种光合细菌菌粉,30℃好氧培养7d后得到;Further, in the step (1), the photosynthetic bacteria culture solution is composed of 0.2% ammonium chloride, 0.02% dipotassium hydrogen phosphate, 0.4% sodium acetate, 0.2% sodium bicarbonate, 0.1% sodium chloride by weight percentage , 0.015% yeast extract, 0.02% magnesium sulfate, and 99.045% water, which are autoclaved at 121°C, inoculated with photosynthetic bacteria powder according to the inoculation amount of 5% of the photosynthetic bacteria culture solution weight, and obtained after aerobic cultivation at 30°C for 7 days;

所述酵母菌培养液按重量百分比计,由1%酵母膏、2%蛋白胨、2%葡萄糖、95%水组成,经121℃高压灭菌,按照酵母菌培养液重量的1%接种量接种酵母菌菌粉,28℃好氧培养48h后得到;The yeast culture solution is composed of 1% yeast extract, 2% peptone, 2% glucose, and 95% water in terms of weight percentage, and is sterilized by autoclaving at 121° C., and the yeast is inoculated according to the inoculation amount of 1% of the weight of the yeast culture solution. Bacteria powder, obtained after aerobic culture at 28°C for 48 hours;

所述乳酸菌培养液按重量百分比计,由0.75%酵母膏、0.75%蛋白胨、1%葡萄糖、0.02%KH2PO4、0.05%吐温80、97.43%水组成,经121℃高压灭菌,按照乳酸菌培养液重量的1%接种量接种乳酸菌菌粉,37℃厌氧培养48h后得到;The lactic acid bacteria culture solution is composed of 0.75% yeast extract, 0.75% peptone, 1% glucose, 0.02% KH 2 PO 4 , 0.05% Tween 80, and 97.43% water in terms of weight percentage, and is sterilized by high pressure at 121°C according to Inoculate the lactic acid bacteria powder with 1% inoculum weight of the lactic acid bacteria culture solution, and obtain it after anaerobic culture at 37°C for 48 hours;

所述放线菌培养液按重量百分比计,由2%可溶性淀粉、0.05%K2HPO4、0.05%MgSO4·7H2O、0.05%NaCl、0.001%FeSO4、97.848%水组成,经121℃高压灭菌,按照放线菌培养液重量的1%接种量接种放线菌菌粉,28℃好氧培养7d后得到;The actinomycetes culture solution is composed of 2% soluble starch, 0.05% K 2 HPO 4 , 0.05% MgSO 4 ·7H 2 O, 0.05% NaCl, 0.001% FeSO 4 , and 97.848% water by weight percentage. ℃ autoclave, inoculate the actinomycetes powder according to the inoculum amount of 1% of the weight of the actinomycetes culture solution, obtain after 7 days of aerobic culture at 28 ℃;

所述丝状菌培养液按重量百分比计,由1%酵母膏、2%蛋白胨、2%葡萄糖、95%水经121℃高压灭菌,按照丝状菌培养液重量的1%接种量接种丝状菌菌粉,28℃好氧培养7d后得到;The filamentous bacteria culture solution is calculated by weight percentage, and is sterilized by 1% yeast extract, 2% peptone, 2% glucose, and 95% water by autoclaving at 121 ° C. Bacteria powder, obtained after aerobic culture at 28°C for 7 days;

所述醋酸菌培养液按重量百分比计,由10%葡萄糖、1%酵母膏、89%水经121℃高压灭菌,按照醋酸菌培养液重量的1%接种量接种醋酸菌菌粉,好氧培养12h后得到;Described acetic acid bacterium culture fluid is calculated by weight percentage, by 10% glucose, 1% yeast extract, 89% water through 121 ℃ autoclave sterilization, according to the 1% inoculation amount of acetic acid bacterium culture fluid weight inoculation acetic bacteria powder, aerobic Obtained after culturing for 12 hours;

步骤(2)中,所述灭菌培养基按重量百分比计,由3%甘蔗糖蜜、2%蛋白胨、95%水组成,经121℃高压灭菌得到。In step (2), the sterilized medium is composed of 3% sugarcane molasses, 2% peptone, and 95% water by weight percentage, and is obtained by autoclaving at 121°C.

其中,本发明中使用的光合细菌菌粉、酵母菌菌粉、乳酸菌菌粉、放线菌菌粉、丝状菌菌粉、醋酸菌菌粉购买自山东济宁金山生物工程有限公司。Wherein, the photosynthetic bacteria powder, saccharomyces powder, lactic acid bacteria powder, actinomycetes powder, filamentous bacteria powder, and acetic acid bacteria powder used in the present invention were purchased from Shandong Jining Jinshan Bioengineering Co., Ltd.

本发明的有益效果是:The beneficial effects of the present invention are:

本发明采用四步连续处理方法,即采用布袋除尘、碱液吸收、高压喷雾吸附、生物液喷淋分别对粉尘、挥发性有机酸、硫化氢气体、醇、酯等异味气体等进行净化处理。本发明工艺对尾气的异味去除率高、成本低、高效环保无二次污染,适合在发酵饲料行业大规模推广应用。The present invention adopts a four-step continuous treatment method, that is, dust, volatile organic acids, hydrogen sulfide gas, alcohol, ester and other odorous gases are respectively purified by bag dust removal, lye absorption, high-pressure spray adsorption, and biological liquid spray. The process of the invention has high tail gas odor removal rate, low cost, high efficiency, environmental protection and no secondary pollution, and is suitable for large-scale popularization and application in the fermented feed industry.

附图说明Description of drawings

图1为本发明实施例1中未经处理的尾气中挥发性物质TIC图;Fig. 1 is the TIC figure of the volatile matter in the untreated tail gas in the embodiment of the present invention 1;

图2为本发明实施例1中经过处理后的尾气中挥发性物质TIC图。Fig. 2 is a TIC diagram of volatile substances in the treated tail gas in Example 1 of the present invention.

具体实施方式Detailed ways

以下结合实例对本发明的原理和特征进行描述,所举实例只用于解释本发明,并非用于限定本发明的范围。The principles and features of the present invention are described below in conjunction with examples, which are only used to explain the present invention and are not intended to limit the scope of the present invention.

实施例1Example 1

发酵花生粕生产尾气的净化方法,步骤如下:A method for purifying tail gas produced by fermenting peanut meal, the steps are as follows:

(1)布袋除尘器除尘:在发酵饲料烘干过程中,沸腾干燥机烘干的尾气在抽风机作用下,经过布袋除尘器进行一级除尘;(1) Dust removal by bag filter: During the drying process of fermented feed, the tail gas dried by the boiling dryer is subjected to primary dust removal through the bag filter under the action of the exhaust fan;

(2)碱液吸收:经步骤(1)处理后的尾气通入碱液喷淋室,碱液喷淋室顶部装有雾化喷头,下层为碱液循环池,碱液循环池通过碱液添加泵连通至碱液储箱;尾气从碱液喷淋室侧方进入,经过顶部密集排列的雾化喷头喷淋吸收,去除硫化氢、有机酸等刺激性酸性气体,同时进行二级除尘;(2) Alkali absorption: the tail gas treated in step (1) is passed into the lye spray room, the top of the lye spray room is equipped with an atomizing nozzle, the lower layer is the lye circulation pool, and the lye circulation pool passes through the lye Add the pump to connect to the lye storage tank; the tail gas enters from the side of the lye spray room, sprays and absorbs through the densely arranged atomizing nozzles on the top, removes irritating acid gases such as hydrogen sulfide and organic acids, and performs secondary dust removal at the same time;

其中,控制碱液循环池内的碱液pH值为9.5,碱液储箱内浓度为400g/L的氢氧化钠溶液;Wherein, the lye pH value in the control lye circulation pool is 9.5, and the concentration in the lye storage tank is a sodium hydroxide solution of 400g/L;

(3)高压喷雾吸附:经步骤(2)处理后的尾气进入排气管道,在排气管道内安装高压喷雾嘴,利用高压泵将储罐中的除味吸附剂加压至0.4MPa,除味吸附剂通过高压喷雾嘴雾化,形成直径3-10μm的雾滴,对尾气进行除味、降温;尾气中的醛、吡嗪、醇类物质显著减少;(3) High-pressure spray adsorption: the tail gas treated in step (2) enters the exhaust pipe, installs a high-pressure spray nozzle in the exhaust pipe, and utilizes a high-pressure pump to pressurize the deodorizing adsorbent in the storage tank to 0.4MPa, deodorizing The odor adsorbent is atomized through the high-pressure spray nozzle to form droplets with a diameter of 3-10 μm, which deodorizes and cools the exhaust gas; aldehydes, pyrazines, and alcohols in the exhaust gas are significantly reduced;

其中,所述除味吸附剂由十六烷基三甲基溴化铵5重量份、纳米二氧化硅2重量份和水600重量份组成;Wherein, the deodorizing adsorbent is composed of 5 parts by weight of cetyltrimethylammonium bromide, 2 parts by weight of nano silicon dioxide and 600 parts by weight of water;

(4)生物液喷淋:经步骤(3)处理后的尾气在引风机作用下、从生物液喷淋塔底部进入,生物液喷淋塔内的生物吸收液从上向下分三层喷淋,进一步去除尾气中的异味气体,尾气中仅含有少量大分子烷类物质,达到排放标准,尾气经喷淋处理后25米高空排放。(4) Biological liquid spraying: The tail gas treated in step (3) enters from the bottom of the biological liquid spray tower under the action of the induced draft fan, and the biological absorption liquid in the biological liquid spray tower is sprayed in three layers from top to bottom. Spraying, to further remove the odor gas in the tail gas, the tail gas only contains a small amount of macromolecular alkanes, which meets the emission standards, and the tail gas is discharged at a height of 25 meters after being sprayed.

检测detection

采用固相微萃取结合气质联用仪对实施例1各步骤的发酵饲料尾气进行成分检测,检测方法如下:The components of the fermented feed tail gas in each step of Example 1 were detected by using solid-phase microextraction combined with gas chromatography-mass spectrometer, and the detection method was as follows:

(1)样品收集:用内壁硅烷化的气体采样袋收集尾气,密封,12h内完成检测;(1) Sample collection: use a gas sampling bag with a silanized inner wall to collect the exhaust gas, seal it, and complete the test within 12 hours;

(2)活化萃取头:选用固相微萃取手动进样(DVB/CAR/PDMS)萃取头,50/30μm DVB/CAR on PDMS;将气质联用仪的进样口温度设置为250℃,再将萃取头插入气质联用仪进样口进行活化,以除去原先吸附在萃取头的物质,活化时间为30-40min;(2) Activation of the extraction head: select the manual injection (DVB/CAR/PDMS) extraction head of solid phase microextraction, 50/30 μm DVB/CAR on PDMS; Insert the extraction head into the inlet of the GC-MS instrument for activation to remove the substances that were originally adsorbed on the extraction head. The activation time is 30-40 minutes;

(3)进样:将活化好的萃取头插入步骤(1)的尾气采样袋中,推出萃取头后,在35-45℃恒温条件下顶空吸附50-60min后,于250℃解析5min;(3) Sample injection: Insert the activated extraction head into the tail gas sampling bag in step (1), push out the extraction head, and then absorb in the headspace for 50-60 minutes at a constant temperature of 35-45°C, then analyze at 250°C for 5 minutes;

(4)气相色谱条件:(4) Gas chromatography conditions:

毛细管柱:DB-5MS色谱柱(30m×0.25mm×0.25μm);Capillary column: DB-5MS chromatographic column (30m×0.25mm×0.25μm);

气相柱温升温程序:40℃保持2min,以5℃/min的升温速率升温至220℃,保持10min;Gas phase column temperature rise program: keep at 40°C for 2 minutes, raise the temperature to 220°C at a heating rate of 5°C/min, and keep for 10 minutes;

汽化室温度:250℃;Vaporization chamber temperature: 250°C;

氦气流速:0.8mL/min;Helium flow rate: 0.8mL/min;

进样方式:不分流进样;Injection method: splitless injection;

(5)质谱条件:电子轰击离子源(EI);电子能量70eV;离子源温度230℃;灯丝发射电流200μA;接口温度为250℃;全谱扫描,扫描质量范围m/z 35-450。(5) Mass spectrometry conditions: electron bombardment ion source (EI); electron energy 70eV; ion source temperature 230°C; filament emission current 200μA; interface temperature 250°C; full-spectrum scanning, scanning mass range m/z 35-450.

通过计算机检索与NIST谱库(107000个化合物的数据)匹配确定未知化合物的名称及相关信息,仅报道相似度大于80(最大值为100)的相关鉴定结果。各组分的相对含量由峰面积归一化法计算得到。The names and related information of unknown compounds were determined by matching with the NIST spectral library (data of 107,000 compounds) by computer search, and only relevant identification results with a similarity greater than 80 (the maximum value was 100) were reported. The relative content of each component was calculated by the peak area normalization method.

表1为实施例1中发酵花生粕生产尾气中的挥发性物质含量;表2为实施例1中经过步骤(2)碱液吸收后的尾气中挥发性物质含量;表3为实施例1中经过步骤(3)高压喷雾吸附后的尾气中挥发性物质含量;表4为实施例1中经过步骤(4)生物液喷淋后的尾气中挥发性物质含量。Table 1 is the content of volatile substances in the tail gas produced by fermented peanut meal in Example 1; Table 2 is the content of volatile substances in the tail gas after step (2) lye absorption in Example 1; Table 3 is the content of volatile substances in the tail gas in Example 1 The content of volatile substances in the tail gas after step (3) high-pressure spray adsorption; Table 4 shows the content of volatile substances in the tail gas after step (4) biological liquid spraying in Example 1.

表1Table 1

保留时间keep time 物质名称Substance name 相对含量%Relative content % 2.6022.602 醋酸acetic acid 7.257.25 3.7943.794 戊醇pentanol 13.4113.41 5.7925.792 丁酸butyric acid 23.3223.32 8.5838.583 戊酸Valeric acid 19.9719.97 9.2069.206 2,5-二甲基吡嗪2,5-Dimethylpyrazine 5.895.89 12.03112.031 三甲基吡嗪Trimethylpyrazine 2.672.67 13.0613.06 苯甲醇Benzyl alcohol 1.251.25 14.45114.451 3-乙基-2,5-二甲基吡嗪3-Ethyl-2,5-dimethylpyrazine 1.71.7 15.5315.53 苯乙醇Phenyl alcohol 9.779.77 16.36216.362 庚烷醚Heptane ether 0.770.77 16.65316.653 3-甲基丁酯3-Methylbutyl Ester 0.60.6 18.0718.07 庚烷醇Heptanol 5.365.36 18.22318.223 龙脑borneol 1.341.34 22.66922.669 呋喃酮Furanone 0.220.22 23.50423.504 十四烷Tetradecane 1.111.11 28.40328.403 二十烷Eicosane 0.810.81

表2Table 2

表3table 3

表4Table 4

保留时间keep time 物质名称Substance name 相对含量%Relative content% 13.0613.06 苯甲醇Benzyl alcohol 5.215.21 15.5315.53 苯乙醇Phenyl alcohol 5.765.76 20.30920.309 壬烷Nonane 18.1518.15 20.84920.849 十二烷dodecane 15.0315.03 23.51423.514 十四烷Tetradecane 27.2127.21 28.41128.411 二十烷Eicosane 28.6428.64

由表1-表4中数据可以看出,发酵花生粕尾气经过碱液吸收、阳离子吸附、生物液喷淋之后,挥发性物质中小分子有机酸、吡嗪、醇、酯等物质依次减少,最后排放气体中仅能检出醇和烷,经第三方检测达到排放标准。From the data in Table 1-Table 4, it can be seen that after the tail gas of fermented peanut meal is absorbed by lye, absorbed by cations, and sprayed with biological fluid, the small molecular organic acids, pyrazines, alcohols, esters and other substances in the volatile substances are successively reduced, and finally Only alcohol and alkanes can be detected in the exhaust gas, and the emission standards have been met through third-party testing.

实施例2Example 2

发酵芝麻粕生产尾气的净化方法,步骤如下:A method for purifying tail gas produced by fermenting sesame meal, the steps are as follows:

(1)布袋除尘器除尘:在发酵饲料烘干过程中,沸腾干燥机烘干的尾气在抽风机作用下,经过布袋除尘器进行一级除尘;(1) Dust removal by bag filter: During the drying process of fermented feed, the tail gas dried by the boiling dryer is subjected to primary dust removal through the bag filter under the action of the exhaust fan;

(2)碱液吸收:经步骤(1)处理后的尾气通入碱液喷淋室,碱液喷淋室顶部装有雾化喷头,下层为碱液循环池,碱液循环池通过碱液添加泵连通至碱液储箱;尾气从碱液喷淋室侧方进入,经过顶部密集排列的雾化喷头喷淋吸收,去除硫化氢、有机酸等刺激性酸性气体,同时进行二级除尘;(2) Alkali absorption: The tail gas treated in step (1) is passed into the lye spray room, the top of the lye spray room is equipped with an atomizing nozzle, the lower layer is the lye circulation pool, and the lye circulation pool passes through the lye Add the pump to connect to the lye storage tank; the tail gas enters from the side of the lye spray room, and is sprayed and absorbed by the densely arranged atomizing nozzles on the top to remove irritating acid gases such as hydrogen sulfide and organic acids, and perform secondary dust removal at the same time;

其中,控制碱液循环池内的碱液pH值为8,碱液储箱内浓度为450g/L的氢氧化钠溶液;Wherein, the lye pH value in the control lye circulation pool is 8, and the concentration in the lye storage tank is a sodium hydroxide solution of 450g/L;

(3)高压喷雾吸附:经步骤(2)处理后的尾气进入排气管道,在排气管道内安装高压喷雾嘴,利用高压泵将储罐中的除味吸附剂加压至0.4MPa,除味吸附剂通过高压喷雾嘴雾化,形成直径3-10μm的雾滴,对尾气进行除味、降温;尾气中的醛、吡嗪、醇类物质显著减少;(3) High-pressure spray adsorption: the tail gas treated in step (2) enters the exhaust pipe, installs a high-pressure spray nozzle in the exhaust pipe, and utilizes a high-pressure pump to pressurize the deodorizing adsorbent in the storage tank to 0.4MPa, deodorizing The odor adsorbent is atomized through the high-pressure spray nozzle to form droplets with a diameter of 3-10 μm, which deodorizes and cools the exhaust gas; aldehydes, pyrazines, and alcohols in the exhaust gas are significantly reduced;

其中,所述除味吸附剂由十八烷基二甲基氯化铵8重量份、纳米二氧化硅3重量份和水900重量份组成;Wherein, the deodorizing adsorbent is composed of 8 parts by weight of octadecyldimethylammonium chloride, 3 parts by weight of nano silicon dioxide and 900 parts by weight of water;

(4)生物液喷淋:经步骤(3)处理后的尾气在引风机作用下、从生物液喷淋塔底部进入,生物液喷淋塔内的生物吸收液从上向下分三层喷淋,进一步去除尾气中的异味气体,尾气中仅含有少量大分子烷类物质,达到排放标准,尾气经喷淋处理后25米高空排放。(4) Biological liquid spraying: The tail gas treated in step (3) enters from the bottom of the biological liquid spray tower under the action of the induced draft fan, and the biological absorption liquid in the biological liquid spray tower is sprayed in three layers from top to bottom. Spraying, to further remove the odor gas in the tail gas, the tail gas only contains a small amount of macromolecular alkanes, which meets the emission standards, and the tail gas is discharged at a height of 25 meters after being sprayed.

检测detection

采用固相微萃取结合气质联用仪对实施例2各步骤的发酵饲料尾气进行成分检测,检测方法如下:The components of the fermented feed tail gas in each step of Example 2 were detected by using solid-phase microextraction combined with gas chromatography-mass spectrometer, and the detection method was as follows:

(1)样品收集:用内壁硅烷化的气体采样袋收集尾气,密封,12h内完成检测;(1) Sample collection: use a gas sampling bag with a silanized inner wall to collect the exhaust gas, seal it, and complete the test within 12 hours;

(2)活化萃取头:选用固相微萃取手动进样(DVB/CAR/PDMS)萃取头,50/30μm DVB/CAR on PDMS;将气质联用仪的进样口温度设置为250℃,再将萃取头插入气质联用仪进样口进行活化,以除去原先吸附在萃取头的物质,活化时间为30-40min;(2) Activation of the extraction head: select the manual injection (DVB/CAR/PDMS) extraction head of solid phase microextraction, 50/30 μm DVB/CAR on PDMS; Insert the extraction head into the inlet of the GC-MS instrument for activation to remove the substances that were originally adsorbed on the extraction head. The activation time is 30-40 minutes;

(3)进样:将活化好的萃取头插入步骤(1)的尾气采样袋中,推出萃取头后,在35-45℃恒温条件下顶空吸附50-60min后,于250℃解析5min;(3) Sample injection: Insert the activated extraction head into the tail gas sampling bag in step (1), push out the extraction head, and then absorb in the headspace for 50-60 minutes at a constant temperature of 35-45°C, then analyze at 250°C for 5 minutes;

(4)气相色谱条件:(4) Gas chromatography conditions:

毛细管柱:DB-5MS色谱柱(30m×0.25mm×0.25μm);Capillary column: DB-5MS chromatographic column (30m×0.25mm×0.25μm);

气相柱温升温程序:40℃保持2min,以5℃/min的升温速率升温至220℃,保持10min;Gas phase column temperature rise program: keep at 40°C for 2 minutes, raise the temperature to 220°C at a heating rate of 5°C/min, and keep for 10 minutes;

汽化室温度:250℃;Vaporization chamber temperature: 250°C;

氦气流速:0.8mL/min;Helium flow rate: 0.8mL/min;

进样方式:不分流进样;Injection method: splitless injection;

(5)质谱条件:电子轰击离子源(EI);电子能量70eV;离子源温度230℃;灯丝发射电流200μA;接口温度为250℃;全谱扫描,扫描质量范围m/z 35-450。(5) Mass spectrometry conditions: electron bombardment ion source (EI); electron energy 70eV; ion source temperature 230°C; filament emission current 200μA; interface temperature 250°C; full-spectrum scanning, scanning mass range m/z 35-450.

通过计算机检索与NIST谱库(107000个化合物的数据)匹配确定未知化合物的名称及相关信息,仅报道相似度大于80(最大值为100)的相关鉴定结果。各组分的相对含量由峰面积归一化法计算得到。The names and related information of unknown compounds were determined by matching with the NIST spectral library (data of 107,000 compounds) by computer search, and only relevant identification results with a similarity greater than 80 (the maximum value was 100) were reported. The relative content of each component was calculated by the peak area normalization method.

表5为实施例2中发酵芝麻粕生产尾气中的挥发性物质含量;表6为实施例2中经过步骤(2)碱液吸收、步骤(3)高压喷雾吸附、步骤(4)生物液喷淋后的尾气中挥发性物质含量。Table 5 is the content of volatile substances in the tail gas produced by fermenting sesame meal in Example 2; Table 6 is the content of lye in Example 2 through step (2) lye absorption, step (3) high-pressure spray adsorption, step (4) biological liquid spray The content of volatile substances in the exhaust gas after leaching.

表5table 5

表6Table 6

保留时间keep time 物质名称Substance name 相对含量%Relative content% 13.0613.06 苯甲醇Benzyl alcohol 3.863.86 18.0718.07 庚烷醇Heptanol 6.36.3 19.74119.741 苯乙基酯Phenyl ethyl ester 12.1712.17 20.84920.849 十二烷dodecane 18.8518.85 23.51423.514 十四烷Tetradecane 29.1429.14 28.41128.411 二十烷Eicosane 29.6829.68

由表5-表6中数据可以看出,发酵芝麻粕尾气经本发明方法净化处理后,有机酸、吡嗪等异味物质明显减少,经第三检测达到排放标准。It can be seen from the data in Table 5-Table 6 that after the tail gas of fermented sesame meal is purified by the method of the present invention, organic acids, pyrazines and other odorous substances are significantly reduced, and the third detection reaches the emission standard.

以上所述仅为本发明的较佳实施例,并不用以限制本发明,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included in the protection of the present invention. within range.

Claims (7)

1.一种发酵饲料生产尾气的净化方法,其特征在于,步骤如下:1. a purification method of fermented feed production tail gas, is characterized in that, step is as follows: (1)布袋除尘器除尘:在发酵饲料烘干过程中,沸腾干燥机烘干的尾气在抽风机作用下,经过布袋除尘器进行一级除尘;(1) Dust removal by bag filter: During the drying process of fermented feed, the tail gas dried by the boiling dryer is subjected to primary dust removal through the bag filter under the action of the exhaust fan; (2)碱液吸收:经步骤(1)处理后的尾气通入碱液喷淋室,碱液喷淋室顶部装有雾化喷头,下层为碱液循环池,碱液循环池通过碱液添加泵连通至碱液储箱;尾气从碱液喷淋室侧方进入,经过顶部密集排列的雾化喷头喷淋吸收,去除刺激性气体,同时进行二级除尘;(2) Alkali absorption: The tail gas treated in step (1) is passed into the lye spray room, the top of the lye spray room is equipped with an atomizing nozzle, the lower layer is the lye circulation pool, and the lye circulation pool passes through the lye The adding pump is connected to the lye storage tank; the tail gas enters from the side of the lye spray room, and is sprayed and absorbed by the densely arranged atomizing nozzles on the top to remove the irritating gas and perform secondary dust removal at the same time; (3)高压喷雾吸附:经步骤(2)处理后的尾气进入排气管道,在排气管道内安装高压喷雾嘴,除味吸附剂被加压至高压喷雾嘴雾化,形成雾滴,对尾气进行除味、降温;(3) High-pressure spray adsorption: the tail gas processed in step (2) enters the exhaust pipe, and a high-pressure spray nozzle is installed in the exhaust pipe, and the deodorizing adsorbent is pressurized to the high-pressure spray nozzle to atomize to form droplets, The tail gas is deodorized and cooled; (4)生物液喷淋:经步骤(3)处理后的尾气在引风机作用下、从生物液喷淋塔底部进入,生物液喷淋塔内的生物吸收液从上向下分多层喷淋,尾气经喷淋处理后高空排放。(4) Biological liquid spraying: The tail gas treated in step (3) enters from the bottom of the biological liquid spray tower under the action of the induced draft fan, and the biological absorption liquid in the biological liquid spray tower is sprayed in multiple layers from top to bottom. Spraying, the tail gas is discharged at high altitude after spraying treatment. 2.根据权利要求1所述的净化方法,其特征在于,步骤(2)中,碱液储箱内的碱液通过碱液添加泵按照100-200mL/min的流速向碱液循环池内补充碱液,控制碱液循环池内的碱液pH值在8-10。2. purification method according to claim 1, is characterized in that, in step (2), the lye in the lye storage tank replenishes alkali in the lye circulation pool according to the flow velocity of 100-200mL/min by the lye adding pump Liquid, control the pH value of the lye in the lye circulation pool at 8-10. 3.根据权利要求1或2所述的净化方法,其特征在于,步骤(2)中,所述碱液中的溶质物质为氢氧化钠、氢氧化钾、生石灰、碳酸钠或碳酸氢钠;所述碱液储箱内的碱液配制为:向1L水中加入400-500g的溶质物质。3. according to claim 1 and 2 described purification methods, it is characterized in that, in step (2), the solute substance in the described lye is sodium hydroxide, potassium hydroxide, unslaked lime, sodium carbonate or sodium bicarbonate; The lye in the lye storage tank is prepared as follows: add 400-500g of solute substances into 1L of water. 4.根据权利要求1所述的净化方法,其特征在于,步骤(3)中,所述除味吸附剂由阳离子表面活性剂3-9重量份、纳米二氧化硅1-3重量份和水500-1000重量份组成。4. purification method according to claim 1, is characterized in that, in step (3), described deodorizing adsorbent is made of cationic surfactant 3-9 weight part, nano silicon dioxide 1-3 weight part and water 500-1000 parts by weight. 5.根据权利要求4所述的净化方法,其特征在于,所述的阳离子表面活性剂为十六烷基三甲基溴化铵、十八烷基三甲基溴化铵或十八烷基二甲基氯化铵。5. purification method according to claim 4 is characterized in that, described cationic surfactant is hexadecyl trimethyl ammonium bromide, octadecyl trimethyl ammonium bromide or octadecyl trimethyl ammonium bromide Dimethyl ammonium chloride. 6.根据权利要求1所述的净化方法,其特征在于,步骤(4)中,生物吸收液的制备方法如下:6. purification method according to claim 1, is characterized in that, in step (4), the preparation method of biological absorption liquid is as follows: (1)将光合细菌培养液、酵母菌培养液、乳酸菌培养液、放线菌培养液、丝状菌培养液、醋酸菌培养液按照重量比2:2:2:1:1:1混合,得混合液;(1) Mix photosynthetic bacteria culture fluid, yeast culture fluid, lactic acid bacteria culture fluid, actinomycetes culture fluid, filamentous bacteria culture fluid, and acetic acid bacteria culture fluid in a weight ratio of 2:2:2:1:1:1, get the mixture; (2)取步骤(1)的混合液,接入灭菌培养基中,每隔12h通气1h,培养60天后,用水稀释1000-2000倍作为生物吸收液。(2) Take the mixed solution of step (1), insert it into the sterilized medium, ventilate it for 1 hour every 12 hours, and after culturing for 60 days, dilute it with water 1000-2000 times as a bioabsorption solution. 7.根据权利要求6所述的净化方法,其特征在于,步骤(1)中,所述光合细菌培养液按重量百分比计,由0.2%氯化铵、0.02%磷酸氢二钾、0.4%乙酸钠、0.2%碳酸氢钠、0.1%氯化钠、0.015%酵母膏、0.02%硫酸镁、99.045%水组成,经121℃高压灭菌,按照光合细菌培养液重量的5%接种量接种光合细菌菌粉,30℃好氧培养7d后得到;7. purification method according to claim 6, is characterized in that, in step (1), described photosynthetic bacteria culture fluid is by weight percentage, is made of 0.2% ammonium chloride, 0.02% dipotassium hydrogen phosphate, 0.4% acetic acid Sodium, 0.2% sodium bicarbonate, 0.1% sodium chloride, 0.015% yeast extract, 0.02% magnesium sulfate, 99.045% water, after autoclaving at 121 ℃, inoculate photosynthetic bacteria according to the inoculation amount of 5% of the weight of photosynthetic bacteria culture solution Bacteria powder, obtained after aerobic culture at 30°C for 7 days; 所述酵母菌培养液按重量百分比计,由1%酵母膏、2%蛋白胨、2%葡萄糖、95%水组成,经121℃高压灭菌,按照酵母菌培养液重量的1%接种量接种酵母菌菌粉,28℃好氧培养48h后得到;The yeast culture solution is composed of 1% yeast extract, 2% peptone, 2% glucose, and 95% water in terms of weight percentage, and is sterilized by autoclaving at 121° C., and the yeast is inoculated according to the inoculation amount of 1% of the weight of the yeast culture solution. Bacteria powder, obtained after aerobic culture at 28°C for 48 hours; 所述乳酸菌培养液按重量百分比计,由0.75%酵母膏、0.75%蛋白胨、1%葡萄糖、0.02%KH2PO4、0.05%吐温80、97.43%水组成,经121℃高压灭菌,按照乳酸菌培养液重量的1%接种量接种乳酸菌菌粉,37℃厌氧培养48h后得到;The lactic acid bacteria culture solution is composed of 0.75% yeast extract, 0.75% peptone, 1% glucose, 0.02% KH 2 PO 4 , 0.05% Tween 80, and 97.43% water in terms of weight percentage, and is sterilized by high pressure at 121°C according to Inoculate the lactic acid bacteria powder with 1% inoculum weight of the lactic acid bacteria culture solution, and obtain it after anaerobic culture at 37°C for 48 hours; 所述放线菌培养液按重量百分比计,由2%可溶性淀粉、0.05%K2HPO4、0.05%MgSO4·7H2O、0.05%NaCl、0.001%FeSO4、97.848%水组成,经121℃高压灭菌,按照放线菌培养液重量的1%接种量接种放线菌菌粉,28℃好氧培养7d后得到;The actinomycetes culture solution is composed of 2% soluble starch, 0.05% K 2 HPO 4 , 0.05% MgSO 4 ·7H 2 O, 0.05% NaCl, 0.001% FeSO 4 , and 97.848% water by weight percentage. ℃ autoclave, inoculate the actinomycetes powder according to the inoculum amount of 1% of the weight of the actinomycetes culture solution, obtain after 7 days of aerobic culture at 28 ℃; 所述丝状菌培养液按重量百分比计,由1%酵母膏、2%蛋白胨、2%葡萄糖、95%水经121℃高压灭菌,按照丝状菌培养液重量的1%接种量接种丝状菌菌粉,28℃好氧培养7d后得到;The filamentous bacteria culture solution is calculated by weight percentage, and is sterilized by 1% yeast extract, 2% peptone, 2% glucose, and 95% water by autoclaving at 121 ° C. Bacteria powder, obtained after aerobic culture at 28°C for 7 days; 所述醋酸菌培养液按重量百分比计,由10%葡萄糖、1%酵母膏、89%水经121℃高压灭菌,按照醋酸菌培养液重量的1%接种量接种醋酸菌菌粉,好氧培养12h后得到;Described acetic acid bacterium culture fluid is calculated by weight percentage, by 10% glucose, 1% yeast extract, 89% water through 121 ℃ autoclave sterilization, according to the 1% inoculation amount of acetic acid bacterium culture fluid weight inoculation acetic bacteria powder, aerobic Obtained after culturing for 12 hours; 步骤(2)中,所述灭菌培养基按重量百分比计,由3%甘蔗糖蜜、2%蛋白胨、95%水组成,经121℃高压灭菌得到。In step (2), the sterilized medium is composed of 3% sugarcane molasses, 2% peptone, and 95% water by weight percentage, and is obtained by autoclaving at 121°C.
CN201910870552.0A 2019-09-16 2019-09-16 Purification method of fermented feed production tail gas Active CN110496486B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910870552.0A CN110496486B (en) 2019-09-16 2019-09-16 Purification method of fermented feed production tail gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910870552.0A CN110496486B (en) 2019-09-16 2019-09-16 Purification method of fermented feed production tail gas

Publications (2)

Publication Number Publication Date
CN110496486A true CN110496486A (en) 2019-11-26
CN110496486B CN110496486B (en) 2021-10-26

Family

ID=68591869

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910870552.0A Active CN110496486B (en) 2019-09-16 2019-09-16 Purification method of fermented feed production tail gas

Country Status (1)

Country Link
CN (1) CN110496486B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101531969A (en) * 2008-03-13 2009-09-16 王峰 Microbial antibacterial environment-friendly deodorization bacterial system
CN201415107Y (en) * 2009-06-29 2010-03-03 佛山市顺德区全兴水产饲料有限公司 A feed waste gas deodorization treatment device
CN104174256A (en) * 2014-08-19 2014-12-03 西安交通大学 Combination solution for purifying air and application thereof
CN104845910A (en) * 2015-05-13 2015-08-19 河海大学 Biochemical reagent and preparation method and application thereof
CN206556396U (en) * 2017-02-22 2017-10-13 湖北楚襄化工股份有限公司 Calcium hydrophosphate fodder production drying tail gas desulphurizing system
CN110090502A (en) * 2019-05-30 2019-08-06 福建傲农生物科技集团股份有限公司 A kind of deodorizing device and technique for feed processing

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101531969A (en) * 2008-03-13 2009-09-16 王峰 Microbial antibacterial environment-friendly deodorization bacterial system
CN201415107Y (en) * 2009-06-29 2010-03-03 佛山市顺德区全兴水产饲料有限公司 A feed waste gas deodorization treatment device
CN104174256A (en) * 2014-08-19 2014-12-03 西安交通大学 Combination solution for purifying air and application thereof
CN104845910A (en) * 2015-05-13 2015-08-19 河海大学 Biochemical reagent and preparation method and application thereof
CN206556396U (en) * 2017-02-22 2017-10-13 湖北楚襄化工股份有限公司 Calcium hydrophosphate fodder production drying tail gas desulphurizing system
CN110090502A (en) * 2019-05-30 2019-08-06 福建傲农生物科技集团股份有限公司 A kind of deodorizing device and technique for feed processing

Also Published As

Publication number Publication date
CN110496486B (en) 2021-10-26

Similar Documents

Publication Publication Date Title
CN202961941U (en) Multilevel combined waste gas purification treatment system
CN206550126U (en) Contaminated soil steam extracts repair system
CN105056726A (en) A VOC ozone micro-nano bubble treatment system
CN207838678U (en) A kind of combination deodoration system of paper industry sewage plant
CN106563346A (en) Reaction type VOCs absorbent
CN108786383A (en) A kind of VOCs absorbent and its application
CN107715691A (en) A kind of photocatalysis aqueous vapor treating column
CN105130077A (en) Pre-treatment process of aldehyde ammonia method pyridine production wastewater
CN104832938A (en) High-temperature flue gas recovery and heat energy utilization device and method for bamboo charcoal pyrolysis process
CN103961735B (en) A kind of microbial deodorant and preparation method thereof
CN111569642B (en) Method for removing volatile organic pollutants in air by vacuum ultraviolet light catalytic oxidation
CN110496486A (en) A kind of purification method of fermented feed production tail gas
CN109621697A (en) A method of removing indoor formaldehyde
CN104857852A (en) VOCs removing method based on photocatalytic free radical advanced oxidation
Wei et al. High-efficiency carbon-coated steel wool filter for controlling cooking-induced oil smoke
CN103537171B (en) A kind of method of emulsion, the device administering organic exhaust gas and the improvement organic exhaust gas for administering organic exhaust gas
CN105688631B (en) A kind of hydroxyl oxygen eliminates smelly processing method and system
CN108786382A (en) A kind of absorption process of VOCs
CN112999845A (en) Catalyst and low-temperature plasma combined toluene degradation method
CN114681650B (en) Composition with deodorizing function and preparation method thereof
CN103083852B (en) Formaldehyde biological degrading agent and preparation method thereof
CN111437717A (en) Plant enzyme peculiar smell-removing compound biological enzyme formaldehyde-removing preparation and preparation method thereof
CN100354234C (en) Treating process of amino acid fermenting effluent
CN109850974B (en) Sewage treatment deodorization method
CN212091675U (en) A kind of dissolved gas biological deodorization device

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
CP03 Change of name, title or address

Address after: 265200, No. 39 East Longmen Road, Yantai, Shandong, Laiyang

Patentee after: Shandong Luhua Group Co.,Ltd.

Country or region after: China

Patentee after: Laiyang Luhua Biological Protein Co.,Ltd.

Address before: No. 39 Longmen East Road, Laiyang City, Yantai City, Shandong Province

Patentee before: SHANDONG LUHUA GROUP Co.,Ltd.

Country or region before: China

Patentee before: Laiyang Luhua Biological Protein Co.,Ltd.

CP03 Change of name, title or address