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Isolation of Crude Oil Degrading Marine Bacteria and Assessment for Biosurfactant Production

机译:原油降解海洋细菌的分离和生物表面活性剂生产的评估

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Ten bacterial isolates recovered from the crude oil contaminated sea water samples from a ship yard in Alang coast, Gujarat showed optimum growth in presence of crude oil. The crude oil degrading isolates were identified as species of genera Acinetobacter, Marinococcus, Micrococcus, Planococcus, Methylobacterium, Rhodococcus and Noccardia. All the ten isolates degraded 1% crude oil in Bushnell Haas broth. Highest biodegradation of crude oil was found to be 70% by the isolate M2 which belonged to genus Marinococcus. Other isolates showed biodegradation in the range of 55-30%. On addition of 1% Tween 80 biodegradation reduced in majority of cases. 70% of the bacterial isolates scored positive for biosurfactant production and emulsified toluene however emulsion stability varied drastically among the isolates. None of the biosurfactant producing bacterial isolates was hemolytic.Key words: Biodegradation, Biosurfactant, Emulsion, Hemolytic. Introduction In quantitative terms, crude oil is one of the most important organic pollutants in marine environment and it has been estimated that worldwide somewhere between 1.7- 8.8×106 tons of petroleum hydrocarbons impact marine waters and estuaries annually (1). Reports have been appearing since last three decades on the biodegradability of crude oil by bacteria which can use hydrocarbons as source of carbon and energy (2). When micro organisms grow in environment rich in hydrocarbon, they undergo many adaptations. One such adaptation is biosurfactant production which is a frequently encountered feature in hydrocarbon degrading bacteria or sometimes even a prerequisite for growth on hydrocarbons (3). Biosurfactant production helps the hydrocarbon degrading bacterium to gain better access to their hydrophobic substrates as it brings about changes like reduction of surface tension of the environment around the bacterium, reduction of interfacial tension between bacterial cell wall and hydrocarbon molecules, membrane modifications like increasing the hydrophobicity of cell wall by reducing the lipopolysaccharide content of cell wall, enhancing the dispersion of hydrocarbon by encapsulation of the hydrocarbon into micelles etc (4,5,6,7). Amongst the above changes reduction in surface and interfacial tension is a universal phenomenon displayed by almost all types of biosurfactant whereas changes like membrane modifications and emulsion formation strictly depends upon type of biosurfactant for e.g. glycolipids, lipopepetides, polymeric or particulate etc. Enhancement in hydrocarbon degradation may occur by cumulative effect of above changes.Here we present a report on isolation of crude oil degrading marine bacteria from oil contaminated sea water, their screening for crude oil degradation and biosurfactant production. Methods Collection of sampleSea water samples were collected in sterilized glass bottles from a ship yard at Alang coast, Gujarat. Isolation and screening of crude oil degrading bacteriaIsolation of crude oil degrading marine bacteria was carried out by spreading 100 μL of serially diluted seawater samples on mineral salt medium (MM2). An ethereal solution of crude oil (10% w/v) was uniformly sprayed over the surface of agar plate. The ether immediately vaporized and thin layer of oil remained on the entire surface. The crude oil was obtained from ONGC plant at Chandkheda near Ahmedabad, Gujarat. The plates were incubated at 25oC for 20 days. The bacterial isolates which appeared on MM2 plate after incubation were screened for crude oil degradation by overlay technique (8).Crude oil biodegradationCrude oil biodegradation experiment was performed by modifying the technique described by Pirnik et al. (9) by adding the inoculating cells of density 108 mL-1 to BHM with 1% crude oil added as sole carbon source. To study effect of Tween 80 on biodegradation of crude oil a similar set of experiment as described was performed with 1% Tween 80 added to all the flasks (10). The estimation of
机译:从古吉拉特邦阿朗海岸一个船厂的原油污染海水样品中回收的十种细菌分离株在存在原油的情况下显示出最佳生长。原油降解分离物被鉴定为不动杆菌属,马氏球菌属,微球菌属,平球菌属,甲基杆菌属,红球菌属和夜曲属。布什内尔·哈斯(Bushnell Haas)肉汤中的所有十个分离株均降解了1%的原油。通过属于Marinococcus属的分离物M2发现,原油的最高生物降解率为70%。其他分离株显示出55-30%的生物降解率。在大多数情况下,添加1%Tween 80可以减少生物降解。 70%的细菌分离物的生物表面活性剂生产和乳化甲苯得分为阳性,但是在分离物中,乳剂的稳定性变化很大。产生细菌的生物表面活性剂中没有一种是溶血的。关键词:生物降解生物表面活性剂乳液溶血性简介从数量上讲,原油是海洋环境中最重要的有机污染物之一,据估计,全世界每年约有1.7- 8.8×106吨的石油碳氢化合物会影响海洋水域和河口(1)。自从过去的三十年以来,已经出现了有关细菌可利用碳氢化合物作为碳和能源的生物降解性的报道(2)。当微生物在富含碳氢化合物的环境中生长时,它们会经历许多适应。一种这样的适应方法是生物表面活性剂的生产,这是烃降解细菌中经常遇到的特征,有时甚至是在烃上生长的先决条件(3)。生物表面活性剂的生产有助于碳氢化合物降解细菌更好地利用其疏水性底物,因为它带来的变化包括降低细菌周围环境的表面张力,降低细菌细胞壁与碳氢化合物分子之间的界面张力,膜修饰(例如提高疏水性)通过减少细胞壁中脂多糖的含量,通过将碳氢化合物包封到胶束等中来增强碳氢化合物的分散作用(4、5、6、7)。在上述变化中,表面和界面张力的降低是几乎所有类型的生物表面活性剂所表现出的普遍现象,而诸如膜改性和乳液形成的变化严格取决于例如表面活性剂的类型。上述变化的累积效应可能会导致碳氢化合物降解的增强。在此,我们提供了一份报告,介绍了从受油污染的海水中分离出降解原油的海洋细菌,筛选原油降解和生物表面活性剂的方法。 。方法的样品收集海水样品收集在古吉拉特邦阿朗海岸的一个船厂的消毒玻璃瓶中。原油降解细菌的分离和筛选通过将100 µL连续稀释的海水样品铺在矿物盐培养基(MM2)上,进行原油降解海洋细菌的分离。将原油的醚溶液(10%w / v)均匀地喷雾在琼脂平板的表面上。乙醚立即蒸发,薄薄的一层油留在整个表面上。原油是从古吉拉特邦艾哈迈达巴德附近Chandkheda的ONGC工厂获得的。将板在25℃温育20天。孵育后出现在MM2平板上的细菌分离物通过覆盖技术(8)进行了原油降解的筛选。原油生物降解通过修改Pirnik等人的技术进行原油生物降解实验。 (9)将密度为108 mL-1的接种细胞添加到BHM中,并添加1%的原油作为唯一碳源。为了研究吐温80对原油生物降解的影响,在向所有烧瓶中添加1%吐温80的同时进行了与上述类似的实验(10)。估计

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