Группа авторов

Biosurfactants for a Sustainable Future


Скачать книгу

of oil field soil being a repository for bacteria‐producing biosurfactants that help in the desorption of oil during microbial degradation, their isolation, and screening techniques. This could be of enormous scope for industrial application and bioremediation. In addition, this article discusses current developments in the research on molecular techniques such as metagenomics combined with a stable isotope probe (SIP) for the discovery of new microbial strains that produce biosurfactants.

Chemical structure of application of the metagenomic technique for environmental management of advanced biomedical applications.

      Techniques of metagenomics may also be used to classify genes/microbes from environmental samples that produce biomolecules. These multifunctional, fascinating biomolecules with diverse structural complexities can be used in a number of advanced environmental and bio‐science applications [15].

      Biosurfactants are key agents in the remediation of persistent heavy metals in soil. They have been found to be effective in the remediation of heavy metals contaminated soil by the formation of a surfactant‐associated complex which has already been established [3]. Metagenomics figure centrally in this context as well. For instance, metallothionein (MT) genes have been discovered from soil microbiomes using this approach. MT genes from novel metal‐tolerant bacterial strains that confer Cu/Cd resistance and biosorption have been used for the development of metal bioremediation tools [13]. Similarly, metagenomics can help isolate genes that specifically target the degradation of PAHs in contaminated soil. This is crucial in the context of producing biosurfactants since they play a significant role in the biodegradation of polyaromatic hydrocarbons (PAHs) from soil. Biosurfactants increase the mobility of PAHs by reducing surface and interface stresses [17] and reduce the half‐life of three‐ and five‐ring PAHs by accelerating the degradation process of contaminated soil PAHs [4]. In addition to PAH degradation, biosurfactants are used to clean oil sludge from storage tanks, enhance oil recovery from refinery sludge and reservoirs, and mobilize oil flow through pipelines [4, 5, 18].

      Metagenomics is further employed in a range of other diverse sectors. In the food sector, it can be used in the detection of potential microbes for biosurfactant production for use in food industries. While the use of biosurfactants has not been very common in the food industry, they are being used to stabilize the agglomeration of fat globules and to improve the quality of foods based on fat [3]. In the field of agriculture, they are mainly used to monitor plant pathogens. Early detection of pathogens may help prevent plant diseases and minimize the loss of economically important crop plants [14]. They can also be used to successfully track viral pathogens, which often pose difficulties in screening using other conventional methods.

      From this, it becomes evident that metagenomics has become an integral technique with multiple uses, from the detection of new molecules to advanced medical technology. Enzymes and other industrially important bioactive compounds, such as biosurfactants, have led to sustainable industrial growth through metagenomics. This technology also greatly contributes to the environmental monitoring of microbes and toxins, leading to the identification, treatment, and prevention of many diseases, and to the prevention of epidemics. Early identification with microbial metagenomics contributes to the reduction and elimination of health threats. Bioremediation and innovation of new drugs also help to improve the quality of life. Given the novelty of this technique, however, many other aspects of metagenomics are yet to be explored.

      Exploration of crude oil often results in accidental spillage and environmental contamination due to its various toxic components [22, 23]. Crude oil exploration fields are also home to oil‐degrading microbes that are capable of using spilled oil as their carbon source and can remove crude oil from contaminated sites [24]. Numerous oil‐degrading bacteria strains have been isolated from both cold [9] and hot [25] environments. Microbe‐enhanced oil recovery tests performed using biosurfactant‐producing microorganisms are briefly described in Chapter 5.

      In the last few years, attempts have been made to identify possible biosurfactant‐producing microorganisms [4]. Some of the key genera that make biosurfactants are Acinetobacter, Bacillus, Azotobacter, Candida [18], Enterobacter, Micrococcus, Oceanobacillus, Pseudomonas, Rhodococcus, Serratia and Stenotrophomonas [18, 26]. Rhodococcus sp. HL‐6 reported from petroleum‐contaminated soil produces glycolipid biosurfactants and has been successfully exploited for the remediation of crude oil contaminated sites [27]. Pseudomonas is one of the most widely described genera for the production of biosurfactants [28]. Bacillus subtilis and Pseudomonas aeruginosa have also been reported from oil‐contaminated soils and have been shown to be a potential candidate for the degradation of petroleum hydrocarbons [18, 28, 29]. Similarly, biosurfactants derived from the consortium of P. aeruginosa and Rhodococcus strains have been reported to degrade more than 90% of oil sludge [30]. P. aeruginosa RS29 isolated from crude oil‐contaminated sites has been reported to produce potent biosurfactants with enhanced foaming and emulsifying properties [28]. The thermophilic hydrocarbon‐degrading bacteria P. aeruginosa AP02‐1 are known to produce biosurfactants using hydrocarbon as the sole source of carbon [31]. Biosurfactant BSW10 derived from P. aeruginosa W10 has been successful in phenanthrene and fluoranthene biodegradation from oil‐contaminated sites [32].