Elsevier

Bioresource Technology

Volume 223, January 2017, Pages 277-286
Bioresource Technology

Review
Microbial degradation of petroleum hydrocarbons

https://doi.org/10.1016/j.biortech.2016.10.037Get rights and content

Highlights

Abstract

Petroleum hydrocarbon pollutants are recalcitrant compounds and are classified as priority pollutants. Cleaning up of these pollutants from environment is a real world problem. Bioremediation has become a major method employed in restoration of petroleum hydrocarbon polluted environments that makes use of natural microbial biodegradation activity. Petroleum hydrocarbons utilizing microorganisms are ubiquitously distributed in environment. They naturally biodegrade pollutants and thereby remove them from the environment. Removal of petroleum hydrocarbon pollutants from environment by applying oleophilic microorganisms (individual isolate/consortium of microorganisms) is ecofriendly and economic. Microbial biodegradation of petroleum hydrocarbon pollutants employs the enzyme catalytic activities of microorganisms to enhance the rate of pollutants degradation. This article provides an overview about bioremediation for petroleum hydrocarbon pollutants. It also includes explanation about hydrocarbon metabolism in microorganisms with a special focus on new insights obtained during past couple of years.

Introduction

Petroleum hydrocarbons are important energy resource and a raw material for various industries. Increasing demand for petroleum products in day to day life may cause their scarcity and increase their cost as suitable alternatives are still not found (Varjani et al., 2015, Varjani and Upasani, 2016b). Petroleum hydrocarbon pollutants are recalcitrant compounds and are classified as priority pollutants (ATSDR, 2011, Costa et al., 2012). Anthropogenic activities such as industrial and municipal runoffs; effluent release; offshore and onshore petroleum industry activities as well as accidental spills cause petroleum hydrocarbon pollution. This pollution affects the environment and pose direct or indirect health risk to all life forms on planet earth (Margesin and Schinner, 2001, Deppe et al., 2005, Souza et al., 2014, Sajna et al., 2015). Marine environment is considered as the ultimate and largest sink for petroleum hydrocarbon pollutants, therefore it is necessary to combat pollution problem (Ron and Rosenberg, 2014, Varjani and Srivastava, 2015). Remediation of hydrocarbon pollutants and enhanced oil recovery are two main burning issues of petroleum industry (Sajna et al., 2015, Varjani et al., 2015, Varjani and Upasani, 2016a, Varjani and Upasani, 2016c). To understand the scope and strategies of pollutant bioremediation it is essential to first understand properties of crude oil, environment of concern, fate of oil in that environment, mechanisms of crude petroleum biodegradation and factors that control its rate (Atlas, 1981, Boopathy, 2000, Varjani, 2014).

Mainly petroleum is constituted by saturates/paraffins, aromatics, resins and asphaltenes (Varjani, 2014). Crude oil is a mixture of variety of simple and complex hydrocarbons which are degraded by several indigenous microorganisms, each capable of breaking down a specific group of molecules (Zanaroli et al., 2010). Sugiura et al. (1997), and Ghazali et al. (2004), have reported that same compound in different crude oil samples was degraded to different extents by same organisms/consortium, the reason could be bioavailability of a particular compound in a crude oil sample and not it’s chemical structure.

Bioremediation of crude oil polluted sites is often limited due to poor biodiversity of indigenous microflora and/or scarcity of native specialized microbes with complementary substrate specificity required for degrading different hydrocarbons occurring at polluted site (Ron and Rosenberg, 2014). There are various reports available on metabolic versatility of mixed cultures that have demonstrated superiority of mixed cultures to pure cultures to utilize hydrocarbon pollutants in petroleum crude as sole carbon source (Cerqueira et al., 2011, Das and Chandran, 2011, Varjani et al., 2013). Bacterial and fungal co-culture(s) have shown improved degradation rates of diesel oil and many polyaromatic hydrocarbons (PAHs) when checked in laboratory conditions (Li et al., 2008, Wang et al., 2012, Varjani and Upasani, 2013). Hence catabolic cooperation between different microbial groups during biodegradation is very important (Atlas, 1981, Varjani et al., 2015).

The intent of present review is to expand bioremediation scope of petroleum hydrocarbon pollutants. It includes consideration of toxicity and fate of petroleum hydrocarbons in environment. It also discusses factors affecting biodegradation rate, microbial metabolism of petroleum hydrocarbon pollutants, pathways for hydrocarbon pollutants degradation and types of bioremediation technologies as well as processes.

Section snippets

Composition of crude petroleum oil

Petroleum is produced by thermal decay of buried organic material over millions of years. Crude oil (naturally occurring raw oil) once extracted from subsurface is transported to refineries where it undergoes distillation to produce various products (Speight, 2007, Varjani, 2014). Petroleum, in Latin means “rock oil”, which occurs as a dark, sticky, viscous liquid (Vieira et al., 2007). Petroleum hydrocarbons mainly consists of varying proportions carbon and hydrogen. However they also contain

Petroleum hydrocarbons toxicity

Hydrocarbon pollutants are one of the persistent organic pollutants. Due to their bio-magnification they cause extensive and/or permanent damage to ecosystems (Chandra et al., 2013). Widespread release of hydrocarbon pollutants through spillages and leakage from underground tanks, steamers, unplugging of oil wells, abandoned oil refinery sites cause contamination of surface soil, groundwater and ocean (Saeki et al., 2009, Janbandhu and Fulekar, 2011, Prince et al., 2013, Souza et al., 2014).

Fate of petroleum hydrocarbons in environment

It is critical to gain knowledge about the fate of hydrocarbons within environment in order to control and combat pollution (Walker, 2006, CCME, 2010). Petroleum crude is subjected to several weathering processes such as spreading, evaporation, dispersion, sinking, dissolution, emulsification, photo-oxidation, resurfacing, tar ball formation and biodegradation, which naturally degrades it’s hydrocarbon components (Al-Majed et al., 2012, Souza et al., 2014). Effect of photo-oxidation is limited because it

Physico-chemical vs. biological methods

Many conventional engineering based physico-chemical decontamination methods are expensive due to the cost of excavation and transportation of large quantities of contaminated materials for ex-situ treatment viz. soil washing, chemical inactivation (use of potassium permanganate and/or hydrogen peroxide as a chemical oxidant to mineralize non-aqueous contaminants such as petroleum) and incineration (Chaudhry et al., 2005, Farhadian et al., 2008, Varjani and Srivastava, 2015). Other

Biodegradation/bioremediation of petroleum hydrocarbons

Microbial bioremediation is widely used technique for treating petroleum hydrocarbon pollution in both terrestrial and aquatic ecosystems (Varjani and Upasani, 2012, Abbasian et al., 2015, Varjani and Srivastava, 2015). Numerous research studies concerning biodegradation of hydrocarbon pollutants has been done in last decade (Farhadian et al., 2008, Sajna et al., 2015, Varjani et al., 2015, Varjani and Upasani, 2016c). Many reviews have been published outlining general mechanisms and pathways

Petroleum hydrocarbons bioegradation: metabolic aspects

Biodegradation of a pollutant involves series of steps using different enzymes (Abbasian et al., 2015). Hydrocarbons can selectively be metabolized by individual strain of microorganism or consortium of microbial strains belonging to either same or different genera (Boopathy, 2000, Varjani et al., 2015, Varjani and Upasani, 2016c). However, consortium has been proved to be more potential than individual cultures for metabolizing/degrading complete assortments of hydrocarbons (Deziel et al., 1996,

Factors affecting biodegradation of petroleum hydrocarbon pollutants

Microorganisms are highly sensitive to growth environment and respond to changes in their surrounding environment (Boopathy, 2000). Biodegradation rates are influenced by many factors viz. (a) pollutant characteristics viz. availability, type and length of hydrocarbons, dispersion into aqueous phase and volatilization (Chaudhry et al., 2005, Rojo, 2009, Beskoski et al., 2011, Chandra et al., 2013), (b) microorganisms, cell metabolic pathways and several structural changes from inclusions to

Conclusion

Petroleum hydrocarbon pollutants are priority pollutants as they are resistant to degradation due to their low reactivity. These persistent organic pollutants (POPs) pose serious threat to the human and environmental health. Bioremediation is recognized as an efficient, economic and versatile alternative to physico-chemical treatment. Biodegradation of this pollutants can be performed using oleophilic microorganisms either as individual organism or consortium of microorganisms to control

Acknowledgements

I am grateful to managent of Puri Foundation to provide facilities necessary for performing literature review presented in this paper. I express my gratitude to academic and administrative staff of Indian Institute of Advanced Research for their kind support.

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