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CN1800361A - Method of nicotine biological degradation - Google Patents

Method of nicotine biological degradation Download PDF

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CN1800361A
CN1800361A CN 200510122831 CN200510122831A CN1800361A CN 1800361 A CN1800361 A CN 1800361A CN 200510122831 CN200510122831 CN 200510122831 CN 200510122831 A CN200510122831 A CN 200510122831A CN 1800361 A CN1800361 A CN 1800361A
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nicotine
tobacco
bacteria suspension
thalline
cultivation
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CN100422311C (en
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陆兆新
袁勇军
吕凤霞
别小妹
李颖
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Nanjing Agricultural University
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Nanjing Agricultural University
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Abstract

本发明涉及一种生物降解烟碱的方法,它是以烟碱降解细菌(Ochrobactrum intermedium)DN2为菌种,利用Ochrobactrum intermedium DN2或Ochrobactrum intermedium DN2的尼古丁降解酶作用于复烤烟叶、烟丝、工农业烟草下脚料以及烟草废弃物以及上述各种对象的水提液,使烟碱发生部分或全部的降解。采用本发明可使复考烟叶的烟碱降解40~ 48%;烟丝中的烟碱降解降低35~56%;烟草抽提液中的烟碱降解75~98%。该法属于生物降解法,特异性强,效果显著,生产成本低,可用于烟草加工,烟草造纸以及环境保护等领域。The invention relates to a method for biologically degrading nicotine. It uses nicotine-degrading bacteria (Ochrobactrum intermedium) DN2 as the strain, and uses Ochrobactrum intermedium DN2 or the nicotine-degrading enzyme of Ochrobactrum intermedium DN2 to act on recured tobacco leaves, shredded tobacco, industrial and agricultural products. Tobacco leftovers and tobacco waste, as well as the aqueous extracts of the above-mentioned various objects, cause partial or complete degradation of nicotine. The invention can degrade 40-48% of the nicotine in re-examined tobacco leaves; reduce 35-56% of nicotine in shredded tobacco; and 75-98% of nicotine in tobacco extract. The method belongs to the biodegradation method, has strong specificity, remarkable effect and low production cost, and can be used in the fields of tobacco processing, tobacco papermaking, environmental protection and the like.

Description

一种生物降解烟碱的方法A method for biodegrading nicotine

技术领域technical field

本发明涉及利用烟碱降解细菌(Ochrobactrum intermedium)DN2降解烟碱的方法,属于一种生物降解烟碱的生产方法,专用于生物降解烟碱。The invention relates to a method for degrading nicotine by using a nicotine-degrading bacterium (Ochrobactrum intermedium) DN2, which belongs to a production method for biodegrading nicotine, and is specially used for biodegrading nicotine.

背景技术Background technique

烟碱是普通烟草中的生物碱,俗称尼古丁(nicotine),其主要作用在于它所产生的生理强度,即通常所说的劲头,该强度与烟碱含量成正比。烟碱对人的中枢神经有强烈的刺激和麻痹作用,少量使人兴奋,大量会引起眩晕、呕吐甚至中毒死亡,成人一次摄入40mg~60mg尼古丁,就可能致命。因此,烟草中的烟碱含量过高,就会严重危害烟民的健康。Nicotine is an alkaloid in common tobacco, commonly known as nicotine (nicotine), its main function lies in the physiological strength it produces, that is, the so-called strength, which is proportional to the nicotine content. Nicotine has a strong stimulating and paralyzing effect on the central nervous system of people. A small amount can excite people, and a large amount can cause dizziness, vomiting and even poisoning death. Adults can be fatal if they ingest 40mg-60mg of nicotine at a time. Therefore, if the nicotine content in tobacco is too high, it will seriously endanger the health of smokers.

我国部分烟区所产烟叶,尤其是上部烟叶烟碱含量偏高。据报道,目前我国烤烟烟碱平均含量为3%~4%,白肋烟高达6%,而正常情况下烤烟应低于3%,白肋烟应在2%~4%。国内各大烟厂贮存的上部烟叶较多,一般因其烟碱含量较高,而不易用于叶组配方中。对于上述烟碱含量高的上部烟叶,卷烟生产厂家一般是通过逐步消化的方法来实现其应用。但由于消化速度慢,仍然有大量的上部烟叶得不到有效的利用而造成浪费。也有的厂家为了回收烟叶的收购成本,干脆就用这些上部烟叶来生产低档次的卷烟,使上部烟叶的工业可用性和商业附加值得不到充分体现。近年来,随着世界范围反吸烟运动的不断深入和消费者对自身健康的更加关注,几乎所有类型的卷烟产品都在向低焦油和低烟碱的淡味型卷烟方向发展,且其发展速度十分迅猛。目前我国强制规定,对于卷烟烟气中烟碱的含量大于15mg/支的烤烟型卷烟不得生产和流通,且这个规定的值将来还会降低。此外,为创收外汇,我国也有少量的卷烟出口,这些卷烟的烟碱含量一般都很低。出口卷烟的生产厂家为了生产低烟碱的卷烟,除了配方上的改进外,通常需要精挑细选“上乘烟叶”来满足其生产需求,费时费力费财,且不能保证大量生产此类卷烟对原料的需求。因此降低卷烟中烟碱的含量已经成为卷烟生产厂家的当务之急。虽然目前已有一些降低烟草中烟碱含量的方法,如农业措施和浸提法,但这些技术在降低烟碱的同时,也会降低那些对香烟品质有贡献的成分。The tobacco leaves produced in some tobacco areas in my country, especially the upper tobacco leaves, have high nicotine content. According to reports, the average content of nicotine in flue-cured tobacco in my country is 3% to 4%, and Burley tobacco is as high as 6%. Under normal circumstances, flue-cured tobacco should be less than 3%, and Burley tobacco should be 2% to 4%. There are many upper tobacco leaves stored in major domestic tobacco factories, which are generally not easy to use in leaf group formulas because of their high nicotine content. For the upper tobacco leaves with high nicotine content, cigarette manufacturers generally realize their application by gradually digesting them. However, due to the slow digestion rate, there is still a large amount of upper tobacco leaves that cannot be effectively utilized and cause waste. In order to recover the purchase cost of tobacco leaves, some manufacturers simply use these upper tobacco leaves to produce low-grade cigarettes, so that the industrial availability and commercial additional value of the upper tobacco leaves cannot be fully reflected. In recent years, with the continuous deepening of the worldwide anti-smoking campaign and consumers’ greater concern for their own health, almost all types of cigarette products are developing towards low-tar and low-nicotine light-flavored cigarettes, and the development speed is very fast. Swift. At present, our country compulsorily stipulates that flue-cured cigarettes with a nicotine content greater than 15 mg/stick in cigarette smoke must not be produced and distributed, and this value will be reduced in the future. In addition, in order to earn foreign exchange, my country also exports a small amount of cigarettes, which generally have low nicotine content. In order to produce low-nicotine cigarettes, manufacturers of export cigarettes usually need to carefully select "superior tobacco leaves" to meet their production needs, in addition to improving the formula, which is time-consuming, laborious and expensive, and cannot guarantee the impact of mass production of such cigarettes. raw material demand. Therefore reducing the content of nicotine in cigarettes has become an urgent task for cigarette manufacturers. Although there are some methods to reduce the nicotine content in tobacco, such as agricultural measures and extraction methods, while these technologies reduce nicotine, they will also reduce those components that contribute to the quality of cigarettes.

烟碱也是一种环境有毒物质,烟气环境中就含有大量的烟碱。在烟草制品的生产过程中会产生大量的固体,液体和气体废弃物,其中烟碱的平均含量高达18g烟碱/kg干重。在欧洲,当每千克废弃物(干重)中烟碱含量超过500mg时,就被归类为“有毒和有害物质”。1994年以来,美国一直把烟碱列在美国排放毒性化学品目录(Toxics ReleaseInventory,TRI)中。据报道,我国每年产生的烟草废弃物约100万吨。这些废弃物如果不加处理就投放到环境中,会严重破坏生态环境,危害人类的健康。Nicotine is also an environmentally toxic substance, and the smoke environment contains a large amount of nicotine. During the production of tobacco products, a large amount of solid, liquid and gaseous wastes are produced, and the average content of nicotine is as high as 18g nicotine/kg dry weight. In Europe, when the nicotine content per kilogram of waste (dry weight) exceeds 500mg, it is classified as "toxic and harmful substances". Since 1994, the United States has listed nicotine in the Toxics Release Inventory (TRI) of the United States. According to reports, my country produces about 1 million tons of tobacco waste every year. If these wastes are thrown into the environment without treatment, they will seriously damage the ecological environment and endanger human health.

综上所述,有效地控制和降低卷烟制品和环境中的烟碱含量,对于保护环境、维护人类健康有着深远的意义。目前,国外研究者已从环境中分离了多种烟碱降解菌。【文摘】利用Deharyomyces nicotianae和Micrococcus nicotianae的培养液进行工业发酵处理烟草,试验表明,这两种菌液既能改善烟草的风味和香气,也能分别使烟草的烟碱含量降解了0.45%和0.83%,而两种混合菌液处理的烟草烟碱含量降低了0.61%。Tobacco,1947,51:6-15。【文摘】在合成介质上,用由土壤中分离出的假单胞菌属(Pseudomonas)第41小种处理烟碱溶液24h后,烟碱含量大幅度降低,由于pH值的降低和菌落数的增大,烟碱的分解停止,约有75%的起始烟碱发生降解。Arch Biochem Biophys,1958,72(2):145-162。【文摘】从烟叶中分离出可将烟碱氧化成γ-氨基丁酸的细菌。Journal of Bacterial,1958,(75):474~479。【文摘】从烟叶仓库中分离出烟草节细菌(Arthrobacter nicotianae),该菌在烟碱-琼脂上大量繁殖并使烟碱降解。Coresta,1959,3:2595。【文摘】使用0.2%烟碱作为唯一碳源的培养基,从烟草生长土壤和烟叶表面上分离出能够降解烟碱的细菌:争论产碱菌(Alcaligenes paradoxus)和球形节杆菌(Arthrobacter globiformils),若培养基中有葡萄糖存在,它们会具有高烟碱降解活性,但是在烟碱浓度为0.5%时,菌的生长受到抑制;当把争论产碱菌喷洒到潮湿的烟叶上时,五天内都没有产生明显的降解;但是若同时在培养基中加入葡萄糖,将在两天之内产生明显降烟碱的效果。Science Paper,1976,118:197-201。【文摘】从干烟叶表面分离出一株能够降解烟碱的菌株,经鉴定为阴沟肠杆菌(Enterobacter cloacae)E-150。在含有烟碱(小于5g/L)的培养基中34℃、pH7.0的条件下进行发酵,此发酵过程中该菌降烟碱的能力得到诱导。另外,这种菌还能代谢烟酸,但不能降解去甲烟碱和新烟碱。Degrader(Spain),1983,22:85-98。【文摘】布朗威&廉森公司从Puerto Rican雪茄烟叶上分离出可降解烟碱的恶臭假单胞菌(Pseudomonas putida)和可同时除去烟碱和硝酸盐的纤维单胞菌属(Cellulomana ssp)。将此微生物接种到白肋烟叶片上,同时添加足量的水和氨水,使烟叶的水分含量和pH值分别达到65%~75%和6.1。而后于30℃下堆积发酵,16h白肋烟叶片中的烟碱已基本耗尽。化学分析和评吸结果表明,与未处理烟叶加工的卷烟相比,由处理烟叶加工的卷烟配方及其烟气中的烟碱分别降低48%和42%,其感官评吸结果优良。US Patent,No.4037609【文摘】用假单胞菌降解烟尘废料中烟碱的研究。其实验是,取1kg烟尘样品(烟碱2.0%~2.5%),加2.0~2.5L含有假单胞菌的水溶液浸润,使之完全浸透烟粉,室温下放置数天,并偶尔搅拌一下,约一周后,烟碱含量在4.0×10-4~7.0×10-4之间。国内在这方面的研究较少。Information Bulletin of Coresta Congress,1994,ST8。【文摘】王革从烟叶上分离3株降解烟碱能力较强的菌株。供试菌株在无蛋白质培养基上生长至一定浓度后,将菌液均匀喷淋在供试烟叶上,处理样与对照样放置于40℃培养箱中发酵。试验结果表明,烟叶经微生物发酵后,所有处理烟样烟碱含量较对照样均有不同程度减少,最高减少60.15%,最低也能减少5.90%,平均减少21.35%。烟草科学研究,2001,(2):66-68。To sum up, effectively controlling and reducing the nicotine content in cigarette products and the environment has far-reaching significance for protecting the environment and maintaining human health. At present, foreign researchers have isolated a variety of nicotine-degrading bacteria from the environment. 【Abstract】Using the culture liquid of Deharyomyces nicotianae and Micrococcus nicotianae for industrial fermentation treatment of tobacco, experiments show that these two bacterial liquids can not only improve the flavor and aroma of tobacco, but also degrade the nicotine content of tobacco by 0.45% and 0.83% respectively. %, while the nicotine content of tobacco treated with the two mixed bacterial solutions decreased by 0.61%. Tobacco, 1947, 51:6-15. [Abstract] On the synthetic medium, after treating the nicotine solution with Pseudomonas race 41 isolated from the soil for 24 hours, the nicotine content was greatly reduced, due to the decrease of the pH value and the number of colonies. Increase, the decomposition of nicotine stops, and about 75% of the starting nicotine is degraded. Arch Biochem Biophys, 1958, 72(2): 145-162. 【Abstract】The bacteria that can oxidize nicotine to γ-aminobutyric acid were isolated from tobacco leaves. Journal of Bacterial, 1958, (75): 474-479. 【Abstract】Arthrobacter nicotianae was isolated from a tobacco leaf warehouse. The bacteria multiplied on nicotine-agar and degraded nicotine. Coresta, 1959, 3:2595. 【Abstract】Using 0.2% nicotine as the only carbon source medium, bacteria capable of degrading nicotine were isolated from tobacco growth soil and tobacco leaf surface: Alcaligenes paradoxus and Arthrobacter globiformils, If glucose exists in the culture medium, they will have high nicotine degrading activity, but when the nicotine concentration is 0.5%, the growth of bacteria is inhibited; There was no obvious degradation; however, if glucose was added to the medium at the same time, a significant effect of nornicotine would be produced within two days. Science Paper, 1976, 118: 197-201. 【Abstract】A strain capable of degrading nicotine was isolated from the surface of dried tobacco leaves and identified as Enterobacter cloacae (Enterobacter cloacae) E-150. Fermentation is carried out in a medium containing nicotine (less than 5g/L) under the conditions of 34°C and pH 7.0, and the nornicotine ability of the bacterium is induced during the fermentation process. In addition, this bacteria can also metabolize niacin, but cannot degrade nornicotine and neonicotinoid. Degrader (Spain), 1983, 22:85-98. 【Abstract】Pseudomonas putida, which can degrade nicotine, and Cellulomana ssp, which can simultaneously remove nicotine and nitrate, were isolated from Puerto Rican cigar leaves by Brownway & Williamson . The microorganism is inoculated on the leaves of Burley tobacco, and sufficient water and ammonia water are added at the same time, so that the moisture content and pH value of the tobacco leaves reach 65%-75% and 6.1 respectively. Then pile up and ferment at 30°C, and the nicotine in the Burley tobacco leaves has been basically exhausted within 16 hours. The results of chemical analysis and smoking evaluation showed that compared with the cigarettes processed from untreated tobacco leaves, the nicotine in the formula and smoke of the processed tobacco leaves decreased by 48% and 42%, respectively, and the sensory evaluation and smoking results were excellent. US Patent, No.4037609 [Abstract] Degradation of nicotine in soot waste with Pseudomonas bacteria. The experiment is to take 1 kg of smoke samples (nicotine 2.0% ~ 2.5%), add 2.0 ~ 2.5L of aqueous solution containing Pseudomonas to infiltrate, so that it is completely soaked in smoke powder, put it at room temperature for several days, and occasionally stir it, After about a week, the nicotine content is between 4.0×10 -4 and 7.0×10 -4 . Domestic research in this area is less. Information Bulletin of Coresta Congress, 1994, ST8. 【Abstract】Wang Ge isolated 3 strains with strong ability to degrade nicotine from tobacco leaves. After the test strain grew to a certain concentration on the protein-free medium, the bacterial solution was evenly sprayed on the test tobacco leaves, and the treated samples and control samples were placed in a 40°C incubator for fermentation. The test results showed that after the tobacco leaves were fermented by microorganisms, the nicotine content of all treated tobacco samples was reduced to varying degrees compared with the control sample, the highest reduction was 60.15%, the lowest reduction was 5.90%, and the average reduction was 21.35%. Tobacco Science Research, 2001, (2): 66-68.

实践证明,生物降解法是去除或减少烟草废弃物中烟碱的有效途径。通过降低烟叶中烟碱的含量,可以解决我国上部烟叶的工业可用性问题,增加烟叶的附加值;通过生物降解法可以使生产低烟碱卷烟的原料来源具有一般性,节约生产成本,扩大出口创汇;降解烟草废弃物中的烟碱,可以保护环境,维护人类健康。因此,利用生物降解烟碱具有重要的经济和社会意义。Practice has proved that biodegradation is an effective way to remove or reduce nicotine in tobacco waste. By reducing the content of nicotine in tobacco leaves, it can solve the problem of industrial usability of upper tobacco leaves in my country and increase the added value of tobacco leaves; through biodegradation, the source of raw materials for the production of low-nicotine cigarettes can be made general, saving production costs and expanding export earnings ; Degradation of nicotine in tobacco waste can protect the environment and maintain human health. Therefore, the use of biodegradable nicotine has important economic and social significance.

烟碱降解细菌(Ochrobactrum intermedium)DN2是从土壤中分离的烟碱降解细菌,我们报道了该菌的分离和鉴定结果(微生物学报,2005,45(2):181-184)。该菌的生物学特性为:革兰氏染色阴性,无芽孢,短杆状,2根端生鞭毛;在牛肉膏蛋白胨琼脂平板上菌落白色,光滑,边缘整齐;接触酶、氧化酶反应呈阳性,严格好氧,能以烟碱为唯一碳源进行生长,最适生长温度和pH分别为30℃、7.0,氧化葡萄糖产酸,硝酸盐还原阳性,V.P.、M.P.反应阴性;在金氏培养基B中不产生水溶性色素,该菌不水解淀粉和明胶,能够利用葡萄糖、麦芽糖等,对黏菌素不敏感。但是目前尚未报道Ochrobactrum intermedium DN2降解烟碱的工艺。利用其为菌种降解烟碱可以运用于烟草制造、烟叶造纸以及环境保护等领域。Nicotine-degrading bacteria (Ochrobactrum intermedium) DN2 is a nicotine-degrading bacterium isolated from soil. We reported the results of the isolation and identification of this bacterium (Acta Microbiology, 2005, 45(2): 181-184). The biological characteristics of the bacteria are: negative Gram stain, no spores, short rod shape, 2 terminal flagella; colonies on the beef extract peptone agar plate are white, smooth, and the edges are neat; the reaction of contact enzyme and oxidase is positive , Strictly aerobic, can grow with nicotine as the only carbon source, the optimum growth temperature and pH are 30°C and 7.0 respectively, oxidize glucose to produce acid, positive for nitrate reduction, negative for V.P., M.P. reaction; in King's medium B does not produce water-soluble pigments, the bacteria does not hydrolyze starch and gelatin, can utilize glucose, maltose, etc., and is not sensitive to colistin. However, the process of Ochrobactrum intermedium DN2 to degrade nicotine has not been reported yet. Using it as a bacterial strain to degrade nicotine can be used in the fields of tobacco manufacturing, tobacco leaf papermaking, environmental protection and the like.

发明内容Contents of the invention

技术问题technical problem

本发明的目的在于提供一种生物降解烟碱的方法,利用烟碱降解细菌(Ochrobactrum intermedium)DN2或Ochrobactrum intermedium DN2的尼古丁降解酶降解烟碱,使复烤烟叶的烟碱降解40~48%;烟丝中的烟碱降解降低35~56%;烟草抽提液中的烟碱降解75~98%。通过降低烟叶或烟草抽提液中烟碱的含量,可以既可以解决我国上部烟叶的工业可用性问题,也可以解决烟草废弃物中烟碱对环境的污染问题。The object of the present invention is to provide a method for biodegrading nicotine, using nicotine degrading enzymes of nicotine degrading bacteria (Ochrobactrum intermedium) DN2 or Ochrobactrum intermedium DN2 to degrade nicotine, so as to degrade 40% to 48% of nicotine in recured tobacco leaves; The degradation of nicotine in shredded tobacco is reduced by 35-56%, and the degradation of nicotine in tobacco extract is 75-98%. By reducing the content of nicotine in tobacco leaves or tobacco extract, it can not only solve the problem of industrial usability of upper tobacco leaves in my country, but also solve the problem of environmental pollution caused by nicotine in tobacco waste.

技术方案Technical solutions

本发明一种生物降解烟碱的方法,其特征在于A method for biodegrading nicotine of the present invention is characterized in that

1)烟碱降解细菌(Ochrobactrum intermedium)DN2的扩大培养1) Expanded culture of nicotine-degrading bacteria (Ochrobactrum intermedium) DN2

普通培养基g/L:胰蛋白胨11.34、牛肉膏3.00、NaCl5.00、MgSO4·7H2O3.71、pH值7.23;Ordinary medium g/L: tryptone 11.34, beef extract 3.00, NaCl5.00, MgSO 4 7H 2 O3.71, pH 7.23;

基础培养基g/L:NH4NO31.00、MgSO4·7H2O 0.50、(NH4)2SO40.50、KH2PO40.50、NaCl 0.50、K2HPO41.50、pH值7.0;Basal medium g/L: NH 4 NO 3 1.00, MgSO 4 7H 2 O 0.50, (NH 4 ) 2 SO 4 0.50, KH 2 PO 4 0.50, NaCl 0.50, K 2 HPO 4 1.50, pH 7.0;

烟草抽提液:烟草废弃物和水按1∶10的比例混合成水提液,过夜,水提液用4N NaOH或1N HCl将pH值调到7.0;Tobacco extract: Tobacco waste and water are mixed at a ratio of 1:10 to form an aqueous extract, overnight, and the pH of the aqueous extract is adjusted to 7.0 with 4N NaOH or 1N HCl;

以上培养基121℃高压蒸汽灭菌30min;The above medium was sterilized by high-pressure steam at 121°C for 30 minutes;

2)菌悬液的制备2) Preparation of bacterial suspension

菌体的普通培养:将Ochrobactrum intermedium DN2接种到普通培养基中,32℃、120r/min摇床培养34h,获得普通培养液,10000r/min离心10min,收集菌体,用50mM,pH7.0的PBS将上述菌体配制菌悬液,获得普通培养的菌悬液;Ordinary culture of bacteria: Inoculate Ochrobactrum intermedium DN2 into ordinary culture medium, culture at 32°C and 120r/min shaker for 34h to obtain ordinary culture medium, centrifuge at 10000r/min for 10min, collect bacteria, and use 50mM, pH7.0 Prepare the bacterial suspension from the above bacterial cells in PBS to obtain the common cultured bacterial suspension;

菌体的诱导培养:将32℃、120r/min条件下培养34h的普通培养液以5%的比例接入烟碱浓度为500mg/L的基础培养基中,30℃、120r/min摇床培养36h,然后将培养液10000r/min离心10min,收集菌体,用50mM,pH7.0PBS将上述菌体配制菌悬液,获得诱导培养的菌悬液;Bacterial induction culture: Put the common culture solution cultured at 32°C and 120r/min for 34h into the basal medium with a nicotine concentration of 500mg/L at a ratio of 5%, and cultivate on a shaking table at 30°C and 120r/min 36h, then centrifuge the culture solution at 10000r/min for 10min, collect the bacteria, prepare the above bacteria suspension with 50mM, pH7.0PBS, and obtain the culture suspension;

3)粗酶液的的制备3) Preparation of crude enzyme solution

采用以上方法获得的诱导培养菌悬液,按1000mL培养菌悬液加60mL 50mM,pH7.0PBS缓冲液超声波破碎,超声波条件为400w,超声5s,间歇10s,90次,4℃、10000r/min离心10min,上清液即为粗酶液;For the induced culture suspension obtained by the above method, add 60mL 50mM, pH7.0PBS buffer solution to 1000mL culture suspension and ultrasonically break it. 10min, the supernatant is the crude enzyme solution;

4)烟碱的生物降解4) Biodegradation of nicotine

在复烤烟草中烟碱的生物降解为:用无菌水将复烤烟叶的水分调节到60%-85%后,分别将上述方法获得的普通培养菌悬液、诱导培养菌悬液或粗酶液以10-20%接种量接入复烤烟叶中,充分混匀菌体,于25~40℃固体发酵,每隔6h翻抖通气;The biodegradation of nicotine in re-cured tobacco is as follows: after adjusting the moisture content of re-cured tobacco leaves to 60%-85% with sterile water, the common culture suspension obtained by the above method, the induced culture suspension or the crude The enzyme solution is inserted into the re-cured tobacco leaves with 10-20% inoculation amount, fully mixed the bacteria, fermented in solid state at 25-40 °C, and ventilated by shaking every 6 hours;

或者在烟丝中烟碱的生物降解为:用无菌水将烟丝的水分调节到60%-85%后,分别将上述方法获得的普通培养菌悬液、诱导培养菌悬液或粗酶液以10-20%接种量接入烟丝中,充分混匀菌体,于25~40℃固体发酵,每隔6h翻抖通气;Or the biodegradation of nicotine in shredded tobacco is as follows: after adjusting the moisture of shredded tobacco to 60%-85% with sterile water, the common culture suspension, induced culture suspension or crude enzyme solution obtained by the above method are respectively mixed with Put 10-20% of the inoculum into the shredded tobacco, fully mix the bacteria, ferment in solid state at 25-40°C, and shake for ventilation every 6 hours;

或者在烟草抽提液中烟碱的生物降解为:分别将上述方法获得的普通培养菌悬液、诱导培养菌悬液或粗酶液以10-20%接种量接入烟草抽提液中,30℃、120r/min摇床培养。Or the biodegradation of nicotine in the tobacco extract is as follows: respectively inserting the common culture suspension, the induced culture suspension or the crude enzyme solution obtained by the above method into the tobacco extract with an inoculation amount of 10-20%, Cultivate on a shaker at 30°C and 120r/min.

有益效果Beneficial effect

本发明对首次从环境中分离一株具有较强的烟碱降解能力的细菌Ochrobactrumintermedium DN2进行开发利用。利用Ochrobactrum intermedium DN2或Ochrobactrumintermedium DN2的尼古丁降解酶降解烟碱,使复烤烟叶的烟碱降解40~48%;烟丝中的烟碱降解降低35~56%;烟草抽提液中的烟碱降解75~98%。The invention develops and utilizes a bacterium Ochrobactrum intermedium DN2 with strong nicotine degradation ability isolated from the environment for the first time. The nicotine degrading enzyme of Ochrobactrum intermedium DN2 or Ochrobactrum intermedium DN2 is used to degrade nicotine, so that the nicotine degradation of re-cured tobacco leaves is 40-48%; the nicotine degradation in shredded tobacco is reduced by 35-56%; ~98%.

通过降低烟叶中烟碱的含量,可以解决上部烟叶的工业可用性问题,增加烟叶的附加值;通过生物降解法可以使生产低烟碱卷烟的原料来源具有一般性,节约生产成本,扩大出口创汇;降解烟草废弃物中的烟碱,可以保护环境,维护人类健康。By reducing the content of nicotine in the tobacco leaves, the industrial usability of the upper tobacco leaves can be solved and the added value of the tobacco leaves can be increased; through the biodegradation method, the source of raw materials for the production of low-nicotine cigarettes can be made general, saving production costs and expanding export earnings; Degradation of nicotine in tobacco waste can protect the environment and maintain human health.

具体实施方式Detailed ways

【实施例1】【Example 1】

将Ochrobactrum intermedium DN2接种到普通培养基(g/L):胰蛋白胨11.34、牛肉膏3.00、NaCl5.00、MgSO4·7H2O 3.71、pH值7.23,32℃、120r/min摇床培养34h,10000r/min离心10min,收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液,以15g/L的接种量接入烟草抽提液(烟草废弃物和水按1∶10的比例混合,过夜,水提液用4N NaOH或1N HCl将pH值调到7.0)中,于pH6.5~8.5,28~40℃下搅拌反应2~4d,烟碱降解率为85~98%。Inoculate Ochrobactrum intermedium DN2 into common medium (g/L): tryptone 11.34, beef extract 3.00, NaCl5.00, MgSO 4 7H 2 O 3.71, pH 7.23, culture at 32°C, 120r/min shaker for 34h, Centrifuge at 10000r/min for 10min, collect the thalline, prepare the bacterium suspension with the above-mentioned thalline with PBS (50mM, pH7.0), insert the tobacco extract with the inoculation amount of 15g/L (tobacco waste and water press 1: Mix at a ratio of 10, overnight, adjust the pH value of the water extract to 7.0 with 4N NaOH or 1N HCl), and stir at pH 6.5 to 8.5 at 28 to 40°C for 2 to 4 days, and the degradation rate of nicotine is 85 to 40°C. 98%.

【实施例2】[Example 2]

Ochrobactrum intermedium DN2经过普通培养基扩大培养(方法同实施例1)后,10000r/min离心10min,收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液,以10%接种量接入含水量为60~85%的复烤烟叶中,于28~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为40~48%。After Ochrobactrum intermedium DN2 is expanded and cultivated through ordinary medium (the method is the same as in Example 1), centrifuge at 10000r/min for 10min, collect the thalline, prepare the bacterium suspension with the above-mentioned thalline with PBS (50mM, pH7.0), inoculate with 10% The amount is added to the re-cured tobacco leaves with a moisture content of 60-85%, solid fermentation at 28-40°C, and shaking every 6h for ventilation. The degradation rate of nicotine from 2 to 4 days was 40 to 48%.

【实施例3】[Example 3]

Ochrobactrum intermedium DN2经过普通培养基扩大培养(方法同实施例1)后,10000r/min离心10min,收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液,以18%接种量接入含水量为60~85%的烟丝中,于28~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为40~56%。After Ochrobactrum intermedium DN2 is expanded and cultivated with ordinary medium (the method is the same as in Example 1), it is centrifuged at 10000r/min for 10min to collect the thalline, and the above-mentioned thalline is prepared into a bacterial suspension with PBS (50mM, pH7.0), and inoculated with 18% The amount is inserted into shredded tobacco with a water content of 60-85%, solid fermentation is carried out at 28-40°C, and ventilation is stirred every 6 hours. The degradation rate of nicotine in 2-4 days was 40-56%.

【实施例4】【Example 4】

将Ochrobactrum intermedium DN2在普通培养基(同实施例1)中32℃、120r/min条件下培养34h,以5%的比例接入基础培养基(g/L,NH4NO31.00、MgSO4·7H2O 0.50、(NH4)2SO40.50、KH2PO40.50、NaCl0.50、K2HPO41.50、pH值7.0,烟碱为0.5)中,30℃、120r/min摇床培养36h,然后将培养液10000r/min离心10min,收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液,接入含烟碱的基础培养基中进行诱导培养,离心收集菌体,以15g/L的接种量接入烟草抽提液中,于pH6.5~8.5,25~40℃下搅拌反应2~4d,烟碱降解率为85~98%。Ochrobactrum intermedium DN2 was cultured for 34 h at 32° C. and 120 r/min in common medium (same as Example 1), and then inserted into the basal medium (g/L, NH 4 NO 3 1.00, MgSO 4 . 7H 2 O 0.50, (NH 4 ) 2 SO 4 0.50, KH 2 PO 4 0.50, NaCl 0.50, K 2 HPO 4 1.50, pH 7.0, nicotine 0.5), 30°C, 120r/min shaker culture 36h, then centrifuge the culture solution at 10000r/min for 10min, collect the bacteria, use PBS (50mM, pH7.0) to prepare the above bacteria into a bacterial suspension, insert it into the basal medium containing nicotine for induction culture, and collect by centrifugation The bacterium is inserted into the tobacco extract with an inoculation amount of 15g/L, stirred and reacted at pH 6.5-8.5 at 25-40°C for 2-4 days, and the nicotine degradation rate is 85-98%.

【实施例5】【Example 5】

Ochrobactrum intermedium DN2先在普通培养基培养,后接入含烟碱的基础培养基中进行诱导培养,离心收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液(方法同实施例4),以10-20%接种量接入含水量为60~85%的复烤烟叶中,于28~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为40~48%。Ochrobactrum intermedium DN2 was first cultured in ordinary culture medium, then inserted into basal medium containing nicotine for induction culture, the bacteria were collected by centrifugation, and the above bacteria were prepared into bacterial suspension with PBS (50mM, pH7.0) (the method was the same as Example 4), insert 10-20% inoculum amount into re-cured tobacco leaves with a moisture content of 60-85%, ferment in solid state at 28-40° C., and shake and ventilate every 6 hours. The degradation rate of nicotine from 2 to 4 days was 40 to 48%.

【实施例6】[Example 6]

Ochrobactrum intermedium DN2先在普通培养基培养,后接入含烟碱的基础培养基中进行诱导培养,离心收集菌体,用PBS(50mM,pH7.0)将上述菌体配制菌悬液(方法同实施例4),以10-20%接种量接入含水量为60~85%的烟丝中,于28~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为40~56%。Ochrobactrum intermedium DN2 was first cultured in ordinary culture medium, then inserted into basal medium containing nicotine for induction culture, the bacteria were collected by centrifugation, and the above bacteria were prepared into bacterial suspension with PBS (50mM, pH7.0) (the method was the same as Example 4), insert 10-20% inoculum amount into shredded tobacco with a water content of 60-85%, ferment in solid state at 28-40° C., and shake and ventilate every 6 hours. The degradation rate of nicotine in 2-4 days was 40-56%.

【实施例7】[Example 7]

将Ochrobactrum intermedium DN2经烟碱诱导培养后(同实施例4),按1000mL培养液菌体细胞加60mLPBS缓冲液(50mM,pH7.0)超声波破碎,超声波条件为400w,超声5s,间歇10s,90次。4℃、10000r/min离心10min,上清液即为粗酶液,将粗酶液或粗酶液以10-20%接种量接入烟草抽提液中,于pH6.5~8.5,25~40℃下搅拌反应2~4d,烟碱降解率为75~86%。After Ochrobactrum intermedium DN2 was cultured by nicotine induction (same as in Example 4), 1000mL of culture liquid bacterial cells plus 60mL of PBS buffer (50mM, pH7.0) was ultrasonically broken, the ultrasonic conditions were 400w, ultrasonic 5s, intermittent 10s, 90 Second-rate. Centrifuge at 4°C and 10000r/min for 10min, the supernatant is the crude enzyme solution, add the crude enzyme solution or the crude enzyme solution with 10-20% inoculation amount into the tobacco extract, at pH6.5~8.5, 25~ The reaction was stirred at 40°C for 2-4 days, and the degradation rate of nicotine was 75-86%.

【实施例8】[Embodiment 8]

将Ochrobactrum intermedium DN2经烟碱诱导培养后,采用超声波破壁获得粗酶液(方法同实施例7),将粗酶液以10-20%接种量入含水量为65~85%的复烤烟叶中,于25~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为40~48%。After the Ochrobactrum intermedium DN2 was induced and cultured by nicotine, the crude enzyme solution was obtained by breaking the wall with ultrasonic waves (the method is the same as in Example 7), and the crude enzyme solution was injected into the recured tobacco leaves with a water content of 65-85% at an inoculation amount of 10-20%. During solid fermentation at 25-40°C, shake and ventilate every 6 hours. The degradation rate of nicotine from 2 to 4 days was 40 to 48%.

【实施例9】[Example 9]

将Ochrobactrum intermedium DN2经烟碱诱导培养后,采用超声波破壁获得粗酶液(方法同实施例7),将粗酶液以10-20%接种量接入含水量为65~85%的烟丝中,于25~40℃固体发酵,每隔6h翻抖通气。2~4d的烟碱降解率为35~45%。After Ochrobactrum intermedium DN2 was cultured by nicotine induction, the crude enzyme solution was obtained by breaking the wall with ultrasonic waves (the method is the same as in Example 7), and the crude enzyme solution was inserted into cut tobacco with a water content of 65-85% at an inoculum amount of 10-20% , solid fermentation at 25 ~ 40 ° C, shaking every 6 hours to ventilate. The degradation rate of nicotine in 2-4 days is 35-45%.

Claims (1)

1, a kind of method of biological degradation nicotine is characterized in that:
1) enlarged culturing of nicotine degradation bacterium (Ochrobactrum intermedium) DN2
Ordinary culture medium g/L: Tryptones 11.34, extractum carnis 3.00, NaCl 5.00, MgSO 47H 2O 3.71, pH value 7.23;
Basic medium g/L:NH 4NO 31.00, MgSO 47H 2O 0.50, (NH 4) 2SO 40.50, KH 2PO 40.50, NaCl0.50, K 2HPO 41.50, pH value 7.0;
The tobacco extract: tobacco waste and water become the water extract by 1: 10 mixed, spend the night, and the water extract is transferred to 7.0 with 4N NaOH or 1N HCl with the pH value;
121 ℃ of high pressure steam sterilization 30min of above substratum;
2) preparation of bacteria suspension
The common cultivation of thalline: Ochrobactrum intermedium DN2 is inoculated in the ordinary culture medium, 32 ℃, 120r/min shaking table cultivation 34h, obtain common nutrient solution, the centrifugal 10min of 10000r/min, collect thalline, use 50mM, the PBS of pH7.0 obtains the bacteria suspension of common cultivation with above-mentioned thalline preparation bacteria suspension;
The inducing culture of thalline: it is in the basic medium of 500mg/L that the common nutrient solution of cultivating 34h under 32 ℃, 120r/min condition is inserted nicotinic density with 5% ratio, 30 ℃, 120r/min shaking table cultivation 36h, then with the centrifugal 10min of nutrient solution 10000r/min, collect thalline, use 50mM, pH7.0 PBS obtains the bacteria suspension of inducing culture with above-mentioned thalline preparation bacteria suspension;
3) crude enzyme liquid preparation
The inducing culture bacteria suspension that adopts above method to obtain is cultivated bacteria suspension by 1000mL and is added 60mL 50mM, pH7.0PBS damping fluid ultrasonic disruption, the ultrasonic wave condition is 400w, ultrasonic 5s, intermittently 10s, 90 times, 4 ℃, the centrifugal 10min of 10000r/min, supernatant liquor is crude enzyme liquid;
4) biological degradation of nicotine
The biological degradation of nicotine is in the redrying tobacco: after with sterilized water the moisture of redried leaf tobacco being adjusted to 60%-85%, common cultivation bacteria suspension, inducing culture bacteria suspension or crude enzyme liquid that aforesaid method is obtained insert in the redried leaf tobacco with the 10-20% inoculum size, abundant mixing thalline, in 25~40 ℃ of solid fermentations, turn over every 6h and to tremble ventilation;
Perhaps the biological degradation of nicotine is in pipe tobacco: after with sterilized water the moisture of pipe tobacco being adjusted to 60%-85%, common cultivation bacteria suspension, inducing culture bacteria suspension or crude enzyme liquid that aforesaid method is obtained insert in the pipe tobacco with the 10-20% inoculum size, abundant mixing thalline, in 25~40 ℃ of solid fermentations, turn over every 6h and to tremble ventilation;
Perhaps the biological degradation of nicotine is in the tobacco extract: common cultivation bacteria suspension, inducing culture bacteria suspension or crude enzyme liquid that aforesaid method is obtained insert in the tobacco extract with the 10-20% inoculum size, 30 ℃, the cultivation of 120r/min shaking table.
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CN102994462A (en) * 2011-12-20 2013-03-27 辽宁中科生物工程有限公司 Pesticide degradation enzyme and preparation method thereof
CN103937722A (en) * 2014-04-24 2014-07-23 烟台海上传奇生物科技有限公司 Ochrobactrum intermedium, microbial agent and applications of ochrobactrum intermedium and microbial agent
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CN101856143B (en) * 2010-05-17 2013-07-24 山东大学 Tobacco leaf extract culture medium and application thereof
CN102994462A (en) * 2011-12-20 2013-03-27 辽宁中科生物工程有限公司 Pesticide degradation enzyme and preparation method thereof
CN102994462B (en) * 2011-12-20 2014-05-28 辽宁中科生物工程有限公司 Pesticide degradation enzyme and preparation method thereof
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