The Role of Mycobacteria in Biodegradation

Q4 Environmental Science
M. Keikha
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引用次数: 0

Abstract

Crude oiland petrochemical-induced contamination of the environment has gained considerable attention in recent decades. Today, leakage and spread of oil contamination due to inefficient extraction, transmission and crude oil refinery processes along with occurrence of different incidents in various sections of oil industry like oil production site, oil refineries and transmission lines are inevitable (1). Crude oil product may enter into the environmental resources and exert harmful effects such as health risks, contamination of natural resources and underground water. In addition to their effects on the environment, these compounds have harmful effects on human. Studies have shown that oil compounds can cause mutation and cancer, and negatively affect human neonates (1,2). Therefore, cleaning the oil-contaminated areas is one of the main environmental concerns. For this purpose, different physical, chemical, and biological methods have been proposed (1,3). Biodegradation is one of the most important solutions to clean these compounds from the environment. During this natural process, microorganisms break the organic chemicals into simpler forms. Chemical and mechanical methods, in addition to being costly, do not clean these compounds effectively and can transmit the contamination to other areas. While biodegradation is a cost-effective and efficient method in comparison with the two mentioned methods, it is now recognized as one of the important strategies in environmental protection (4,5). Presence of microorganisms in contaminated site is another advantage of this method. So far, more than 200 microorganisms with such capabilities have been identified among which Pseudomonas, Actinomyces (especially mycobacteria), Flavobacterium, Bacillus, Alcaligenes and Micrococcus can be mentioned (6). Non-tuberculous mycobacteria live in the environmental resources including soil, water, dust, milk, and animals. Today, this group of bacteria are known as one of the important biodegrading bacteria and can degrade pollutants. Based on the literature, various species of environmental mycobacteria have been reported with biodegradation properties (4,7). The most important molecular method used for the identification of mycobacterial species is gene sequence investigation of 16S rRNA in A (125-270), B (408-502) positions and rpoB gene in V (2581-3300) position and also the sequence of hsp65 in 624-664 and 683-725 positions (8). Among nontuberculous mycobacteria, the species with profound biodegradation properties are: M. fredriksbergense, M. austroafricanum, M. obuense, M. phocaicum, M. paragordonae, M. lentiflavum, M. ratisbonense and M. fortuitum (4,7,8). Presence of fatty acid-saturated cell wall and also presence and expression of biodegradation genes such as nidA, ABC transporter, alkB and so on have enabled the mycobacteria to biodegrade the pollutants (9,10). Among the methods used to evaluate the biodegradation, methods such as chromatography (i.e. HPLC), enrichment technique, spray plate technique and gibbs and turbidometric methods can be mentioned. Among them, enrichment method is one of the most accurate ones in which a salt-based varied medium of methylsulfonylmethane (MSM), which contains the minimum mineral and the studied pollutant, is used as the only source of carbon (9-13). Recently, by advancement in genetic sciences and achievements in getting information of genomics of organisms, researchers are now able to identify the biodegrading bacteria by means of whole genome sequencing (14). In general, previous studies have shown that mycobacteria are one of the bacterial species which possess biodegradation properties. Moreover, presence of fatty acid-saturated cell wall has enhanced the resistance of this bacterium against toxic and harsh environmental conditions; which helps this microorganism to survive in contaminated ecosystems. As non-tuberculous mycobacteria exist in various environments such as water and soil, these bacteria can be used for contamination removal from water and soil.
分枝杆菌在生物降解中的作用
近几十年来,原油和石化引起的环境污染引起了人们的极大关注。如今,由于低效的开采、输送和原油精炼工艺,石油污染的泄漏和扩散,以及石油工业各个部门(如石油生产现场、炼油厂和输电线)发生的不同事件,是不可避免的(1)。原油产品可能进入环境资源,并产生健康风险、污染自然资源和地下水等有害影响。这些化合物除了对环境有影响外,对人类也有有害影响。研究表明,油化合物可导致突变和癌症,并对人类新生儿产生负面影响(1,2)。因此,清洁受石油污染的区域是主要的环境问题之一。为此,已经提出了不同的物理、化学和生物方法(1,3)。生物降解是从环境中清除这些化合物的最重要的解决方案之一。在这个自然过程中,微生物将有机化学物质分解成更简单的形式。化学和机械方法不仅成本高昂,而且不能有效清洁这些化合物,并可能将污染传播到其他区域。虽然与上述两种方法相比,生物降解是一种成本效益高、效率高的方法,但它现在被认为是环境保护的重要策略之一(4,5)。这种方法的另一个优点是在受污染的场地中存在微生物。到目前为止,已经鉴定出200多种具有这种能力的微生物,其中可以提到假单胞菌、放线菌(尤其是分枝杆菌)、黄杆菌、芽孢杆菌、产碱菌和微球菌(6)。非结核分枝杆菌生活在土壤、水、灰尘、牛奶和动物等环境资源中。如今,这群细菌被认为是重要的生物降解细菌之一,可以降解污染物。根据文献,已经报道了具有生物降解特性的各种环境分枝杆菌(4,7)。用于鉴定分枝杆菌物种的最重要的分子方法是A(125-270)、B(408-502)位置的16S rRNA和V(2581-3300)位置的rpoB基因的基因序列研究,以及624-664和683-725位置的hsp65序列(8)。在非结核分枝杆菌中,具有深刻生物降解特性的物种有:M.fredriksbergense、M.austroafricanum、M.obuense、M.phocaicum、M.paragordonae、M.lentflavum、M.ratisbonese和M.fortitum(4,7,8)。脂肪酸饱和细胞壁的存在以及nidA、ABC转运蛋白、alkB等生物降解基因的存在和表达使分枝杆菌能够生物降解污染物(9,10)。在用于评估生物降解性的方法中,可以提到色谱法(即HPLC)、富集技术、喷雾板技术以及吉布斯和浊度法。其中,富集法是最准确的方法之一,其中甲基磺酰甲烷(MSM)的盐基可变介质是唯一的碳源,该介质含有最少的矿物和所研究的污染物(9-13)。最近,通过基因科学的进步和获得生物体基因组学信息的成就,研究人员现在能够通过全基因组测序来识别生物降解细菌(14)。一般来说,先前的研究表明分枝杆菌是具有生物降解特性的细菌物种之一。此外,脂肪酸饱和细胞壁的存在增强了这种细菌对有毒和恶劣环境条件的抵抗力;这有助于这种微生物在受污染的生态系统中生存。由于非结核分枝杆菌存在于水和土壤等各种环境中,这些细菌可用于去除水和土壤中的污染物。
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来源期刊
Avicenna Journal of Environmental Health Engineering
Avicenna Journal of Environmental Health Engineering Environmental Science-Health, Toxicology and Mutagenesis
CiteScore
1.00
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0.00%
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8
审稿时长
8 weeks
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